Final Endangerment Assessment, Tutu Wells Site, St. Thomas, Virgin Islands, Volume II of IV

Collection: Federal Reference
Sub-shelf: EPA SEMS (Superfund, Region 2)
Kind: Government Report
Island: St. Thomas
Date: 1995-03-24
Pages: 373
Text: Native Text

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m. / !*••• ' REMEDIAL PLAIiNiNO ACTiflTiES UNCONTROLLED HAZARDOUS SUBSTANCE DISPOSAL SITES WITHIN EPA REGION II (NY, NJ, PR, VI) TUT 006 7.. CDM Federed Programs Corporation *64941* 64941 FINAL ENDANGERMENT ASSESSMENT TUTU WELLS SITE ST. THOMAS, VIRGIN ISLANDS VOLUME H OF IV Prepared for U.S. ENVIRONMENTAL PROTECTION AGENCY Office of Waste Programs Enforcement Washington, DC 20460 EPA Work Assignment No. EPA Region Site No. Contract No. Document Control No. Prepared by Work Assignment Project Manager Telephone Number EPA Work Assignment Manager Telephone Number Date Prepared 073-2P1D n VID982272569 68-W9-0024 7720-073-RA-CFKJ COM Federal Programs Corporation Sally Odland (212) 393-9634 Caroline Kwan (212) 637-4275 March 24, 1995 TUT 006 2442 APPENDIX A 95 PERCENT UPPER CONFIDENCE LIMIT CALCULATIONS TUT OO6 2443 TILLETT GARDENS AND Air.-CEl;NTER-SURFACE SOIL PCB: Sample Location SS-5-AVS eTT-14s eTT-15s AROCLOR 1242 Concentration Q (mg/kg) NA 0.29 UU 120 J Log of Concentration (mg/kg) -1.2 4.8 Frequency: Average: Average log: UCL: Maximum: 1/2 60.15 1.77 3.50E+107 120.00 Sample Std. Dev. 84.65 Sample Std. Dev. 4.26 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. —=c H O Cr- M TILLETT GARDENS AND ART CENTER - SURFACE SOIL INORGANIC: Sample Location SS-5-AVS eTT-14s eTT-15s ANTIMONY Concentration Q (mg/kg) 5.05 BNJ NA NA Log of Concentration (mg/kg) 1.6 Frequency: Average: Average log: UCL: Maximum: 1/1 5.05 1.62 - 5.05 Sample Std. Dev. Sample Std. Dev. (log value) •H C T-.J^ £. CJi TILLETT GARDENS AND ART CEK, Jh - SURFACE SOIL INORGANIC: Sample Location SS-5-AVS eTT-Us eTT-15s ARSENIC Concentration Q (mg/kg) 10 NA NA Log of Concentration (mg/kg) 2.3 Frequency: Average: Average log: UCL: Maximum: 1/1 10.00 2.30 10.00 Sample Std. Dev. Sample Std. Dev. (log value) H w T1 S> TILLETT GARDENS AND ART CEN i bR - SURFACE SOIL INORGANIC: Sample Location SS-5-AVS eTT-14s eTT-15s BARIUM Concentration Q (mg/kg) 70.5 NA NA Log of Concentration (mg/kg) 4.3 Frequency: Average: Average log: UCL: Maximum: 1/1 70.50 4.26 - 70.50 Sample Std. Dev. Sample Std. Dev. (log value) _l TILLETT GARDENS AND ART CENIER - SURFACE SOIL INORGANIC: Sample Location SS-5-AVS eTT-14s eTT-15s HEXAVALENT CHROMIUM " Concentration Q (mg/kg) 3.6NJ NA NA Log of Concentration (mg/kg) 1.3 Frequency: Average: Average log: UCL: Maximum: 1/1 3.60 1.28 - 3.60 Sample Std. Dev. Sample Std. Dev. (log value) ** - One-seventh of the detected total chromium concentration was assumed to be hexavalent per IRIS (1994). cH W 4s £. CO TILLETT GARDENS AND ART CEN. ^-R - SURFACE SOIL INORGANIC: Sample Location SS-5-AVS eTT-14s eTT-15s MANGANESE Concentration Q (mg/kg) 869 NA NA Log of Concentration (mg/kg) 6.8 Frequency: Average: Average log: UCL: Maximum: 1/1 869.00 6.77 - 869.00 Sample Std. Dev. Sample Std. Dev. (log value) •*= •& •43 TILLETT GARDENS AND ART CE, -SURFACE SOIL INORGANIC: Sample Location SS-5-AVS eTT-14s eTT-15s VANADIUM Concentration Q (mg/kg) 95.9 NJ NA NA Log of Concentration (mg/kg) 4.6 Frequency: Average: Average log: UCL: Maximum: 1/1 95.90 4.56 95.90 Sample Std. Dev. Sample Std. Dev. (log value) H o FIRE DEPARTMENT/TEXACO GAS STATION/ ANTILLES AUTO PARTS/ RAMSAY MOTOR CO. - SURFACE SOIL SVOC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s BENZO(B)FLUORANTHENE Concentration Q Log of (mg/kg) Concentration 0.7 U NA NA NA NA 0.87 J (mg/kg) -0.4 -0.1 Frequency: Average: Average log: UCL: Maximum: 1/2 0.79 -0.25 1.26 0.87 Sample Std. Dev. 0.12 Sample Std. Dev. 0.15 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. en H- J.._uE: FIRE DEPARTMENT/TEXACO GAS STATIONS AN, .-JES AUTO PARTS/ RAMSAY MOTOR CO. - SURFACE SOIL SVOC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s BENZO(A)PYRENE Concentration Q (mg/kg) 0.27 J NA NA NA NA 0.77 J Log of Concentration (mg/kg) -1.3 -0.3 Frequency: Average: Average log: UCL: Maximum: 2/2 0.52 -0.79 838.86 0.77 Sample Std. Dev. 0.35 Sample Std. Dev. 0.74 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. FIRE DEPARTMENT/ TEXACO GAS STATION/ ANT ILLES AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s ANTIMONY Concentration Q (mg/kg) 5.9BJ NA NA NA NA NA Log of Concentration (mg/kg) 1.8 Frequency: Average: Average log: UCL: Maximum: 1/1 5.90 1.77 - 5.90 Sample Std. Dev. Sample Std. Dev. (log value) -i C 0" M c.n FIRE DEPARTMENT/ TEXACO GAS STATION/ AN, ...LES AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s 6R-02-02S BARIUM Concentration Q (mg/kg) 67.2 NA NA NA NA NA Log of Concentration (mg/kg) 4.2 Frequency: Average: Average log: UCL: Maximum: 1/1 67.20 Sample Std. Dev. 4.21 Sample Std. Dev. (log value) 67.20 r-j FIRE DEPARTMENT/ TEXACO GAS STATION/ AN • ,^£S AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s BERYLLIUM Concentration Q (mg/kg) 0.26 B NA NA NA NA NA Log of Concentration (mg/kg) -1.3 Frequency: Average: Average log: UCL: Maximum: 1/1 0.26 -1.35 0.26 Sample Std. Dev. Sample Std. Dev. (log value) —•• O 0- FIRE DEPARTMENT/ TEXACO GAS STATION/ AN i ,^hS AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s HEXAVALENT CHROMIUM Concentration Q (mg/kg) 4.53 NA NA NA NA NA ** Log of Concentration (nig/kg) 1.5 Frequency: Average: Average log: UCL: Maximum: 1/1 4.53 1.51 4.53 Sample Std. Dev. Sample Std. Dev. (log value) ** - One-seventh of the detected total chromium concentration was assumed to be hexavalent per IRIS (1994). cH tfi FIRE DEPARTMENT/ TEXACO GAS STATION/ AN, .alES AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s MANGANESE Concentration Q (mg/kg) 834 NA NA NA NA NA Log of Concentration (mg/kg) 6.7 Frequency: Average: Average log: UCL: Maximum: 1/1 834.00 6.73 - 834.00 Sample Std. Dev. Sample Std. Dev. (log value) c-i FIRE DEPARTMENT/ TEXACO GAS STATION/ AN i ,uCES AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s NICKEL Concentration Q (mg/kg) 17.5 NA NA NA NA NA Log of Concentration (mg/kg) 2.9 Frequency: Average: Average log: UCL: Maximum: 1/1 1 7.50 Sample Std. Dev. 2.86 Sample Std. Dev. (log value) 17.50 Oa- _ CO FIRE DEPARTMENT/ TEXACO GAS STATION/ AN i .utES AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s SILVER Concentration Q (mg/kg) 2.2 J NA NA NA NA NA Log of Concentration (mg/kg) 0.8 Frequency: Average: Average log: UCL: Maximum: 1/1 2.20 Sample Std. Dev. 0.79 Sample Std. Dev. (log value) 2.20 H (Jl -0 FIRE DEPARTMENT/ TEXACO GAS STATION/ ANT tutES AUTO PARTS/ RAMSAY MOTOR CO.- SURFACE SOIL INORGANIC: Sample Location B-2 eC-09s eC-10s eR-07s eR-08s eR-02-02s VANADIUM Concentration Q (mg/kg) 119 NA NA NA NA NA Log of Concentration (mg/kg) 4.8 Frequency: Average: Average log: UCL: Maximum: 1/1 119.00 Sample Std. Dev. 4.78 Sample Std. Dev. (log value) 119.00 —iin •H oo cr- CURRICULUM CENTER BUinu^JNG- PRESENT -SURFACESOIL SVOC: Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-01s eL-02-02s eL-02-03s MWS-16-AVD 2-METHYLPHENOL Concentration Q (mg/kg) R 5.5 UJ 0.185 U 0.195 U 0.185U 320 1.95U 0.425 U 0.175 U Log of Concentration (mg/kg) 1.7 -1.7 -1.6 -1.7 5.8 0.7 -0.9 -1.7 Frequency: Average: Average log: UCL: Maximum: 1/8 41.08 0.07 315633 320.00 Sample Std. Dev. 112.72 Sample Std. Dev. 2.64 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. 0- K3 *= 0" H- CURRICULUM CENTER BUILDING - PRESENT - SURFACE SOIL SVOC: Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-01s eL-02-02s eL-02-038 MWS-16-AVD 4-METHYLPHENOL Concentration Q (mg/kg) R 5.5 UJ 0.185 U 0.195 U 0.185 U 1300 J 1.95 U 0.425 U 0.175 U Log of Concentration (mg/kg) 1.7 -1.7 -1.6 -1.7 7.2 0.7 -0.9 -1.7 Frequency: Average: Average log: UCL: Maximum: 1/8 163.58 0.24 1.56E+07 1300.00 Sample Std. Dev. 459.19 Sample Std. Dev. 3.08 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. ~i W CURRICULUM CENTER BUiuDING - PRESENT - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-013 eL-02-028 eL-02-03s MWS-16-AVD ANTIMONY Concentration Q (mg/kg) 4.63 BNJ 4.08 BNJ 7.3 BNJ 6.4 BNJ 6. 8 BNJ NA NA NA 2.55 UJ Log of Concentration (mg/kg) 1.5 1.4 2.0 1.9 1.9 0.9 Frequency: Average: Average log: UCL: Maximum: 5/6 5.29 Sample Std. Dev. 1.84 1.61 Sample Std. Dev. 0.40 8.67 * (log value) 7.30 * - 95% UCL exceeds the maximum concentration detected in the samples. H C o CURRICULUM CENTER BUILDING - PRESENT - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-01s eL-02-023 eL-02-038 MWS-16-AVD ARSENIC Concentration Q (mg/kg) 2.3 B 1.46BWJ 0.23 U 1.3B 11.6 NA NA NA 2.1 Log of Concentration (mg/kg) 0.8 0.4 -1.5 0.3 2.5 0.7 Frequency: Average: Average log: UCL: Maximum: 5/6 3.17 Sample Std. Dev. 4 . 20 0.53 Sample Std. Dev. 1.26 7 1 * (log value) 11.60 * - 95% UCL exceeds the maximum concentration detected in the samples. C —r •£, Cr- •*> ING-I CURRICULUM CENTER BUuJlNG - PRESENT - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-013 aL-02-02s eL-02-03s MWS-16-AVD BERYLLIUM Concentration Q (mg/kg) 0.19 B 0.09 U 0.115U 0.115 U 0.11 U NA NA NA 0.27 B Log of Concentration (mg/kg) -1.7 -2.4 -2.2 -2.2 -2.2 -1.3 Frequency: Average: Average log: UCL: Maximum: 2/6 0.15 -1.99 0.24 0.27 Sample Std. Dev. 0.07 Sample Std. Dev. 0.41 (log value) 0- '£> CURRICULUM CENTER Bb,-/iNG- PRESENT -SURFACESOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-01s eL-02-02s eL-02-03s MWS-16-AVD MANGANESE Concentration Q (mg/kg) 863.5 676.5 757 809 599 NA NA NA 872.5 Log of Concentration (mg/kg) 6.8 6.5 6.6 6.7 6.4 6.8 Frequency: Average: Average log: UCL: Maximum: 6/6 762.92 6.63 874 872.50 Sample Std. Dev. 108.28 Sample Std. Dev. 0.15 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. K5 4=- CURRICULUM CENTER BUiLUlNG - PRESENT - SURFACE SOIL INORGANIC Sample Location SS-3-AVS SS-4-AVS B-14 B-15 B-16 eL-02-01s eL-02-02s eL-02-03s MWS-16-AVD VANADIUM Concentration Q (mg/kg) 95.15 NJ 96.5 NJ 95.8 NJ 98.8NJ 79.7NJ NA NA NA 114.5 Log of Concentration (mg/kg) 4.6 4.6 4.6 4.6 4.4 4.7 Frequency: Average: Average log: UCL: Maximum: 6/6 96.74 4.57 107 114.50 Sample Std. Dev. 11.08 Sample Std. Oev. 0.12 (log value) CURRICULUM CENTER BUiLUiNG - FUTURE - SURFACE SOIL SVOC: Sample Location SS-3-AVS SS-4-AVS 0L-02-01S eL-02-02s eL-02-038 MWS-16-AVD 2-METHYLPHENOL Concentration Q (mg/kg) R 5.5UJ 320 1.95U 0.425 U 0.175 U Log of Concentration (mg/kg) 1.7 5.8 0.7 -0.9 -1.7 Frequency: Average: Average log: UCL: Maximum: 1/5 65.61 1.11 1.65E+11 320.00 Sample Std. Dev. 142.22 Sample Std. Dev. 2.93 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. oo 0- 0-- 03 CURRICULUM CENTER BUYING - FUTURE - SURFACE SOIL SVOC: Sample Location SS-3-AVS SS-4-AVS eL-02-Ols eL-02-02s eL-02-03s MWS-16-AVD 4-METHYLPHENOL Concentration Q (mg/kg) R 5.5 UJ 1300 J 1.95U 0.425 U 0.175 U Log of Concentration (mg/kg) 1.7 7.2 0.7 -0.9 -1.7 Frequency: Average: Average log: UCL: Maximum: 1/5 261.61 1.39 4.05E-f15 1300.00 Sample Std. Dev. 580.48 Sample Std. Dev. 3.50 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. O 5- o- CURRICULUM CENTER BUiu^rNG - FUTURE - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS el-02-01s eL-02-023 eL-02-03s MWS-16-AVD ANTIMONY Concentration Q (mg/kg) 4.63 BNJ 4.08 BNJ NA NA NA 2.55 UJ Log of Concentration (mg/kg) 1.5 1.4 0.9 Frequency: Average: Average log: UCL: Maximum: 2/3 3.75 Sample Std. Dev. 1.29 Sample Std. Dev. 9.52* (log value) 4.63 1.08 0.31 * - 95% UCL exceeds the maximum concentration detected in the samples. H r~ O O Xi O .^JING-I CURRICULUM CENTER BU^ JING - FUTURE - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS eL-02-Ols eL-02-02s eL-02-03s MWS-16-AVD ARSENIC Concentration Q (mg/kg) 2.3 B 1 .46 BWJ NA NA NA 2.1 Log of Concentration (mg/kg) 0.8 0.4 0.7 Frequency: Average: Average log: UCL: Maximum: 3/3 1.95 Sample Std. Dev. 0.65 Sample Std. Dev. 3.70 * (log value) 2.30 0.44 0.24 * - 95% UCL exceeds the maximum concentration detected in the samples. c CURRICULUM CENTER BUILDING - RJTURE - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS eL-02-01s eL-02-02s eL-02-03s MWS-16-AVD BERYLLIUM Concentration Q (mg/kg) 0.19 B 0.09U NA NA NA 0.27 B Log of Concentration (mg/kg) -1.7 -2.4 -1.3 Frequency: Average: Average log: UCL: Maximum: 2/3 0. 1 8 Sample Std. Dev. -1.79 Sample Std. Dev. 3.33 * (log value) 0.27 0.09 0.56 * - 95% UCL exceeds the maximum concentration detected in the samples. CURRICULUM CENTER Be. -FUTURE -SURFACESOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS el_-02-01s eL-02-02s eL-02-03s MWS-16-AVD MANGANESE Concentration Q (mg/kg) 863.5 676.5 NA NA NA 872.5 Log of Concentration (mg/kg) 6.8 6.5 6.8 Frequency: Average: Average log: UCL: Maximum: 3/3 804.17 6.68 1097.23 872.50 Sample Std. Dev. 110.65 Sample Std. Dev. 0.14 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. —! •'•• "f •k Si C-4 CURRICULUM CENTER Bb.^rflG - FUTURE - SURFACE SOIL INORGANIC: Sample Location SS-3-AVS SS-4-AVS eL-02-Ols eL-02-02s eL-02-03s MWS-16-AVD VANADIUM Concentration Q (mg/kg) 95.15 NJ 96.5 NJ NA NA NA 114.5 Log of Concentration (mg/kg) 4.6 4.6 4.7 Frequency: Average: Average log: UCL: Maximum: 3/3 102.05 4.62 124.84 114.50 Sample Std. Dev. 10.80 Sample Std. Dev. 0.10 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. —*c o OHENRY DRY CLEANERt.... ,6 LIQUOR BARN - SURFACE SOIL VOC: Sample Location SS-6-AVS B-13A e-01 eO-02-01 eO-02-02 eO-02-03 TETRACHLOROETUENE Concentration Q (mg/kg) 0.0059 U 0.015 440 170 180 D 0.058 J Log of Concentration (mg/kg) -5.1 -4.2 6.1 5.1 5.2 -2.8 Frequency: 5/6 Average: 131.68 Average log: 0.71 UCL 4.83E+26 Maximum: 440.00 Sample Std. Dev. 173.70 Sample Std. Dev. 5.28 (bg value) * - 95% UCL exceeds the maximum concentration detected in the samples. c _! Cfl 0-HENRY DRY CLEANERS MIND LIQUOR BARN - SURFACE SOIL INORGANIC: Sample Location SS-6-AVS B-13A e-01 eO-02-01 eO-02-02 eO-02-03 ANTIMONY Concentration Q (mg/kg) 6.35 BNJ 2.15 UNJ NA NA NA NA Log of Concentration (mg/kg) 1.8 0.8 Frequency: 1/2 Average: 4.25 Average log: 1.31 UCL: 8820.26 Maximum: 6.35 Sample Std. Dev. 2.97 Sample Std. Dev. 0.77 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. 0" OHENRY DRYCLEANERb™,.J LIQUOR BARN - SURFACE SOIL INORGANIC: Sample Location SS-6-AVS B-13A e-01 eO-02-01 eO-02-02 eO-02-03 ARSENIC Concentration Q (mg/kg) 18.65 J 13.7 NA NA NA NA Log of Concentration (mg/kg) 2.9 2.6 Frequency: Average: Average log: UCL: Maximum: 2/2 16.18 Sample Std. Dev. 2.77 Sample Std. Dev. 33.57 * (tog value) 18.65 3.50 0.22 * - 95% UCL exceeds the maximum concentration detected in the samples. cH ©•HENRY DRY CLEANERv. . to LIQUOR BARN - SURFACE SOIL INORGANIC: Sample Location SS-6-AVS B-13A e-01 eO-02-01 eO-02-02 eO-02-03 MANGANESE Concentration Q (mg/kg) 669. 5 J 870 NA NA NA NA Log of Concentration (mg/kg) 6.5 6.8 Frequency: 2/2 Average: 769.75 Average log: 6.64 UCL: 1428.34 Maximum: 870.00 Sample Std. Dev. 141.77 Sample Std. Dev. 0.19 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. --i ) OHENRY DRY CLEANERS *ND LIQUOR BARN - SURFACE SOIL INORGANIC: Sample Location SS-6-AVS B-13A e-01 eO-02-01 eO-02-02 eO-02-03 VANADIUM Concentration Q (mg/kg) 72.65 NJ 83.1 NA NA NA NA Log of Concentration (mg/kg) 4.3 4.4 Frequency: Average: Average log: UCL: Maximum: 2/2 77.88 Sample Std. Dev. 4.35 Sample Std. Dev. 101.31 * (log value) 83.10 7.39 0.10 * - 95% UCL exceeds the maximum concentration detected in the samples. '"i TILLETT GARDENSAND AH , CENTER - SUBSURFACE SOIL SVOC: Sample Location B-8-AVD MWS-5-AVS BENZO(A)PYRENE Concentration Q { mg/kg) 0.1875 J 0.1725 UU Log of Concentration (mg/kg) -1.7 -1.8 Frequency: Average: Average log: UCL: Maximum: 1/2 0.18 -1.72 0.20* 0.19 Sample Std. Dev. Sample Std. Dev. (log value) 0.01 0.06 * - 95% UCL exceeds the maximum concentration detected in the samples. TILLETT GARDENS AND ART CENTER - SUBSURFACE SOIL INORGANIC: Sample Location B-8-AVD MWS-5-AVS ANTIMONY Concentration Q (mg/kg) 3.65 BNJ 5.10BNJ Log of Concentration (mg/kg) 1.3 1.6 Frequency: Average: Average log: UCL: Maximum: 2/2 4.38 Sample Std. Dev. 1.46 Sample Std. Dev. 10.65* (tog value) 5.10 1.03 0.24 *. - 95% UCL exceeds the maximum concentration detected in the samples. c hJ Js 03 H- TILLETT GARDENS AND AM i CENTER - SUBSURFACE SOIL INORGANIC: Sample Location B-8-AVD MWS-5-AVS ARSENIC Concentration Q (mg/kg) 49.15 J 0.77 B Log of Concentration (mg/kg) 3.9 -0.3 Frequency: Average: Average log: UCL: Maximum: 2/2 24.96 1.82 5.37E+52 49.15 Sample Std. Dev. 34.21 Sample Std. Dev. 2.94 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. H C —: CD to TILLETT GARDENS AND An • CENTER - SUBSURFACE SOIL INORGANIC: Sample Location B-8-AVD MWS-5-AVS BERYLLIUM Concentration Q (mg/kg) 0.36 B 0.46 B Log of Concentration (mg/kg) -1.0 -0.8 Frequency: Average: Average log: UCL: Maximum: - 2/2 0.41 -0.90 0.73* 0.46 Sample Std. Dev. Sample Std. Dev. (log value) 0.07 0.17 * - 95% UCL exceeds the maximum concentration detected in the samples. c CD TILLETT GARDENS AND ART CENTER - SUBSURFACE SOIL INORGANIC: Sample Location B-8-AVD MWS-5-AVS MANGANESE Concentration Q (mg/kg) 745.5 763 Log of Concentration (mg/kg) 6.6 6.6 Frequency: Average: Average log: UCL: Maximum: 2/2 754.25 6.63 770.98 763.00 Sample Std. Dev. 12.37 Sample Std. Dev. 0.02 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. r-J 4* CO TILLETT GARDENS AND H. ,, CENTER - SUBSURFACE SOIL INORGANIC: Sample Location B-8-AVD MWS-5-AVS VANADIUM Concentration Q (mg/kg) 157.3 108 Log of Concentration (mg/kg) 5.1 4.7 Frequency: Average: Average log: UCL: Maximum: 2/2 132.65 4.87 402.38 157.30 Sample Std. Dev. 34.86 Sample Std. Dev. 0.27 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. o CO FIRE DEPARTMENT/ TEXACO GAS STATION/ AN i itLES AUTO PARTS/ RAMSAY MOTOR CO. - SUBSURFACE SOIL INORGANIC: Sample Location B-7 MWS-3 B-4 MWS-4 MWS-4D B-3 B-5 eT-028-AVD MWS-15 MWS-17 ARSEMC Concentration Q (mg/kg) 1.0B R 0.54 BWJ 1.8 BJ 0.23U 1.2B 0.23 U NA 0.82 B NA Log of Concentration (mg/kg) 0.0 -0.6 0.6 -1.5 0.2 -1.5 -0.2 Frequency: Average: Average log: UCL: Maximum: 5/7 0.83 -0.43 2.52 1.80 Sample Std. Dev. 0.56 Sample Std. Dev. 0.80 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. c o Kl •£• CO 0- FIRE DEPARTMENT/ TEXACO GAS STATION/ Ai,. AES AUTO PARTS/ RAMSAY MOTOR CO. - SUBSURFACE SOIL INORGANIC: Sample Location B-7 MWS-3 B-4 MWS-4 MWS-4D B-3 B-5 eT-02s-AVD MWS-15 MWS-17 BARIUM Concentration Q (mg/kg) 36.9 B 59.8 J 42.9 BJ 55 J 59.4 J 184 38.4 B NA 81.1 NA Log of Concentration (mg/kg) 3.6 4.1 3.8 4.0 4.1 5.2 3.6 4.4 Frequency: Average: Average log: UCL: Maximum: 8/8 69.69 4.10 112.40 184.00 Sample Std. Dev. 48.39 Sample Std. Dev. 0.52 (log value) c CO x' FIRE DEPARTMENT/ TEXACO GAS STATION/ AN, ...ilES AUTO PARTS/ RAMSAY MOTOR CO. - SUBSURFACE SOIL -i 0- INORGANIC: Sample Location B-7 MWS-3 B-4 MWS-4 MWS-4D B-3 B-5 eT-02s-AVD MWS-15 MWS-17 BERYLUUM Concentration Q (mg/kg) 0.105 U 0.115 U 0.27BJ 0.12 U 0.115U 0.42 B 0.115U NA 0.34 NA Log of Concentration (mg/kg) -2.3 -2.2 -1.3 -2.1 -2.2 -0.9 -2.2 -1.1 Frequency: Average: Average log: UCL: Maximum: 2/8 0.20 -1.76 0.36 0.42 Sample Std. Dev. 0.13 Sample Std. Dev. 0.58 (log value) CD 03 FIRE DEPARTMENT/ TEXACO GAS STATION/ ANTILLES AUTO PARTS/ RAMSAY MOTOR CO. - SUBSURFACE SOIL INORGANIC: Sample Location B-7 MWS-3 B-4 MWS-4 MWS-4D B-3 B-5 eT-02s-AVD MWS-15 MWS-17 CADMIUM Concentration Q (mg/kg) 0.31 U 0.34 U 0.35 U 0.73 BJ 0.345 U 0.35 U 0.345 U NA 1.1 B NA Log of Concentration (mg/kg) -1.2 -1.1 -1.0 -0.3 -1.1 -1.0 -1.1 0.1 Frequency: Average: Average log: UCL: Maximum: 2/8 0.48 -0.84 0.73 1.10 Sample Std. Dev. 0.28 Sample Std. Dev. 0.46 (log value) CO ••& FIRE DEPARTMENT/ TEXACO GAS STATION/ AN. _ES AUTO PARTS/ RAMSAY MOTOR CO. - SUBSURFACE SOIL INORGANIC: Sample Location B-7 MWS-3 B-4 MWS-4 MWS-4D B-3 B-5 eT-02s-AVD MWS-15 MWS-17 HEXAVALENT CHROMIUM Concentration Q (mg/kg) 4.1 4.5 J 4.5 J 5.4EJ 3.9 J 5.1 4.8 NJ NA 4.74 J NA ** Log of Concentration (mg/kg) 1.4 1.5 1.5 1.7 1.4 1.6 1.6 1.6 Frequency: Average: Average log: UCL: Maximum: 8/8 4.63 1.53 5.00 5.40 Sample Std. Dev. 0.49 Sample Std. Dev. 0.11 (log value) H C .*> " - One-seventh of the detected total chromium concentration was assumed to be hexavalent per IRIS (1994). w* ••0 FIRE DEPARTMENT/ TEXACO GAS STATION/ AN i .uIES AUTO PARTS/ RAMSAY MOTOR CO. - SUBSURFACE SOIL INORGANIC: Sample Location B-7 MWS-3 B-4 MWS-4 MWS-4D B-3 B-5 eT-02s-AVD MWS-15 MWS-17 MANGANESE Concentration Q (mg/kg) 828 725 J 941 J 947 EJ 717 J 506 861 NA 622 NA Log of Concentration (mg/kg) 6.7 6.6 6.8 6.9 6.6 6.2 6.8 6.4 Frequency: Average: Average log: UCL: Maximum: 8/8 768.38 6.62 907.17 947.00 Sample Std. Dev. 155.21 Sample Std. Dev. 0.22 (log value) c H- CURRICULUM CENTER Bb,_. -SUBSURFACE SOIL INORGANIC: Sample Locatbn B-14-AVD B-15 B-16 B-1-AVS B-6-AVS MWS-1 MWS-1D MWS-1 3 MWS-13D MWS-1 4 ARSENIC Concentration Q (mg/kg) 0.23U 1.3B 11.6 0.81 B 0.51 B 0.45 BJ 0.23 LW 0.71 B 1.7 BJ 0.67 BJ Log of Concentration (mg/kg) -1.5 0.3 2.5 -0.2 -0.7 -0.8 -1.5 -0.3 0.5 -0.4 Frequency: Average: Average log: UCL: Maximum: 8/10 1.82 -0.21 5.54 11.60 Sample Std. Dev. 3.47 Sample Std. Dev. 1.14 (tog value) —ic o W & -0w CURRICULUM CENTER Bv. M3-SUBSURFACESOIL INORGANIC: Sample Location B-14-AVD B-15 B-16 B-1-AVS B-6-AVS MWS-1 MWS-1D MWS-1 3 MWS-1 3D MWS-1 4 BERYLLIUM Concentration Q (mg/kg) 0.115U 0.115U 0.11 U 0.21 U 0.205 U 0.115U 0.23 BJ 0.22 B 0.105 U 0.11 U Log of Concentration (mg/kg) -2.2 -2.2 -2.2 -1.6 -1.6 -2.2 -1.5 -1.5 -2.3 -2.2 Frequency: Average: Average log: UCL: Maximum: 2/10 0.15 -1.93 0.19 0.23 Sample Std. Dev. 0.05 Sample Std. Dev. 0.34 (log value) H C H Ki •£ •>0w ) CURRICULUM CENTER BUuJING - SUBSURFACE SOIL INORGANIC: Sample Location B-14-AVD B-15 B-16 B-1-AVS B-6-AVS MWS-1 MWS-1D MWS-1 3 MWS-13D MWS-1 4 CADMIUM Concentration Q (mg/kg) 0.35 U 0.35 U 0.99 B 2.77 2.87 0.34 U 0.34 U 0.43 U 0.315 U 0.335 U Log of Concentration (mg/kg) -1.0 -1.0 0.0 1.0 1.1 -1.1 -1.1 -0.8 -1.2 -1.1 Frequency: Average: Average log: UCL: Maximum: 3/10 0.91 -0.53 2.07 2.87 Sample Std. Dev. 1.03 Sample Std. Dev. 0.89 (log value) ••G CURRICULUM CENTER Be, ^iNG-SUBSURFACESOIL INORGANIC: Sample Location B-14-AVD B-15 B-16 B-1-AVS B-6-AVS MWS-1 MWS-1D MWS-1 3 MWS-13D MWS-1 4 MANGANESE Concentration Q (mg/kg) 698.5 609 599 803 972.5 734 J 833 J 705 820 EJ 883 EJ Log of Concentration (mg/kg) 6.5 6.7 6.4 6.7 6.9 6.6 6.7 6.6 6.7 6.8 Frequency: Average: Average log: UCL: Maximum: 10/10 785.70 6.66 855.10 972.50 Sample Std. Dev. 105.55 Sample Std. Dev. 0.14 (log value) o :": 0- ••£ r n CURRICULUM CENTER BUit^iNG - SUBSURFACE SOIL INORGANIC: Sample Location B-14-AVD B-15 B-16 B-1-AVS B-6-AVS MWS-1 MWS-1D MWS-1 3 MWS-1 3D MWS-1 4 MERCURY Concentration Q (mg/kg) 0.03 U 0.03 U 0.57 0.065 U 0.065 U 0.03 U 0.03 U 0.025 U 0.025 U 0.03 U Log of Concentration (mg/kg) -3.5 -3.5 -0.6 -2.7 -2.7 -3.5 -3.5 -3.7 -3.7 -3.5 Frequency: Average: Average log: UCL: Maximum: 1/10 0.09 -3.09 0.19 0.57 Sample Std. Dev. 0.17 Sample Std. Dev. 0.96 (log value) -ic. -0 0- ESSO GAS STATION AND Sr _ .SH AND DASH CAR WASH - SUBSURFACE SOIL INORGANIC: Sample Location B-9 MWS-8-AVS MWS-9-AVS MWS-10 MWS-10D MWS-18 MWS-25 ARSENIC Concentration Q (mg/kg) 1.6BJ 0.225 UJ 0.47BJ 1.2U 1.1 U 1.3B 0.94 B Log of Concentration (mg/kg) 0.5 -1.5 -0.8 0.2 0.1 0.3 -0.1 Frequency: Average: Average log: UCL Maximum: 4/7 0.98 -0.19 2.41 * 1.60 Sample Std. Dev. Sample Std. Dev. (log value) 0.48 0.69 * - 95% UCL exceeds the maximum concentration detected in the samples. 0 !> •-0xi ESSO GAS STATION AND ShL^SHAND DASH CAR WASH - SUBSURFACE SOIL INORGANIC: Sample Location B-9 MWS-8-AVS MWS-9-AVS MWS-10 MWS-10D MWS-18 MWS-25 BARIUM Concentration Q (mg/kg) 33.8 BJ 22.75 BJ 21.85 BJ 120 199 37.9 B 114 Log of Concentration (mg/kg) 3.5 3.1 3.1 4.8 5.3 3.6 4.7 Frequency: Average: Average log: UCL Maximum: 111 78.47 4.03 291.13* 199.00 Sample Std. Dev. Sample Std. Dev. (log value) 67.66 0.89 * - 95% UCL exceeds the maximum concentration detected in the samples. H C "•-. O o-- •-G 03 ESSO GAS STATION AND SHtASH AND DASH CAR WASH - SUBSURFACE SOIL INORGANIC: Sample Location B-9 MWS-8-AVS MWS-9-AVS MWS-10 MWS-10D MWS-18 MWS-25 BERYLLIUM Concentration Q (mg/kg) 0.23 BJ 0.16 B 0.09 U 0.27 B 0.28 B 0.28 B 0.35 B Log of Concentration (mg/kg) -1.5 -1.8 -2.4 -1.3 -1.3 -1.3 -1.0 Frequency: Average: Average log: UCL Maximum: 6/7 0.24 Sample Std. Dev. -1 .52 Sample Std. Dev. 0.38 * (log value) 0.35 0.09 0.46 * - 95% UCL exceeds the maximum concentration detected in the samples. H M •£. •a •-o ESSO GAS STATION AND S, JH AND DASH CAR WASH - SUBSURFACE SOIL INORGANIC: Sample Location B-9 MWS-8-AVS MWS-9-AVS MWS-10 MWS-10D MWS-18 MWS-25 CADMIUM Concentration Q (mg/kg) 0.32 U 0.245 U 0.24 U 0.355 U 0.325 U 0.455 U 0.95 B Log of Concentration {mg/kg) -1.1 -1.4 -1.4 -1.0 -1.1 -0.8 -0.1 Frequency: Average: Average log: UCL Maximum: 1/7 0.41 Sample Std. Dev. -1 .00 Sample Std. Dev. 0.65 (log value) 0.95 0.25 0.47 O i'*"*: S- ESSO GAS STATION AND SPLASH AND DASH CAR WASH - SUBSURFACE SOIL INORGANIC: Sample Location B-9 MWS-8-AVS MWS-9-AVS MWS-10 MWS-10D MWS-18 MWS-25 HEXAVALENT CHROMIUM Concentration Q (mg/kg) 5.0 J 2.6 J 2.9 J 0.81 0.64 3.93 J 1.93 J Log of Concentration (mg/kg) 1.6 1.0 1.1 -0.2 -0.4 1.4 0.7 Frequency: Average: Average log: UCL Maximum: 7/7 2.54 Sample Std. Dev. 0.71 Sample Std. Dev. 7.50 * (log value) 5.00 1.59 0.78 * - 95% UCL exceeds the maximum concentration detected in the samples. ** - One-seventh of the detected total chromium concentration was assumed to be hexavalent per IRIS (1994). O Xj o ESSO GAS STATION AND ShLrtSH AND DASH CAR WASH - SUBSURFACE SOIL INORGANIC: Sample Location B-9 MWS-8-AVS MWS-9-AVS MWS-10 MWS-10D MWS-18 MWS-25 MANGANESE Concentration Q (mg/kg) 760 J 773. 5 J 775.5 J 480 435 472 1250 Log of Concentration (mg/kg) 6.6 6.7 6.7 6.2 6.1 6.2 7.1 Frequency: Average: Average log: UCL Maximum: 7/7 706.57 Sample Std. Dev. 6.50 Sample Std. Dev. 1014.26 (log value) 1250.00 285.05 0.38 oo OWENRY DRY CLEANER:!*,,„«> LIQUOR BARN - SUBSURFACE SOIL INORGANIC: Sample Location B-10 B-11 B-12-AVS B-13 ARSENIC Concentration Q (mg/kg) 1.1 U 5.0 18.3 185 J Log of Concentration (mg/kg) 0.1 1.6 2.9 5.2 Frequency: Average: Average log: UCL: Maximum: 3/4 52.35 2.46 5.69E+11 185.00 Sample Std. Dev. 88.74 Sample Std. Dev. 2.17 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. QHENRY DRY CLEANERS AND LIQUOR BARN - SUBSURFACE SOIL INORGANIC: Sample Location B-10 B-11 B-12-AVS B-13 BARIUM Concentration Q (mg/kg) 498 124 172 29 B Log of Concentration (mg/kg) 6.2 4.8 5.1 3.4 Frequency: 4/4 Average: 205.75 Average log: 4.89 UCL: 2.42E+05 Maximum: 498.00 Sample Std. Dev. 203.69 Sample Std. Dev. 1.17 (tog value) * - 95% UCL exceeds the maximum concentration detected in the samples. c —4 o O O O OHENRY DRY CLEANERS *ND LIQUOR BARN - SUBSURFACE SOIL INORGANIC: Sample Location B-10 B-11 B-12-AVS B-13 MANGANESE Concentration Q (mg/kg) 2200 768 2070 430 Log of Concentration (mg/kg) 7.7 6.6 7.6 6.1 Frequency: Average: Average log: UCL: Maximum: 4/4 1367.00 7.01 42006.84 2200.00 Sample Std. Dev. 899.05 Sample Std. Dev. 0.79 (log value) * - 95% UCL exceeds the maximum concentration detected in the samples. o O O O U! GROUNDWATER —I *.—H O O •si VOC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-1 20 MW-1 3D MW-14-AVS Eglin 1-2 Eglin It-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin 1-3 Eglin 11-3 BENZENE Concentration Q (mg/l) 0.025 U R 0.005 U 0.0125 U 0.005 U 0.005 U 0.9625 0.005 U 0.005 U 0.005 U 0.005 U 0.027 0.016 0.0165 U 0.025 U 0.005 U 0.005 U 0.005 UU 0.005 U 0.0005 UJ 0.0005 UU 0.0005 UJ 0.0005 UJ 0.0005 U 0.05 U 0.0005 U 0.006 U 0.0005 U 0.0005 U 0.0005 U 0.0025 U 0.027 R R Log of Concentration (mg/l) -3.7 -5.3 -4.4 -5.3 -5.3 0.0 -5.3 -5.3 -5.3 -5.3 -3.6 -4.1 -4.1 -3.7 -5.3 -5.3 -5.3 -5.3 -7.6 -7.6 -7.6 -7.6 -7.6 -3.0 -7.6 -5.1 -7.6 -7.6 -7.6 -6.0 -3.6 Frequency: 34/168 Average: 0.35 Average log: -5.99 UCL: 0.06 Maximum: 21.00 , Sample Std. Dev. 2.41 Sample Std. Dev. 2.27 (log value) O .s:, 0- Eglin 111-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin HI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steete-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin 111-6 Gassett-6 Harvey-6 0.00025 UJ 0.00025 UU 0.00025 UJ 0.00025 UJ 0.00025 UU 0.00025 U R 0.00025 UJ 0.00025 U 0.003 0.0005 U 0.0006 U 0.00005 J 0.00033 J 0.0025 U 0.00025 U 0.00025 U 0.00125 U 0.0006 U 0.00025 U 0.0001 J 0.00008 J 0.0645 DJ 0.00025 U 0.00025 U 0.00025 U 0.0008 0.0027 0.00007 J 0.00025 U 0.0001 5 J 0.00025 U 0.00025 U 0.00025 U 0.00007 J 0.00125 U 0.0017 0.00025 U 0.00007 J 0.00025 U 0.00025 U 0.0031 U -8.3 -8.3 -8.3 -8.3 -8.3 -8.3 -8.3 -8.3 -5.8 -7.6 -7.4 -9.9 -8.0 -6.0 -8.3 -8.3 -6.7 -7.4 -8.3 -9.2 -9.4 -2.7 -8.3 -8.3 -8.3 -7.1 -5.9 -9.6 -8.3 -8.8 -8.3 -8.3 -8.3 -9.6 -6.7 -6.4 -8.3 -9.6 -8.3 -8.3 -5.8 l« •••4 ~i LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin HI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin 111-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Oelegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin HI-9 FourWindsl-9 0.001 U 0.00025 U 0.00075 U 0.0006 U 0.0008 J 0.00025 U 0.00025 U 0.00025 U 0.00125 U 0.001 U 0.00025 U 0.0025 U 0.00029 J 0.00025 U 0.001 25 U 0.001 U 0.007 0.004 U 0.004 U 0.004 U 0.004 U 0.00014 J 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.0065 0.0005 U 0.0005 U 0.0005 U 0.0005U 1.7 0.005 U 0.005 U 0.00025 U 0.00017 JB 0.005 LU 0.005 U 0.005 U 0.005 U 0.005 U -6.9 -8.3 -7.2 -7.4 -7.1 -8.3 -8.3 -8.3 -6.7 -6.9 -8.3 -6.0 -8.1 -8.3 -6.7 -6.9 -5.0 -5.5 -5.5 -5.5 -5.5 -8.9 -5.5 -5.5 -5.5 -5.5 -5.5 -5.0 -7.6 -7.6 -7.6 -7.6 0.5 -5.3 -5.3 -8.3 -8.7 -5.3 -5.3 -5.3 -5.3 -5.3 oo CO o I"'"*- I%-." X| FourWinds!!9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.005 U 0.00025 U 0.005 U 0.005 U 0.005 U 0.005 U 0.02 U 0.005 UJ 0.0125U 0.005 UU 0.005 UJ 0.46 DJ 0.005U 0.005 U 0.021 0.005 UJ 0.01 UJ 0.0125 UJ 0.005 UJ 0.005 U 0.005 UJ 0.005 UJ 0.005 UJ 0.005 U 0.1 U 0.005 U NA 0.005 UJ 0.005 UJ 0.005 UU 0.005 UU R 0.005 UU 0.005 UU 0.005 U 0.005 U 0.005 U 0.005 U 0.005 U 0.005U 0.005 UJ 0.005 U -5.3 -8.3 -5.3 -5.3 -5.3 -5.3 -3.9 -5.3 -4.4 -5.3 -5.3 -0.8 -5.3 -5.3 -3.9 -5.3 -4.6 -4.4 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -2.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -0 O •s-ioo I- 6-9- O-E 9'0 O'E E'S- E'2- E'9- E'9- £'9- E'2 9'0- n n a a n r n 9oo'o r o t r 99'0 6-1 VHIA 6-9-iJ. 6-fr-li 6-QE-U QAV-6-2-ii 6-Ql-ii 6-i-ii QAV-6-Z-MS 6-9-MS 6-9-MS 6-t--MS 6-E-MS 6-2-MS GROUNOWATEh VOC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-1 20 MW-1 3D MW-14-AVS Eglin 1-2 Eglin It-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin 1-3 Eglin 11-3 1,2 DICHLOROETHENE Concentration Q (mg/l) 1.0 0.6 0.026 0.53 E 0.082 J 0.15 0.03 J 0.005 U 0.0365 0.17 0.14 0.005 U 0.002 J 0.13 0.18 0.005 U 0.002 J 0.005 U 0.041 J 0.06 J 0.072 DJ 0.045 J 0.23 D 0.0005 U 0.16 0.195 D 0.021 0.001 J 0.0005 U 0.042 J 0.044 0.2D 0.068 DJ 0.13 DJ (TOTAL) Log of Concentration (mg/l) 0.0 -0.5 -3.6 -0.6 -2.5 -1.9 -3.5 -5.3 -3.3 -1.8 -2.0 -5.3 -6.2 -2.0 -1.7 -5.3 -6.2 -5.3 -3.2 -2.8 -2.6 -3.1 -1.5 -7.6 -1.8 -1.6 -3.9 -6.9 -7.6 -3.2 -3.1 -1.6 -2.7 -2.0 Frequency: 142/169 Average: 0.13 Average log: -3.45 UCL: 0.39 Maximum: 2.10 Sample Std. Dev. 0.30 Sample Std. Dev. 2.00 (log value) Nj Eglin HI-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin HI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 0.069 DJ 0.13 DJ 0.00025 UJ 0.08 DJ 0.21 DEJ 0.036 J 0.002 J 0.062 D 0.18DJ 0.4 DEJ 0.045 0.067 0.051 0.089 D 0.19 0.00025 U 0.038 0.17 D 0.019 0.0028 0.056 D 0.15 D 0.145D 0.017 0.02 0.039 0.15 D 0.13 0.00011 J 0.039 0.14 D 0.017 0.017 0.00025 U 0.048 D 0.11 0.023 0.013 0.031 0.031 0.00025 U 0.041 -2.7 -2.0 -8.3 -2.5 -1.6 -3.3 -6.2 -2.8 -1.7 -0.9 -3.1 -2.7 -3.0 -2.4 -1.7 -8.3 -3.3 -1.8 -4.0 -5.9 -2.9 -1.9 -1.9 -4.1 -3.9 -3.2 -1.9 -2.0 -9.1 -3.2 -2.0 -4.1 -4.1 -8.3 -3.0 -2.2 -3.8 -4.3 -3.5 -3.5 -8.3 -3.2 O H O LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tiliett-6 Eglin 1-7 Eglin 11-7 Eglin HI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin HI-9 FourWindsl-9 0.1 0.0095 0.0385 0.15 D 0.47 DJ 0.012 0.011 0.032 0.17 0.099 0.00025 U 0.049 0.13 0.0014 0.06 0.14 0.29 0.012 0.027 0.14 0.004 U 0.0465 D 0.11 0.0014 0.004 U 0.052 0.13 0.2 NA NA NA NA 0.05 U 0.042 0.091 0.0074 J 0.00025 U 0.092 J 0.043 0.002 J 0.031 0.064 -2.3 -4.7 -3.3 -1.9 -0.8 -4.4 -4.5 -3.4 -1.8 -2.3 -8.3 -3.0 -2.0 -6.6 -2.8 -2.0 -1.2 -4.4 -3.6 -2.0 -5.5 -3.1 -2.2 -6.6 -5.5 -3.0 -2.0 -1.6 -3.0 -3.2 -2.4 -4.9 -8.3 -2.4 -3.1 -6.2 -3.5 -2.7 o0 s! FourWindsll9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.0595 0.00025 U 0.021 0.095 0.015 0.95 D 0.5 0.0045 U - 0.44 D 0.076 J 0.064 J 0.019 J 0.1 0.022 0.18 0.088 J 0.006 J 0.076 J 0.11 J 0.002 J 0.067 J 0.005 UJ 0.005 ULJ 1.5D 2.1 0.053 NA 0.013 J 0.013 J 0.005 UU 0.035 J 0.011 J 0.004 J 0.005 UJ 0.027 0.012 0.009 J 0.008 J 0.023 0.005 U 0.039 J 0.1 -2.8 -8.3 -3.9 -2.4 -4.2 -0.1 -0.7 -5.4 -0.8 -2.6 -2.7 -4.0 -2.3 -3.8 -1.7 -2.4 -5.1 -2.6 -2.2 -6.2 -2.7 -5.3 -5.3 0.4 0.7 -2.9 -4.3 -4.3 -5.3 -3.4 -4.5 -5.5 -5.3 -3.6 -4.4 -4.7 -4.8 -3.8 -5.3 -3.2 -2.3 SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA 1-9 0.5 UJ 0.5 UJ 0.038J 0.004 J 0.005 U 0.075 U) 0.36 D 0.012 J 0.01 0.33 0.28 2.5 U 0.18 0.00015 J -0.7 -0.7 -3.3 -5.5 -5.3 -2.6 -1.0 -4.4 -4.6 -1.1 -1.3 0.9 -1.7 -8.8 GRGUNDWATtM VOC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-12D MW-1 3D MW-14-AVS Eglin 1-2 Eglin 11-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodrlguez-2 Smith-2 Steele-2 Tillett-2 Eglin 1-3 Eglin 11-3 TETRACHLOROETHENE Concentration Q (mg/l) 0.12 J 0.19 J 0.015 0.017 J 0.026 J 0.044 0.25 U 0.005 U 0.0135 0.025 J 0.011 J 0.005 U 0.005 U 0.025 J 0.01 J 0.005 U 0.005 U 0.007 J 0.001 J 0.026 0.034 DJ 0.0355 0.09 D 0.0005 U 1.5 0.105 D 0.076 0.016 0.0005 U 0.16 J 0.065 0.1 D 0.032 J 0.061 DJ Log of Concentration (mg/l) -2.1 -1.7 -4.2 -4.1 -3.6 -3.1 -1.4 -5.3 -4.3 -3.7 -4.5 -5.3 -5.3 -3.7 -4.6 -5.3 -5.3 -5.0 -6.9 -3.6 -3.4 -3.3 -2.4 . -7.6 0.4 -2.3 -2.6 -4.1 -7.6 -1.8 -2.7 -2.3 -3.4 -2.8 Frequency: 143/173 Average: 0.10 Average log: -3.61 UCL: 0.20 Maximum: 1.50 Sample Std. Dev. 0.24 Sample Std. Dev. 1.77 (log value) O O !-=• o-- H i—— H Eglin HI-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin 111-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthlas-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin 111-6 Gassett-6 Harvey-6 0.04 J 0.034 DJ 0.00025 UU 0.53 DEJ 0.076 DJ 0.059 DJ 0.016 0.19 D 0.15 DJ 0.18DJ 0.024 0.054 0.036 0.036 0.08 0.00025 U 0.67 D 0.1 D 0.081 0.019 0.25 D 0.054 D 0.0645 D 0.016 0.016 0.041 D 0.075 D 0.00125 U 0.00025 U 0.5 D 0.0825 D 0.06D 0.023 0.00025 U 0.23 D 0.055 0.023 0.014 0.036 0.039 0.00025 U 0.35 -3.2 -3.4 -8.3 -0.6 -2.6 -2.8 -4.1 -1.7 -1.9 -1.7 -3.7 -2.9 -3.3 -3.3 -2.5 -8.3 -0.4 -2.3 -2.5 -4.0 -1.4 -2.9 -2.7 -4.1 -4.1 -3.2 -2.6 -6.7 -8.3 -0.7 -2.5 -2.8 -3.8 -8.3 -1.5 -2.9 -3.8 -4.3 -3.3 -3.2 -8.3 -1.0 LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillatt-6 Eglin 1-7 Eglin 11-7 Eglin HI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin 1-9 Eglin HI-9 FourWindsl-9 0.06 0.02 0.145 D 0.04 0.2 0.011 0.011 0.034 0.078 0.038 0.00025 U 0.26 0.067 0.016 0.17 0.065 0.14 0.0093 0.03 0.062 0.004 U 0.3 DJ 0.062 0.016 0.004 U 0.17 0.081 0.14 0.018 0.3 D 0.008 0.25 D 0.05 U 0.012 0.036 0.015 J 0.016 0.042 J 0.018 0.01 0.031 0.025 -2.8 -3.9 -1.9 -3.2 -1.6 -4.5 -4.5 -3.4 -2.6 -3.3 -8.3 -1.3 -2.7 -4.1 -1.8 -2.7 -2.0 -4.7 -3.5 -2.8 -5.5 -1.2 -2.8 -4.1 -5.5 -1.8 -2.5 -2.0 -4.0 -1.2 -4.8 -1.4 -3.0 -4.4 -3.3 -4.2 -4.1 -3.2 -4.0 -4.6 -3.5 -3.7 H- 0J c —! oo xi FourWindsll9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 NW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.023 0.00025 U 0.1 0.058 0.03 0.33 D 0.36 0.004 U) 0.056 0.02 J 0.017 J 0.004 J 0.031 0.01 0.13 0.038 J 0.01 Ul 0.034 J 0.048 J 0.001 J 0.033 J 0.004 J 0.028 J 0.12 0.071 J 0.037 NA 0.005 UU 0.002 J 0.005 UJ 0.022 J 0.045 J 0.004 J 0.001 J 0.011 0.01 0.026 0.006J 0.14 0.011 0.11 J 0.04 -3.8 -8.3 -2.3 -2.8 -3.5 -1.1 -1.0 -5.5 -2.9 -3.9 -4.1 -5.5 -3.5 -4.6 -2.0 -3.3 -4.6 -3.4 -3.0 -6.9 -3.4 -5.5 -3.6 -2.1 -2.6 -3.3 -5.3 -6.2 -5.3 -3.8 -3.1 -5.5 -6.9 -4.5 -4.6 -3.6 -5.1 -2.0 -4.5 -2.2 -3.2 •43' SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.5 UJ 0.5 UJ 0.015 J 0.004 J 0.005 U 0.075 UJ 0.18 0.05 U 0.005 U 0.0905 0.023 2.5 U 0.003 J 0.0019 -0.7 -0.7 -4.2 -5.5 -5.3 -2.6 -1.7 -3.0 -5.3 -2.4 -3.8 0.9 -5.8 -6.3 GROUNOWATER VOC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-12D MW-1 3D MW-14-AVS Eglin I-2 Eglin II-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin I-3 Eglin II-3 TOLUENE Concentration Q (mg/l) 0.025 U R 0.005 U 0.0125U 0.005 U 0.005 U 0.1775 J 0.005 U 0.005U 0.005 U 0.005 U 0.005 U 0.002 J 0.0165U 0.025U 0.005 U 0.001 J 0.001 J 0.005 U 0.0005 UU 0.0005 UU 0.0005 UJ 0.0005 UJ 0.044 D 0.05 U 0.0005 U 0.006 U 0.0005 U 0.0005U 0.0005 U 0.0025 U 0.001 R R Log of Concentration Frequency: 32/168 (mg/l) Average: 0.22 Sample Std. Dev. 1.81 Average log: -6.25 Sample Std. Dev. 2.12 -3.7 UCL: 0.03 (log value) Maximum: 17.00 -5.3 -4.4 -5.3 -5.3 -1.7 -5.3 -5.3 -5.3 -5.3 -5.3 -6.2 -4.1 -3.7 -5.3 -6.9 -6.9 -5.3 -7.6 -7.6 -7.6 -7.6 -3.1 -3.0 -7.6 -5.1 -7.6 -7.6 -7.6 -6.0 -6.9 o Eglin HI-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin 111-4 FourWindsl-4 FourWlndsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin 111-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 0.00025 UU 0.00025 UU 0.00025 UJ 0.00025 UJ 0.00175 UJ 0.00025 UJ R 0.00025 UU 0.00025 UU 0.0008 J 0.0005 U 0.0006 U 0.00025 U 0.00025 U 0.0025 U 0.00025 U 0.00025 U 0.00125 U 0.0006 U 0.00025 U 0.00025 U 0.00025 U 0.00255 J 0.006 J 0.00025 U 0.00025 U 0.00025 U 0.00125 U 0.000385 U 0.00006 J 0.00011 J 0.00025 U 0.00025 U 0.00025 U 0.00005 J 0.00125 U 0.00005 J 0.00006 J 0.00025 U 0.00025 U 0.00025 U 0.0031 U -8.3 -8.3 -8.3 -8.3 -6.3 -8.3 -8.3 -8.3 -7.1 -7.6 -7.4 -8.3 -8.3 -6.0 -8.3 -8.3 -6.7 -7.4 -8.3 -8.3 -8.3 -6.0 -5.1 -8.3 -8.3 -8.3 -6.7 -7.9 -9.7 -9.1 . -8.3 -8.3 -8.3 -9.9 -6.7 -9.9 -9.7 -8.3 -8.3 -8.3 -5.8 o l"% Kl H J 1™^oxl LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin HI-7 FourWlndsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin 111-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin HI-9 FourWindsl-9 0.001 U 0.00025 U 0.00075 U 0.0006 U 0. 00125 U 0.00025 U 0.00008 J 0.00025 U 0.00125 U 0.001 U 0.00025 U 0.0025 U 0.000315 UU 0.00025 U 0.00125 U 0.001 U 0.0005 J 0.00005 J 0.00018 J 0.004 U 0.00006 J 0.00009 J 0.004 U 0.004 U 0.00007 J 0.004 U 0.004 U 0.00042 J 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.1.8 0.005 U 0.005 U 0.00025 U 0.0001 5 JB 0.005 UU 0.005 UJ 0.005 UJ 0.005 UJ 0.005 U -6.9 -8.3 -7.2 -7.4 -6.7 -8.3 -9.4 -8.3 -6.7 -6.9 -8.3 -6.0 -8.1 -8.3 -6.7 -6.9 -7.6 -9.9 -8.6 -5.5 -9.7 -9.3 -5.5 -5.5 -9.6 -5.5 -5.5 -7.8 -7.6 -7.6 -7.6 -7.6 -1.7 -5.3 -5.3 -8.3 -8.8 -5.3 -5.3 -5.3 -5.3 -5.3 O O Nj FourWindsll9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 M W-18-9 MW-18R-9 NW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.005 U 0.00025 U 0.005U 0.005U 0.005 U 0.005 U 0.02 U 0.005 LU 0.0125 U 0.005 UU 0.005 UJ 0.02 J 0.005 U 0.005U 0.005 U 0.005 UJ 0.01 UJ 0.0125 UU 0.005 UJ 0.005 U 0.005 UJ 0.005 UJ 0.005 UJ 0.005 U 0.1 U 0.005 U NA 0.005 UJ 0.005 UJ 0.005 UJ 0.005 UJ R 0.005 UJ 0.005 UJ 0.005 U 0.005 U 0.005 U 0.005 U 0.005U 0.005 U 0.005 UJ 0.005 U -5.3 -8.3 -5.3 -5.3 -5.3 -5.3 -3.9 -5.3 -4.4 -5.3 -5.3 -3.9 -5.3 -5.3 -5.3 -5.3 -4.6 -4.4 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -2.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -1q SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.36 J 3.2 J 0.005 ULI 0.005 U 0.005 U 0.075 UU 0.002 J 16 D 0.048 0.0125 U 0.01 U 17 0.005 U 0.00014 JB -1.0 1.2 -5.3 -5.3 -5.3 -2.6 -6.2 2.8 -3.0 -4.4 -4.6 2.8 -5.3 -8.9 .o GROUNDWATh,. VOC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-12D MW-1 3D MW-14-AVS Eglin 1-2 Eglin 11-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steete-2 Tillett-2 Eglin 1-3 Eglin 11-3 VINYL CHLORIDE Concentration Q (mg/l) 0.025 U R 0.005 U 0.14 0.005 U 0.005 U 0.25 U 0.005 UJ 0.005 UJ 0.005 U 0.005U 0.005 U 0.005 U 0.0165 U 0.025 U 0.005 U 0.005 U 0.005 UJ 0.0175 J R R 0.001 UJ 0.001 UJ 0.001 U 0.1 U 0.001 U 0.0125 U R 0.001 U R 0.005 U 0.007 R R Log of Concentration Frequency: 21/164 (mg/l) Average: 0.04 Sample Std. Dev. 0.23 Average log: -5.87 Sample Std. Dev. 1.81 -3.7 UCL: 0.02 (log value) Maximum: 1.30 -5.3 -2.0 -5.3 -5.3 -1.4 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -4.1 -3.7 -5.3 -5.3 -5.3 -4.0 -6.9 -6.9 -6.9 -2.3 -6.9 -4.4 -6.9 -5.3 -5.0 o ••-i H C H Eglin HI-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin 111-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 0.0005 UU 0.0005 UU 0.0005 UJ 0.003 0.0005 UU 0.0005 UU R 0.0005 UJ 0.004 0.005 0.0005 U 0.0006 U 0.00025 U 0.00025 U 0.0025 U 0.00025 U 0.0021 0.00125 U 0.0006 U 0.00025 U 0.00025 U 0.0025 0.014 J 0.00025 U 0.00025 U 0.00025 U 0.00022 J 0.00125 U 0.00025 U 0.0022 0.00025 U 0.00025 U 0.00025 U 0.00025 U 0.00025 U 0.0014 J 0.00025 U 0.00025 U 0.00025 U 0.00025 U 0.00025 U 0.0031 U -7.6 -7.6 -7.6 -5.8 -7.6 -7.6 -7.6 -5.5 -5.3 -7.6 -7.4 -8.3 -8.3 -6.0 -8.3 -6.2 -6.7 -7.4 -8.3 -8.3 -6.0 -4.3 -8.3 -8.3 -8.3 -8.4 -6.7 -8.3 -6.1 -8.3 -8.3 -8.3 -8.3 -8.3 -6.6 -8.3 -8.3 -8.3 -8.3 -8.3 -5.8 LaP!ace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin 111-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin HI-9 FourWindsl-9 0.001 U 0.00025 U 0.00075 U 0.002 0.0032 0.00025 U 0.00025 U 0.00025 U 0. 00125 U 0.001 U 0.00025 U 0.0025 U 0.001 U 0.00025 U 0.00125 U 0.0033 0.0025 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.004 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.05 U 0.005 U 0.005 U 0.00025 U 0.00025 U 0.005 LU 0.005U 0.005 U 0.005 U 0.005 U -6.9 -8.3 -7.2 -6.2 -5.7 -8.3 -8.3 -8.3 -6.7 -6.9 -8.3 -6.0 -6.9 -8.3 -6.7 -5.7 -6.0 -5.5 -5.5 -5.5 -5.5 -5.5 -5.5 -5.5 -5.5 -5.5 -5.5 -5.5 -7.6 -7.6 -7.6 . -7.6 -3.0 -5.3 -5.3 -8.3 -8.3 -5.3 -5.3 -5.3 -5.3 -5.3 oo •X! FourWinds!l9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OIHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.001 J 0.00025 U 0.005 U 0.005 U 0.005 U 0.005 U 0.02 U 0.005 UU 0.048 0.005 UU 0.005 UJ 0.005UJ 0.005 U 0.005 U 0.005 U 0.005 UJ 0.01 UJ 0.0125 UJ 0.005 UJ 0.005 U 0.005 UJ 0.005 UJ 0.005UJ 0.26 D 1.3 0.005 U NA 0.005 UJ 0.005 UJ 0.005 UJ 0.005 UJ R 0.005 UJ 0.005 UJ 0.005 U 0.005 U 0.005 U 0.005 U 0.005 U 0.005 U 0.005 UJ 0.005 U •6.9 -8.3 -5.3 -5.3 •5.3 -5.3 -3.9 -5.3 -3.0 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -4.6 -4.4 -5.3 -5.3 -5.3 -5.3 -5.3 -1.3 0.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 -5.3 O r; cH SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.5 UU 0.5 Ul 0.005 UJ 0.005 U 0.005 U 0.075UJ 0.005 U 0.05 U 0.005 U 0.0125 U 0.009 J 2.5 U 0.042 0.00025 U -0.7 -0.7 -5.3 -5;3 -5.3 -2.6 -5.3 -3.0 -5.3 -4.4 -4.7 0.9 -3.2 -8.3 O O GROUNBWATt.. INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-1 20 MW-13D MW-14-AVS Eglin 1-2 Eglin 11-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin 1-3 Eglin 11-3 ANTIMONY Concentration Q (mg/l) 0.01 U 0.01 UU 0.01 U 0.01 U 0.0155 0.01 U 0.00775 U 0.01 U 0.00775 U 0.01 U 0.01 U 0.01 U 0.01 U 0.01 U 0.01 U 0.01 U 0.01 U 0.01 U 0.00775 U NA 0.0135 U 0.0135 U 0.0135 U NA 0.0135 U NA NA NA 0.0135 U 0.0135 U 0.0135 U NA NA NA Log of Concentration Frequency: 22/115 (mg/l) Average: 0.02 Sample Std. Dev. 0.041 Average log: -4.50 Sample Std. Dev. 0.57 -4.6 UCL: 0.01 (log value) -4.6 Maximum: 0.424 -4.6 -4.6 -4.2 -4.6 -4.9 -4.6 -4.9 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.9 -4.3 -4.3 -4.3 -4.3 -4.3 -4.3 -4.3 Eglin 111-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Egtin 11-4 Eglin 111-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 , Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.00885 U 0.00885 U 0.00885 U 0.0091 U 0.0091 U 0.0091 U 0.00885 U 0.009 U 0.0091 U 0.0091 U 0.019 0.0091 U 0.0091 U 0.0091 U NA NA NA NA NA 1 -4.7 -4.7 -4.7 -4.7 -4.7 -4.7 -4.7 -4.7 -4.7 -4.7 -4.0 -4.7 -4.7 -4.7 ~i Vf LaPlacs-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin HI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillatt-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CGT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin 1-9 Eglin HI-9 FourWindsl-9 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0105 U 0.0105 U 0.0105 U 0.0105 U 0.0105U 0.0105 U 0.0105 U 0.0105 U 0.0105U 0.0105U 0.0105 U NA NA NA NA 0.0075 U 0.0075 U 0.0075 U 0.15 U NA 0.0075 U 0.0375 U 0.0075 U 0.0075 U 0.0075 U i -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.6 -4.9 -4.9 -4.9 -1.9 -4.9 -3.3 -4.9 -4.9 -4.9 -ic FourWindsllDAV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 ^ MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.0148 B 0.0075U 0.0075 U 0.0075 U 0.0075 U 0.0176B 0.0075 U 0.015 B 0.017 B 0.0201 B 0.0075 U 0.0201 B 0.0253 B 0.0075 U 0.0213 B 0.0075 U 0.0075 U 0.0075 U 0.0075 U 0.0075 U 0.0075 U 0.0075 U 0.424 B 0.0075 U 0.0075 U 0.0075 U 0.0206 BJ NA 0.0075 UU 0.0075 U 0.0075 U 0.0196 B 0.0223 BJ 0.0075 U 0.0075 U 0.0161 BJ 0.0075 U 0.0507 B 0.0075 UJ 0.015 U 0.0075 U 0.0075 U -4.2 -4.9 -4.9 -4.9 -4.9 -4.0 -4.9 -4.2 -4.1 -3.9 -4.9 -3.9 -3.7 -4.9 -3.8 -4.9 -4.9 -4.9 -4.9 -4.9 -4.9 -4.9 -0.9 -4.9 -4.9 -4.9 -3.9 -4.9 -4.9 -4.9 . -3.9 -3.8 -4.9 -4.9 -4.1 -4.9 -3.0 -4.9 -4.2 -4.9 -4.9 _4cH SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.0154 BJ 0.0164 BJ 0.0075 U 0.0075 U 0.015U 0.0184 BJ 0.0075 U 0.0197 B 0.0075 U 0.0075 U 0.019 B 0.0075 U 0.0075 U 0.0206 B -4.2 -4.1 -4.9 -4.9 -4.2 -4.0 -4.9 -3.9 -4.9 -4.9 -4.0 -4.9 -4.9 -3.9 Oo~ GROUNDWATtn C o INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-12D MW-1 3D MW-14-AVS Eglin I-2 Eglin II-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin I-3 Eglin II-3 ARSENIC Concentration Q (mg/l) 0.001 U 0.001 UU 0.001 UW 0.001 UW 0.00125 UWJ 0.001 U 0.00408 B 0.001 UW 0.00125 UWJ 0.001 U 0.001 UW 0.0092 J R 0.0055 B 0.001 U 0.001 U 0.001 U 0.001 U 0.00125 UWJ NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Log of Concentration (mg/l) -6.9 -6.9 -6.9 -6.9 -6.7 -6.9 -5.5 -6.9 -6.7 -6.9 -6.9 -4.7 -5.2 -6.9 -6.9 -6.9 -6.9 -6.7 Frequency: 24/107 Average: 0.003 Average log: -6.89 UCL: 0.001 Maximum: 0.0808 Sample Std. Dev. 0.008 Sample Std. Dev. 0.62 (log value) oo Eglin HI-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin HI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0016 B 0.0005 U 0-0005 U 0.001 B 0.0005 U 0.003 B 0.0011 B 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U NA NA NA NA NA 1 -6.4 -7.6 -7.6 -6.9 -7.6 -5.8 -6.8 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 oo H C -4 *•-.! LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin MI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CGT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin MI-9 FourWindsl-9 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U NA NA NA NA 0.0047 B 0.001 U 0.001 U 0.001 U NA 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 1 -6.9 -6.9 -6.9 -6.9 -6.9 -6.9 -6.9 -6.9 -6.9 -6.9 -6.9 00 oo FourWindsll9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.0033 B 0.001 U 0.001 U 0.001 U 0.0038 B 0.001 U 0.001 U 0.0092 B 0.0024 B 0.0065 B 0.003 B 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.001 U 0.0034 BJ NA 0.001 UJ 0.001 U 0.001 U 0.001 U 0.0022 BJ 0.001 U 0.001 U 0.003 BJ 0.0808 J 0.0182 0.001 UU 0.001 U 0.001 U 0.001 U •43 c-i O SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tiilett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.0059 BJ 0.0102 J 0.001 U 0.001 U 0.001 U 0.0026 BJ 0.001 U 0.0029 B 0.001 U 0.001 U 0.001 U 0.0078 B 0.001 U 0.001 U s O GROUNDWATEH INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MVMD MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-1 10 MW-12D MW-13D MW-14-AVS Eglin 1-2 Eglin 11-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin 1-3 Eglin 11-3 BERYLLIUM Concentration Q (mg/l) 0.0005 U 0.0005 UU 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.00075 B 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Log of Concentration (mg/l) -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.2 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 Frequency: 8/108 Average: 0.001119 Average log: -7.52 UCL 0.001 Maximum: 0.0408 Sample Std Dev. 0.0041 Sample Std. Dev. 0.78 (log value) Eglin ill-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Egtin 1-4 Eglin 11-4 Eglin HI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin 111-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVO Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tlllett-5 Eglin 1-6 Eglin 11-6 Eglin 111-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.000265 U 0.000265 U 0.000265 U 0.000125 U 0.0001 25 U 0.000125 U 0.000265 U 0.0005 U 0.001 B 0.000125 U 0.001 B 0.0001 25 U 0.0001 25 U 0.000125 U NA NA NA NA NA i -8.2 -8.2 -8.2 -9.0 -9.0 -9.0 -8.2 -7.6 -6.9 -9.0 -6.9 -9.0 -9.0 -9.0 O O H f— '.———H LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Egiin 11-7 Eglin 111-7 FourWinds!-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U 0.0005 U NA NA NA NA CHT-3-9 0.0005 U CHT-6D-9 0.0005 U CHT-7D-9 0.0005 UU Delegarde-9 0.01 U Delegarde-9* NA DW-1-9 0.01 UU DW-2-9 0.0025 U Eglin I-9 0.0005 U Eglin III-9 0.0005 U FourWindsl-9 0.001 B i -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -4.6 -4.6 -6.0 -7.6 -7.6 -6.9 o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o « o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o e v i o o o o o p o o o o p p p p o p p o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o o 11112 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2222§§§ TUT 007 0044 SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.0005 UU 0.0023 BJ 0.0005 U 0.0005 U 0.001 U 0.0005 UU 0.0005 U 0.0005 UJ 0.0005 UJ 0.0005 UJ 0.0005 U 0.0005 U 0.0005 UU 0.0005 U -7.6 -6.1 -7.6 -7.6 -6.9 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 -7.6 GROUNDWATtn —; C -4 INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-1 20 MW-1 3D MW-14-AVS Eglin I-2 Eglin II-2 Eglinlll-2-AVD FoufWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin I-3 Eglin II-3 HEXAVALENT CHROMIUM Concentration Q (mg/l) 0.0009 U 0.0033 J 0.0006 B 0.0025 0.0035 0.0003 U 0.002 0.0297 0.0044 0.0017 0.0016 0.0016 U 0.0028 U 0.0027 0.006 B 0.0136 0.0091 0.0102 0.0022 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA ** Log of Concentration Frequency: 63/107 (mg/l) Average: 0.02 Sample Std. Dev. 0.09 Average log: -6.36 Sample Std. Dev. 1 .99 -7.0 UCL: 0.02 (log value) -5.7 Maximum: 0.659 -7.4 -6.0 -5.7 -8.1 -6.2 -3.5 -5.4 -6.4 -6.4 -6.4 -5.9 -5.9 -5.1 -4.3 -4.7 -4.6 -6.1 H H O Eglin 111-3 FourWlndsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin 111-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVO Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0003 U 0.0007 B 0.0003 U 0.00025 U 0.00025 U 0.0005 B 0.0003 U 0.0003 U 0.0156 0.00025 U 0.0268 0.0069 0.00025 U 0.0016 NA NA NA NA NA i -8.1 -7.3 -8.1 -8.3 -8.3 -7.6 -8.1 -8.1 -4.2 -8.3 -3.6 -5.0 -8.3 -6.4 <o in •* f- cd in o it in in 10 cb CM' OD oo oo 03 D D z z z z z z z z 22200000000000 o o o o o o o o o o o O O p O C3 O O O O p O d d o d d d d d d o ' o o o o o o o o c o o o o o o o o o o o o o o o o o tn 007 OO4S ~i oo ••-.I FourWinds!l9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.0002 U 0.0002 U 0.0002 U 0.0002 U 0.0002U 0.0647 0.0034 0.0884 0.0018 J 0.0047 0.0065 0.0018 0.0046 0.029 0.15 0.03 0.001 B 0.0009 B 0.0022 0.0129 0.0452 0.0015 0.6142 0.0011 B 0.0002 U 0.034 0.0072 J NA 0.0025 0.0021 0.0135 0.0068 0.0018 UU 0.0017 0.0015 0.3143 J 0.0015 0.6586 0.0567 J 0.0043 U 0.0002 U 0.0004 B -8.5 -8.5 -8.5 -8.5 -8.5 -2.7 -5.7 -2.4 -6.3 -5.4 -5.0 -6.3 -5.4 -3.5 -1.9 -3.5 -6.9 -7.0 -6.1 -4.4 -3.1 -6.5 -0.5 -6.8 -8.5 -3.4 -4.9 -6.0 -6.2 -4.3 -5.0 -6.3 -6.4 -6.5 -1.2 -6.5 -0.4 -2.9 -5.4 -8.5 -7.8 o Js SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA 1-9 0.0007 BJ 0.0048 J 0.0002 U 0.0065 0.0016 B 0.0008 BJ 0.0002 U 0.0007 B 0.0002 U 0.0002 U 0.0002 UU 0.0002 U 0.0002 U 0.0002 U -7.3 -5.3 -8.5 -5.0 -6.4 -7.1 -8.5 -7.3 -8.5 -8.5 -8.5 -8,5 -8.5 -8.5 H " - One-seventh of the dtected total chromium comcentration was assumed to be hexavalent per IRIS (1994). O --! GROUNDWATEr, •H C INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-1 10 MW-1 20 MW-1 3D MW-14-AVS Eglinl-2 Eglin II-2 Eglinlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin 1-3 Eglin 11-3 MANGANESE Concentration Q (mg/l) 0.563 0.423 J 0.0854 1.56 1.1 0.0389 J 0.39225 0.0093 B 0.3575 0.126 J 0.0814 2.58 1.7 1.45 0.156 0.0058 B 0.0126 B 0.0158 2.515 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Log of Concentration (mg/l) -0.6 -0.9 -2.5 0.4 0.1 -3.2 -0.9 -4.7 -1.0 -2.1 -2.5 0.9 0.5 0.4 -1.9 -5.1 -4.4 -4.1 0.9 Frequency: 104/107 Average: 0.97 Average log: -1.95 UCL: 4.68 Maximum: 20.40 Sample Std. Dev. 2.53 Sample Std. Dev. 2.32 (log value) o Eglin 111-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin HI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin HI-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0121 B 0.118 0.0229 0.033 0.0068 B 0.07345 0.12 0.00285 B 0.269 0.002 B 0.132 0.108 0.0178 1.11 NA NA NA NA NA t -4.4 -2.1 -3.8 -3.4 -5.0 -2.6 -2.1 -5.9 -1.3 -6.2 -2.0 -2.2 -4.0 0.1 V,'o Si LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin MI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin HI-9 FourWindsl-9 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0285 0.0089 B 0.0128 B 0.0497 0.191 0.0075 B 0.0023 B 0.092 0.0262 0.0364 0.0674 NA NA NA NA R 0.0103 B 0.282 0.163 B NA 0.0243 0.62 0.0022 B 0.0079 B 0.0149 B 1 -3.6 -4.7 -4.4 -3.0 -1.7 -4.9 -6.1 -2.4 -3.6 -3.3 -2.7 -4.6 -1.3 -1.8 -3.7 -0.5 -6.1 -4.8 -4.2 H FourWindslOAV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.122 0.03 0.267 0.002 B 0.0014B 0.57 0.338 0.366 2.54 1.29 0,0551 1.08 0.0045 B 0.736 0.453 2.35 2.56 0.597 0.216 0.0076 B 0.114 0.11 20.4 0.149 0.532 1.55 3.74 NA 0.0726 J 0.997 1.14 0.402 0.0358 UU 0.215 0.982 5.87 J 0.275 3.18 13.5 J 0.001 U 0.0212 0.007 B -2.1 -3.5 -1.3 -6.2 -6.6 -0.6 -1.1 -1.0 0.9 0.3 -2.9 0.1 -5.4 -0.3 -0.8 0.9 0.9 -0.5 -1.5 -4.9 -2.2 -2.2 3.0 -1.9 -0.6 0.4 1.3 -2.6 0.0 0.1 -0.9 -3.3 -1.5 0.0 1.8 -1.3 1.2 2.6 -6.9 -3.9 -5.0 oo CR Js, SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA-1-9 0.943 J 6.34 J 0.165 0.29 0.422 4.17 J 0.934 1.71 1.88 1.285 0.236 0.957 1.11 0.0005 U -0.1 1.8 -1.8 -1.2 -0.9 1.4 -0.1 0.5 0.6 0.3 -1.4 0.0 0.1 -7.6 GROUNDWATEh, INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-10D MW-11D MW-12D MW-1 3D MW-14-AVS Eglin I-2 Eglin II-2 Egllnlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin I-3 Eglin II-3 NICKEL Concentration Q (mg/l) 0.013 B 0.0103 BJ 0.0212 B 0.0087 B 0.025 B 0.004 U 0.05103 0.062 0.02755 B 0.004 U 0.0252 B 0.0192 B 0.0618 0.0181 B 0.004 U 0.0107 B 0.0104B 0.004 U 0.019 B NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Log of Concentration Frequency: 50/107 (mg/l) Average: 0.09 Sample Std. Dev. 0.30 Average log: -4.26 Sample Std. Dev. 1.54 -4.3 UCL: 0.07 (log value) -4.6 Maximum: 2.05 -3.9 -4.7 -3.7 -5.5 -3.0 -2.8 -3.6 -5.5 -3.7 -4.0 -2.8 -4.0 -5.5 -4.5 -4.6 -5.5 -4.0 Ulo- •H Eglin HI-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin MI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin 111-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steele-5 Tillett-5 Eglin 1-6 Eglin 11-6 Eglin HI-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.00475 U 0.00475 U 0.00475 U 0.00355 U 0.00355 U 0.00355 U 0.00475 U 0.005 U 0.0537 0.00355 U 0.4459 0.0184 B 0.00355 U 0.00355 U NA NA NA NA NA i -5.3 -5.3 -5.3 -5.6 -5.6 -5.6 -5.3 -5.3 -2.9 -5.6 -0.8 -4.0 -5.6 -5.6 01 LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin HI-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin HI-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlace-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin I-9 Eglin MI-9 FourWindsl-9 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U 0.0045 U NA NA NA NA R 0.005 U 0.005 U 0.1 U NA 0.005 U 0.374 0.005 U 0.005 U 0.005 U i -5.4 -5.4 -5.4 -5.4 -5.4 -5.4 -5.4 -5.4 -5.4 -5.4 -5.4 -5.3 -5.3 -2.3 -5.3 -1.0 -5.3 -5.3 -5.3 r-, V,' XI FourWinds!l9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.005 U 0.0124 B 0.005 U 0.005 U 0.005 U 0.124 0.0142 0.266 0.005 U 0.0667 0.46 0.005 U 0.0319 B 0.127 0.445 0.109 0.005 U 0.005U 0.01 07 B 0.005U 0.005 U 0.005 U 2.05 0.005 U 0.0114 B 0.14 0.136 J NA 0.0239 BJ 0.0235 B 0.0482 0.0216 B 0.005 UJ 0.005 U 0.0132 B 1.12EJ 0.0146 B 1.84 J 0.603 EJ 0.01 U 0.005 U 0.005 U -5.3 -4.4 -5.3 -5.3 -5.3 -2.1 -4.3 -1.3 -5.3 -2.7 -0.8 -5.3 -3.4 -2.1 -0.8 -2.2 -5.3 -5.3 -4.5 -5.3 -5.3 -5.3 0.7 -5.3 -4.5 -2.0 -2.0 -3.7 -3.8 -3.0 -3.8 -5.3 -5.3 -4.3 0.1 -4.2 0.6 -0.5 -4.6 -5.3 -5.3 ~i o 'xi SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.005 UU 0.0418 J 0.0113 B 0.0172 B 0.01 U 0.005 UU 0.005 U 0.0165 B 0.005 U 0.0092 B 0.005 U 0.0171 B 0.0188 B 0.005 U -5.3 -3.2 -4.5 -4.1 -4.6 -5.3 -5.3 -4.1 -5.3 -4.7 -5.3 -4.1 -4.0 -5.3 GRCUNDWATtti H! C INORGANIC: Sample Location MW-1 MW-1D MW-2 MW-3 MW-4-AVS MW-4D MW-5-AVS MW-6D MW-6R-AVS MW-7-AVD MW-8 MW-9-AVD MW-9S MW-10 MW-1 00 MW-11D MW-12D MW-1 3D MW-14-AVS Eglin I-2 Eglin II-2 Egllnlll-2-AVD FourWindsll-2 Gassett-2 Harvey-2 LaPlace-2-AVD Matthias-2 Ramsay-2 Rodriguez-2 Smith-2 Steele-2 Tillett-2 Eglin I-3 Eglin II-3 VANADIUM Concentration Q (mg/l) 0.0931 J 0.0648 J 0.0368 B 0.0362 B 0.0718 0.0388 B 0.00573 B 0.002 U 0.1225 0.1045 0.042 B 0.0841 0.0651 0.0669 J 0.0697 J 0.002 U 0.002 U 0.0123 B 0.01955 B NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Log of Concentration (mg/l) -2.4 -2.7 -3.3 -3.3 -2.6 -3.2 -5.2 -6.2 -2.1 -2.3 -3.2 -2.5 -2.7 -2.7 -2.7 -6.2 -6.2 -4.4 -3.9 Frequency: 101/107 Average: 0.08 Average log: -3.24 UCL: 0.11 Maximum: 1.00 Sample Std. Oev. 0.14 Sample Std. Dev. 1.23 (log value) o Eglin 111-3 FourWindsl-3 Gassett-3 Harvey-3 LaPlace-3-AVD Matthias-3 Ramsay-3 Smith-3 Steele-3 Tillett-3 Eglin 1-4 Eglin 11-4 Eglin HI-4 FourWindsl-4 FourWindsll-4 Gassett-4 Harvey-4 LaPlace-4 Matthias-4 Ramsay-4 Smith-4 Steele-4 Tillett-4-AVD Eglin 1-5 Eglin 11-5 Eglin 111-5 FourWindsl-5 FourWindsll-5 Gassett-5-AVD Harvey-5 LaPlace-5-AVD Matthias-5 Ramsay-5 Rodriguez-5 Smith-5 Steela-5 THIett-5 Eglin 1-6 Eglin 11-6 Eglin 111-6 Gassett-6 Harvey-6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0303 B 0.0326 B 0.0131 B 0.0591 0.0592 0.005 U 0.0216 B 0.0354 B 0.0426 B 0.0541 0.005 U 0.0163 B 0.005 U 0.0585 NA NA NA NA NA t -3.5 -3.4 -4.3 -2.8 -2.8 -5.3 -3.8 -3.3 -3.2 -2.9 -5.3 -4.1 -5.3 -2.8 H C H .*-•, *•••. *-•• *•••i LaPlace-6 Ramsay-6 Smith-6-AVD Steele-6 Tillett-6 Eglin 1-7 Eglin 11-7 Eglin 111-7 FourWindsl-7 FourWindsll-7 Gassett-7 Harvey-7 LaPlace-7 Ramsay-7-AVD Smith-7 Steele-7 Tillett-7 Eglin 1-8 Eglin 111-8 FourWindsl-8 Gassett-8 Harvey-8-AVD LaPlaca-8 Ramsay-8 Rodriguez-8 Smith-8 Steele-8 Tillett-8 MW01 MW02 MW03-AVD MW04 CHT-3-9 CHT-6D-9 CHT-7D-9 Delegarde-9 Delegarde-9* DW-1-9 DW-2-9 Eglin 1-9 Eglin MI-9 FourWindsl-9 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.0206 B 0.011 B 0.0518 0.006 B 0.1595 B 0.0305 B 0.0452 B 0.0066 B 0.0052 B 0.0092 B 0.0541 NA NA NA NA R 0.0462 B 0.052 0.234 B NA 0.0646 0.241 B 0.0278 B 0.0159 B 0.0551 f -3.9 -4.5 -3.0 -5.1 -1.8 -3.5 -3.1 -5.0 -5.3 -4.7 -2.9 -3.1 -3.0 -1.5 -2.7 -1.4 -3.6 -4.1 -2.9 oo si FourWinds!l9AV Gassett-9 Harvey-9 LaPlace-9 Matthias-9 MW-1-9 MW-1D-9 MW-2-9 MW-3-9 MW-4-9 MW-4D-9 MW-5-9 MW-6D-9 MW-6R-9 MW-7-9 MW-8-9 MW-9S-9 MW-10-9 MW-10D-9 MW-11D-9-AVD MW-12D-9 MW-13-9 MW-13D-9 MW-15-9 MW-16-9 MW-17-9 MW-18-9 MW-18R-9 MW-19-9 MW-20-9 MW-20D-9 MW-21D-9 MW-22D-9 MW-24-9 MW-25-9 OHMW-1-9 OHMW-2-9 OHMW-3-9 OHMW-4-9 Ramsay-9 Smith-9 Steele-9 0.0468 B 0.0061 B 0.0237 B 0.0332 B 0.0116B 0.166 0.0526 0.218 0.0287 B 0.0528 0.0407 B 0.0115 B 0.0631 0.235 0.627 0.0857 0.0124 B 0.0318 B 0.0713 0.0112 B 0.0412 BJ 0.06 0.252 B 0.0651 0.0476 B 0.164 0.166 J NA 0.0326 BJ . 0.056 0.086 0.0509 0.0137 BJ 0.0686 0.138 0.498 J 0.0854 0.624 1 J 0.119 0.0049 B 0.0099B -3.1 -5.1 -3.7 -3.4 -4.5 -1.8 -2.9 -1.5 -3.6 -2.9 -3.2 -4.5 -2.8 -1.4 -0.5 -2.5 -4.4 -3.4 -2.6 -4.5 -3.2 -2.8 -1.4 -2.7 -3.0 -1.8 -1.8 -3.4 -2.9 -2.5 -3.0 -4.3 -2.7 -2.0 -0.7 -2.5 -0.5 0.0 -2.1 -5.3 -4.6 c_ SW-2-9 SW-3-9 SW-4-9 SW-5-9 SW-6-9 SW-7-9-AVD Tillett-9 TT-1-9 TT-1D-9 TT-2-9-AVD TT-3D-9 TT-4-9 TT-5-9 VIHA I-9 0.045 BJ 0.268 J 0.0767 0.0723 0.0639 B 0.0382 BJ 0.0716 0.0209 B 0.0157 B 0.0439 B 0.0248 B 0.0213 B 0.0051 B 0.0604 -3.1 -1.3 -2.6 -2.6 -2.8 -3.3 -2.6 -3.9 -4.2 -3.1 -3.7 -3.8 -5.3 -2.8 0- APPENDIX B TOXICOLOGICAL PROFILES TUT O07 OO66 ANTIMONY Antimony production has been associated with an increase in lung cancer in exposed workers. An inhalation study using rats yielded suggestive evidence that antimony trioxide causes lung and liver tumors, and several antimony compounds were mutagenic when tested using bacterial test systems. Female workers exposed to antimony compounds had an increased incidence of gynecological disorders and spontaneous abortions; similar effects were observed in an animal study. Antimony also causes cardiovascular changes in humans and may damage the myocardia (Clement Associates, Inc., 1985). The EPA has not assigned antimony a weight-of-evidence classification. This chemical has not been reviewed by the EPA for evidence of carcinogenic potential (IRIS, 1994). An oral reference dose (RfD) of 4E-04 mg/kg/day was developed based on a rat chronic oral bioassay by Schroeder et al. (1970), In this study, rats were administered 5 ppm of antimony tartrate in drinking water. Survival rates decreased in male rats as did the blood glucose level. Cholesterol levels were altered in both sexes. A NOEL was not established as only one level of antimony was administered. The LOAEL was 0.35 mg/kg/day. An uncertainty factor of 1000 was applied in developing the oral RfD (IRIS, 1994). An inhalation reference concentration (RfC) has not been developed. TUT 007 0067 ARSRNTr. Acute exposure of humans to the metal arsenic has been associated with gastrointestinal effects, hemolysis, and neuropathy. Chronic exposure of humans to this metal can produce toxic effects on both the peripheral and central nervous systems, keratosis, hyperpigmentation, precancerous dermal lesions, and cardiovascular damage (EPA, 1984). Arsenic is embryotoxic, fetotoxic, and teratogenic in several animals species (EPA, 1984). Arsenic is a known human carcinogen (Group A) (EPA, 1994). Epidemiological studies of workers in smelters and in plants manufacturing arsenical pesticides have shown that inhalation of arsenic is strongly associated with lung cancer and perhaps with hepatic angiosarcoma (EPA, 1984). Ingestion of arsenic has been linked to a form of skin cancer and more recently to bladder, liver, and lung cancer (Tseng et al., 1968). EPA has developed inhalation and oral cancer slope factors for arsenic of 15 (mg/kg/day)"1 and 1.75E+00 (mg/kg/day)'1 (IRIS, 1994), respectively. In developing the inhalation slope factor, a geometric mean was calculated from data sets obtained within distinct exposed populations. The final estimate is the geometric mean of those two values (IRIS, 1994). The oral slope factor was calculated using the unit risk of 5E-05 (ug/1)"1 proposed by the Risk Assessment Forum. This was based on an epidemiological study in Taiwan by Tseng et al. (1977) which indicated an increased incidence of skin cancer in individuals exposed to arsenic in drinking water. TUT 007 OO68 front' EPA (IRIS, 1994) developed an oral reference dose (RfD) of 3E-04 based on the Tseng et al. (1968) study which showed increased incidences of hyperpigmentation and keratosis with age and on the Tseng (1977) study. An uncertainty factor of 3 was used to develop the oral RfD. An inhalation reference concentration (RfC) has not been developed. TUT O07 OO69 RARTTTM Absorption of barium from the gastrointestinal tract following oral exposure has been estimated in one report to be approximately 5% for human adults (EPA, 1987). Specific studies on the extent of absorption of barium following inhalation exposure have not been conducted. However, systemic toxicity has been observed following inhalation exposure to this metal suggesting that absorption of barium from the respiratory tract occurs to some extent (EPA, 1984). Barium carbonate and more soluble barium compounds are quite toxic to humans following oral exposure. Doses of barium carbonate and barium chloride of 57 mg/kg and 12 mg/kg, respectively, have been reported to be fatal when ingested by humans. Adverse effects observed in humans following ingestion of barium have included gastroenteritis, muscular paralysis, hypertension, cardiotoxicity including ventricular fibrillation, and damage to the central nervous system (EPA, 1984; Perry et al., 1983). Chronic oral exposure of rats to barium has been observed to cause significant increases in blood pressure (EPA, 1984). Inhalation of barium sulfate or barium carbonate dust has been associated in occupationally exposed workers with baritosis, a benign pneumoconiosis (Goyer, 1986). Inhalation exposure of male rats to barium carbonate dust has produced such effects as decreased numbers of spermatozoids, decreased numbers of motile sperm forms, and increased fetal mortality TUT O07 O07O RAKTTTM (Cont'd) following mating of treating males with untreated females. Exposure of female rats has been associated with ovarian follicle atresia, increased mortality in subsequent litters, and a general underdevelopment of newborn pups (EPA, 1984). EPA (IRIS, 1994) derived an oral reference dose (RfD) for barium based on epidemiological studies by Wones et al. (1990) and Brenniman and Levy (1984), as well as on rodent studies conducted by Perry et al. (1983), McCauley et al. (1985), Schroeder and Mitchner (1975a, b), and Tardiff et al. (1980). In the Wones et al. (1990) study, barium in the form of barium chloride was administered in drinking water to human volunteers over a 10 week period. Subjects were given 1.5 liters/day of water containing 0, 5 or 10 mg/1 barium. As no increase in blood pressure was observed, the NOAEL of 10 mg/1 barium was identified which corresponds to 0.21 mg/kg/day based on an actual consumption rate of 1.5 liters/day and a 70 kg body weight. In the Brenniman and Levy (1984) study, no significant differences in human mortality and morbidity rates, blood pressure, hypertension prevalence, stroke, or heart and renal disease were observed between populations ingesting 2 to 10 mg/1 barium in drinking water and populations ingesting no or less than 0.2 mg/1 barium in drinking water. EPA does not believe that any single study is adequate to calculate an oral RfD for barium. Therefore, based on these studies, an oral RfD of 7E-02 mg/kg/day was derived using an uncertainty factor of 3 (IRIS, 1994). TUT OO7 OO71 BARIUM (Cont'd) A chronic inhalation reference concentration (RfC) of 5E-04 mg/m3 and converted reference dose of 1.4E-04 mg/kg/day for inhalation exposure to barium has also been derived by EPA (1994). This value was based on an inhalation study by Tarasenko et al. (1977) in which rats were exposed to barium carbonate dust at airborne concentrations of 1.15 mg/m3 for 4 hours/day for 4 months. Adverse effects noted at this concentration included decreased body weight, alterations in liver function, and increased fetal mortality. An uncertainty factor of 1000 was used to develop the chronic inhalation RfC. Barium has not been evaluated by EPA for evidence of human carcinogenic potential. TUT OO7 CK>72 RF.M7.F.MF. Benzene is readily absorbed into the body via ingestion and inhalation (EPA, 1985). The toxic effects of benzene vapors in humans and other animals include central nervous system effects, hematological effects, and immune system depression. In humans, acute exposure to high concentrations of benzene vapors can result in central nervous system effects such as dizziness, nausea, vomiting, headache, drowsiness, narcosis, coma, and death (NAS, 1976). Chronic exposure to benzene vapors can result in reduction in the number of leukocytes, platelets, or red blood cells (EPA, 1985). Benzene has produced solid tumors and leukemias in rats exposed by gavage (Maltoni et al., 1985). Many studies have also described a causal relationship between exposure to benzene (concentrations unspecified) by inhalation (either alone or in combination with other chemicals) and leukemia in humans (IARC, 1982). Benzene is classified by EPA in Group A, Human Carcinogen, based on adequate evidence of carcinogenicity from epidemiological studies. IRIS (1994) derived an inhalation cancer slope factor of 2.9E-02 (mg/kg/day)'1 for benzene based on epidemiological studies (Ott et al., 1978; Rinsky et al., 1981; Wong et al., 1983) in which significantly increased incidences of nonlymphotytic leukemia were observed in workers exposed to benzene principally by inhalation. The oral slope factor of 2.9E-02 (mg/kg/day)"1 was derived based on the same studies used to develop the inhalation slope factor. The oral and inhalation reference dose (RfD) and reference concentration (RfC) are currently undergoing review by EPA; however, the slope factors presented here were used in quantifying risks in this report. TUT 007 (-'O073 BFR-YTJJTTM Beryllium is a metal with a complicated chemistry, and it can form complexes, oxycarboxylates, and chelates with a variety of materials. Inhalation exposure to beryllium causes lung and bone cancer in animals, and epidemiological studies suggest that it may cause lung cancer in humans. Acute respiratory effects include rhinitis, pharyngitis, tracheobronchitis, and acute pneumonitis associated with inhalation of beryllium. Dermal exposure can cause contact dermatitis (Clement Associates, 1985). Beryllium has been reported to cause berylliosis (chronic granulomatous pulmonary disease), in which granulomatous lesions occur in the lungs. In the early stages, the lesions are filled with fluid. As the lesions progress, interstitial fibrosis increases with loss of functioning alveoli and effective air/capillary gas exchange resulting in increasing respiratory dysfunction (Casarett and Doull, 1986). Beryllium has been classified for carcinogenicity by EPA in Group B2 (Probable Human Carcinogen). An inhalation slope factor of 8.4E+00 (mg/kg/day)"1 was developed based on occupational exposure studies (IRIS, 1994). An oral slope factor of 4.3E+00 (mg/kg/day)"1 was developed based on studies from rats exposed to beryllium (5 ppm) in drinking water (Schroeder and Mitehener, 1975). An oral reference dose (RfD) of 5E-03 mg/kg/day was developed based on the same study, with an uncertainty factor of 100 applied. An inhalation reference concentration (RfC) has not been developed (IRIS, 1994). TUT OO7 OO74 rTTROTUTTTM Gastrointestinal absorption of chromium (III) is low, whereas chromium (VI) is more readily absorbed following oral exposure (EPA, 1987). Chromium is an essential micronutrient and is not toxic in trace quantities (EPA, 1980). High levels of soluble chromium (VI) and chromium (III) can produce kidney and liver damage following acute oral exposures, but target organs following chronic oral exposures have not been identified (EPA, 1984). Chronic inhalation exposures may cause respiratory system damage (EPA, 1984). Epidemiological studies of worker populations have clearly established that inhaled chromium (VI) is a human carcinogen, with the respiratory passages and the lungs as the target organs (EPA, 1984). Inhalation of chromium (III) and the ingestion of chromium (VI) or (III) have not been associated with carcinogenicity in humans or experimental animals (EPA, 1984). Certain chromium salts have been shown to be teratogenic and embryotoxic in mice and hamsters following intravenous or intraperitoneal injection (EPA, 1984). EPA has classified inhaled chromium (VI) for carcinogenicity in Group A (Human Carcinogen) (IRIS, 1994). Inhaled chromium (III) and ingested chromium (III) and (VI) have not been classified with respect to carcinogenicity. EPA (IRIS, 1994) has developed an inhalation unit risk of 1.2E-02 (ug/m3)'1 converted to an inhalation slope factor of 4.2E4-01 (mg/kg/day)"1 for chromium (VI) based upon an increased incidence of lung cancer in workers exposed to chromium over a 5 year period, and followed for approximately 40 years (Mancuso, 1975). TUT 007 O075 EPA (IRIS, 1994) has derived an oral reference dose (RfD) for chromium (VI) based on a study by MacKenzie et al. (1958). In this study, no adverse effects were observed in rats exposed to chromium (VI) at concentrations of 2.4 mg/kg/day in drinking water for one year. Using a NOAEL of 2.4 mg/kg/day and applying an uncertainty factor of 500, an oral RfD of 5E-03 mg/kg/day was derived (IRIS, 1994). An inhalation reference concentration (RfC) has not been developed. TUT OO7 OO76 Copper is an essential element. A daily copper intake of 2 mg is considered to be adequate for normal health and nutrition; the minimum daily requirement is 10 ug/kg (EPA, 1985). Adverse effects in humans resulting from acute overexposure to copper by ingestion includes salivation, gastrointestinal irritation, nausea, vomiting, hemorrhagic gastritis, and diarrhea (ACCGIH, 1986). Dermal or ocular exposure of humans to copper salts can produce irritation (ACGIH, 1986). Acute inhalation of dusts or mists of copper salts by humans may produce irritation of the mucous membranes and pharynx, ulceration o the nasal septum, an metal fume fever. The latter condition is characterized by chills, fever, headache, and muscle pain. Limited data are available on the chronic toxicity of copper; however, chronic overexposure to copper by humans has been associated with anemia (ACGIH, 1986). Evidence to date indicates that copper is not teratogenic in experimental animals (EPA, 1980) and various copper compounds are negative for mutagenicity in microbial assay systems (EPA, 1985). Results of several animal bioassays suggest that copper compounds are not carcinogenic by oral administration; however, some copper compounds can induce injection-site tumors in mice (EPA, 1985). EPA's Drinking Water Criteria document concluded that toxicity data were inadequate for calculation of an oral reference dose (RfD) for copper (EPA, 1994). TUT OO7 0077 riS/TR ANS-1,2-DTrHT fVROFTHFNF Cis-l,2-Dichloroethene (cis-l,2-DCE) is a colorless and flammable liquid that is often used as a chemical intermediate in the synthesis of chlorinated solvents. 1,2-DCE is often present as a mixture of both cis-1,2 and trans-l,2-DCE. This compound may be released to the environment from chemical factories, landfills, and industrial waste sites. It may also be present in the environment as a result of the degradation of other chlorinated solvents (ATSDR, 1990). Cis-l,2-DCE is expected to be rapidly absorbed via inhalation. In one study, rats exposed to cis- 1,2-DCE in air achieved equilibrium in the whole body within 1.5 to 2 hours (Filser et al., 1978). Several in vitro studies with isolated rat livers indicated that cis-DCE is metabolized to dichloroacetaldehyde, monochloroacetic acid, and 1,2-dichloroethanol by the rearrangement of epoxide intermediates. Based on the pharmacokinetics of similar chorinated compounds, cis-1,2- DCE is expected to be rapidly absorbed and excreted when ingested and inhaled (Jaegar et al., 1977). DCE has an oral LD50 in rats and mice ranging from 1275 mg/kg/day to 7902 mg/kg/day. Symptoms related to acute exposure to DCE in animals include pulmonary hyperemia, ataxia, depressed respiration, and CNS depression (Barnes et al., 1985; Freundt et al., 1977; Hayes et al., 1987). Human symptoms of acute exposure to trans-l,2-DCE in air include ocular irritation, dizziness, drowsiness, vertigo, and intracranial pressure (ATSDR, 1990). "UT 0078 T.TS/TRANTS-1 ,2-DTrm Animal studies involving intermediate exposure (14-90 days) to 1,2-DCE indicate the heart, liver, and lungs are the likely targets of toxicity. Inhalation exposure of rats to trans-DCE has resulted in pulmonary edema, alveolar septal distention, fibrous swelling in the heart, and fatty degeneration and lipid accumulation in the liver. Similar effects have been observed in rats orally exposed to trans-l,2-DCE (ATSDR, 1990). No data are available regarding the carcinogenicity of cis-1,2-DCE or trans-1,2-DCE from human or animal studies. Cis-l,2-DCE was not mutagenic with or without metabolic activation in several studies with E~ pnli K12, Sacchammyres rarevisiae D7, Chinese hamster cells, and Sftlmmiella typhimnrium. However, cis-DCE was mutagenic in mouse-host mediated assays with Salmonella typhimnrium and Saccharpmyces cerevisiae D7 (ATSDR, 1990). No teratogenicity studies in animals or humans have been conducted to date. EPA (1993) has developed an oral reference dose of 9.0E-03 based on a 2-year study conducted by Quast et al. (1983) in which rats given 1,2-dichloroethene (cis/trans) in drinking water developed liver lesions. An uncertainty factor of 1000 was applied in deriving this value. TUT OO7 0079 TF.AD Absorption of lead from the gastrointestinal tract of humans is estimated at 10 to 15 %. For adult humans, the deposition of paniculate airborne lead is 30 to 50%, and essentially all of the lead deposited is absorbed. Lead is stored in the body in bone, kidney, and liver (EPA, 1984). The major adverse effects in humans caused by lead include alterations in the hematopoietic and nervous systems. The toxic effects are generally related to the concentration of the metal in blood. Blood concentration levels of over 80 ug/L in children and over 100 ug/L in sensitive adults can cause severe, irreversible brain damage, encephalopathy and possible death. Lower blood concentrations of lead (30-40 ug/L) have been associated in humans with altered nerve conduction, altered testicular function, renal dysfunction, and anemia. Lead exposure also has been associated in humans with spontaneous abortions, premature delivery, and early membrane rupture; however, reliable exposure estimates are lacking in these cases. Decreased fertility, phytotoxic effects and skeletal malformations have been observed in experimental animals exposed to lead (EPA, 1984). EPA has classified lead as a Group B2 carcinogen (Probable Human Carcinogen) (IRIS, 1994). This category applies to those agents for which there is sufficient evidence of carcinogenicity in animals and inadequate evidence of carcinogenicity in humans. At present, the pharmacokinetics for lead do not allow an accurate estimate of the potential risks from exposure to lead, therefore, EPA recommends that a numerical estimate not be used. Oral ingestion of certain lead salts (lead acetate, lead phosphate, lead subacetate) has been associated in experimental animals with increased renal tumors, but no quantitative estimate of cancer potency TUT OO7 O08O LEAD (Cont'd) has been developed for these various lead compounds. Doses of lead that induced kidney tumors were high and were beyond the lethal dose in humans (EPA, 1985). EPA has noted that the available data provide an insufficient basis on which to regulate lead acetate, phosphate and subacetate as human carcinogens. EPA (IRIS, 1994) determined that health effects are apparent from exposure to lead at levels so low as to be essentially without a threshold. EPA's Reference Dose (RfD) work groups discussed this issue and considered it inappropriate to develop an oral RfD for inorganic lead. No data are available to develop an inhalation reference concentration (RfC). TUT OO7 OOS1 MAMflANPSP. Manganese is an essential element present in all living organisms. Daily manganese intake ranges from 2 to 9 mg although less than 5 percent is absorbed by the intestines. Acute inhalation exposure in the workplace (i.e., mining or manufacturing) to manganese may cause pneumonitis, a respiratory disease. Chronic inhalation of manganese dioxide in the workplace may result in the more serious central nervous system effects. Those who develop chronic manganese poisoning (manganism) exhibit a psychiatric disorder characterized by irritability, difficulty in walking, speech disturbances, and compulsive behavior. A Parkinson-like syndrome can develop if the condition persists. Recovery is slow, even when removed from excessive exposure (Goyer, 1986). EPA has classified manganese as a Class D carcinogen (not classifiable) (IRIS, 1994). EPA (IRIS, 1994) has developed two oral reference doses (RfDs) for manganese. An oral RfD of 5E- 03 mg/kg/day for manganese in water has been developed based on chronic human ingestion data (KondaMs et al. 1989) in which the criterial effect occurred to the central nervious system. A no- observed-adverse-effect-level (NOAEL) of 0.005 mg/kg/day and a lowest-observed-adverse-effect- level (LOAEL) of 0.06 mg/kg/day were identified in the study. EPA (IRIS, 1994) has developed an oral RfD of 1.4E-01 mg/kg/day for manganese in food based on several studies. An NOAEL of 0.14 mg/kg/day was identified. An uncertainty factor of 1 was used in developing the oral RfD in food. EPA (IRIS, 1994) has also developed an inhalation reference concentration (RfC) of 5E- 05 mg/m3 corresponding to an inhalation reference dose of 1.4E-05 mg/kg/day for manganese using an uncertainty factor of 1000. The RfC was derived based on TUT OO7 OO82 MAMftANTFSF. (Cont'd) an occupational study of workers exposed to manganese dioxide, tetroxide and various salts. The study indicated an increased prevalence of respiratory symptoms and psychomotor disturbances in exposed workers (Roels et al., 1987). TUT 007 0033 ^*^ MFTHYT. TF.KT-BTTTYT. F.TTTRR (MTRR) Methyl-tert-butyl-ether (MTBE), a synthetic flammable liquid made from combinations of such chemicals as isobutylene and methanol, has a distinctive disagreeable odor. It was first introduced as an additive for unleaded gasolines in the 1980s. In city areas where there are concerns over pollutants like carbon monoxide, the USEPA may require the use of either MTBE or ethanol as a cleaner burning oxygenating agent during the winter months. Since most MTBE is mixed with gasoline, people may come in contact with it while using automobile fuels. MTBE may be used as a laboratory chemical or in medicine to dissolve gallstones. (ATSDR, 1994). People exposed to MTBE while pumping gasoline, driving their cars, or working as attendants or mechanics at gas stations have reported headaches, nausea, dizziness, irritation of the nose or throat, and feelings of spaciness or confusion. These symptoms were reported when high levels of MTBE were added to gasoline to lower the amount of carbon monoxide, a known poison, released from cars. MTBE also caused side effects in some patients development or are acquired following repeated acute insults, such as hypersensitivity reactions, asthma, or chronic bronchitis. (ATSDR, 1994). In a chronic inhalation study (Chun et al., 1992), Fischer 344 rats (50 males, 50 females/group) were exposed to analytical mean concentrations of 403, 3023, or 7977 ppm methyl tertiary-butyl ether (MTBE) vapors (1453, 10,899, or 28,760 mg/cu.m) 6 hours/day, 5 days/week for 24 ,/•—x months (duration-adjusted values are 259, 1946, and 5136 mg/cu.m, respectively). The control animals breamed air. Survival times for females were not significantly different between exposed TUT OO7 OOS4 MTTTHYT. TFttT-RTTTYT FTHFJR (Cont'd) and control rats. A slight decrease in mean survival time was observed in the males exposed to the low concentration (controls, 632 days; low-concentration group, 617 days; p < 0.05). Survival time clearly decreased in males exposed to both the mid and high concentrations (mid- concentration group, 587 days; high-concentration group, 516 days; p < 0.01), leading to earlier sacrifice times at 97 and 82 weeks, respectively. According to study pathologists, chronic, progressive nephropathy was the main cause of death in the higher concentration groups and also contributed to a slight increase in mortality in the males exposed to the low concentration (Carman, 1993a, b). (IRIS, 1994). Information regarding death in animals was located only for rats and mice in ATSDR (1994). Acute inhalation 4-hour LCjo values in rats for two grades of MTBE were determined to be 39,395 ppm for ARCO MTBE (96.2% MTBE) and 33,370 ppm for commercial MTBE (99.1 % MTBE) (ARCO, 1980). An acute LC50 in mice following inhalation of MTBE for 10 minutes was determined to be 180,000 ppm (Snamprogetti, 1980). The LT50 (time at which death occurs in 50% of exposed animals) in mice following inhalation exposure to 209,300 ppm MTBE was 5.6 minutes. Intermittent inhalation exposure of Sprague-Dawley rats of both sexes to MTBE for 9 days to concentrations ranging from 100 to 3,000 ppm did not result in any treatment-related deaths (Biodynamics, 1981). Intermittent exposure of rats and mice for 13 days (Dodd and Kintigh, 1989) or to mice for 1 or 2 days (Vergnes and Kintigh, 1993) to concentrations .£.8,000 ppm MTBE was not lethal. TUT O07 OO85 MF.TTTVT. TKRT-BTTTYT. FTWF.R (Cont'd) Intermediate-duration exposure of rats and mice (5-10 minutes/day, 5 days/week for 30 days) to 50,000 and 80,000 ppm MTBE caused no mortality (Snamprogetti, 1980). Similarly, no mortality was observed in rats or mice exposed to j^.8,000 ppm MTBE 6 hours/day, 5 days/week for 4 or 5 weeks (Chun and Kintigh, 1993). No rats died during intermittent exposure to 1,000 ppm MTBE for 13 weeks (Greenough et al., 1980). In a 24-month inhalation study increased mortality and decreased mean survival time occurred in male rats exposed intermittently in 3,000 and 8,000 ppm MTBE (Chun et al., 1992). These groups were sacrificed at weeks 97 and 82, respectively. A slight increase in mortality and a significantly decreased mean survival time also occurred in the male rats exposed to 400 ppm (lowest concentration tested). This group was maintained until the scheduled sacrifice. Chronic progressive nephropathy was the main cause of death. In mice exposed to the same concentrations of MTBE for 18 months increased mortality and decreased mean survival time, due to a slightly increased incidence of obstructive uropathy, occurred in males at 8,000 ppm (Burleigh-Flayer et al., 1992). Although female rats had slightly more deaths from chronic progressive nephropathy (Chun et al., 1992), no significant increase in mortality occurred in the female rats and mice in these studies. (ASTDR, 1994). No studies were located in the literature, according to ATSDR (1994), regarding death in humans following inhalation exposure to MTBE. TUT OO7 OO86 MOTRYT. TFKT-RTTTYT. KTHF.R (Cont'd) An oral RfD for methyl tert-butyl ether is currently not available on the USEPA's on line IRIS data base or HEAST. A risk assessment for this substance is under review by a USEPA work group. (IRIS, 1994). Although limited information on human inhalation of MTBE is available, an inhalation RfC of 3E+0 mg/cu.m is reported in IRIS (1994) based on a chronic rat 24-month inhalation study performed by Chun, et al. 1992. Using an uncertainty factor of 100, an inhalation RfD of 9.0E- 01 mg/kg-day was derived for MTBE. TUT 007 OO87 2-MBTH YT .PHKNOT. 2-Methylphenol, also known as o-cresol, is naturally occurring in coal, petroleum, wood, and natural runoff. It is also found in artificial sources, such as roadway runoff, perfumes, oils, lubricants, and metal cleaning. 2-Methylphenol may be released into the environment in emissions and effluents during its production and use as a disinfectant and solvent. It may also be released in emissions or wastewater during coal tar and petroleum refining, organic chemicals, plastics, and resins manufacturing and in its use as an ore flotation and textile scouring agent. It is found in sewage and in emissions from wood pulping, tobacco smoke and auto and diesel exhaust. It is a product of photooxidation of toluene (EPA, 1993). 2-Methylphenol causes many symptoms in humans, including burning pain in the mouth and throat, white necrotic lesions in the mouth, esophagus, and stomach, abdominal pain, vomiting, and bloody diarrhea. Other symptoms include pallor, sweating, weakness, headache, dizziness, tinnitus, shock, weak and irregular pulse, hypotension, shallow respirations, cyanosis, and a profound fall in body temperature. If 2-methylphenol is spilled on the skin, pain is followed by numbness. The skin becomes blanched, and a dry opaque eschar forms over the burn. When the eschar sloughs off, a brown stain remains (EPA, 1993). 2-Methylphenol is classified by EPA in Group C, Possible Human Carcinogen, based on an increased incidence of skin papillomas in mice in an initiation-promotion study. The three cresol isomers produced positive results in genetic toxicity studies both alone and in combination (IRIS, 1994). Information concerning human carcinogenicity is inadequate, although some anecdotal TUT OO7 OOSS 9-MFTTTYT.PHFNrnT. (fnnf'ri) information is available. Garrett (1975) reported two cases of multifocal transitional cell carcinoma of the bladder following chronic occupational exposure to cresol and creosote. Wlodyka (1964, as cited in EPA, 1979) described a squamous cell carcinoma of the vocal cords in a petroleum refinery worker with a long history of exposure to cresol, dichlorooctane, and chromic acid. EPA has derived an oral reference dose (RfD) for 2-methylphenol of 5E-02 mg/kg/day (IRIS, 1994). An uncertainty factor of 1000 was used to develop the oral RfD. The oral RfD was based on two studies conducted with Sprague-Dawley rats. In a 90-day subchronic toxicity study (EPA, 1986), 30 Sprague-Dawley rats/sex/dose were gavaged daily with 0, 50, 175, or 600 mg/kg/day of o-cresol. At 600 mg/kg/day, o-cresol produced 47% combined mortality and a 30% reduction in body weight at week 1 and 10% at final sacrifice. At 450 mg/kg/day, combined mortality was 20%. In the 175 mg/kg/day group, two animals exhibited tremors on day 1 during the hours following gavage administration, and one of these animals became comatose during that time. At 50 mg/kg/day, no significant adverse effects were observed. In a 90-day neurotoxicity study (EPA, 1987), the lowest dose of o-cresol (50 mg/kg/day) given to Sprague-Dawley rats caused clinical signs of CNS-stimulation post dosing; however, these symptoms were low in incidence and sporadic in nature. In this study, 10 Sprague-Dawley rats/sex/dose were gavaged with o-cresol daily at 0, 50, 175, 450, or 600 mg/kg/day. Higher TUT OO7 OO89 THYT .PHF-NTnT. (Cont'd) doses of o-cresol (greater than 450 mg/kg/day) produced significant neurological events. High dosed animals showed abnormal patterns in the neurobehavorial tests. The NOAEL was based on systemic toxicity was 50 mg/kg/day in rats. Based on a review and assessment of the available literature, primarily studies conducted by Uzhdavini et al. (1972), NIOSH (1978) recommended a TLV-TWA of lOmg/cu.m. An RfD of 5E-02 mg/kg/day can also be derived from this value; this lends support to the RfD derived from the subchronic toxicity studies. TUT OO7 OO9O 4-XTFTH YT .PHF.MOT. 4-Methylphenol, also known as p-cresol, is naturally occurring in Acacia farnesiana, Ylang-Ylang oil, jasmine absolute, orange oil from leaves, the essence from flowers of Lilium candidum, anise- seed oil, the essence of Artemisia santnlinnfHa, and some sea algae. 4-Methylphenol may be released into the environment in emissions and effluents during its production and use as a disinfectant. It may also be released in emissions or wastewater during coal tar refining, metal refining, and chemical manufacturing. It is found in sewage and in emissions from wood pulping, brewing, tobacco smoke and auto and diesel exhaust. It is a product of photooxidation of toluene (EPA, 1993). 4-Methylphenol causes many symptoms in humans, including burning pain in the mouth and throat, white necrotic lesions in the mouth, esophagus, and stomach, abdominal pain, vomiting, and bloody diarrhea. Other symptoms include pallor, sweating, weakness, headache, dizziness, tinnitus, shock, weak and irregular pulse, hypotension, shallow respirations, cyanosis, and a profound fell in body temperature. If 4-methylphenol is spilled on the skin, pain is followed by numbness. The skin becomes blanched, and a dry opaque eschar forms over the burn. When the eschar sloughs off, a brown stain remains (EPA, 1993). 4-Methylphenol is classified by EPA in Group C, Possible Human Carcinogen, based on an increased incidence of skin papillomas in mice in an initiation-promotion study. The three cresol isomers produced positive results in genetic toxicity studies both alone and in combination (IRIS, 1994). Information concerning human carcinogenicity is inadequate, although some anecdotal TUT 007 0091 information is available. Garrett (1975) reported two cases of multifocal transitional cell carcinoma of the bladder following chronic occupational exposure to cresol and creosote. Wlodyka (1964, as cited in EPA, 1979) described a squamous cell carcinoma of the vocal cords in a petroleum refinery worker with a long history of exposure to cresol, dichlorooctane, and chromic acid. EPA has derived an oral reference dose (RfD) for 4-methylphenol of 5E-03 mg/kg/day (EPA, 1994). An uncertainty factor of 1000 was used to develop the oral RfD. TUT OO7 OO92 Nickel compounds can be absorbed following inhalation, ingestion, or dermal exposure. The amount absorbed depends on the dose administered and the chemical and physical form or the particular nickel compound (EPA, 1986). Adverse effects associated with acute exposure in animals have included depressed weight gain, altered hematological parameters, and increased iron deposition in blood, heart, liver, and testes (EPA, 1987). Chronic or subchronic exposure of experimental animals to nickel has been associated with reduced weight gain, degenerative lesions of the male reproductive tract, asthma, nasal septal perforations, rhinitis, sinusitis, hyperglycemia, decreased prolactin levels, decreased iodine uptake, and vasoconstriction of the coronary vessels. Dermal exposure of humans to nickel produces allergic contact dermatitis (EPA, 1986). Teratogenic and phytotoxic effects have been observed in the offspring of exposed animals (EPA, 1986). Certain nickel compounds are genotoxic in bacterial and mammalian assay systems (EPA, 1986). Inhalation exposure of experimental animals to nickel carbonyl or nickel subsulfide induces pulmonary tumors (EPA, 1986). Several nickel salts caused localized tumors when administered by subcutaneous injection or implantation. Epidemiological evidence indicates that inhalation of nickel refinery dust and nickel subsulfide is associated with cancers of the nasal cavity, lung, larynx, kidney, and prostate (EPA, 1986). There is no evidence that nickel is carcinogenic in animals or humans when the metal is ingested, and EPA (1987) does not consider nickel to be carcinogenic by the oral route. TUT OO7 0093 i. (Cont'd) EPA (IRIS, 1994) has derived an oral reference dose (RfD) for nickel (soluble salts) based on a study by Ambrose et al. (1976). In this study, rats were administered nickel in the diet for 2 years at concentrations of 0, 100, 1000, or 2500 pm. Decreased organ and body weights were observed at nickel concentrations greater than 1000 ppm diet (50 mg/kg/day). Using a NOAEL of 100 ppm diet (5 mg/kg/day) and applying an uncertainty factor of 300, an oral reference dose (RfD) of 2E- 02 mg/kg/day was derived (IRIS, 1994). An inhalation reference concentration (RfC) for nickel is under review by an EPA work group. "UT OO7 OO94 POT YfHT.nKTNATF.r> TUPHFNYT.S PCBs are very persistent in the natural environment and are readily bioaccumulated. Human exposure to PCBs has been associated with chloracne, impairment of liver function, a variety of neurobehavioral symptoms, menstrual disorders, minor birth abnormalities, and increased incidence of cancer (Clement Associates, Inc., 1985). PCBs have been given an EPA classification for carcinogenicity of B2 (Probable Human Carcinogen) based on hepatocellular carcinomas in three strains of rats and two strains of mice and inadequate yet suggestive evidence of excess risk of liver cancer in humans by ingestion and inhalation or dermal contact (IRIS, 1994). The slope factor developed for PCBs of 7.7E+00 (mg/kg/day)"1 is based on the studies performed by Norback and Weltman (1985). Sprague- Dawley rats were fed a diet containing Aroclor 1260 at 100 ppm for 16 months, followed by a 50 ppm diet for an additional 8 months, and then a basal diet for 5 months. Among animals that survived for at least 18 months, female rats exhibited a 91% incidence of hepatocellular carcinomas. In addition, the Norback and Weltman study is preferred over Kimbrough et al. (1974) because Sprague-Dawley rats are known to have low incidence of spontaneous hepatocellular neoplasms. This study spanned the natural life of the animal, and concurrent morphologic liver studies showed the sequential progression of liver lesions to hepatocellular carcinomas. Although it is known that PCB congeners vary greatly as to their potency in producing biological effects, for purposes of this assessment, Aroclor 1260 is intended to be representative of all PCB mixtures. An inhalation slope factor was not determined. No oral reference dose or inhalation reference concentration has been developed. TUT 007 0095 pnrvrvrT jr AKOMATrr HYPRorARRnNS (PAHS;) Polycyclic aromatic hydrocarbons (PAHs) occur in the environment as complex mixtures of many components with varying noncarcinogenic and carcinogenic potencies. Only a few components of these mixtures have been adequately characterized, and only limited information is available on the relative potencies of different compounds. The PAHs are often separated into two categories for risk assessment purposes: carcinogenic and noncarcinogenic PAHs. PAH absorption following oral exposure is inferred from the demonstrated toxicity of PAHs following ingestion (EPA, 1984a). PAH absorption following inhalation exposure is inferred from the demonstrated toxicity of PAHs following inhalation (EPA, 1984a). It has been suggested that simultaneous exposure to carcinogenic PAHs, such as benzo(a)pyrene, and particulate matter can increase the effective dose of the compound (ATSDR, 1987). PAHs are also absorbed following dermal exposure (Kao et ah, 1985). Acute effects from direct contact with PAHs and related materials are limited primarily to phototoxicity; the primary effect is dermatitis (NIOSH, 1977). PAHs have also been shown to cause cytotoxicity in rapidly proliferating cells throughout the body; the hematopoietic system, lymphoid system, and testes are frequent targets (Santodonato et al., 1981). Some of the noncarcinogenic PAHs have been shown to cause systemic toxicity but these effects are generally seen only at rather high doses (Santodonato et al., 1981). Slight morphological changes in the liver and kidneys of rats have been reported following oral exposure to acenaphthene. Oral TUT OO7 OO96 /*—N POT^Yrvri jr AKOMATTP HYDROCARBONS (PAHS) (Cont'd) administration of naphthalene to rabbits and rats has resulted in cataract formation (EPA, 1984b). Non-neoplastic lesions are seen in animals exposed to the more potent carcinogenic PAHs only after exposure to levels well above those required to elicit a carcinogenic response. Carcinogenic PAHs are believed to induce tumors both at the site of application and systemically. Neal and Rigdon (1967) reported that oral administration of benzo(a)pyrene led to forestomach tumors in mice. Thyssen et al. (1981) observed respiratory tract tumors in hamsters exposed to benzo(a)pyrene. Benzo(a)pyrene is representative of the carcinogenic PAHs and is classified by EPA as a B2 carcinogen (Probable Human Carcinogen) based on sufficient evidence of carcinogenicity from animal studies and inadequate evidence from epidemiological studies (IRIS, 1994). EPA (IRIS, 1994) calculated a value of 7.3E+00 (mg/kg/day)"1 for the slope factor for oral exposure to carcinogenic PAHs (specifically benzo(a)pyrene) based on the study by Neal and Rigdon (1967). In this study, mice given benzo(a)pyrene in the diet developed increased incidences of forestomach * tumors (IRIS, 1994). The oral slope factor is currently undergoing a reevaluation based on recalculation of the data. The slope factor for the carcinogenic PAH benzo(b)fluoranthene was calculated based on the benzo(a)pyrene slope factor and relative potency values. TUT OO7 OO97 AROMATIC Hvrranr APRONS (PAEk) (Cont'd) Benzo(b)fluoranthene is classified by EPA as a B2 carcinogen. This chemical produced tumors in mice after lung implantation, intraperitoneal or subcutaneous injection, and skin painting (IRIS, 1994). No human data specifically link exposure to benzo(b)fluoranthene to human cancers, although it is a component of mixtures that have been associated with human cancer (IRIS, 1994). An oral slope factor of 7.3E-01 (mg/kg/day)"1 was calculated by using a relative potency value of 0. 1 multiplied by the benzo(a)pyrene oral slope factor (EPA, 1993). TUT OO7 OO98 Tetrachloroethene (PCE) is a volatile, colorless, nonflammable liquid. It has widespread use as a solvent in dry cleaning operations, metal degreasing, and as a paint remover. In a National Cancer Institute bioassay (NCI, 1977), a high incidence of hepatocellular was observed in both sexes of B6C3Fj mice administered tetrachloroethylene in com oil by gavage five days per week for 78 weeks. Time-weighted average doses were 536 and 1,072 mg/kg/day in males and 386 and 772 mg/kg/day in females. No conclusion concerning the effects on Osborne- Mendel rats administered 471 to 949 mg/kg/day by gavage could be made because of high mortality rates and other technical flaws (NCI, 1977). NTP has reported the results of inhalation studies concerning carcinogenicity of tetrachloroethene. There was some evidence of carcinogenicity in F344/N rats (EPA, 1985a). Evidence of carcinogenicity was also observed in B6C3F, mice of both sexes (EPA, 1985a). The offspring of female rats and mice exposed to tetrachloroethene at 2,000 mg/m3 for seven hours daily on days 6-15 of gestation showed toxic effects, including a decrease in fetal body weight in mice and a small but significant increase in fetal resorptions in rats (EPA, 1985a,b). Mice also exhibited teratogenic effects, including subcutaneous edema and delayed ossification of skull bones and sternebrae (EPA, 1985a,b). TUT OO7 0099 .) (Cont'd) The principal toxic effects of tetrachloroethene in humans and laboratory animals from both acute and longer-term exposures include central nervous system depression and fatty infiltration of the liver and kidney with concomitant changes in serum enzyme activity levels indicative of tissue damage (EPA, 1985a; EPA, 1985b). Individuals exposed to concentrations of tetrachloroethene ranging from 6,258 to 10,600 mg/m3 experienced lassitude, mental fogginess, and exhilaration, progressing at the higher dose to signs of inebriation (EPA, 1980). Signs of central nervous system depression and cholinergic stimulation were also observed at concentrations of 1,622 mg/kg tetrachloroethene in an animal study in rabbits, monkeys, rats, and guinea pigs (EPA, 1980). Rats exposed to 1,600 mg/kg tetrachloroethene seven hours per day, five days per week, 18 times over 25 days exhibited central nervous system depression and hepatic and renal hypertrophy. Rats exposed to 230 mg/kg and 470 mg/kg tetrachloroethene, eight hours a day, five days a week over a period of seven months, exhibited congestion and swelling of kidneys and liver, respectively (Carpenter, 1937). Female Sprague-Dawley rats exposed to tetrachloroethene in air five days a week for 12 months at concentrations of 300 to 600 mg/kg showed liver atrophy, and high-dose females developed an increased incidence of fluid-filled cysts in the liver (EPA, 1980). TUT OO7 O100 TFTEAr.rn.nttOFTRF.NF. (PPF) (Cont'd) Fatty infiltration in livers and other liver function alterations were noted in mice, guinea pigs, and rabbits (EPA, 1985a; EPA, 1985b; NCI, 1977). Three of seven men occupationally exposed to tetrachloroethene at concentrations of 1,890 to 2,600 mg/m3 showed evidence of impaired liver function (EPA, 1980). Tetrachloroethene was formerly classified as a Group B2 carcinogen (EPA, 1985a). This classification is currently under reconsideration (IRIS, 1994). The decision whether tetrachloroethene will be classified as a Group B2 or Group C carcinogen is pending. Cancer slope factors for exposure to tetrachloroethene by ingestion and inhalation are currently under review but have been provided by the Superfund Health Risk Technical Support Center as 5.2E-02 (mg/kg/day)'1 and 2.0E-03 mg/kg/day, respectively (EPA, 1994). The oral RfD of IE-02 mg/kg/day (IRIS, 1994) is based on a study conducted by Buben and O'Flaherty (1985), in which Swiss-Cox mice were exposed to tetrachloroethene in corn oil by gavage at doses of 0, 20, 100, 200, 500, 1,500, and 2,000 mg/kg for 5 days/week for 6 weeks. Several parameters were monitored to evaluate liver toxicity, including liver weight/body weight ratio, hepatic triglyceride concentration, DNA content, histopathological evaluation and serum enzyme levels. At doses of 100 mg/kg, liver triglyceride levels and liver weight/body weight ratios were significantly higher than in control animals. The no observed adverse effect level TUT 007 010 ) (Cont'd) (NOAEL) of 20 mg/kg/day was adjusted for the treatment schedule of 5 days/ week to arrive at a NOAEL of 14 mg/kg/day. An uncertainty factor of 1,000 was applied to the NOAEL to account for intraspecies variability, interspecies variability, and extrapolation of a subchronic effect level to its chronic variability (IRIS, 1994). TUT 007 0102 TOT.TTP.NF. In humans, toluene is absorbed quickly through the respiratory tract; dermal absorption of aqueous toluene is directly related to concentration (EPA, 1985). In humans, the primary acute effects of exposure to toluene vapor are central nervous system (CNS) depression and narcosis; in experimental animals, acute oral and inhalation exposures to toluene can result in central nervous system depression and histological changes in the lungs, liver, and kidneys (EPA, 1987). In humans, chronic exposure to toluene vapors at levels if approximately 200 and 800 ppm has been associated with CNS and possibly, peripheral nervous system effects, hepatomegaly, and hepatic and renal functions changes (EPA, 1987). Toxic effects following prolonged exposure of ^ experimental animals to toluene are similar to those seen following acute exposure, predominantly to the CNS, liver, kidneys, and lungs (EPA, 1987). There is some evidence in experimental animals that oral and inhalation exposure to toluene during gestion results in embryotoxicity and skeletal malformations (Nawrot and Staples 1979; Hudak and Ungvary, 1978). EPA has classified toluene as a Class D carcinogen (Not Classifiable) (IRIS, 1994). EPA (IRIS, 1994) derived an oral reference dose (RfD) of 2E-01 mg/kg/day for toluene based on a 13-week rat gavage study (NTP, 1989); reporting changes in liver and kidney weight. A no-observed- adverse-effect-level (NOAEL) of 312 mg/kg (converted to 223 mg/kg/day) and an uncertainty factor of 1,000 was the basis for the RfD. EPA (IRIS, 1994) derived an inhalation reference concentration (RfC) of 4E-01 mg/m3 '"UT 007 TnT.TTF.NTF. (Cont'd) corresponding to an inhalation RfD of 1. IE-01 mg/kg/day. The RfC was based on the lowest- observed-adverse effect level (LOAEL) from two studies (Foo et al., 1990; NTP, 1990) and an uncertainty factor of 300. TUT O07 0104 TOTAT.PFTRnT F.TTM HYDRnrARRONTS (TPHs) Total petroleum hydrocarbons (TPHs) are petroleum distillates that include a variety of hydrocarbon mixtures. Gasoline, motor oil, kerosene, jet fuel, diesel fuel, red seal oil, and furniture polish are some examples of hydrocarbon mixtures (Klaassen et ah, 1986); ATSDR, 1993). Each of these hydrocarbon mixtures is composed of numerous organic chemicals that vary in contribution depending upon the manufacturing process. Gasoline, for example, typically contains more than 150 chemicals including benzene, toluene, and xylene, but varies in composition due to origin of the petroleum starting material, the manufacturer, and the time of year (ATSDR, 1993). The toxicity of the hydrocarbon mixture is generally indirectly proportional to its viscosity. Viscosity within the 30 to 35 range or lower represents an extreme aspiration risk. High viscosity, of 150 to 250 , signifies only limited aspiration risk and is present in heavy greases and oils. Oral ingestion of petroleum hydrocarbons is often associated with the following symptoms: mucous membrane irritation, vomiting, and central nervous system depression. Aspiration of petroleum hydrocarbons may cause cyanosis, tachycardia, and tachypnea with the subsequent development of chemical pneumonitis. Other symptoms of petroleum hydrocarbon exposure include albuminuria, cardiac arrhythmias (Klaassen et al., 1986). Oral doses as low as 10 ml have been reported as fatal, while reports of survival after the ingestion of 60 ml of petroleum distillates extist (Rumack, 1977 as cited in Klaassen et al., 1986). TUT OO7 0105 VANAHTTTM Limited information is available regarding the toxicity of vanadium. Pentavalent vanadium compounds are generally considered to be more toxic than vanadium compounds having other valence states. In humans, short-term and long-term occupational exposure to vanadium by inhalation has been associated with irritation of the respiratory tract, coughing, labored breathing, bronchitis, and chest pains. Vanadium is also reported to cause ocular and dermal irritation in humans. Adverse effects observed in experimental animals following such chronic inhalation exposure to vanadium have included renal, hepatic, and pulmonary lesions (NIOSH, 1977; NAS, 1974). EPA (1994) has established an oral reference dose (RfD) for vanadium of 7.0E-03 mg/kg/day. This value is based on a study by Schroeder et al. (1970) in which rats exposed to 5 ppm of vanadium in drinking water over a lifetime showed no adverse effects (EPA, 1994). An uncertainty factor of 100 was applied to develop the RfD. EPA has not developed inhalation criteria for vanadium. TUT 007 0106 VTNYT. r Vinyl chloride is a human carcinogen that causes angiosarcomas of the liver and tumors of the brain, lung, and hemolymphopoietic system. There is suggestive evidence that vinyl chloride has teratogenic and reproductive effects in both humans and animals. Chronic human exposure to vinyl chloride is associated with multiple systemic disorders, including a sclerotic syndrome, acro- osteolysis, and liver damage. Acute human exposure to high concentrations can cause narcosis, respiratory tract irritation, bronchitis, and memory disturbances. Chronic exposure by animals can result in lesions of the liver, kidneys, spleen, and lungs (Clement Associates, Inc., 1985). Vinyl chloride is classified as a Group A chemical (Human Carcinogen) (EPA, 1994). EPA (1994) has developed an oral slope factor of 1.9E+00 (mg/kg/day)"1 based on a dietary study in which rats fed vinyl chloride for 1001 days developed lung and liver tumors. An inhalation slope factor of 3E-01 (mg/kg/day)"1 has also been developed based on a rat study in which liver tumors resulted (EPA, 1994). Both slope factors are currently under review. No oral references doses (RfDs) or inhalation reference concentrations (RfCs) have been developed for vinyl chloride. TUT OO7 O1O7 REFERENCES Antimony Clement Associates, Inc. 1985. Chemical, Physical, and Biological Properties of Compounds Present at Hazardous Waste Sites. Final Report. September 27, 1985. Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency on-line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. Schroeder, H., Mitehener, M., and Nasor, A. 1970. Zirconium, niobium, antimony, vanadium and lead in rats: Life-term studies. J. Nutrition. 100:59-66. Arsenic Environmental Protection Agency (EPA). 1984. Health Assessment Document for Inorganic Arsenic. Office of Health and Environmental Assessment, Washington, D.C. March 1984. EPA 600/8-83-02 IF. Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency. On- line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. Tseng, W.P., Chu, H.M., How, S.W., Fong, J.M., Lin C.S., and Yeh, S. 1968. Prevalence of Skin Cancer in an Endemic Area of Chronic Arsenicism in Taiwan. J. Natl. Cancer Inst. 40:453-463. . Tseng, W.P. 1977. Effects and Dose-Response Relationships of Skin Cancer and Blackfoot Disease with Arsenic. Environ. Health Perspect. 19:109-119. Barium Brenniman, G. and Levy. P. 1984. High Barium Levels in Public Drinking Water and its association with Elevated Blood Pressure. In: Advances in Modern Toxicology IX, EJ. Calabrese, Ed. Princeton Scientific Publications, Princeton, N.J. pp. 231-249. Environmental Protection Agency (EPA). 1984. Health Effects Assessment for Barium. Environmental Criteria and Assessment Office, Cincinnati, Ohio. September 1984. EPA 540/1- 86-021. Environmental Protection Agency (EPA). 1987. Health Advisory for Barium. Office of Drinking Water, Washington, D.C. March 31, 1987. TUT 007 oioe REFERENCES (Cont'd) Environmental Protection Agency (EPA). 1994. Health Effects Assessment Summary Tables (HEAST) FY-1994 Annual Update. Office of Research and Development. OERR 9200.6-303- (94-1) March. Goyer, R. A. 1986. Toxic Effects of Metals. In: Casarett and Doull's Toxicology: The Basic Science of Poisons, 3rd Ed., Klaassen, C.D., Amdur, M.D. and Doull, J. (eds.). Macmillan Publishing Co., New York, Toronto, and London, pp. 623-624. Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency. On- line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. McCauley, P.T., Douglas, B.H., Laurie, R.D. and Bull, R.J. 1985. Investigations into the effect of drinking water barium on rats. Environ. Health Perspect. Vol. IX, E.J. Calabrese, Ed. Princeton Scientific Publications, Princeton, NJ. pp. 197-210. Perry, H.M., Kopp, S.J., Erlanger, M.W. and Perry, E.F. 1983. Cardiovascular effects of chronic barium ingestion. In: Trace Substances in Environmental Health, XVII, D.D. Hemphill, Ed. Proc. Univ. Missouri's 17th Ann. Conf. on Trace Substances in Environmental Health. University of Missouri Press, Columbia, MO. Schroeder, H.A. and Mitchener, M. 1975a. Life-term effects of mercury, methyl mercury and nine other trace metals on mice. J. Nutr. 105: 452-458. Schroeder, H.A. and Mitchener M. 1975b. Life-time studies in rats: Effects of aluminum, barium, beryllium, and tungsten. J. Nutr. 105: 421-427. Tardiff, R.G., Robinson, M. and Ulmer, N.S. 1980. Subchronic oral toxicity of BaC12 in rats. J. Environ. Pathol. Toxicol. 4: 267-275. Tarasenko, M., Promin, O., and Silayev, A. 1977. Barium Compounds as Industrial Poisons (an experimental study). J. Hyg. Epiderm. Microbial. Immunol. 21:361. As cited in EPA, 1984. Wones et al. 1990. Lack of Effect of Drinking Water Barium on Cardiovascular Risk Factor. Environ. Health Perspect. 85:1-13. Environmental Protection Agency (EPA). 1985. Drinking Water Criteria Document for Benzene (Final Draft). Office of Drinking Water, Washington, D.C. April 1985. TUT OO7 01O9 PF.FFRP.NrRS (Cont'd) Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency on-line data base toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. International Agency for Research on Cancer (IARC). 1982. IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans. Volume 27: Some Aromatic Amines, Anthraquinones and Nitroso Compounds, and inorganic Fluorides Used in Drinking Water and Dental Preparations, World Health Organization, Lyon, France. Maltoni, C., Conti, B., Cotti, G., and Belpoggi, F. 1985. Experimental studies on benzene carcinogenicity at the Bologna Institute of Oncology: Current results and ongoing research. Am. J. Ind. Med. 7:415-446. National Academy of Science (NAS). 1976. Health Effects of Benzene: A Review Committee on Toxicology, Assembly of Life Sciences. National Research Council, Washington, D.C. Ott, M., Townsend, J., Fishbeck, W., and Langner, R. 1978. Mortality among individuals occupationally exposed to benzene. Arch. Environ. Health 33:3-10. Rinsky, R., Young, R., and Smith, A. 1981. Leukemia in benzene workers. Am. J. Ind. Med. 3:217-245. Wong, O., Morgan, R., and Whorton, M. 1983. Comments on the NIOSH Study of Leukemia in Benzene Workers. Technical Report Submitted to Gulf Canada, Ltd., by Environmental Health Associates, August 31. Cited in EPA 1985. Beryllium Clement Associates, Inc. 1985. Chemical, Physical, and Biological Properties of Compounds Present at Hazardous Waste Sites. Final Report prepared for U.S. EPA. September 27, 1985. Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency. On- line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. Klaassen, C., Amdur, O., and Doull, J. (Eds). 1986. Casarett and Doull's Toxicology. The Basic Science of Poisons. Third Edition. Macmillan Publishing Co., New York. Schroeder, H.A. and M. Mitchner. 1975. Life-term studies in Rats: Effects of Aluminum, Barium, Beryllium and Tungsten. J. Nutr. 105:421-427. TUT OO7 O11O S (Cont'd) Chromium Environmental Protection Agency (EPA). 1980. Ambient Water Quality Criteria for Chromium. Office of Water Regulations and Standards, Washington, D.C. EPA 440/5-80-035. Environmental Protection Agency (EPA). 1984. Health Assessment Document for Chromium. Environmental Criteria and Assessment Office. Research Triangle Park, North Carolina. EPA 600/8-83-014F. Environmental Protection Agency (EPA). 1987. Draft Health Advisory for Chromium. Office of Drinking Water, Washington, D.C. March 31, 1987. Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency. On- line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. Mackenzie, R.D., Byerrum, R.U., Decker, C.F., Hoppert, C.A., and Longham, R.F. 1958. Chronic Toxicity Studies II. Hexavalent and Trivalent Chromium Administered in Drinking Water to Rats. Am. Med. Assoc. Arch. Ind. Health. 18:232-234. As cited in IRIS, 1993. Mancuso, T.F. 1975. International Conference on Heavy Metals in the Environment, Toronto, Canada. As cited in EPA 1984. American Conference of Governmental Industrial Hygienists (ACGIH). 1986. Documentation of the Treshold Limit Values and Biological Exposure Indices, 5th Ed. Cincinnati, Ohio. Environmental Protection Agency (EPA). 1980. Ambient Water Quality Criteria for Copper. Office of Water Regulations and Standards, Criteria and Standards Division, Washington, D.C. October 1980. EPA 440/5-80-036. Environmental Protection Agency (EPA). 1985. National Primary Drinking Water Regulations; Synthetic Organic Chemicals, Inorganic Chemicals and Microorganisms. 40 CFR Part 141 Fed. Reg. 50:46967-47025 (November 13, 1985). Environmental Protection Agency (EPA). 1994. Health Effects Assessment Summary Tables (HEAST) FY-1994 Annual Update. Office of Research and Development. OERR 9200.6- 303(94-1). March. TUT OO7 Oil! EF.FF.ttF.MrRS (Cont'd) Tis/Trans-1 2-nic Agency for Toxic Substances and Disease Registry (ATSDR). 1990. lexicological Profile for cis-l,2-Dichloroethene, trans-l,2-Dichloroethene, 1,2-Dichloroethene. U.S. Public Health Service 1990. Barnes D.W., Sanders, V.M., White, K.L. Jr. et al. 1985. Toxicology of trans-1,2- dichloroethylene in the mouse. Drug Chem. Toxicol. 8:373-392. Filser J.G., Bolt, H.M., Kimmich K. et al. 1978. Exhalation of acetone by rats on exposure to trans-l,2-dichloroethene and related compounds. Toxicol. Lett. 2:247-252. Freundt K.G., Liebaldt G.P., and Lieberwirth E. 1977. Toxicity studies on trans-1,2- dichloroethylene. Toxicology 7:141-153. Hayes, J.R., Condie L.W. Jr., Egle J.L. Jr. et al. 1987. The acute and subchronic toxicity in rats of trans-l,2-dichloroethylene in drinking water. J.A. Coll. Toxicol. 6:471-478. Henschler, D., Hoos, R. Metaboolic activation and deactivation mechanisms of di, tri, and tetrachloroethylenes. InSnyder, R. etal., Eds. Biological Reactive Intermediates-II: Chemical Mechanisms and Biological Effects. Plenum Press, New York. pp. 659-666. Jaeger, R.J., Shoner, L.H., and Coffman, L. 1977. 1,1-Dichloroethylene hepatotoxicity: Proposed mechanism of action and distribution and binding of 14C radioactivity following inhalation exposure in rats. Environ. Health Perspec. 21:113-119. Quast et al. 1983. A Chronic Toxicity and Oncogenicity Study in Rats and Subchronic Toxicity Study in Dogs on Ingested Vinylidene Chloride. Fund Appl. Toxicol 3(1): 55-62. Environmental Protection Agency (EPA). 1984. Health Effects Assessment for Lead. Environmental Criteria and Assessment Office, Cincinnati, Ohio. EP A/540/ 1-86-055. Environmental Protection Agency (EPA). 1985. National Primary Drinking Water Regulations; Synthetic Organic Chemicals, Inorganic Chemicals and Microorganisms; Proposed Rule. 40 CFR Part 141. Fed. Reg. 50:46967-47025 (November 13, 1985). Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency. On- line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. June. TUT 007 011.2 FRRFNrFS (Cont'd) Manganese Goyer, R.A. 1986. Toxic Effects of Metals. In: Casarett and Doull's Toxicology: The Basic Science of Poisons 3rd ed. Klaassen, C., Amdur, M. and Doull, J. (ed). Macmillan Publishing Co., New York, Toronto and London, p. 614. Integrated Risk Information System (IRIS). 1994. U.S. Environmental Protection Agency. On- line data base of toxicity measures. Office of Research and Development, Environmental Criteria and Assessment Office, Cincinnati, OH. August. Kondakis, et al. 1989. Possible Health Effects of High Manganese Concentration in Drinking Water. Arch. Environ. Health. 44:175-178. Roels, H., Lauwerys, R., Buchet J.P. et al. 1987. Epidemiological Survey Among Workers Exposed to Manganese: Effects on Lung, Central Nervous System, and Some Biological Indices. Am. J. Ind. Med. 11:307-327. Methyl fert-Rntyl Kther Agency for Toxic Substances and Disease Registry (ATSDR). 1994. Toxicological Profile for Methyl-t-Butyl Ether (Draft). U.S. Public Health Service, August 1994. ARCO Chemical Company. 1980. Methyl tertiary-butyl ether: acute lexicological studies. Unpublished study from ARCO Research and Development, Glenolden, PA. Biodynamics Inc. 1981. Nine day inhalation toxicity study of MTBE in the rat. Project no. 80-1452. East Millstone, NJ: Unpublished report submitted to American Petroleum Institute, Washington, DC. Burleigh-Flayer H.D., Chun J.S., Kintigh W.J. 1992. Methyltertiary butyl ether: vapor inhalation oncogenicity study in CD-10 mice. Bushy Run Research Center, Export PA. Chun J.S., Burleigh-Flayer H.D., Kintigh W.J. 1992. Methyl tertiary butyl ether: vapor inhalation oncogenicity study in Fischer 344 rats. Bushy Run Research Center, Export, PA. Project No. 91N0013B. Chun J.S., Kintigh W.J. 1993. Methyl tertiary butyl ether: twenty-eight day vapor inhalation study in rats and mice. Laboratory project ID 93N1241. Bushy Run Research Center, Export, PA. (unpublished study to be peer reviewed). TUT OO7 Oil3 ./—N. REEERENCES-(Cont'd) DoddD.E.,KnitighWJ. 1989. Methyl tertiary butyl ether (MTBE): Repeated (13- week) vapor inhalation study in rats with neurotoxicity evaluation (unpublished study). Union Carbide, Bushy Run Research Center, Export, PA. Environmental Protection Agency (EPA). 1991. Alpha-2u-globulin: Association with chemically induced renal toxicity and neoplasia in the male rat. Risk Assessment Forum. EPA/625/3- 91/019F. Carman, R.H. 1993a. Bushy Run Research Center. Correspondence to Larry S. Andrews of ARCO Chemical Company. May 3. Carman, R.H. 1993b. Bushy Run Research Center. Correspondence to Larry S. Andrews of ARCO Chemical Company. Mary 15. Greenough R.J., McDonald P., Robinson P., et al. 1980. 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TUT 007 0120 APPENDIX C SPREADSHEET CALCULATIONS TUT OO7 O121 10/28*4 SS-IN-RES.XLS TABLE C-1 7 ' ' SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake- Soil X (mg/kg-day) Concentration mg/kg X Soil Chemicals Concentration Arock>H242 1.20E+02 Arsenic 1.00E+01 Ingestion Rate 100 mg/day Ingestion Rate 100 100 X Conversion X Factor X 1kg X 1000000 mg Conversion Factor 1.0E-06 1.0E-06 Fraction Ingested 1 (unitless) Fraction Ingested 1 1 X Exposure X Frequency X 350 days/year X Exposure Frequency 350 350 Exposure X Duration 24 years X Exposure Duration 24 24 1 Body Weight 1 70kg Body Weight 70 70 X 1 Averaging Time X 1 25550 days Averaging Chronic Daily Slope Time Intake (GDI) Factor (SF) 25550 5.6E-05 7.7E+00 25550 4.7E-06 1.75E+00 TOTAL RISK - RISK = (CDI*SF) 4.3E-04 8.2E-06 4.4E-04 CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Children (0 - 6 years) H H Oq o H- Chronic Daily Intake. Soil X (mg/kg-day) Concentration mg/kg X Soil Chemicals Concentration Arock>H242 1.20E+02 Arsenic 1.00E+01 Ingestion Rate 200 mg/day Ingestion Rate 200 200 X Conversion X Factor X 1kg X 1000000 mg Conversion Factor 1.0E-06 1.0E-06 Fraction Ingested 1 (unitless) Fraction Ingested 1 1 X Exposure X Frequency X 350 days/year X Exposure Frequency 350 350 Exposure X Duration 6 years X Exposure Duration 6 6 1 Body Weight 1 15kg Body Weight 15 15 X 1 Averaging Time X 1 25550 days Averaging Chronic Daily Slope Time Intake (GDI) Factor (SF) 25550 1.3E-04 7.7E+00 25550 1.1E-05 1.75E+00 TOTAL RISK » 30-YEAR COMBINED RISK (ADULT -i- CHILD) * ' RISK = (CDI'SF) 1.0E-03 1.9E-05 1.0E-03 1.5E-03 10/28/94 SS-IN-RES.XLS TABLE C-1 7 •' i SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION Chronic Daily Intake- Soil X Ingestion X Conversion X Fraction (mg/kg-day) Concentration Rate Factor Ingested mg/kg X 100 mg/day X 1 kg X 1 Chemicals Antimony Arsenic Manganese Vanadium Soil Concentration 5.05E+00 1.00E+01 8.69E+02 9.59E+01 Ingestion Rate 100 100 100 100 1000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 (unitless) Fraction Ingested 1 1 1 1 EXPOSURE: Adults X Exposure X Exposure Frequency Duration X 350 days/year X 24 years Exposure Frequency 350 350 350 350 Exposure Duration 24 24 24 24 X 1 Body Weight X 1 70kg Body Weight 70 70 70 70 X 1 Averaging Time X 1 8760 days Averaging Time 8760 8760 8760 8760 Chronic Daily Intake (CDI) 6.9E-06 1.4E-05 1.2E-03 1.3E-04 Reference Dose (RfD) 4.0E-04 3.0E-04 5.0E-03 7.0E-03 HAZARD INDEX - NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION Chronic Daily Intake- (mg/kg-day) Chemicals Antimony Arsenic Manganese Vanadium Soil X Concentration mg/kg X Soil Concentration 5.05E+00 1.00E+01 8.69E+02 9.59E+01 Ingestion Rate 200 mg/day Ingestion Rate 200 200 200 200 X Conversion X Factor X 1kg X 1 000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 Fraction Ingested 1 (unitless) Fraction Ingested 1 1 1 1 HQ= CDI/RfD 1.7E-02 4.6E-02 2.4E-01 1.9E-02 3.2E-01 EXPOSURE: Children (0-6 years) X Exposure X Frequency X 350 days/year X Exposure Frequency 350 350 350 350 Exposure Duration 6 years Exposure Duration 6 6 6 6 X 1 Body Weight X 1 15kg Body Weight 15 15 15 15 X 1 Averaging Time X 1 21 90 days Averaging Time 2190 2190 2190 2190 30-YEAR COMBINED Chronic Daily Intake (CDI) 6.5E-05 1.3E-04 1. IE-02 1.2E-03 Reference Dose (RfD) 4.0E-04 3.0E-04 5.0E-03 7.0E-03 HAZARD INDEX . HAZARD (ADULT + CHILD) = i HQ» CDI/RfD 1.6E-01 4.3E-01 2.2E+00 1.8E-01 3.0E+00 3.3E+00 o H- HV2SW SS-DC-RES.XLS TABLE C-2 SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lnlake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X (mg/kg-day) Chemicals Aroclor 1242 Concentration mg/kg X Soil Concentration 1.20E+02 Factor 1kg X 1000000 mg Conversion Factor 1.0E-06 Area 5065 cm2/day Skin Surface Area 5065 Factor X 1mgfcm2 Adherence Factor 1 Factor X (unitless) Absorption Factor 0.06 Frequency X 350 events/year Exposure Frequency 350 Duration X 24 years Exposure Duration 24 Body Weight Averaging Time X 1 X 1 70kg 25550 days Body Averaging Weight Time 70 25550 Chronic Daily Intake (CDI) 1.7E-04 Slope Factor (SF) 7.7E+00 RISK = (CDI'SF) 1.3E-03 TOTAL RISK = 1.3E-03 CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Children (0-6 years) Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X 1 (mg/kg-day) Chemicals Aroclor 1242 Concentration mg*g X Soil Concentration 1.20E+02 Factor 1kg X 1000000 mg Conversion Factor 1.0E-06 Area 1270cm2/day Skin Surface Area 1270 Factor X 1 mg/cm2 Adherence Factor 1 Factor X (unitless) Absorption Factor 0.06 Frequency X 350 events/year Exposure Frequency 350 Duration X 6 years Exposure Duration 6 Body Weight Averaging Time X 1 X 1 15kg 25550 days Body Averaging Weight Time 15 25550 Chronic Daily Intake (CDI) 5.0E-05 Slope Factor (SF)' 7.7E+00 RISK = (CDI'SF) 3.9E-04 H C O TOTAL RISK - 3.9E-04 30-YEAR COMBINED RISK (ADULT + CHILD)« 1.7E-03 O !-=• 1(V2»94 ' TABLE C-2 SSDC-RES.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS • REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X 1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mgfcg. X 1kg X 5065cm2/day X 1 mg/cm2 X (uniUess) X 350 events/year X 24 years X.I X 1 1000000 mg 70kg 8760 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Reference HQ= Chemicals_______Concentration Factor_____Area_____Factor___Factor____Frequency Duration Weight______Time____Intake (GDI) Dose (RfD) GDI/RID A chronic noncarcinogenic oral reference dose is not currently established for Aroclor 1242. NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Children (0-6 years) Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X 1 (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1kg X 1270cm2/day X 1 mg/cm2 X (unittess) X 350 events/year X 6 years X 1 X 1 1000000 mg 15kg 2190 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Reference HQ= Chemicals_______Concentration Factor_____Area_____Factor___Factor____Frequency Duration Weight_____Time____Intake (GDI) Dose (RID) CDI/RfD A chronic noncarcinogenic oral reference dose is not currently established for Aroclor 1242. I H O O 1W2OT4 •' 1 TABu_ J-3 SS-IH-RES1.XLS SURFACE SOIL INHALATION OF PARTICULATES PATHWAY / • TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO RESIDENTS (INSIDE AND OUTSIDE RESIDENCE) IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adults Susp. Chronic Daily Intake^ Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mgfeg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor mg/kg X 0.070 mo/m3 X (unitless) X 0.83 m3/hr X 18 hrs'day X 350 days/yr X 24 years X 1 kg 1000000 mg Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Chemicals Concen. Concen. Fraction Rate Time Frequency Duration Factor Arsenic 1.00E+01 7.0E-02 0.75 0.83 18 350 24 1.0E-06 CARCINOGENS • REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Children (04 ywr.) Susp. Chronic Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mg/kg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor mg/kg X 0.070 mo/mS X (unitless) X 0.83 m3/hr X 18 hrs'day X 350 days/yr X 6 years X 1 kg 1000000 mg Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Chemicals Concen. Concen. Fraction Rate Time Frequency Duration Factor Arsenic 1.00E+01 7.0E-02 0.75 0.83 18 350 6 1.0E-06 d H O O si O k) X 1 X 1 BodyWt AvgingTime X 1 X 1 70 kg 25550 days Body Averaging Chronic Daily Slope Weight Time Intake (GDI) Factor (SF) 70 25550 3.7E-08 1.50E+01 TOTAL RISK = X 1 X 1 BodyWt AvgingTime X 1 X 1 15kg 2190 days Body Averaging Chronic Daily Slope Weight Time Intake (CDI) Factor (SF) 15 25550 4.3E-08 1.50E+01 TOTAL RISK = 30- YEAR COMBINED RISK (ADULT + CHILD) = RISK = (CDI'SF) 5.5E-07 5.5E-07 ,RISK = (CDI'SF) 6.4E-07 6.4E-07 1.2E-06 SS-IH-RES1.XLS i TABui. C-3 SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO RESIDENTS (INSIDE AND OUTSIDE RESIDENCE! IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE - Adult* Chronic Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X (mgftg-day) Concen. Conoen. Fraction Rate Time Frequency Duration Chemicals Manganese mg/kg Soil Concen. 8.69E+02 X 0.070 mg/m3 Susp. Soil Conoen. 7.0E-02 X (unilless) X 0.83 m3/hr X Resp. Inhalation Fraction Rate 0.75 0.83 18 hrs/day X Exposure Time 18 350 days/yr X 24 years X Exposure Exposure Frequency Duration 350 24 Conv. X Factor 1kg X 1000000 mg Conv. Factor 1.0E-06 1 BodyWt 1 70kg Body Weight 70 X 1 Avging Time X 1 8760 days Averaging Time 8760 Chronic Daily Intake (CDI) 9.3E-06 Reference Dose (RfD) 1.4E-05 HAZARD INDEX = NONCARCINOGENS - Chronic Daily Intake^ (mg/kg-day) Chemicals Manganese HQ= CDI/RfD 6.7E-01 6.7E-01 REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE - Children (0-6 years) Soil Concen. mg/kg Soil Concen. 8.69E+02 X Soil Concen. X 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 X Resp. X Inhalation X Fraction Rate X (unitless) X 0.83 m3/hr X Resp. Inhalation Fraction Rate 0.75 0.83 Exposure X Time 18 hrs/day X Exposure Time 18 Exposure X Exposure X Frequency Duration 350 days/yr X 6 years X Exposure Exposure Frequency Duration 350 6 Conv. X Factor 1kg X 1000000 mg Conv. Factor 1.0E-06 1 BodyWt 1 15kg Body Weight 15 X 1 Avging Time X 1 2190 days Averaging Time 2190 Chronic Daily Intake (CDI) 4.4E-05 Reference Dose (RfD) 1.4E-05 HAZARD INDEX = 30-YEARCOKffilNED HAZAFID INDEX (ADUILT + CHILD) = ) HQ= CDI/RfD 3.1E+00 3.1E+00 3.8E+00 p w-J 10/58/94 TABLE C-4 SS-IN-SWTEX.XLS SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake- Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X___1___X____1_____ (mg/kg-day) Concentration Rate Factor Ingested Frequency Duration Body Weight Averaging Time mg/kg X 50mg/day X 1kg X 1 X 250 days/year X 25 years X 1 X 1 1000000 mg (unitiess) 70kg 25550 days Soil Ingestion Conversion Fraction Exposure Exposure Body Averaging Chronic Daily Slope RISK = Chemicals_______Concentration___Rate______Factor___Ingested Frequency Duration___Weight_____Time____Intake (GDI) Factor (SF) (CDI'SF) Benzo(b)fluoranthene 8.70E-01 50 1.0E-06 1 250 25 70 25550 1.5E-07 7.3E-01 1.IE-07 Benzo(a)pyrene 7.70E-O1 50 1.0E-06 1 250 25 70 25550 1.3E-07 7.3E+00 9.8E-07 Beryllium 2.60E-01 50 1.0E-06 1 250 25 70 25550 4.5E-08 4.3E+00 2.0E-07 TOTAL RISK- 1.3E-06 C H Oo •--I 10/26/34 SS-IN-SWTEX.XLS TABLE C-4 SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake* (mg/kg-day) Soil X Ingestion X Conversion X Fraction X Concentration Rate Factor Ingested Exposure X Exposure X Frequency 1 1 Duration Body Weight Averaging Time Chemicals Antimony Beryllium Manganese Vanadium mg/kg . X Soil Concentration 5.90E+00 2.60E-01 8.34E+02 1.19E+02 50 mg/day Ingestion Rate 50 50 50 50 X 1kg X 1 X 250 days/year X 25 years X 1000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 (unitiess) Fraction Ingested 1 1 1 1 Exposure Frequency 250 250 250 250 Exposure Duration 25 25 25 25 1 X 1 70kg Body Weight 70 70 70 70 9125 days Averaging Time 9125 9125 9125 9125 Chronic Daily Intake (CDI) 2.9E-06 1.3E-07 4.1E-04 5.8E-05 Reference Dose (RfD) 4.0E-04 5.0E-03 5.0E-03 7.0E-03 HQ= CDI/RfD 7.2E-03 2.5E-05 8.2E-02 8.3E-03 HAZARD INDEX- 9.7E-02 —i C H- W •-0 s T*m c rL«; ../ BW94 ' TABLE C-5 SS-DC-SWTEX.XLS SURFACE SGML DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE FIRE DEPT/TEXACQ GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adult. Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X_ (mg/kg-day) Chemicals Concentration mg/kg X Soil Concentration Factor Ikfl X 1000000 mg Conversion Factor Area 1940 cm2/day Skin Surface Area Factor X 1 mg/cm2 Adherence factor Factor Frequency X (unittess) X 250 events/year Absorption Exposure Factor Frequency . Duration X 25 years Exposure Duration Body Weight X 1 70kg Body Weight Averaging Time X 1 25550 days Averaging Time Chronic Dairy Intake (CDI) Slope Factor (SF) RISK = (CDI'SF) No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. O O ••4 BW94 TABLE C-5 SS-DC-SWTEX.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adult. Chronic Daily lntake= (mgfcgxtay) Chemicals Concentration Factor Area Factor Factor Frequency mg/kg X 1kg X 1940cm2/day X 1 mg/cm2 X (unitfess) X 250 events/year 1 000000 mg Soil Conversion Skin Surface Concentration Factor Area Adherence Absorption Factor Factor Exposure Frequency Duration X 25 years X Exposure Duration Body Weight Averaging Time 1 X 1 70kg Body Weight 91 25 days Averaging Time Chronic Daily Reference Intake (GDI) Dose(RfD) HQ= CDt/RfD No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. H oo . KKWW / ( TAl. y-6 SS-IH-SWTEXJ(L3 SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE FIRE DEPT^EXACQ GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adults Susp. Chronic Daily lntake= Soil X Soil X Rasp. X Inhalation X Exposure X Exposure X Exposure X Conv. X 1 X 1 (mg/kg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime mg/kg X 0.070 mg/m3 X (unitless) X 0.83 m3/hr X 8 hrs/day X 250 daysfyr X 25 years X 1 kg XIX 1 1000000 mg 70kg 25550 days Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Body Averaging Chronic Daily Slope RISK = Chemicals________Concen. Concen. Fraction Rate_____Time Frequency Duration Factor___Weight___Time Intake (GDI) Factor (SF) (CDI'SF) Beryllium 2.60E-01 7.0E-02 0.75 0.83 8 250 25 1.0E-06 70 25550 3.2E-10 8.4E+00 2.7E-09 TOTAL RISK = 2.7E-09 i TAu /J-6 SS-IH-SWTEX.XLS SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adult* Susp. Chronic Daily Intake* Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. X__1_ (mg/kg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime mg/kg X 0.070 mg/m3 X (unittess) X 0.83 m3/hr X 8 hrs/day X 250 days/yr X 25 years X 1 kg XIX 1 1000000 mg 70kg 9125 days Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Body Averaging Chronic Daily Reference HQ= Chemicals________Concen. Concen. Fraction Rate____Time Frequency Duration___Factor___Weight Time Intake (GDI) Dose(RtD) CDl/RfD Manganese 8.34E+02 7.0E-02 0.75 0.83 8 250 25 1.0E-06 70 9125 2.8E-06 1.4E-05 2.0E-01 HAZARD INDEX = 2.0E-01 Nj O M. W W io/2B®4 SS-IN-SWCURR.XLS TABLE C-7 SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake* Soil X Ingestion X Conversion X Fraction X Exposure X (mg/kg-day) Concentration Rate Factor Ingested Frequency ma/kg X 50 mg/day X 1 kg X 1 X 250 days/year X Chemicals Arsenic Beryllium Soil Concentration 1.16E+01 2.40E-01 Ingestion Rate 50 50 1000000 mg Conversion Factor 1.0E-06 1.0E-06 (unidess) Fraction Ingested 1 1 Exposure Frequency 250 250 Exposure Duration 25 years Exposure Duration 25 25 X 1 Body Weight X 1 70kg Body Weight 70 70 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 Chronic Daily Intake (GDI) 2.0E-06 4.2E-08 Slope Factor (SF) 1.75E+00 4.3E+00 RISK** (CDI*SF) 35E-06 1.8E-07 TOTAL RISK. 3.7E-06 10/28/84 TABLC C-7 SS-IN-SWCURR.XLS SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake- Soil X (mg/kg-day) Chemicals 2-Methylphenol 4-Methylphenol Antimony Arsenic Beryllium Manganese Vanadium Concentration mg/kg X Soil Concentration 3.20E+02 1.30E+03 7.30E+00 1.16E+01 2.40E-01 B.73E+02 1.07E+02 Ingestion X Conversion Rate Factor SOmg/day X 1kg 1000000 mg Ingestion Conversion Rate Factor 50 50 50 50 50 50 50 .OE-06 .OE-06 .OE-06 .OE-06 .OE-06 .OE-06 .OE-06 X Fraction X Exposure X Exposure X Ingested Frequency Duration X 1 X 250 days/year X 25 years X (unittess) Fraction Exposure Ingested Frequency 1 250 1 250 250 250 250 250 250 Exposure Duration 25 25 25 25 25 25 25 1 X Body Weight 1 X 70kg Body Weight 70 70 70 70 70 70 70 1 Averaging Time 1 9125 days Averaging Time 9125 9125 9125 9125 9125 9125 9125 Chronic Daily Intake (GDI) 1.6E-04 6.4E-04 3.6E-06 5.7E-06 1.2E-07 4.3E-04 5.2E-05 Reference Dose (Rf D) 5.0E-02 5.0E-03 4.0E-04 3.0E-04 5.0E-03 5.0E-03 7.0E-03 HQ= CDI/RfD 3. IE-03 1.3E-01 8.9E-03 1.9E-02 2.3E-05 8.5E-02 7.5E-03 HAZARD INDEX. 2.5E-01 •H C o i~* C-4 Cf! BWM / TABLE C-8 SS.DC-SWCUfln.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT- USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Dairy Intake** Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration mo/kg X 1 kg X 1940cm2/day X 1 mg/cm2 X (unittess) X 250 events/year X 35 years X 1 000000 mg Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Chemicals Concentration Factor Area Factor Factor Frequency Duration 1 X 1 Body Weight Averaging Time 1 X 1 70kg Body Weight 25550 days Averaging Chronic Dairy Sbpe Time Intake (GDI) Factor (SF) RISK = (CDI'SF) No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. 0- e/om ) TABLE C-t / / SS-DC-SWCURR.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT- USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic Daily Intake* Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X 1 (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1 kg X 1940cm2/day X 1 mg/cm2 X (unifless) X 250 events/year X 25 years X 1 X 1 1000000 mg 70kg 9125 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Reference HQ= Chemicals_______Concentration Factor_____Area_____Factor____Factor____Frequency Duration Weight_____Time___Intake (GDI) Dose (RID) GDI/RID No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. C H 10/28/84 SS-IN-SWCURRF.XLS TABLE C-9 SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X (mg/kg-day) Chemicals Arsenic Beryllium Concentration mg/kg X Soil Concentration 2.30E+00 2.70E-01 Rate 50 mg/day Ingestion Rate 50 50 Factor Ingested Frequency Duration X 1kg X 1 X 250 days/year X 25 years X 1 000000 mg Conversion Factor 1.0E-06 1.0E-06 (unidess) Fraction Ingested 1 1 Exposure Frequency 250 250 Exposure Duration 25 25 Body Weight 1 70kg Body Weight 70 70 Averaging Time X 1 25550 days Averaging Time 25550 25550 Chronic Daily Intake (GDI) 4.0E-07 4.7E-08 Slope Factor (SF) 1.75E+00 4.3E+00 RISK- (CDI'SF) 7.0E-07 2.0E-07 TOTAL RISK. 9.1E-07 H C O X! Pagel 10/28/94 SS-IN-SWCURRF.XLS TABLE C-9 SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake- (mg/kg-day) 1 1 Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X_ _______ Concentration Rate Factor Ingested Frequency Duration Body Weight Averaging Time Chemicals 2-Methylphenol 4-Methylphenol Antimony Arsenic Beryllium Manganese Vanadium mg/kg X Soil Concentration 3.20E+02 1.30E+03 4.63E+00 2.30E+00 2.70E-01 8.73E+02 1.15E+02 50 mg/day Ingestion Rate 50 50 50 50 50 50 50 X 1kg X 1 X 250 days/yearX 25 years X 1 X 1 1000000 mg (unitiess) Conversion Fraction Exposure Factor Ingested Frequency 1.0E-06 1.0E-06 1.0E-06 1.0E-06 1.0E-06 1.0E-06 1.0E-06 250 250 250 250 250 250 250 Exposure Duration 25 25 25 25 25 25 25 70kg Body Weight 70 70 70 70 70 70 70 91 25 days Averaging Time 9125 9125 9125 9125 9125 9125 9125 Chronic Daily Intake (CDI) 1.6E-04 6.4E-04 2.3E-06 1.1E-06 1.3E-07 4.3E-04 5.6E-05 Reference Dose (RfD) 5.0E-02 5.0E-03 4.0E-04 3.0E-04 5.0E-03 5.0E-03 7.0E-03 HQ= CDI/RfD 3.1E-03 1.3E-01 5.7E-03 3.8E-03 2.6E-05 8.5E-02 8.0E-03 HAZARD INDEX. 2.3E-01 H O O •••j •-0 09/B4 y TABLE C-10 SS-OC-SWCUHRF.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X_ (mgftg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1kg X 1940cm2/day X 1 mg/cm2 X (unittess) X 250 events/year X 25 years X 1 X 1 1000000 mg 70kg 25550 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Slope RISK = Chemicals_______Concentration Factor_____Area_____Factor Factor Frequency Duration Weight_____Time Intake (GDI) Factor (SF) (CDI'SF) No chemicate of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. O O xi ' TABLE C-10 SS-DC-SWCURRF.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic DaHy lntake= SoH X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X 1 (mgrtcg-day) Chemicals Concentration mg/kg X Soil Concentration Factor 1kg X 1000000 mg Conversion Factor Area 1940cm2/day Skin Surface Area Factor X 1 mg/cm2 Adherence Factor Factor X (unittess) Absorption Factor Frequency Duration Body Weight Averaging Time X 250 events/year X 25 years X Exposure Exposure Frequency Duration 1 70kg Body Weight X 1 91 25 days Averaging Time Chronic Daily Intake (CDI) Reference Dose (RfD) HQ= CDI/RfD No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. Oo 6/io/M SS-IH-SWCURRJCLS • TABLbC-11 SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adult* Chronic Daily lntake= Susp. Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mg/kg-day) Chemicals Arsenic Beryllium Concen. Concen. mg/kg X 0.070 mg/m3 Susp. Soil Soil Concen. Concen. 2.30E+00 2.70E-01 7.0E-02 7.0E-02 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X (unfttess) X 0.83 m3/hr X 8 hrs/day X 250 days/yr X 25 years X 1 kg X 1 X 1 Resp. Inhalation . Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.83 0.75 0.83 8 8 250 250 25 25 1000000 mg Conv. Factor 1.0E-06 1.0E-06 70kg Body Weight 70 70 25550 days Averaging Time 25550 25550 Chronic Daily Intake (CDI) 2.8E-09 3.3E-10 Slope Factor (SF) 1.5E+01 8.4E+00 RISK = (CDI'SF) 4.2E-08 2.8E-09 TOTAL RISK = 4.5E-08 O H- W1IVB4 ' TABLuC-11 SS-IH-SWCURR.XLS SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE CURRICULUM CENTER BUILDING AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adults Susp. Chronic Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. XIX (mg/kg-day) Chemicals Concen. mgykg Soil Concen. Concen. X 0.070 mg/m3 Susp. Soil Concen. Fraction X (unittess) Resp. Fraction Rate X 0.83 m3/hr X Inhalation Rate Time 8 hrs/day Exposure Time Frequency X 250 days/yr Exposure Frequency Duration X 25 years Exposure Duration Factor X 1kg 1 000000 mg Conv. Factor BodyWt X 1 X 70kg Body Weight Avging Time 1 9125 days Averaging Chronic Daily Reference Time Intake (CDI) Dose (RfD) HQ= CDI/RID Manganese 8.73E+02 7.0E-02 0.75 0.83 8 250 25 1.0E-06 70 9125 3.0E-06 1.4E-05 2.1E-01 HAZARD INDEX = 2.1E-01 H 10/28/94 SS-IN-SWOH.XLS TABLE C-1.. -' SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA CARCINOGENS • REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake Soil X digestion X Conversion X Fraction X Exposure X Exposure X_ (mg/kg-day) Chemicals Tetrachloroethene Arsenic Concentration mg/kg X Soil Concentration 4.40E+02 1.87E+01 Rate 50 mg/day digestion Rate 50 50 Factor Ingested Frequency Duration X 1kg X 1 X 250 days/year X 25 years X 1000000 mg Conversion Factor 1.0E-06 1.0E-06 (unitfess) Fraction Ingested 1 1 Exposure Frequency 250 250 Exposure Duration 25 25 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 25550 days Averaging Time 25550 25550 Chronic Daily Intake (GDI) 7.7E-05 3.3E-06 Slope Factor (SF) 5.2E-02 1.75E+00 RISK* (CDI'SF) 4.0E-06 5.7E-06 C-i o TOTAL RISK- 9.7E-06 SS-IN-SWOH.XLS TABLi C-12 SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake* (mg/kg-day) Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X Concentration Rate Factor Ingested Frequency 1 1 mg/kg X 50mg/day X 1 kg Duration Body Weight Averaging Time X 250 days/year X 25 years X 1 X 1 Chemicals Tetrachloroethene Antimony Arsenic Manganese Vanadium Soil Concentration 4.40E+02 6.35E+00 1.87E+01 8.70E+02 8.31 E+01 Ingestion Rate 50 50 50 SO 50 1000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 1.0E-06 (unitiess) Fraction Ingested 1 1 1 1 1 Exposure Frequency 250 250 250 250 250 Exposure Duration 25 25 25 25 25 70kg Body Weight 70 70 70 70 70 9125 days Averaging Time 9125 9125 9125 9125 9125 Chronic Daily Intake (CDI) 2.2E-04 3.1E-06 9.1E-06 4.3E-04 4.1E-05 Reference Dose (RfD) 1.0E-02 4.0E-04 3.0E-04 5.0E-03 7.0E-03 HQ= CDI/RfD 2.2E-02 7.8E-03 3.0E-02 8.5E-02 5.8E-03 HAZARD INDEX- 1.5E-01 si TABLE C-13 SS-DC-SWOH.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SfTE WORKERS/EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure (mgftg-day) Concentration Factor Area Factor Factor Frequency mg/kg X 1kg X 1940cm2/day X 1 mg/cm2 X (unifless) X 250 events/year Chemicals Soil Concentration 1000000 mg Conversion Factor Skin Surface Area Adherence Factor Absorption Factor Exposure Frequency X Exposure Duration X 25 years Exposure Duration X I X Body Weight X 1 X 70kg Body Weight 1 Averaging Time 1 25550 days Averaging Chronic Daily Slope Time Intake (CDI) Factor (SF) RISK = (CDI'SF) No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. ~i 8/9*4 TABLE C-13 SS-DC-SWOH.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X___1_____ (mgfeg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time m9/k9 X 1kg X 1940cm2/day X 1 mg/cm2 X (unittess) X 250 events/year X 25 years X 1 X 1 1000000 mg 70kg 9125 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Reference HQ= Chemicals_______Concentration Factor_____Area_____Factor___Factor____Frequency Duration Weight_____Time___Intake (GDI) Dose (RfD) CDI/RfD No chemicals of potential concern selected for surface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. • TABLb C-14 SS-IH-SWOH.XLS SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adult* Susp. Chronic Daily Intake* Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mg/kg-day) Chemicals Tetrachforoethene Arsenic Concen. mg/kg X Soil Concen. 4.40E+02 1.87E+01 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 7.0E-02 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X (unitless) X 0.83 m3/hr X 8 hrs/day X 250 days/yr X 25 years X 1 kg X 1 X 1 Resp. Inhalation Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.75 0.83 0.83 8 8 250 250 25 25 1000000 mg Conv. Factor 1.0E-06 1.0E-06 70kg Body Weight 70 70 25550 days Averaging Time 25550 25550 Chronic Daily Intake (CDI) 5.4E-07 2.3E-08 Slope Factor (SF) 2.0E-03 1.5E+01 RISK = (CDI'SF) 1. IE-09 3.4E-07 TOTAL RISK = 3.4E-07 —i o •-•i \*-: I-1 £ e/16/94 ' TABU- 0-14 SS-IH-SWOH.XLS SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE - USE SCENARIO RISKS TO SITE WORKERS/EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adult* Susp. Chronic Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. X 1 X 1 (mg/kg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime rngtog X 0.070 mg/m3 X (urttless) X 0.83 m3/hr X 8 hrs/day X 250 days/yr X 25 years X 1kg X 1 X 1 1000000 mg 70 kg 9125 days Susp, Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Body Averaging Chronic Daily Reference HQ= Chemicals________Concen. Concen. Fraction Rate____Time Frequency Duration Factor_____Weight_____Time Intake (GDI) Dose (RfD) CDI/RfD Manganese 8.70E+02 7.0E-02 0.75 0.83 8 250 25 1.0E-06 70 9135 3.0E-06 1.4E-05 2.1E-01 HAZARD INDEX = 2.1E-01 ••0 ' TABLE C-15 SS-IH-OHVOC.XLS SURFACE SOIL INHALATION OF VOCS PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE WORKERS /EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION OF VOCS EXPOSURE: Adults Soil-to-Air Chronic Daily Intake^ (mg/kg-day) Chemicals Tetrachloroethene Soil X Volatilization Concen. Factor mo/kg X 1 41506 m3/kg Soil Volatilization Concen. Factor 4.40E+02 2.4E-05 X Inhalation X Exposure X Exposure X Exposure X 1 X 1 Rate Time Frequency Duration BodyWt AvgingTime X0.83m3/hrX 8 hrs/day X 250 days/yr X 25 year XIX 1 Inhalation Exposure Exposure Exposure Rate Time Frequency Duration 0.83 8 250 25 70kg Body Weight 70 25550 days Averaging Time 25550 Chronic Daily Intake (CDI) 2.5E-04 Slope Factor (SF) 2.0E-03 RISK = (CDI'SF) 4.9E-07 TOTAL RISK = 4.9E-07 H Pagel 8/1064 ' TABLE c-15 SS-IH-OHVOCJCLS SURFACE SOIL INHALATION OF VOCS PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE WORKERS /EMPLOYEES IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION OF VOCS EXPOSURE: Adult* Soil-to-Air Chronic Daily lntake= Soil X Volatilization X Inhalation X Exposure X Exposure X Exposure X_ (mg/kgntay) Chemicals Concen. mg/kg X SON Concen. Factor 1 41506m3/kg Volatilization Factor Rate X 0.83 m3/hr X Inhalation Rate Time 8hrs/day Exposure Time Frequency X 250 days/yr Exposure Frequency Duration X 25 year Exposure Duration BodyWt X 1 70kg Body Weight Avging Time X 1 9125 days Averaging Time Chronic Daily Intake (CDI) Reference Dose (RfD) HQ= CDI/RfD Tetrachloroethene does not currently have an established chronic inhalation reference dose. o H- en 10/28/M TABLE C-v SS-IN-CW.XLS SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake* Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X_ (mg/kg-day) Chemicals Aroctor 1242 Arsenic Concentration mg/kg X Soil Concentration 1.20E+02 1.00E+01 Rate 480 mg/day Ingestion Rate 480 480 Factor Ingested Frequency Duration X 1kg X 1 X 225 days/year X 1 year X 1000000 mg Conversion Factor 1.0E-06 1.0E-06 (unitless) Fraction Ingested 1 1 Exposure Frequency 225 225 Exposure Duration 1 1 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 25550 days Averaging Time 25550 25550 Chronic Daily Intake (CDI) 7.2E-06 6.0E-07 Slope Factor (SF) 7.7E+00 1.75E+00 RISK = (CDI'SF) 5.6E-05 1.1E-06 TOTAL RISK « 5.7E-05 "NJ O ;"! 10/26/94 SS-IN-CW.XLS TABLE C-K SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Adults Subchronic Daily Intake- (mg/kg-day) Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X___1 X____1_____ Concentration Rate Factor Ingested Frequency Duration Body Weight Averaging Time Chemicals Antimony Arsenic Manganese Vanadium mg/kg X Soil Concentration 5.05E+00 1.00E+01 8.69E+02 9.59E+01 480 mg/day Ingestion Rate 480 480 480 480 X 1kg X 1 X 225 days/year X 1 year X 1000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 (unitless) Fraction Ingested 1 1 1 1 Exposure Frequency 225 225 225 225 Exposure Duration 1 1 1 1 1 X 1 70kg Body Weight 70 70 70 70 365 days Averaging Time 365 365 365 365 Subchronic Daily Intake (SDI) 2. IE-05 4.2E-05 3.7E-03 4.1E-04 Reference Dose (RfD) 4.0E-04 3.0E-04 5.0E-03 7.0E-03 HQ= SDI/RfD 5.3E-02 1.4E-01 7.3E-01 5.8E-02 HAZARD INDEX- 9.9E-01 Q H- CJ1 i'-J 8/16/94 SS-DC-CW.XLS TABLE C-1, SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDEN AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= (mg/kg-day) Concentration Factor Chemicals Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X Area Factor Factor Frequency Duration Body Weight Averaging Time m9"<9 X 1 kg X 6125 cm2/day X 1 mg/cm2 X (unless) X 225 evente/yr X 1 year X___1_ X 1 1000000 mg 70kg 25550 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Concentration Factor_____Area_____Factor___Factor___Frequency Duration Weight Averaging Chronic Daily Slope RISK = Time Intake (GDI) Factor (SF) (CDI'SF) Aroclor 1242 1.20E+02 1.0E-06 6125 1 0.06 225 1 70 25550 5.5E-06 7.7E+00 4.3E-05 TOTAL RISK = 4.3E-05 C H O 8/16W TABLEC-17 SS-OC-CW.XLS SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDEN AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Subchronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X I X _ _ _ 1 _ _ _ _ _ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1kg X 6125 cm2/day X 1 mg/cm2 X (unitess) X 225 events/yr X 1 year X 1 X 1 1000000 mg 70 kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor___Factor Frequency Duration Weight_____Time____Intake (SDI) Dose (RfD) SDI/R(D A subchronic noncarcinogenic oral reference dose is not currently established for Aroclor 1242. o 1O28/M SS-IH-CW.XLS i TAbLcC-18 SURFACE SOIL INHALATION OF PARTICIPATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adult* Chronic Daily lntake= Susp. Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. X 1 X (mg/kg-day) Chemicals Arsenic Concen. mg/kg X Son Concen. 1.00E+01 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X (unittess) X 0.83 m3/hr X 8 hrs/day X 225 days/yr X 1 year X 1kg X 1 X 1 Resp. Inhalation Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.83 8 225 1 1 000000 mg Conv. Factor 1.0E-06 70kg Body Weight 70 25550 days Averaging Time 25550 Chronic Daily Intake (CDI) 4.4E-10 Slope Factor (SF) 1.5E+01 RISK = (CDI'SF) 6.6E-09 c-i TOTAL RISK = 6.6E-09 SS-IH-CWJO.S , TABLcC-18 SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE: Adult* Subchronic Daily Intake* (mg/kg-day) Chemicals Manganese Soil X Concen. mg/kg X Soil Concen. 8.69E+02 Susp. Soil Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 X Resp. Fraction X (unittess) Resp. Fraction 0.75 X Inhalation X Rate X 0.83 m3/hr X Inhalation Rate 0.83 Exposure Time 8hrs/day Exposure Time 8 X Exposure Frequency X 225days/yr Exposure Frequency 225 X Exposure Duration X 1 year Exposure Duration 1 X Conv. Factor X 1kg 1000000 mg Conv. Factor 1.0E-06 X 1 X BodyWt X 1 X 70kg Body Weight 70 1 Avging Time 1 365 days Averaging Subchronic Daily Reference Time Intake (SDI) Dose (RID) 365 2.7E-06 1. IE-04 HQ= SDI/RfD 2.4E-02 HAZARD INDEX = 2.4E-02 H TABLE C-lb SO-DC-RES.XLS ' SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: AdulU Chronic DaHy lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X___1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mo/kg X 1kg X 5065 cm2/day X 1 mg/cm2 X (untttess) X 91 events/yr X 1 year X 1 X 1 1000000 mg 70kg 25550 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Slope RISK = Chemicals________Concentration Factor_____Area_____Factor___Factor Frequency Duration Weight_____Time____Intake (GDI) Factor (SF) (CDI'SF) No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. CARCINOGENS • REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Children (0-6 year*) Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X 1 (mo/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time ros^g X 1kg X 1270cm2/day X 1 mg/cm2 X (untttess) X 91 events/yr X 1 year X 1 X 1 1000000 mg 15 kg 25550 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Slope RISK = Chemical's ______Concentration Factor______Area_____Factor____Factor Frequency Duration Weight_____Time____Intake (CDI) Factor (SF) (CDI'SF) No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. A cn 03 WWW TABLE C-1& SODC-RES.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Subchronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X___1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time rug/kg X 1kg X 5065 cm2/day X 1 mg/cm2 X (unffless) X 91 events/yr X 1 year X 1 X 1 1000000 mg 70kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor_____Factor Frequency Duration Weight_____Time____Intake (SDI) Dose (RfD) SD I/RID No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Children (0-6 year*) Subchronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure XI XI (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1kg X 1270cm2/day X 1 mg/cm2 X (unittess) X 91 events/yr X 1 year X IX 1 1000000 mg 15kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor____Factor Frequency Duration Weight_____Time_____Intake (SDI) Dose (RfD) SDI/RID No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. H i— H O O -4 SO-IH-RESJCLS t TAface C-20 SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE RESIDENTS (INSIDE AND OUTSIDE RESIDENCE! IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Susp. Chronic Dairy Intake** Soil X Soil X Resp. X Inhalation X Exposure X (mg/kg-day) Concen. Concen. Fraction Rate Time Chemicals Arsenic Beryllium mg/kg Soil Concen. 4.92E+01 4.60E-01 X 0.070 mg/m3 Susp. Soil Concen. 7.00E-02 7.00E-02 X (unitess) Resp. Fraction 0.75 0.75 X 0.83 rn3/hr X Inhalation Rate 0.83 0.83 18 hrs/day X Exposure Time 18 18 CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Chronic Daily lntake= (mg/kg-day) Chemicals Arsenic Beryllium Soil Concen. mg/kg Soil Concen. 4.92E+01 4.60E-01 X Soil Concen. X 0.070 mg/m3 Susp. Soil Concen. 7.00E-02 7.00E-02 X Resp. Fraction X (unidess) Resp. Fraction 0.75 0.75 X Inhalation X Rate X0.83m3/hr X Inhalation Rate 0.83 0.83 Exposure X Time 18 hrs/day X Exposure Time 18 18 Adults Exposure Frequency 91 days/yr Exposure Frequency 91 91 X Exposure Duration X 1 year Exposure Duration 1 1 X Conv. Factor X 1kg 1000000 mg Conv. Factor 1.0E-06 1.0E-06 X 1 BodyWt X 1 70kg Body Weight 70 70 X 1 Avging Time X I 25550 days Averaging Chronic Daily Slope Time Intake (CDI) Factor (SF) 25550 2.0E-09 1.5E+01 25550 1.8E-11 8.4E+00 TOTAL RISK = RISK = (CDI'SF) 2.9E-08 1.5E-10 3.0E-08 Children (04 y«ars) Exposure Frequency 91 days/yr Exposure Frequency 91 91 X Exposure Duration X 1 year Exposure Duration 1 1 X Conv. Factor X 1kg 1000000 mg Conv. Factor 1.0E-06 1.0E-06 X 1 BodyWt X 1 15kg Body Weight 15 15 X 1 Avging Time X 1 25550 days Averaging Chronic Daily Slope . 1 Time Intake (CDI) Factor (SF) 25550 9.2E-09 1.5E+01 25550 8.6E-11 8.4E+00 TOTAL RISK = COMBINED TOTAL RISK (ADULT + CHILD) = RISK = (CDI'SF) 1.4E-07 7.2E-10 1.4E-07 1.7E-07 0118/94 SO-IH-RESJO.S i TAbuc C-20 SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE RESIDENTS fINSIDE AND OUTSIDE RESIDENCE! IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adult* Susp. Subchronic Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mg/kg-day) Chemicals Manganese Concen. mg/kg X Soil Concen. 7.63E+02 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.00E-02 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X(uni«ess)X0.83m3/hrX 18hrs/dayX 91 days/yr X 1 year X 1 kg X 1 X 1 Resp. Inhalation Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.83 18 91 1 1 000000 mg Conv. Factor 1.0E-06 70kg Body Weight 70 365 days Averaging Subchronic Daily Reference Time Intake (SDI) Dose (RfD) 365 2.1E-06 1.1E-04 HQ= SDI/RfD 1.9E-02 HAZARD INDEX = 1.9E-02 NONCARCINOQENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Children (0-6 years) Subchronic Daily lntake= (mg/kg-day) Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Concen. Concen. Fraction Rate Time Frequency Duration Conv. X I X 1 Factor BodyWt AvgingTime mg/kg X 0.070 mg/m3 X (unittess) X 0.83 m3/hr X 18 hrs/day X 91 days/yr X 1 year X 1kg 1 Chemicals Soil Concen. Susp. Soil Concen. Resp. Inhalation Exposure Exposure Exposure Fraction Rate___ Time___Frequency Duration X 1 X 1000000 mg 15kg 365 days Conv. Body Averaging Subchronic Daily Reference ' HQ= Factor Weight Time Intake (SDI) Dose (RfD) SDI/RfD Manganese 7.63E+02 7.00E-02 0.75 0.83 18 91 1 1.0E-06 15 365 9.9E-06 1.IE-04 9.0E-02 HAZARD INDEX = 9.0E-02 TOTAL HAZARD INDEX (ADULT + CHILD) = 1.1E-01 c —: H- Page2 102*94 / TABLE SO-DC-SWTEX.XL3 SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic Daily lnlake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X_____1_ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time "^9 X 1kg X 1940cm2/day X 1 mg/cm2 X (uniDess) X 65events/yr X 1 year X 1 X 1 1000000 mg 70kg 25550 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Chronic Daily Slope RISK = Chemicals________Concentration Factor_____Area_____Factor___Factor Frequency Duration Weight_____Time____Intake (GDI) Factor (SF) (CDI'SF) No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e. cadmium and PCBs). Therefore, this pathway cannot be evaluated. O H-a- KV28/84 . TABLE C-2i SO-DC-SWTEX.XLS ' SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE FIRE DEPmEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Subchronic DaHy lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X_____1___ (mgfeg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mgfcg X 1kg X 1940cm2/day X 1 mg/cm2 X (unitiess) X 65events/yr X 1 year X 1 X 1 1000000 mg 70kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals _______Concentration Factor_____Area_____Factor___Factor Frequency Duration Weight_____Time____Intake (SDI) Dose (RfD) SDI/RfD No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e. cadmium and PCBs). Therefore, this pathway cannot be evaluated. Page2 SO-IH-SWTEX.XLS • TABLc C-22 SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Chronic Daily lnlake= (mg/kg-day) Chemicals Susp. Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. Concen. Concen. Fraction Rate Time Frequency Duration Factor mg/kg X 0.070 mg/m3 X (unittess) X 0.83 mSyhr X 8hrs/day X 65days/yr X 1 year X 1 kg 1 1 BodyWt AvgingTime X 1 X 1 SoH Concen. Susp. Soil Concen. Resp. Inhalation Exposure Exposure Exposure Fraction___Rate____Time___Frequency Duration 1000000 mg 70kg 25550 days Conv. Body Averaging Chronic Daily Factor Weight Time Intake (CDI) Slope RISK = Factor (SFl (CDI'SF) Arsenic Beryllium 1.80E+00 3.60E-01 7.0E-02 7.0E-02 0.75 0.75 0.83 0.83 65 65 1.0E-06 1.0E-06 70 70 25550 25550 2.3E-11 4.6E-12 1.5E+01 8.4E+00 3.4E-10 3.8E-11 —! TOTAL RISK = 3.8E-10 H- 0'- •£= 1QI2B/B4 SO-IH-SWTCX.XLS ^ C-22 SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE FIRE DEPT/TEXACO GAS STATION/ANTILLES AUTO PARTS/RAMSAY MOTOR CO. AREA NONCARCINOQENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Subchronic Daily Intake Susp. SoH X Soil X Rasp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mg/kg-day) Chemicals Barium Manganese Concen. mg/kg X Soil Concen. 1.12E+02 9.07E+02 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 7.0E-02 Fraction X (unittess) Resp. Fraction 0.75 0.75 Rate X 0.83 m3/hr X Inhalation Rate 0.83 0.83 Time 8hrs/day X Exposure Time 8 8 Frequency 65 days/yr Exposure Frequency 65 65 Duration X 1 year Exposure Duration 1 1 Factor X 1kg 1 000000 mg Conv. Factor 1.0E-06 1.0E-06 BodyWt X 1 X 70kg Body Weight 70 70 Avging Time 1 365 days Averaging Subchronic Daily Reference Time Intake (SDI) Dose (RfD) 365 1.0E-07 1.4E-03 365 8.0E-07 1.1E-04 HQ= SDI/RfD 7.1E-05 7.3E-03 •HC O HAZARD INDEX = 7.4E-03 Page2 11/1/84 / TABLE C-2o SO-DC-SWCURH.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic Daily Intakes Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X (mg/kg-day) Chemicals Concentration mg/kg X Soil Concentration Factor 1kq X 1 000000 mg Conversion Factor Area 1940cm2/day Skin Surface Area Factor X 1 mg/cm2 Adherence Factor Factor X (unitfess) X Absorption Factor Frequency 65 events/yr Exposure Frequency Duration X 1 year Exposure Duration Body Weight Averaging Time X 1 X 1 70kg 25550 days Body Averaging Weight Time Chronic Daily Intake (CDI) Slope Factor (SF) RISK = (CDI*SF) No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e. cadmium and PCBs). Therefore, this pathway cannot be evaluated. •H C £" **" 11/1/94 * TABLE C-^ SO-DC-SWCURR.XLS ' SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE CURRICULUM CENTER BUILDING AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: AdulU Subchronic Daily lnlake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X___1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time ""9*9 X 1kg X1940cm2/day X 1 mg/cm2 X (unitfess) X 65events/yr X 1 year X 1 X.I 1000000 mg 70kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor____Factor Frequency Duration Weight_____Time____Intake (SDI) Dose (RID) SDI/RID No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e. cadmium and PCBs). Therefore, this pathway cannot be evaluated. H C 0'- •-•i SO-IH-SWCURRXL3 ! TAbL.c C-24 SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE CURRICULUM CENTER BUILDING AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Chronic Daily Intake* (mg/kg-day) Chemicals Susp. Soil X Soil X Rasp. X Inhalation X Exposure X Exposure X Exposure X Conv. Concen. Concert. Fraction Rate Time Frequency Duration Factor mg/kg X 0.070 mg/m3 X (unitless) X 0.83 m3/hr X 8 hrs/day X 65 days/yr X 1 year X 1kg Soil Concen. Susp. Soil Concen. Resp. Inhalation Exposure Exposure Exposure Fraction___Rate____Time Frequency Duration J_ Body Wt Avging Time X 1 X 1 1000000 mg" 70 kg 25550 days Conv. Body Averaging Chronic Daily Factor Weight Time Intake (GDI) Slope RISK = Factor (SF) (CDI'SF) Arsenic Beryllium O 5.54E+00 1.90E-01 7.0E-02 7.0E-02 0.75 0.75 0.83 0.83 65 65 1.0E-06 1.0E-06 70 70 25550 25550 7.0E-11 2.4E-12 1.5E+01 8.4E+00 1.1E-09 2.0E-11 TOTAL RISK = 1.1E-09 O £ &- £0 KV2B/94 SO-IH-SWCURR.XLS i T, /C-24 SUBSURFACE SOIL INHALATION OF PARTIGULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE CURRICULUM CENTER BUILDING AREA NONCARCtNOGENS • REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Subchronlc Daily Intakes Susp. Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Com. (mg/kg-day) Chemicals Manganese Concen. mg/kg Sou Concen. 8.55E+02 Concen. X 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 Fraction X (unitless) Resp. Fraction 0.75 Rate X 0.83 m3/hr X Inhalation Rate 0.83 Time 8hrs/day X Exposure Time 8 Frequency 65 days/yr Exposure Frequency 65 Duration X lyear Exposure Duration 1 Factor X 1kg 1000000 mg Conv. Factor 1.0E-06 BodyWt X 1 X 70kg Body Weight 70 Avging Time 1 365 days Averaging Subchronic Dairy Reference Time Intake (SDI) Oose(RfD) 365 7.6E-07 1. IE-04 HQ= SDI/RfD 6.9E-03 HAZARD INDEX = 6.9E-03 cr_i •~ •i 1028/94 x TABLE C-u 7 SO-DC-SWESSO.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure (mg/kg-day) Concentration Factor Area Factor Factor Frequency mo/kg X 1kg X 1940cm2/day X 1 mg/cm2 X (uniHess) X 65events/yr Chemicals Soil Concentration 1000000 mg Conversion Factor Skin Surface Area Adherence Factor Absorption Factor Exposure Frequency X Exposure Duration X 1 year Exposure Duration X 1 X 1 Body Weight X 1 ) 70kg Body Weight Averaging Time ( 1 25550 days Averaging Chronic Daily Slope Time Intake (GDI) Factor (SF) RISK = (CDI'SF) No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e. cadmium and PCBs). Therefore, this pathway cannot be evaluated. C O Pa9» / TARI C r. / TABLE C-t SO-DC-SWESSO.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE ESSO GAS STATION AND SPLASH AND DASH CAR WASH AREA NONCARCINOGENS • REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Subchronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X___1 X___1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time me/kg X 1 kg X 1940cm2/day X 1 mg/cm2 X (unittess) X 65events/yr X 1 year X 1 X 1 1000000 mg 70kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor___Factor Frequency Duration Weight______Time____Intake (SDI) Dose(RfD) SDI/RfD No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e. cadmium and PCBs). Therefore, this pathway cannot be evaluated. H ) ) • ' ) 1W28/94 ' I TAl. -C-26 SO-IH-SWESSOJCLS SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE ESSO GAS STATION AND SPLASH AND DASH CAR WASH AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Susp. Chronic Dairy lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. XI X 1 (mg/kg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime mo/kg X 0.070 mg/m3 X (uniHess) X 0.83 m3/hr X 8 hrs/day X 65 days/yr X 1 year X 1kg XIX 1 1000000 mg 70kg 25550 days Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Body Averaging Chronic Daily Slope RISK = Chemicals_________Concen. Concen. Fraction Rate____Time Frequency Duration Factor___Weight Time Intake (GDI) Factor (SF) (CDI'SF) Arsenic 1.60E+00 7.0E-02 0.75 0.83 8 65 1 1.0E-06 70 25550 2.0E-11 1.5E+01 3.0E-10 Beryllium 3.50E-01 7.0E-02 0.75 0.83 8 65 1 1.0E-06 70 25550 4.4E-12 8.4E+00 3.7E-11 TOTAL RISK = 3.4E-10 KV26/94 SO-IH-SWESSOJCLS . T, C-2 SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUJURE-USE SCENARIO RISKS TO SITE WORKERS IN THE ESSO GAS STATION AND SPLASH AND DASH CAR WASH AREA NONCARCINOGENS • REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Subchronte Daily Intake- Soil X (mg/kg-day) Concert. Susp. Soil Concen. X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. 1 1 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime 1 Chemicals mg/kg X 0.070 mg/m3 X (uniHess) X 0.83 m3/hr X 8hrs/day X 6Sdays/yr X 1 year X 1 kg X I X _ _ _ _ _ _ 1000000 mg 70kg 365 days Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Body Averaging Subchronfc Daily Reference HQ= Concen. Concen. Fraction Rate____Time Frequency Duration___Factor_____Weight Time Intake (SDI) Dose(RfD) SDI/RfD Manganese 1.01E+03 7.0E-02 0.75 0.83 8 65 1 1.0E-06 70 365 9.0E-07 1.1E-04 8.2E-03 HAZARD INDEX = 8.2E-03 awm ' TABLE SO-DC-SWOH.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X_ (mg/kg-day) Chemicals Concentration mg/kg X Soil Concentration Factor 1ka X 1000000 mg Conversion Factor Area 1940cm2/day Skin Surface Area Factor X 1 mg/cm2 Adherence Factor Factor X (unifless) X Absorption Factor Frequency 65 events/yr Exposure Frequency Duration X 1 year Exposure Duration Body Weight Averaging Time X 1 X 1 70kg 25550 days Body Averaging Weight Time Chronic Daily Intake (CDI) Slope Factor (SF) RISK = (CDI'SF) No chemicals of potential concern for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. C O H- •--.I a/am / TABLED SO DC-SWOH.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Subchrontc Daily Intake* Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X___1 X___1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1kg X I940cm2/day X 1 mg/cm2 X (uniBess) X 65events/yr X 1 year X 1 X 1 1000000 mg 70kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor____Factor___Frequency Duration Weight_____Time____Intake (SDI) Dose (RfD) SDI/RtD No chemicals of potential concern for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. O / i TA. 7C-28 SO-IH-SWOH.XLS SUBSURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adult* Susp. Chronic Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Cow. X 1 X (mg/kg-day) Chemicals Arsenic Concert, rag/kg X Soil Concen. 1.85E+02 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X (unitless) X 0.83 m3/hr X 8 hrs/day X 65 days/yr X 1 year X 1 kg X 1 X 1 Resp. Inhalation Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.83 8 65 1 1000000 mg Conv. Factor 1.0E-06 70kg Body Weight 70 25550 days Averaging Time 25550 Chronic Daily Intake (GDI) 2.3E-09 Slope Factor (SF) 1.5E+01 RISK = (CDI-SF) 3.5E-08 TOTAL RISK = 3.5E-08 O H SO-1H-SWOH.XLS SUBSURFACE SOI INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO SITE WORKERS IN THE O'HENRY DRY CLEANERS AND LIQUOR BARN AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adult* Susp. Subchronte Daily lntake= Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. X 1 XI (mg/kg-day) Concen. Concen. Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime mg/kg X 0.070 mg/m3 X (unittess) X 0.83 m3/hr X 8hrs/day X 65 days/yr X 1 year X 1 kg X 1 X 1 1000000 mg 70kg 365 days Susp. Soil Soil Resp. Inhalation Exposure Exposure Exposure Conv. Body Averaging Subchronte Daily Reference HQ= Chemicals_________Concen. Concen. Fraction Rate____Time Frequency Duration___Factor Weight_____Time Intake (SDI) Dose(RtD) SDI/FUD Manganese 2.20E+03 7.0E-02 0.75 0.83 8 65 1 1.0E-06 70 365 2.0E-06 1.IE-04 1.8E-02 HAZARD INDEX = 1.8E-02 £ •-••j. tO/28494 SUBSS-IN-CW.XLS TABLE C-. SUBSURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake- Soil X Ingestion X Conversion X Fraction X Exposure X Exposure X (mg/kg-day) Chemicals Benzo(a)pyrene Arsenic Beryllium Concentration mg/kg X Soil Concentration 1.90E-01 4.92E+01 4.60E-01 Rate Factor Ingested Frequency 480 mg/day X 1 kg X 1 X 65 days/year Ingestion Rate 480 480 480 1000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 (unitless) Fraction Ingested 1 1 1 Exposure Frequency 65 65 65 Duration X 1 year X Exposure Duration 1 1 1 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 70 25550 days Averaging Time 25550 25550 25550 Chronic Daily Intake (CDI) 3.3E-09 8.6E-07 8.0E-09 Slope Factor (SF) 7.3E+00 1.75E-fOO 4.3E+00 RISK = (CDfSF) 2.4E-08 1.5E-06 3.5E-08 TOTAL RISK- 1.6E-06 H Pagel 10/28/94 SUBSS-IN-CW.XLS TABLE C-i., SUBSURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INGESTION EXPOSURE: Adults Subchrom'c Daily Intake- Soil X Ingestkm X Conversion X Fraction X Exposure X Exposure X (mg/kg-day) Chemicals Antimony Arsenic Beryllium Manganese Vanadium Concentration mg/kg X Soil Concentration 5.10E+00 4.92E+01 4.60E-01 7.63E+02 1.57E+02 Rate Factor Ingested Frequency 480 mg/day X 1 kg X 1 X 65 days/year Ingestion Rate 460 480 480 480 480 1000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 1.0E-06 (unittess) Fraction Ingested 1 1 1 1 1 Exposure Frequency 65 65 65 65 65 Duration X 1 year X Exposure Duration 1 1 1 1 1 Body Weight Averaging Time 1 X I 70kg Body Weight 70 70 70 70 70 365 days Averaging Time 365 365 365 365 365 Subchronic Daily Intake (SDI) 6.2E-06 6.0E-05 5.6E-07 9.3E-04 1.9E-04 Reference Dose (RfD) 4.0E-04 3.0E-04 5.0E-03 5.0E-03 7.0E-03 HQ= SDI/RfD 1.6E-02 2.0E-01 1.1E-04 1.9E-01 2.7E-02 HAZARD INDEX- 4.3E-01 •—iC o H- •--.I -0 a/ts/94 7 TABLE C-30 SUBSS-DC-CW.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDEN AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X____1_____ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time nig/kg X 1kg X 6125 cm2/day X 1 mg/cm2 X (urtdess) X 65 events/yr X 1 year X 1 X 1 Chemicals Soil Concentration 1000000 mg Conversion Factor Skin Surface Area Adherence Factor Absorption Factor Exposure Frequency Exposure Duration 70kg Body Weight 25550 days Averaging Time Chronic Daily Slope Intake (GDI) Factor (SF) RISK = (CDI'SF) No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. C —! O H- 03 Pagel W15/94 TABLE C-30 SUBSS-DC-CW.XLS SUBSURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE • FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDEN AND ART CENTER AREA NONCARCINOGENS • REASONABLE MAXIMUM CASE SUBSURFACE SOIL DERMAL CONTACT EXPOSURE: Adult* Subchronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X 1 X___1______ (mg/kg-day) Concentration Factor Area Factor Factor Frequency Duration Body Weight Averaging Time mg/kg X 1kg X6125cm2/day X 1 mg/cm2 X (uniBess) X 65events/yr X 1 year X 1 X 1 1000000 mg 70kg 365 days Soil Conversion Skin Surface Adherence Absorption Exposure Exposure Body Averaging Subchronic Daily Reference HQ= Chemicals________Concentration Factor_____Area_____Factor___Factor Frequency Duration Weight_____Time____Intake (SDI) Dose (RID) SDI/RtD No chemicals of potential concern selected for subsurface soil in this area of concern have established dermal absorption factors (i.e., cadmium and PCBs). Therefore, this pathway cannot be evaluated. 03 !-* B/15W4 SUBSS-IH-CW.XLS 1 TABLc C-31 SUBSURFACE SOIL INHALATION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adults Chronic Daily lntake= Susp. Soil X Soil (mg/kg-day) Chemicals Arsenic Beryllium Concert, mg/kg X Soil Concen. 4.92E+01 4.60E-01 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 7.0E-02 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X (unitless) X O.B3 m3/hr X 8 hrs/day X 65 days/yr X 1 year X 1 kg X 1 X 1 Resp. Inhalation Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.83 0.75 0.83 8 8 65 65 1 1 1000000 mg Conv. Factor 1.0E-06 1.0E-06 70kg Body Weight 70 70 25550 days Averaging Time 25550 25550 Chronic Daily Intake (CDI) 6.2E-10 5.8E-12 Slope Factor (SF) 1.5E+01 8.4E+00 RISK = (CDI'SF) 9.3E-09 4.9E-1 1 TOTAL RISK = 9.4E-09 C —i S/15/94 SUBSS-IH-CW.XLS ' TABLE C-31 SUBSURFACE SOIL INHALATION PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO CONSTRUCTION WORKERS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SUBSURFACE SOIL INHALATION EXPOSURE: Adult* Subcrironic Daily Intake: Susp. Soil X Soil X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. (mg/kg-day) Chemicals Manganese Concen. mg/kg X Soil Concen. 7.63E+02 Concen. 0.070 mg/m3 Susp. Soil Concen. 7.0E-02 Fraction X (unitless) Resp. Fraction 0.75 Rate X 0.83 m3/hr X Inhalation Rate 0.83 Time 8hrs/day X Exposure Time 8 Frequency 65 days/yr Exposure Frequency 65 Duration X 1 year Exposure Duration 1 Factor X 1kg 1000000 mg Conv. Factor 1.0E-06 BodyWt X 1 X 70kg Body Weight 70 Avging Time 1 365 days Averaging Subchronic Daily Reference Time Intake (SDI) Dose (RID) 365 6.8E-07 1. IE-04 HQ= SDI/RlD • 6.2E-03 HAZARD INDEX = 6.2E-03 O Xi O H. 00 H C. O O 12/8/94 QW-IN-RES.XLS TABLE ^ 32 GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION Chronic Daily Intakes Water X Ingeslion X Exposure X (mg/kg-day) Concentration Rate Frequency mg/I X 2 Way X 350 days/year X Chemicals Benzene Telrachloroelhene Vinyl Chloride Arsenic Beryllium Water Concentration 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 Ingestion Rale 2 2 2 2 2 Exposure Frequency 350 350 350 350 350 CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION Chronic Daily lnlake= (mg/kg-day) Chemicals Benzene Tetrachloroelhene Vinyl Chloride Arsenic Beryllium Water X Concentration mg/I X Water Concentration 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 Ingestion Rate 1 1/day Ingestion Rate 1 1 1 1 1 X Exposure X Frequency X 350 days/year X Exposure Frequency 350 350 350 350 350 EXPOSURE: Exposure X Duration 30 years X Exposure Duration 30 30 30 30 30 EXPOSURE: Exposure X Duration 6 years X Exposure Duration 6 6 6 6 6 Adults 1 Body Weight 1 70kg Body Weight 70 70 70 70 70 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Daily Intake (CDI) 7.0E-04 2.3E-03 2.3E-04 1.2E-05 1.2E-05 Slope Factor (SF) 2.9E-02 5.2E-02 1.9E+00 1.75E+00 4.3E+00 TOTAL RISK = RISK = (CDI'SF) 2.0E-05 1.2E-04 4.5E-04 2.1E-05 5.0E-05 6.6E-04 Children (0-6 y«ars) 1 Body Weight 1 15kg Body Weight 15 15 15 15 15 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Daily Intake (CDI) 3.3E-04 1.1E-03 1. IE-04 5.5E-06 5.5E-06 Slope Factor (SF) 2.9E-02 5.2E-02 1.9E+00 1.75E+00 4.3E+00 RISK = (CDI*SF) 9.5E-06 5.7E-05 2.1E-04 9.6E-06 2.4E-05 TOTAL RISK •. 3. IE-04 I2/8/9X GW-IN-RES.XLS ,TABLE. GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS NONCARCINOGENS -REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE: Adults —i Chronic Daily lntake= (mg/kg-day) Chemicals 1 ,2-Dichloroelhene(Tolal) Tetrachtoroethene Toluene Antimony Arsenic BerySium Chromium VI Manganese Nickel Vanadium Water X Ingestion X Concentration Rate mg/l X 2 I/day X Water Concentration 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 Ingestion Rate 2 2 2 2 2 2 2 2 2 2 Exposure Frequency 350 days/year Exposure Frequency 350 350 350 350 350 350 350 350 350 350 X Exposure X Duration X 30 years X Exposure Duration 30 30 30 30 30 30 30 30 30 30 1 X 1 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 70 70 70 70 70 70 70 70 10950 days Averaging Time 10950 10950 10950 10950 10950 10950 10950 10950 10950 10950 Chronic Daily Intake (CDI) 1. IE-02 5.5E-03 8.2E-04 2.7E-04 2.7E-05 2.7E-05 5.5E-04 1.3E-01 1.9E-03 3.0E-03 Reference Dose (RfD) 9.0E-03 1.0E-02 2.0E-01 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HQ= CDI/RfD 1.2E+00 5.5E-01 4. IE-03 6.8E-01 9. IE-02 5.5E-03 1.1E-01 2.6E-t01 9.6E-02 4.3E-01 HAZARD INDEX = 2.9E+01 NONCARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE: Children (0 - 6 years) Chronic Dairy Intake* (mg/kg-day) Chemicals 1 ,2-Dichloroelhene(Total) Tetrachloroethene Toluene Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Water X Ingestion X Exposure Concentration Rate Frequency mg/l X 1 1/day X 350 days/year Water Ingestion Exposure Concentration Rate Frequency 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 350 350 350 350 350 350 350 350 350 350 X Exposure X Duration X 6 years X Exposure Duration 6 6 6 6 6 6 6 6 6 6 1 X 1 Body Weight Averaging Time 1 X 1 15kg Body Weight 15 15 15 15 15 15 15 15 15 15 21 90 days Averaging Time 2190 2190 2190 2190 2190 2190 2190 2190 2190 2190 Chronic Daily Intake (CDI) 2.5B-02 1.3E-02 1.9E-03 6.4E-04 6.4E-05 6.4E-05 1.3E-03 3.0E-01 4.5E-03 70E-03 Reference Dose (RfD) 9.0E-03 1.0E-02 2.0E-01 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HQ= CDI/RfD 2.8E4<X) 1.3E+00 9.6E-03 1.6E«<X) 2. IE-01 1.3E-02 2.6E-01 6.0E+01 2.2E-01 1.0E+00 HAZARD INDEX = 6.7E+01 s 12/9*94 / ( TAu 1-33 / GW-DC-HES.XLS GROUNDWATER DERMAL CONTACT DURING SHOWERING PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE RESIDENTS CARCINOGENS- REASONABLE MAXIMUM CASE GROUNDWATER DERMAL CONTACT EXPOSURE: Adults Chronic Daily Intake- Water XSkin Surface X Permeability X (mg/kg-day) Concentration Area Constant me/I X 18150 cm2 X cm/hr X Water Skin Surface Permeability Chemicals Concentration Area Constant Arsenic 1.00E-03 18150 1.0E-03 Beryllium 1.00E-03 18150 1.0E-03 Exposure X Exposure X Exposure Time Frequency Duration 0.2 hr/day X 350 days/year X 30 years Exposure Exposure Exposure Time Frequency Duration 0.2 350 30 0.2 350 30 CARCINOGENS- REASONABLE MAXIMUM CASE GROUNDWATER DERMAL CONTACT EXPOSURE: Children (0 H C 5 X! 5 0- Chronic Daily lntake= Water XSkin Surface X Permeability X (mc/kg-day) Concentration Area Constant mgrl X 5400 cm2 X cm/hr X Water Skin Surface Permeability Chemicals Concentration Area Constant Arsenic 1.00E-03 5400 1.0E-03 Beryllium 1.00E-03 5400 1.0E-03 Exposure X Exposure X Exposure Time Frequency Duration 0.2 hr/day X 350 days/year X 6 years Exposure Exposure Exposure Time Frequency Duration 0.2 350 6 0.2 350 6 X Conversion Factor X 1L 1000cm3 Conversion Factor 1.0E-03 1.0E-03 - 6 years) X Conversion Factor X 1L 1000cm3 Conversion Factor 1.0E-03 1.0E-03 X 1 Body Weight X 1 70kg Body Weight 70 70 X 1 Body Weight X 1 15kg Body Weight 15 15 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 Chronic Daily Cancer Slope RISK = Intake (CDI) Factor (CSF) (CDI'CSF) 2.1E-08 1.75E+00 3.7E-08 2.1E-08 4.3E+00 9.2E-08 TOTAL RISK = 1 .3E-07 Chronic Daily Cancer Slope j RISK = Intake (CDI) Factor (CSF) (CDI'CSF) 5.9E-09 1.75E+00 1.0E-08 5.9E-09 4.3E+00 2.5E-08 TOTAL RISK = 3.6E-08 TAu fC-33 GROUNDWATER DERMAL CONTACT DURING SHOWERING PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE RESIDENTS H NONCARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= Water XSkin Surface X Permeability X Exposure X Exposure X Exposure X (mg/kg-day) Chemicals Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Concentration Area mg/l X 18150 cm2 Water Skin Surface Concentration Area 1.00E-02 18150 1.00E-03 18150 1.00E-03 18150 2.00E-02 18150 4.68E+00 18150 7.00E-02 18150 1.10E-01 18150 Constant X cm/hr Permeability Constant 1. OE-03 1. OE-03 .OE-03 .OE-03 .OE-03 .OE-04 .OE-03 Time X 0.2 hr/day Exposure Time 0.2 02 02 02 0.2 02 0.2 Frequency X 350 days/year Exposure Frequency 350 350 350 350 350 350 350 Duration X 30 years X Exposure Duration 30 30 30 30 30 30 30 Conversion X Factor 1 L X 1000cm3 Conversion Factor .OE-03 OE-03 .OE-03 .OE-03 .OE-03 .OE-03 .OE-03 1 Body Weight 1 70kg Body Weight 70 70 70 70 70 70 70 X 1 Averaging Time X 1 10950 days Averaging Time 10950 10950 10950 10950 10950 10950 10950 Chronic Daily Intake (CDI) 5.0E-07 5.0E-08 5.0E-08 9.9E-07 2.3E-04 3.5E-07 5.5E-06 Reference Dose {RfD) 4.0E-04 3.0E-04 50E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HAZARD INDEX = NONCARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER Chronic Daily Intake^ (mg/kg-day) Chemicals Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Water XSkin Surface Concentration Area mg/l X 5400 cm2 Water Skin Surface Concentration Area 1.00E-02 5400 1.00E-03 5400 1.00E-03 5400 2.00E-02 5400 4.68E+00 5400 7.00E-02 5400 1.10E-01 5400 X Permeability Constant X cm/hr Permeability Constant 1. OE-03 1. OE-03 1. OE-03 1. OE-03 1. OE-03 1. OE-04 1. OE-03 HQ= CDI/RID 1 .2E-03 1.7E-04 9.9E-06 2.0E-04 4.7E-02 1 .7E-05 7.8E-04 4.9E-02 DERMAL CONTACT EXPOSURE: Children (0 - 6 Years) X Exposure Time X 0.2 hr/day Exposure Time 0.2 0.2 0.2 . 0.2 0.2 0.2 0.2 X Exposure Frequency X 350 days/year Exposure Frequency 350 350 350 350 350 350 350 X Exposure X Duration X 6 years X Exposure Duration 6 6 6 6 6 6 6 Conversion X Factor 1L X 1000cm3 Conversion Factor .OE-03 .OE-03 .OE-03 .OE-03 .OE-03 .OE-03 .OE-03 1 Body Weight 1 15kg Body Weight 15 15 15 15 15 15 15 X 1 Averaging Time X 1 2190 days Averaging Time 2190 2190 2190 2190 2190 2190 2190 Chronic Daily Intake (CDI) 6.9E-07 6.9E-08 6.9E-08 1.4E-06 3.2E-04 4.8E-07 7.6E-06 j Reference Dose (RfD) 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HQ= CDI/RfD 1 .7E-03 2.3E-04 1 .4E-05 2.8E-04 6.5E-02 2.4E-05 1. IE-03 HAZARD INDEX = 6.8E-02 O H- 00 Page; 12/8/94 GW-INH.XLS Equation: TABLE C GROUNDWATER INHALATION (SHOWER MODEL) PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO RESIDENTS C(a) * Concentration of chemical in air (mg/m3) C(aMAX) « Maximum concentration of chemical in air (mg/m3) 11 a Time of shower (hr) (2 » Time after shower (hr) C(a)> [C(aMAX)/2 x (mg/m3) (mg/m3) (hr) (C(aMAX) x (mg/m3) (tl (hr) Chemicals: Benzene Tetrachloroethene Toluene Vinyl Chloride 0.450 1.500 0.225 0.150 0.281 0.938 0.141 0.094 0.2 0.2 0.2 0.2 0.563 1.875 0.281 0.188 0.3 0.3 0.3 0.3 (hr) 0.5 0.5 0.5 0.5 Equation: C(aMAX) - Maximum air concentration in bathroom (mg/m3) C(w) m Water concentration (mg/l) f" Fraction volatilized (unidess) F(w) - Water flow rate (l/hr) V(a) > Bathroom volume (m3) Chemicals: Benzene ' Tetrachloroethene Toluene Vinyl Chloride C(aMAX) » (mg/m3) 0.563 1.875 0.281 0.188 (C(w) (mg/l) 6.00E-02 2.00E-01 3.00E-02 2.00E-02 x f x (unitless) 0.75 0.75 0.75 0.75 F(w) x (l/hr) 750 750 750 750 til (hr) 0.2 0.2 0.2 0.2 / V(a) (m3) 12 12 12 12 o CD 03 Pagel 12/8/94 GW-INH.XLS TABLE C I i GROUNDWATER INHALATION (SHOWER MODEL) PATHWAY TUTU WELLS SITE • PRESENT/FUTURE-USE SCENARIO RISKS TO RESIDENTS CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INHALATION EXPOSURE: Chronic Daily Intake* Air X Inhalation X Exposure X Exposure (mg/kg-day) Concentration Rate Time Frequency mg/m3 X 0.6 m3/hr X 0.2 hrs/day X 350 days/year Chemicals Benzene Tetrachtoroethene Vinyl Chloride Air Concentration 4.50E-01 1.50E+00 1.50E-01 Inhalation Rate 0.6 0.6 0.6 Exposure Time 0.2 0.2 0.2 CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INHALATION Chronic Daily Intake- (mg/kg-day) Chemicals Benzene Tetrachtoroethene Vinyl Chloride C o •-•J. Air Concentration mg/m3 Air Concentration 4.50E-01 1.50E+00 1.50E-01 X Inhalation Rate X 0.6 m3/hr Inhalation Rate 0.6 0.6 0.6 X Exposure X Time X 0.2 hrs/day X Exposure Time 0.2 0.2 0.2 Exposure Frequency 350 350 350 EXPOSURE: Exposure Frequency 350 days/year Exposure Frequency 350 350 350 Adults X Exposure Duration X 30 years Exposure Duration 30 30 30 X 1 Body Weight X 1 70kg Body Weight 70 70 70 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 25550 Chronic Daily Intake (GDI) 3.2E-04 1.1E-03 1. IE-04 Slope Factor (SF) 2.9E-02 2.0E-03 3.0E-01 TOTAL RISK « RISK = (CDI*SF) 9.2E-06 2. IE-06 3.2E-05 4.3E-05 Children (0 - 6 years) X Exposure Duration X 6 years Exposure Duration 6 6 6 X 1 Body Weight X 1 15kg Body Weight 15 15 15 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 25550 Chronic Daily Intake (CDI) 3.0E-04 9.9E-04 9.9E-05 Slope Factor (SF) 2.9E-02 2.0E-03 3.0E-01 TOTAL RISK - t RISK = (CDI'SF) 8.6E-06 2.0E-06 3.0E-05 4.0E-05 -0 12/8/94 J OW-INH.XLo NONCARCINOGENS • REASONABLE Chronic Daily Intake** (mg/kg-day) Chemicals Toluene NONCARCINOGENS - REASONABLE Chronic Daily Intake* (mg/kg-day) Chemicals Toluene TABLE C / / t GROUNDWATER INHALATION (SHOWER MODEL) PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO RESIDENTS MAXIMUM CASE GROUNDWATER INHALATION EXPOSURE Air X Concentration mg/m3 X Air Concentration 2.25E-01 Inhalation Rate 0.6 m3/hr Inhalation Rate 0.6 X Exposure Time X 0.2 hrs/day Exposure Time 0.2 X Exposure X Frequency X 350 days/year X Exposure Frequency 350 MAXIMUM CASE GROUNDWATER INHALATION EXPOSURE Air X Concentration mg/m3 X Air Concentration 2.25E-01 Inhalation Rate 0.6 m3/hr Inhalation Rate 0.6 X Exposure Time X 0.2 hrs/day Exposure Time 0.2 X Exposure X Frequency X 350 days/year X Exposure Frequency 350 : Adults Exposure X Duration 30 years X Exposure Duration 30 : Children (0 Exposure X Duration 6 years X Exposure Duration 6 1 Body Weight 1 70kg Body Weight 70 - 6 years) 1 Body Weight 1 15kg Body Weight 15 X 1 Averaging Time X 1 10950 days Averaging Time 10950 X 1 Averaging Time X 1 2190 days Averaging Time 2190 Chronic Daily Reference HQ= Intake (CD]) Dose (RID) CDI/RfD 3.7E-04 1.10E-01 3.4E-03 TOTAL HAZARD * 3.4E-03 I Chronic Daily Reference HQ= Intake (CDI) Dose (RfD) CDI/RfD 1.7E-03 1.10E-01 1.6E-02 TOTAL HAZARD « 1.6E-02 •-0 TABLE GW-IN-SW.XLS GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE WORKERS CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE: Adults Chronic Daily Intake^ (mg/kg-day) Water X Ingestion X Exposure Concentration Rate Frequency 1 1 X Exposure X_ ___ _________ Duration Body Weight Averaging Time mg/l X 1 1/day X Chemicals Benzene Tetrachloroethene Vinyl Chloride Arsenic Beryllium Water Concentration 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 Ingestion Rate 1 1 1 1 1 250 days/year Exposure Frequency 250 250 250 250 250 X 25 years X Exposure Duration 25 25 25 25 25 1 X 1 70kg Body Weight 70 70 70 70 70 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Daily Intake (CDI) 2.1E-04 7.0E-04 7.0E-05 3.5E-06 3.5E-06 Slope Factor (SF) 2.9E-02 5.2E-02 1 .9E+00 1.75E-fOO 4.3E+00 RISK = (CDI'SF) 6. IE-06 3.6E-05 1.3E-04 6.1E-06 1.5E-05 TOTAL RISK. 2.0E-04 -a \tj\si GW-IN-SW.XLS TABLE o ) GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE WORKERS DNCARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE: Adults Chronic Daily Intake- Water X Ingestion X Exposure X Exposure XIX 1 (mg/kg-day) Chemicals 1,2-Dichloroetriene (Total) Tetrachloroethene Toluene Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Concentration Rate mg/l X 1 1/day X Water Concentration 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 Ingestion Rate 1 1 1 1 1 1 1 1 1 1 Frequency 250 days/year Exposure Frequency 250 250 250 250 250 250 250 250 250 250 Duration X 25 years X Exposure Duration 25 25 25 25 25 25 25 25 25 25 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 70 70 70 70 70 70 70 70 9125 days Averaging Time 9125 9125 9125 9125 9125 9125 9125 9125 9125 9125 Chronic Daily Intake (GDI) 3.8E-03 2.0E-03 2.9E-04 9.8E-05 9.8E-06 9.8E-06 2.0E-04 4.6E-02 6.8E-04 1. IE-03 Reference Dose (RfD) 9.0E-03 1.0E-02 2.0E-01 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 , HQ= CDI/RfD 4.2E-01 2.0E-01 1.5E-03 2.4E-01 3.3E-02 2.0E-03 3.9E-02 9.2E+00 3.4E-02 1.5E-01 HAZARD INDEX 1.0E+01 ••0 QW-INCW.XLS TABLt^ GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - FUTURE - USE SCENARIO RISKS TO CONSTRUCTION WORKERS CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE Chronic Daily Intake- (mg/kg-day) Water X Ingestion X Concentration Rate 1 1 Exposure X Exposure X ____ _____ Frequency Duration Body Weight Averaging Time TOTAL RISK mg/l X 1 1/day X Chemicals Benzene Tetrachloroethene Vinyl Chloride Arsenic Beryllium Water Concentration 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 Ingestion Rate 1 1 1 1 1 225 days/year Exposure Frequency 225 225 225 225 225 X 1 year X Exposure Duration 1 1 1 1 1 1 X 1 70kg Body Weight 70 70 70 70 70 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Daily Intake (CDI) 7.5E-06 2.5E-05 2.5E-06 1.3E-07 1.3E-07 Slope Factor (SF) 2.9E-02 5.2E-02 1.9E+00 1.75E+00 4.3E+00 RISK* (CDI'SF) 2.2E-07 1.3E-06 4.8E-06 2.2E-07 5.4E-07 7.1E-06 Pagel o GW-IN-CW.XLS TABLE GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - FUTURE - USE SCENARIO RISKS TO CONSTRUCTION WORKERS ONCARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE Subchronic Daily Intake* Water X Ingestion X Exposure X Exposure X 1 X 1 (mg/kg-day) Chemicals 1,2-Dichloroethene (Total) Tetrachloroethene Toluene Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Concentration Rate Frequency Duration Body Weight Averaging Time mg/l X 1 1/day X 225 days/year X 1 year X 1 X 1 Water Ingestion Concentration Rate 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 1 7.00E-02 1 1.10E-01 1 70kg Exposure Exposure Body Frequency Duration Weight 225 225 225 225 225 225 225 225 70 70 70 70 70 70 70 70 225 1 70 225 1 70 365 days Averaging Time 365 365 365 365 365 365 365 365 365 365 Subchronic Daily Reference Intake (SDI) Dose (RfD) 3.4E-03 1.8E-03 2.6E-04 8.8E-05 8.8E-06 8.8E-06 1.8E-04 4.1E-02 6.2E-04 9.7E-04 9.0E-03 1.0E-01 2.0E-fOO 4.0E-04 3.0E-04 5.0E-03 2.0E-02 5.0E-03 2.0E-02 7.0E-03 HAZARD INDEX « HQ= SDI/R«D 3.8E-01 1.8E-02 1.3E-04 2.2E-01 2.9E-02 1.8E-03 8.8E-03 8.2E+00 3. IE-02 1.4E-01 9.1E+00 I APPENDIX D CENTRAL TENDENCY CALCULATIONS j$fS®&*^ TUT 007 0195 iz/21/84 ) TABLE D-1 ) ) SS-IN-RESCTC.ALS CENTRAL TENDENCY CALCULATION SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - SURFACE SOIL INGESTION EXPOSURE: Adults Chronic Daily Intake. Soil X Ingestion X Conversion X Fraction (mg/kg-day) Concentration Rate Factor Ingested mo/kg X SOmg/day X 1kg X 1 1000000 mg (unitless) Soil Ingestion Conversion Fraction Chemicals Concentration Rate Factor Ingested Arock>r1242 1.20E+02 50 1.0E-06 1 Arsenic 1.00E+01 50 1.0E-06 1 CARCINOGENS - SURFACE SOIL INGESTION EXPOSURE: Children (0 - 6 years) Chronic Daily Intake. Soil X Ingestion X Conversion X Fraction (mg/kg-day) Concentration Rate Factor Ingested mg/kg X lOOmg/day X 1kg X 1 1000000 mg (unitless) Soil Ingestion Conversion Fraction Chemicals Concentration Rate Factor Ingested Arock>r1242 1.20E+02 100 1.0E-06 1 Arsenic 1.00E+01 100 1.0E-06 1 d ~\ 6 '~~'i -.0 i> X Exposure X Exposure Frequency Duration X 275 days/year X 9 years Exposure Exposure Frequency Duration 275 9 275 9 iX Exposure X Exposure Frequency Duration X 275 days/year X 6 years Exposure Exposure Frequency Duration 275 6 275 6 X 1 Body Weight X 1 70kg Body Weight 70 70 X 1 Body Weight X 1 15kg Body Weight 15 15 X 1 Averaging Time X 1 25550 days Averaging Chronic Daily Slope Time Intake (GDI) Factor (SF) 25550 8.3E-06 7.7E+00 25550 6.9E-07 1.75E+00 TOTAL RISK - X 1 Averaging Time X 1 25550 days Averaging Chronic Daily Slope Time Intake (GDI) Factor (SF) 25550 5.2E-05 7.7E+00 25550 4.3E-06 1.75E+00 TOTAL RISK - 30-YEAR COMBINED RISK (ADULT + CHILD) . RISK. (CDI'SF) 6.4E-05 1.2E-06 6.5E-05 RISK- (CDI*SF)_ 4.0E-04 7.5E-06 4. IE-04 4.7E-04 12/27/94 SS-IN.HESCTCwO:XLS TABLE D-1 CENTRAL TENDENCY CALCULATION SURFACE SOIL INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INGESTION EXPOSURE: Children (0-6 years) Chronic Daily Intake* (mg/kg-day) Concentration Ingestkm Rate Conversion Factor Fraction Ingested Exposure Frequency X Exposure Duration 1 1 Body Weight Averaging Time Chemicals Antimony Arsenic Manganese Vanadium mg/kg X Soil Concentration S.05E+00 1.00E+01 8.69E+02 9.59E+01 100mg/day Ingestion Rate 100 100 100 100 X 1kg X 1 X 275 days/year X 6 years X 1 000000 mg Conversion Factor 1.0E-06 1.0E-06 1.0E-06 1.0E-06 (unitless) Fraction Ingested 1 1 1 1 Exposure Frequency 275 275 275 275 Exposure Duration 6 6 6 6 1 X 1 15kg Body Weight 15 15 15 15 21 90 days Averaging Time 2190 2190 2190 2190 Chronic Daily Intake (CDI) 2.5E-05 5.0E-05 4.4E-03 4.8E-04 Reference Dose (RfD) 4.0E-04 3.0E-04 5.0E-03 7.0E-03 HQ= CDI/RfD 6.3E-02 1.7E-01 8.7E-01 6.9E-02 HAZARD INDEX = 1.2E+00 -0 amas ' TABLE D-a SS-DC-RESCTC.XLS CENTRAL TENDENCY CALCULATION SURFACE SOIL DERMAL CONTACT PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS IN THE TILLETT GARDENS AND ART CENTER AREA CARCINOGENS - SURFACE SOIL DERMAL CONTACT EXPOSURE: Adults Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X (mg/kg-day) Chemicals Aroclor 1242 Concentration rngftg X Soil Concentration 1.20E+02 Factor 1kg X 1 000000 mg Conversion Factor 1.0E-06 Area 5065 cm2/day Skin Surface Area 5065 Factor X0.6mg/cm2X Adherence Factor 0.6 Factor (unitless) Absorption Factor 0.03 Frequency Duration X 275 events/year X 9 years Exposure Exposure Frequency Duration 275 9 Body Weight X 1 70kg Body Weight 70 Averaging Time X 1 25550 days Averaging Time 25550 Chronic Daily Intake (CDI) 1 .7E-05 Slope Factor (SF) 7.7E+00 RISK = (CDI'SF) 1.3E-04 TOTAL RISK = 1.3E-04 CARCINOGENS - SURFACE SOIL DERMAL CONTACT EXPOSURE: Children (0-6 years) Chronic Daily lntake= Soil X Conversion X Skin Surface X Adherence X Absorption X Exposure X Exposure X_ 1 X 1 (mg/kg-day) Chemicals Arodor 1242 Concentration mg/kg X Soil Concentration 1.20E+02 Factor 1kg X 1000000 mg Conversion Factor 1.0E-06 Area 1270cm2/day Skin Surface Area 1270 Factor Factor X0.6mg/cm2X (unitless) Adherence Absorption Factor Factor 0.6 0.03 Frequency X 275 events/year Exposure Frequency 275 Duration X 6 years Exposure Duration 6 Body Weight X 1 15kg Body Weight 15 Averaging Time X 1 25550 days Averaging Time 25550 Chronic Daily Intake (CDI) 1.3E-05 Slope Factor (SF) 7.7E+00 RISK = (CDI'SF) 1.0E-04 ft O TOTAL RISK = 1.0E-04 30-YEAR COMBINED RISK (ADULT + CHILD) = 2.3E-04 -0 CG Pagel 12#7»4 ' TABi. SS-IH-RES1CTC.XLS CENTRAL TENDENCY CALCULATIONS SURFACE SOIL INHALATION OF PARTICULATES PATHWAY TUTU WELLS SITE - FUTURE-USE SCENARIO RISKS TO RESIDENTS (INSIDE AND OUTSIDE RESIDENCE) IN THE TILLETT GARQENS AND ART CENTER AREA NONCARCINOGENS - REASONABLE MAXIMUM CASE SURFACE SOIL INHALATION EXPOSURE - Children (0-6 years) Chronic Daily lntake= Soil X Soil (mg/kg-day) Concen. Concert. mg/kg X 0.070 mo/m3 Susp. Soil Soil Chemicals Concen. Concen. Manganese 8.69E+02 7.0E-02 X Resp. X Inhalation X Exposure X Exposure X Exposure X Conv. X 1 X 1 Fraction Rate Time Frequency Duration Factor BodyWt AvgingTime X (unittess) X 0.83 m3/hr X 12hrs/day X 275days/yr X 6 years X 1 kg X 1 X 1 Resp. Inhalation Exposure Exposure Exposure Fraction Rate Time Frequency Duration 0.75 0.83 12 275 6 1000000 mg Conv. Factor 1.0E-06 15kg Body Weight 15 2190 days Averaging Time 2190 Chronic Daily Reference Intake (CDI) Dose (RfD) 2.3E-05 1.4E-05 HQ= CDI/RfD 1.6E+00 HAZARD INDEX = 1.6E+00 ••0 •-0 GW-IN-RESCTC.XLS TABLfc •' CENTRAL TENDENCY CALCULATIONS GROUNDWATERINGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS CARCINOGENS - GROUNDWATER INGESTION EXPOSURE: Adults Chronic Daily lnlake= Water X Ingestion X Exposure X Exposure X_ CARCINOGENS - GROUNDWATER INGESTION EXPOSURE: Children (0-6 years) (mgrttg-day) Chemicals Benzene Tetrachloroelhene Vinyl Chloride Arsenic Beryllium Concentration Rate mg/l X 1.4 Way X Water Concentration 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 Ingestion Rate 1.4 1.4 1.4 1.4 1.4 Frequency 275 days/year Exposure Frequency 275 275 275 275 275 Duration X 9 years X Exposure Duration 9 9 9 9 9 Body Weight Averaging Time 1 X 1 70kg Body Weiqht 70 70 70 70 70 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Daily Intake (CDI) 1.2E-04 3.9E-04 3.9E-05 1.9E-06 1.9E-06 Slope Factor (SF) 2.9E-02 5.2E-02 1.9E+00 1.75E+00 4.3E+00 RISK = (CDI'SF) 3.4E-06 2.0E-05 7.4E-05 3.4E-06 8.3E-06 TOTAL RISK = 1.IE-04 Chronic Daily Intakes (mg/kg-day) Chemicals Benzene Telrachloroethene Vinyl Chloride Arsenic Beryllium Water X Ingestion X Concentration Rate mg/l X 0.7 Way X Water Ingestion Concentration Rate 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 0.7 0.7 0.7 0.7 0.7 Exposure Frequency 275 days/year Exposure Frequency 275 275 275 275 275 X Exposure X Duration X 6 years X Exposure Duration 6 6 6 6 6 1 Body Weight 1 15kg Body Weight 15 15 15 15 15 X 1 Averaging Time X 1 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Dairy Intake (CDI) 1.8E-04 6.0E-04 6.0E-05 3.0E-06 3.0E-06 Slope Factor (SF) 2.9E-02 5.2E-02 1.9E+00 1.75E+00 4.3E+00 RISK = (CDI'SF) 5.2E-06 3. IE-05 1. IE-04 5.3E-06 1.3E-05 TOTAL RISK = 1.7E-04 /27/w OW-IN-RESCTC.XLS TABLt CENTRAL TENDENCY CALCULATIONS GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE - USE SCENARIO RISKS TO RESIDENTS DNCARCINOGENS -GROUNDWATER INGESTION EXPOSURE: Adult* Chronic Daily Intake^ Water X Ingestbn X Exposure X Exposure X (mg/kg-day) Chemicals 1 ,2-Dichloroethene(Total) Tetrachloroethene Toluene Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Concentration Rate mg/l X 1.4 I/day X Water Ingestbn Concentration Rate 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 .4 .4 .4 .4 .4 .4 .4 .4 .4 .4 Frequency 275 days/year Exposure Frequency 275 275 275 275 275 275 275 275 275 275 Duration X 9 years X Exposure Duration 9 9 9 9 9 9 9 9 9 9 1 X 1 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 70 70 70 70 70 70 70 70 3285 days Averaging Time 3285 3285 3285 3285 3285 3285 3285 3285 3285 3285 Chronic Daily Intake (GDI) 5.9E-03 3.0E-03 4.5E-04 1.5E-04 1.5E-05 1.5E-05 3.0E-04 7. IE-02 1.1E-03 1.7E-03 Reference Dose (RfD) 9.0E-03 1.0E-02 2.0E-01 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HQ= CDI/RfD 6.5E-01 3.0E-01 2.3E-03 3.8E-01 5.0E-02 3.0E-03 6.0E-02 1.4E401 5.3E-02 2.4E-01 HAZARD INDEX = 1.6E-t01 NONCARCINOGENS -GROUNDWATER INGESTION EXPOSURE: Children (0 - 6 years) Chronic DaiV lntake= (mg/kg-day) Chemicals 1 .2-Dichtoroethene(Total) Telrachloroethene Toluene Antimony Arsenic Berylium Chromium VI Manganese Nickel Vanadium Water X Ingestion X Concentration Rate mg/l X 0.7 Way X Water Concentration 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 Ingestbn Rate 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 Exposure Frequency 275 days/year Exposure Frequency 275 275 275 275 275 275 275 275 275 275 X Exposure X Duration X 6 years X Exposure Duration 6 6 6 6 6 6 6 6 6 6 1 X 1 Body Weight Averaging Time 1 X 1 15kg Body Weight 15 15 15 15 15 15 15 15 15 15 2190 days Averaging Time 2190 2190 2190 2190 2190 2190 2190 2190 2190 2190 Chronic Daily Intake (CDI) 1.4E-02 7.0E-03 1. IE-03 3.5E-04 3.5E-05 3.5E-05 7.0E-04 1.6E-01 2.5E-03 3.9E-03 Reference Dose (RfD) 9.0E-03 1.0E-02 2.0E-01 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HQ= CDI/RfD 1.5E+00 7.0E-01 5.3E-03 8.8E-01 1.2E-01 7.0E-03 1.4E-01 3.3E+01 1.2E-01 5.5E-01 O XT HAZARD INDEX = 3.7E+01 O hJ O H- 3/7/9:. TABLE L-w GW-IN.SWCTC.XLS CENTRAL TENDENCY CALCULATION GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE WORKERS CARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE: Adults 1 X Chronic Daily Intake* (mg/kg-day) Water X Ingestion X Concentration Rate Exposure X Exposure X 1_____ X ____1_____ Frequency Duration Body Weight Averaging Time mg/l X 1 1/day X Chemicals Benzene Tetrachloroethene Vinyl Chloride Arsenic Beryllium Water Concentration 6.00E-02 2.00E-01 2.00E-02 1.00E-03 1.00E-03 Ingestion Rate 1 1 1 1 1 185 days/year Exposure Frequency 185 185 185 185 185 X 25 years X Exposure Duration 25 25 25 25 25 1 X 1 70kg Body Weight 70 70 70 70 70 25550 days Averaging Time 25550 25550 25550 25550 25550 Chronic Daily Intake (GDI) 1.6E-04 5.2E-04 5.2E-05 2.6E-06 2.6E-06 Slope Factor (SF) 2.9E-02 5.2E-02 1.9E+00 1.75E+00 4.3E+00 RISK = (CDI'SF) 4.5E-06 2.7E-05 9.8E-05 4.5E-06 1.1E-05 TOTAL RISK. 1.5E-04 Oo •-.i Pagel -i GW-IN-SWCTC.XLS TABLt CENTRAL TENDENCY CALCULATION GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - PRESENT/FUTURE-USE SCENARIO RISKS TO SITE WORKERS ONCARCINOGENS - REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE: Adults Chronic Daily Intake* Water X Ingestion X Exposure X Exposure XIX 1 (mg/kg-day) Chemicals 1,2-Dichtoroelnene (Total) Tetrachloroethene Toluene Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Concentration Rate mg/l X 11/day X Water Concentration 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 Ingestion Rate 1 1 1 1 1 1 1 1 1 1 Frequency 185 days/year Exposure Frequency 185 185 185 185 185 185 185 185 185 185 Duration X 25 years X Exposure Duration 25 25 25 25 25 25 25 1 25 25 25 Body Weight Averaging Time 1 X 1 70kg Body Weight 70 70 70 70 70 70 70 70 70 70 9125 days Averaging Time 9125 9125 9125 9125 9125 9125 9125 9125 9125 9125 Chronic Dairy Intake (GDI) 2.8E-03 1.4E-03 2.2E-04 7.2E-05 7.2E-06 7.2E-06 1.4E-04 3.4E-02 5.1E-04 8.0E-04 Reference Dose (RfD) 9.0E-03 1.0E-02 2.0E-01 4.0E-04 3.0E-04 5.0E-03 5.0E-03 5.0E-03 2.0E-02 7.0E-03 HQ= CDI/RfD 3.1E-01 1.4E-01 1. IE-03 1.8E-01 2.4E-02 1.4E-03 2.9E-02 6.8E400 2.5E-02 1. IE-01 HAZARD INDEX •. 7.6E+00 O 6W-IN-CWCTC .XLS TABLE u-o CENTRAL TENDENCY CALCULATIONS GROUNDWATER INGESTION PATHWAY TUTU WELLS SITE - FUTURE - USE SCENARIO RISKS TO CONSTRUCTION WORKERS ONCARCINOGENS • REASONABLE MAXIMUM CASE GROUNDWATER INGESTION EXPOSURE Subchronic Daily Intake- Water X Ingestion X Exposure X Exposure X 1 X 1 (mg/kg-day) Chemicals 1,2-DicNoroethene (Total) Tetrachloroethene Toluene Antimony Arsenic Beryllium Chromium VI Manganese Nickel Vanadium Concentration Rate Frequency Duration Body Weight Averaging Time mg/l X 1 1/day X 130 days/year X 1 year X 1 X 1 Water Ingestion Exposure Concentration Rate Frequency 3.90E-01 2.00E-01 3.00E-02 1.00E-02 1.00E-03 1.00E-03 2.00E-02 4.68E+00 7.00E-02 1.10E-01 130 130 130 130 130 130 130 130 130 130 Exposure Duration 1 1 1 1 1 1 1 1 1 1 1 70kg Body Weight 70 70 70 70 70 70 70 70 70 70 365 days Averaging Time 365 365 365 365 365 365 365 365 365 365 Subchronic Daily Intake (SDI) 2.0E-03 1.0E-03 1.5E-04 5. IE-05 5. IE-06 5.1E-06 1.0E-04 2.4E-02 3.6E-04 5.6E-04 Reference Dose (RfD) 9.0E-03 1.0E-01 2.0E+00 4.0E-04 3.0E-04 5.0E-03 2.0E-02 5.0E-03 2.0E-02 7.0E-03 HQ= SDI/RfD 2.2E-01 1.0E-02 7.6E-05 1.3E-01 1.7E-02 1.0E-03 5.1E-03 4.8E+00 1.8E-02 8.0E-02 HAZARD INDEX > 5.2E+00 r--J O -is, Pagel APPENDIX E SITE DATA TUT 007 0205 Tutu, St. Thomas, U.S. Virgin Islands Subsurface Soil - Background Inorganic Analytes 08/18/1994 9:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg Dig/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MWS-2 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 13,300.00 4.50 UNJ 3.00 81.00 0.22 U 0.67 U 68.500.00 *J 16.10 NJ 11.30 40.00 NJ 21,700.00 5.60 J 9,160.00 582.00 0.06 U 12.70 557.00 B 0.45 U 0.89 U 717.00 B 0.67 U 58.00 NJ 66.20 0.56 U MWS-2-FR 08/13/92 SOIL 0.0'-2.0' V.SV.l.T 15,700.00 4.60 UNJ 1.20 B 45.60 B 0.23 U 0.69 U 8,720.00 *J 7.60 NJ 12.80 58.00 NJ 30,800.00 1.90 J 9,640.00 1,110.00 0.06 U 5.60 B 299.00 B 0.46 U 1.20 B 536.00 B 0.69 U 52.80 NJ 119.00 0.57 U MUS-2-AVD 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 14,500.00 4.55 UNJ 2.10 B 63.30 0.23 U 0.68 U 38,610.00 *J 11.85 NJ 12.05 49.00 NJ 26,250.00 3.75 J 9,400.00 846.00 0.06 U 9.15 B 428.00 B 0.46 U 0.82 B 626.50 B 0.68 U 95.40 NJ 92.60 0.57 U M O 0- OO Nl Tutu, St. Thomas, U.S. Virgin Islands Tillett Gardens Area - Surface Soil Organic Compounds 06/17/1994 8:10 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHAME BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-OICHLOROETHENE 1,1 -01 CHLOROETHANE 1.2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-DICHLOROETHANE 2-BUTANONE 1.1,1 -TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMODICHLOROMETHANE 1.2-DICHLOROPROPANE cis 1,3-DlCHLOROPROPENE TRICHLOROETHYLENE D I BROMOCHLOROMETHANE 1.1. 2- TRICHLOROETHANE BENZENE Trans 1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHYLENE 1 , 1 , 2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZNE STYRENE XYLENES (TOTAL) 1,2-DlBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg . ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-5 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 10.00 J 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ SS-5 -COM 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 16.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA NA NA SS-5-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 u 11.00 U 9.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 UJ 11.00 U 11.00 U 11.00 UJ NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ err- us 09/13/88 SOIL 0.0'-2.0' V.P.T R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R 11.00 J NA NA NA eTT-155 09/13/88 SOIL 0.0'-2.0' V.P.T 15.00 U 15.00 U 15.00 U 15.00 U 62.00 U 62.00 UJ r.oo u 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 15.00 U 7.00 U 7.00 U 15.00 UJ 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 15.00 UJ 15.00 UJ 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U 7.00 U NA NA NA KiO •'•4 O Tutu, St. Thomas, U.S. Virgin Islands Tiltett Gardens Area - Surface Soil Organic Compounds 06/24/1994 2:02 PH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1 , 2 , 4 - TR I CHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6- TRICHLOROPHENOL 2,4,5-TRlCHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg • ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-5 08/19/92 SOIL 0.0'-2.0' V.SV.I 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 950.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U SS-5-CDM 08/19/92 SOIL 0.0--2.0' V.SV.I 370.00 UJ 370.00 UJ 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 900.00 U 370.00 U 900.00 UJ 370.00 U 370.00 U 370.00 U SS-5-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 380.00 UJ 380.00 UJ 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 U 475.00 U 380.00 U 475.00 UJ 380.00 U 380.00 U 380.00 U eTT-145 09/13/88 SOIL 0.0'-2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eTT-155 09/13/88 SOIL 0.0--2.01 V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA o K3 OO Tutu, St. Thomas, U.S. Virgin Islands Til Lett Gardens Area - Surface Soil Organic Compounds 06/17/1994 8;15 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHEMOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4,6-DlNITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CO) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-5 08/19/92 SOIL 0.0'-2.0- V.SV.I 950.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U 55.00 J 100.00 J 76.00 J 190.00 J 390.00 U 390.00 U 59.00 J 430.00 U 390.00 U 84.00 J 390.00 UJ 390.00 U 390.00 U 390.00 U 82.00 J SS-5-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I 900.00 UJ 370.00 U 900.00 UJ 900.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 900.00 UJ 900.00 U 370.00 U 370.00 U 370.00 U 900.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 78.00 J 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U SS-5-AVS 08/19/92 SOIL 0.0'-2.0' v.sv.i 925.00 UJ 380.00 U 925.00 UJ 925.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 925.00 UJ 925.00 U 380.00 U 380.00 U 380.00 U 925.00 U 380.00 U 380.00 U 380.00 U 55.00 J 100.00 J 76.00 J 154.00 J 380.00 U 380.00 U 59.00 J 400.00 U 380.00 UJ 84.00 J 380.00 UJ 380.00 U 380.00 U 380.00 U 82.00 J eTT-148 09/13/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eTT-155 09/13/88 SOIL 0.0'-2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA • -i Tutu, St. Thomas, U.S. Virgin Islands Til Lett Gardens Area - Surface Soil Organic Compounds 06/17/1994 8:14 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides ALPHA-BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDRIN HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4, 4' -DDE ENDRIN, TOTAL ENDOSULFAN II 4, 4' -ODD ENDOSULFAN SULFATE 4,4' -DOT METHOXYCHLOR ENDRIN KETONE ALPHA- CHLORDANE CAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 rf ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ss-5 08/19/92 SOIL O.O'-Z.O' V.SV.I NA HA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-5-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-5-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA ,MA 'NA NA NA NA NA NA eTT-US 09/13/88 SOIL O.O'-Z.O1 V,P,T 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 20.00 UJ 20.00 UJ 20.00 UJ 20.00 UJ 20.00 UJ 20.00 UJ 20.00 UJ 99.00 UJ 20.00 UJ 99.00 UJ 99.00 UJ 200.00 UJ 99.00 UJ 99.00 UJ 99.00 UJ 580.00 UJ 99.00 UJ 200.00 UJ 200.00 UJ eTT-155 09/13/88 SOIL 0.0'-2.0' V,P,T ,700.00 UJ ,700.00 UJ ,700.00 UJ ,700.00 UJ ,700.00 UJ ,700.00 UJ ,700.00 UJ ,700.00 UJ 3,400.00 UJ 3,400.00 UJ 3,400.00 UJ 3,400.00 UJ 3,400.00 UJ 3,400.00 UJ 3,400.00 UJ 17,000.00 UJ 3,400.00 UJ 17,000.00 UJ 17,000.00 UJ 34,000.00 UJ 17,000.00 UJ 17,000.00 UJ 17,000.00 UJ 120,000.00 J 17,000.00 UJ 34,000.00 UJ 34,000.00 UJ H-O Tutu, St. Thomas, U.S. Virgin Islands Til Lett Gardens Area - Surface Soil Inorganic Analytes 06/17/1994 8:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, total mg/kg rag/kg mg/kg ntg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg SS-5 08/19/92 SOIL O.O'-Z.O' V.SV.I 17,700.00 8.20 BNJ 3.50 97.00 0.22 U 0.66 U 35,800.00 17.60 NJ 19.40 J 79.20 NJ 28,100.00 149.00 SJ 13,600.00 708.00 0.19 12.60 4,170.00 0.44 U 2.80 349.00 B 0.66 U 78.80 NJ 216.00 0.55 U SS-5-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I 24,900.00 3.80 U 16.50 134.00 0.28 B 0.35 U 36,000.00 33.00 20.70 80.10 37,400.00 23.70 12,900.00 1,030.00 0.10 U 15.10 2,610.00 J 0.80 U 1.50 B 306.00 B 0.20 UJ 113.00 121.00 0.55 U SS-5-AVS 08/19/92 SOIL 0.0'-2.0' V,SV,I 21,300.00 5.05 BNJ 10.00 70.50 0.20 B 0.51 U 35,900.00 25.30 NJ 20.05 J 79.65 NJ 32,750.00 86.35 SJ 13,250.00 869.00 0.12 13.85 3,390.00 J 0.62 U 2.15 B 327.50 B ,0.43 UJ 95.90 NJ 168.50 0.55 U eTT-14S 09/13/88 SOIL 0.0'-2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eTT-155 09/13/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA c Tutu, St. Thomas, U.S. Virgin Islands Tillett Gardens Area - Surface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS Dig/kg SS-5 08/19/92 SOIL O.O'-Z.O' V.SV.I NA SS-5-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.l NA SS-5-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I NA eTT-148 09/13/88 SOIL 0.0'-2.0' V.P.T 0.18 J 06/17/1994 8:15 AM eTT-15S 09/13/88 SOIL 0.0'-2.0' V,P,T 0.22 J -f o NJ Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:12 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1-D I CHLOROETHANE 1,2-DICHLOROETHEME (TOTAL) CHLOROFORM 1,2-DJ CHLOROETHANE 2-BUTANONE 1,1,1-TR I CHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-DICHLOROPROPENE TRICHLOROETHENE D I BROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans-1 ,3-OICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0' v.sv.i 13.00 U 13.00 U 13.00 U 13.00 U 22.00 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 35.00 13.00 U 13.00 U NA 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 4.00 J 13.00 U 3.00 J 13.00 U 19.00 6.40 U 13.00 UJ 6.40 UJ NA SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,I 65.00 U 65.00 U 65.00 U 65.00 U 84.00 UJ 91.00 UJ 65.00 U 65.00 U 65.00 U 65.00 U 7.00 J 65.00 UJ 54.00 J 65.00 U 65.00 U NA 65.00 U 65.00 U 65.00 U 65.00 J 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U NA NA NA NA SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 39.00 U 39.00 U 39.00 U 39.00 U 22.00 52.00 UJ 39.00 U 39.00 U 39.00 U 39.00 U 6.75 J 39.00 UJ 44.50 J 39.00 U 39.00 U NA 39.00 U 39.00 U 39.00 U 65.00 J 39.00 U 19.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 4.00 J 39.00 U 3.00 J 39.00 U 19.00 6.40 U 13.00 UJ 6.40 UJ NA SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 8.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ NA SS-4-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,I 11.00 U 11.00 U 11.00 U 11.00 U 22.00 UJ 14.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA NA NA NA SS-4-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 8.00 J 125.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 UJ 11.00 U 11.00 U 11.00 UJ NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ NA c /.oo mi 03 <•» -> x w m r> — < — » •••• » co •• -< — 4 «H z o<* OJ-DT roi--<zr-i--» so SB -"=j— in -*oo<n-*r\>-*n — »~»-*n> i i so -i m» •- so **•« so •— >« > » z» » » ^o iz3EOa> z -»O>~B> t\>oa5;o-»cor\jr-r\J-»-»som m m x 3 M- so o > > 36 -< CD- c > O ' > i o » — i x— low miuQz-»OQr-o-»-»o:ooc»ooO ~ m z co o z- o » z -n • z i at i— - — o z i 3> — o— — — zz oo «/i m rn GO m roz z -< o -»m -4 o o wo — > — i z n -n o n o m :o z m it— or- TO> so o » i o r o o — ijoozozazzo '^ IMSB -H o z: i i w ~a:oor-zmm — zr"soi— r-r-— m M msomro > n r~ m ~ o r- -< -H omo Z Q Q Q in -i o i o KO-<r>soo3»soz so sasSsec: som -o — r~ ?o.:x 3= o so — 4 ^ r~ o ooor* > -< m o O o m i— -u o m r> o ni mmrn-n nz z z SB X z o -4 i— ommso m - 4 O -HZ z> J » z o m z o > f n s o z m * x i m m z Q m m m 'o z m m -u o m r> o so ae ac om r- ' c - H O > z 50 - so z > —< m zzzo m > m m zzz m m m 2g Sooooooogggggooooooogooooog C C C C C C C C . C C - C C C C C C C C C C C C C C C C goggg C C C C ooooooooooooooooooooo ooooooooooooooooooooo ooooooooooooooo ooooooooooooooo C C C C C C C C C CC C CCC.CCC C C C C C CC C C CC CCCC o-o^o oooooooooooooo ooo ooooooooooooooo ooooooooooooooooooooo ccccccee-c ooooooooooooooo c c= c c c c IV)o ooooooo ooooooo ooooooooooooooooooooo ooooooooooooooooooooo C C C C C C C C oooo oooo oooooooooooooooooooooooooooo ^3 O O €3 O O C3 O O O O O O c-CC C C C C C C C C C ooooooooooooooooooooooooooooo oooo ooooooooooooooooooooooooooooo oooo cerc c c cccccccccccccccccc cccc TJ -D -H —4 m m z .-=0 § S r ^ « PJOT *-CD ~. O^ i • O-"C-» -4 - r- N) js *»BJ . O— -O-^ -t - i— ruui § PJCO *• GO . O""- i o — o-« p < fvi ID §7 2 r o* . _»</) CT« I -o - o— oo-» -4 - 1— >O<O o n <. or- - o o^ i en - "»o i -o. o- - < PJ • Ul (/) - -^8 §7 orj c> • _ •-. o — o»OJ r- ^ (/> oc •o ^. 0) ™*J IV) CD •« -O n -***. ro -* c oo Xi Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:12 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1 -01 CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-DICHLOROETHANE 2-BUTANONE 1.1,1-TR I CHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-DICHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans-1 ,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1,1,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg • ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-16 04/04/94 SOIL 0.0- - 2.0' V.SV.I.T 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 72.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 55.00 U R R HWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 11.00 UJ 11.00 U 11.00 U 11.00 U 1.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 u 11.00 u 35.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 55.00 U R R MUS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 11.00 UJ 11.00 U 11.00 U 11.00 U 1.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 53.50 J 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00U NA 55.00 U R R H- (P. Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present • Surface Soil Organic Compounds 07/29/1994 7:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE D1METHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0' V.SV.l R R R R R NA R R R R R R R R R R NA R R R R R R R R R R R R R R R R SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I R 13000.0 UJ R 13000.0 UJ 13000.0 UJ NA 13000.0 UJ R 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R R NA 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ R R 13000.0 UJ 32000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I R 13000.0 UJ R 13000.0 UJ 13000.0 UJ NA 13000.0 UJ R 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R R NA 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ R R 13000.0 UJ 32000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-4 08/19/92 SOIL 0.0'-2.0' v.sv.i R R R R R NA R R R R R R R R R R NA R R R R R R R R R R R R R R R R SS-4-CDM 08/19/92 SOIL 0.0--2.01 V.SV.I 11000.0 UJ 11000.0 UJ 11000.0 uj 11000.0 uj 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ SS-4-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ c —! Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:13 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-D!CHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DlMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DlCHLOROPHENOL 1,2,4-TRlCHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRlCHLOROPHENOL 2 , 4 , 5 - TR I CHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE OIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-14 08/14/92 SOIL 0.0'-2.0' V,SV,I,T 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U NA 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U NA 370.0 U 370.0 U 370.0 U 370.0 U 370.0 UJ 370.0 UJ 370.0 U 370.0 U 370.0 UJ 370.0 U 910.0 UJ 370.0 U 910.0 U 370.0 U 370.0 U 370.0 U B-15 08/14/92 SOIL 0.0--2.0' V.SV.I.T 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U NA 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U NA 390.0 U 390.0 U 390.0 U 390.0 U 390.0 UJ 390.0 UJ 390.0 U 390.0 U 390.0 UJ 390.0 U 950.0 UJ 390.0 U 950.0 U 390.0 U 390.0 U 390.0 U B-16 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U NA 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U NA 370.0 U 370.0 U 370.0 U 370.0 U 570. 0 UJ 370.0 UJ 370.0 U 370.0 U 370.0 UJ 370.0 U 890.0 UJ 370.0 U 890.0 U 370.0 U 370.0 U 370.0 U eL-02-018 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 900000.0 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 320000.0 78000.0 U 1300000.0 J 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 42000.0 J 380000.0 U 78000.0 U 78000.0 U 78000.0 U 7700.0 J 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 380000.0 U 78000.0 U 380000.0 U 78000.0 U 78000.0 U 78000.0 U eL-02-02S 06/06/89 SOIL O.O'-O.S' V,SV,P,T 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 19000.0 U 3900.0 U 3900.0 U 3900.0 U 4100.0 3900.0 U 3900.0 U 3900.0 U 750.0 J 3900.0 U 3900.0 U 19000.0 U 3900.0 U 19000.0 U 3900.0 U 3900.0 U 3900.0 U eL-02-03S 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 4100.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 4100.0 U 850.0 U 4100.0 U 850.0 U 850.0 U 850.0 U O hJ —I Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CNLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-MEtHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI -N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-OIHETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NltROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MWS-16 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U NA 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U NA 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 UJ 360.0 U 880.0 U 360.0 U 880.0 U 360.0 U 360.0 U 360.0 U MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U NA 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U NA 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 810.0 U 340.0 U 810.0 U 340.0 U 340.0 U 340.0 U MWS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U NA 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U NA 350.0 U 350:0 u 350.0 U 350.0 U 550. 0 U 350.0 U 350.0 U 350.0 U 350.0 UJ 350.0 U 845.0 U 350.0 U 845.0 U 350.0 U 350.0 U 350.0 U O H U~H Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolati les-2 3-NITROAN1LINE ACENAPHTHENE 2,4-DINlTROPHENOL 4-NITROPHENOL D1BENZOFURAN 2,4-DINlTROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4,6-DINITRO-2-METHYLPHENOL N-N1TROSOOIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DlCHLOROB£NZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B)FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE D I BENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0' V.SV.I R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R SS-3-CDM 08/19/92 SOIL O.O'-Z.O1 V.SV.I 32000.0 UJ 13000.0 UJ R R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 32000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 9400.0 J 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 1300Q.O UJ SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 32000.0 UJ 13000.0 UJ R R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 32000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 9400.0 J 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-4 08/19/92 SOIL O.O'-Z.O1 V,SV,I R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R SS-4-CDM 08/19/92 SOIL O.O'-Z.O' V.SV.I 28000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ ' 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 1800.0 J 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ SS-4-AVS 08/19/92 SOIL O.O'-Z.O' v.sv.i 28000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 1800.0 J 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 uj 11000.0 uj 11000.0 uj 11000.0 UJ K3 Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE DIETHYLPHTHALATE 4 - CHLOROPHENYL - PHEN YLETHER FLUORENE 4-NITROANILINE 4.6-DINITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-6ROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-OICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B)FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1.2,3-CD) PYRENE DIBEMZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-14 08/14/92 SOIL 0.0'-2.0' V,SV,!,T 910.0 UJ 370.0 U 910.0 U 910.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 910.0 U 910.0 U 370.0 U 370.0 U 370.0 UJ 910.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 UJ 370.0 U 370.0 U 370.0 U 370.0 U B-15 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 950.0 UJ 390.0 U 950.0 U 950.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 950.0 U 950.0 U 390.0 U 390.0 U 390.0 UJ 950.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 U 390.0 UJ 390.0 U 390.0 U 390.0 U 390.0 U B-16 08/14/92 SOIL 0.0'-2.0' V.SV.IJ 890.0 UJ 370.0 U 890.0 U 870.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 890.0 U 890.0 U 370.0 U 370.0 U 370.0 UJ 890.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U '58.0 J 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 U 370.0 UJ 370.0 U 370.0 U 370.0 U 370.0 U CL-02-01S 06/06/89 SOIL 0.25--1.0' V.SV.P.T 380000.0 U 78000.0 U 380000.0 U R 78000.0 U R 78000.0 U 78000.0 U 78000.0 U 380000.0 U 380000.0 U 78000.0 U 78000.0 U 78000.0 U R 78000.0 U 78000.0 U NA 78000.0 U 78000.0 U 78000.0 U 78000.0 U 160000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U eL-02-025 06/06/89 SOIL 0.0--0.5' V.SV.P.T 19000.0 U 3900.0 U 19000.0 U 19000.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 19000.0 U 19000.0 U 3900.0 U 3900.0 U 3900.0 U 19000.0 U 3900.0 U 3900.0 U NA 3900.0 U 3900.0 U 3900.0 U 3900.0 U 7900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U eL-02-03S 06/06/89 SOIL 0.25--1.0' V,SV,P,T 4100.0 U 850.0 U 4100.0 U 4100.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 4100.0 U 4100.0 U 850.0 U 850.0 U 850.0 U 4100.0 U 850.0 U 850.0 U NA 850.0 U 850.0 U 850.0 U 120.0 J 1700.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U OO o Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolati les-2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-N1TROANILINE 4.6-D1NITRO-2-METHYLPHENOL N-NITROSCOIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3>-DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B)FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg . ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-16 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 880.0 UJ 360.0 U 880.0 UJ 880.0 UJ 360.0 U 360.0 U 360.0 UJ 360.0 U 360.0 U 880.0 UJ 880.0 U 360.0 U 360.0 U 360.0 U 880.0 UJ 360.0 U 360.0 U 360.0 UJ 52.0 J 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U MUS-16-FR 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 810.0 UJ 340.0 U 810.0 UJ 810.0 UJ 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 810.0 U 810.0 UJ 340.0 U 340.0 U 340.0 U 810.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U MWS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 845.0 UJ 350.0 U 845.0 UJ 845.0 UJ 350.0 U 350.0 U 350.0 UJ 350.0 U 350.0 U 845.0 UJ 845.0 UJ 350.0 U 350.0 U 350.0 U 845.0 UJ 350.0 U 350.0 U 350.0 UJ 52.0 J 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U K3 I-* c —1 f~l Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides\Pcbs ALPHA-BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDR1N HEPTACHLOR EPOXIDE ENDOSULFAN I OIELDRIN 4.4-DDE ENDR1N, TOTAL ENDOSULFAN II 4,4-DDD ENDOSULFAN SULFATE 4,4-DDT METHOXYCHLOR ENDRIN KETONE ALPHA-CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-12S4 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-3-CDM 08/19/92 SOIL 0.0--2.0' V,SV,I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-4-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-4-AVS 08/19/92 SOIL 0.0*-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA --i oO Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides \Pcbs ALPHA-BHC BETA-BHC DELTA-BHC L1NDANE, TOTAL HEPTACHLOR ALDR1N HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4,4-ODE ENDR1N, TOTAL ENDOSULFAN II 4,4-DDD ENDOSULFAN SULFATE 4,4-DDT METHOXYCHLOR ENDRtN KETONE ALPHA-CHLORDANE GAMNA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-14 08/14/92 SOIL 0.0'-2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA B-15 08/14/92 SOIL 0.0'-2.0' V,SV,I,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA B-16 08/14/92 SOIL 0.0'-2.0' V,SV,I,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA eL-02-015 06/06/89 SOIL 0.25'-1.0- V,SV,P,T 47.00 U 47.00 U 47.00 U 47.00 U 47.00 U 47.00 U 47.00 U 92.00 94.00 U 94.00 U 94.00 U 94.00 U 94.00 U 94.00 U 94.00 U 470.00 U 94.00 U 470.00 U 470.00 U 940.00 U 470.00 U 470.00 U 470.00 U 470.00 U 470.00 U 940.00 U 940.00 U eL-02-02S 06/06/89 SOIL 0.0--0.5' V,SV,P,T 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 75.00 U 75.00 U 75.00 U 75.00 U 75.00 U 75.00 U 75.00 U 380.00 U 75.00 U 380.00 U 380.00 U 750.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 750.00 U 750.00 U eL-02-035 06/06/89 SOIL 0.25'-1.0' V,SV,P,T 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 100.00 U 20.00 U 100.00 U 100.00 U 200.00 U 100.00 U 100.00 U 100.00 U 100.00 U 100.00 U 200.00 U 200.00 U O f..". Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Organic Compounds 07/29/1994 7:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides\Pcbs ALPHA-BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACNLOR ALDRIN HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4,4-DDE ENDRIN, TOTAL ENDOSULFAN II 4,4-DDD ENDOSULFAN SULFATE 4, 4 -DOT METHOXYCHLOR ENDRIN KETONE ALPHA-CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOft-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-16 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MUS-16-AVD 04/04/94 SOIL O.O1 - 2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Inorganic Analytes 07/29/1994 7:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg rag/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg SS-3 08/19/92 SOIL 0.0'-2.0' V,SV,I 23,100.00 7.20 BNJ 1.70 B 94.20 0.26 U 0.77 U 56,500.00 33.80 NJ 22.10 J 72.80 NJ 55,400.00 12.20 J 18,700.00 886.00 0.06 U 19.20 7,140.00 0.51 U 2.10 B 476.00 B 0.77 U 88.30 NJ 258.00 0.96 SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,1 26,900.00 4.10 U 2.90 98.30 0.25 B 0.37 U 49,600.00 34.10 23.40 75.00 42,200.00 27.70 18,700.00 841.00 0.12 U 17.10 8,110.00 J 0.88 UJ 1.70 B 501.00 B 0.22 UJ 102.00 313.00 0.62 U SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 25,000.00 4.63 BNJ 2.30 B 96.25 0.19 B 0.57 U 53,050.00 33.95 NJ 22.75 J 73.90 NJ 48,800.00 19.95 J 18,700.00 863.50 0.09 U 18.15 7,625.00 J 0.70 UJ 1.90 B 488.50 B 0.50 UJ 95.15 NJ 285.50 0.64 SS-4 08/19/92 SOIL 0.0--2.0- V,SV,I 23,000.00 6.50 BNJ 0.92 BUJ 39.40 B 0.22 U 0.66 U 61,100.00 25.10 NJ 20.90 J 62.90 NJ 29,800.00 9.10 J 19,300.00 634.00 0.05 U 16.80 673.00 B 0.44 U 0.93 B 352.00 B 0.66 U 86.00 NJ 265.00 0.57 U SS-4-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,I 30,900.00 3.30 U 2.00 B 49.00 0.14 U 0.30 U 51,000.00 31.80 21.30 71.50 35,100.00 13.50 18,500.00 719.00 0.10 U 16.10 1,150.00 J 0.73 U 1.40 B 453.00 B 0.18 UJ 107.00 371 .00 0.50 U SS-4-AVS 08/19/92 SOIL 0.0'-2.0' V,SV,I 26,950.00 4.08 BNJ 1.46 BUJ 44.20 B 0.18 U 0.48 U 56,050.00 28.45 NJ 21.10 J 67.20 NJ 32.450.00 11.30 J 18,900.00 676.50 0.08 U 16.45 911.50 BJ 0.59 U 1.17 B 402.50 B 0.42 UJ 96.50 NJ 318.00 0.54 U H I1""': W K3 fjt Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Inorganic Analytes 07/29/1994 7:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-14 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 25,300.00 7.30 BNJ 0.46 U 34.50 B 0.23 U 0.70 U 120,000.00 * 13.80 NJ 20.00 48.30 NJ 28,000.00 2.90 J 26,200.00 757.00 0.06 U 11.10 161.00 B 0.46 UWJ 0.93 B 181.00 B 0.70 U 95.80 NJ 50.90 0.58 U B-15 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 26,400.00 6.40 BNJ 1.30 B 32.10 B 0.23 U 0.70 U 89,400.00 * 27.30 NJ 23.20 65.90 NJ 32,600.00 12.20 J 22,900.00 809.00 0.06 U 16.50 389.00 B 0.46 UUJ 1.10 B 281.00 B 0.70 U 98.80 NJ 206.00 0.75 B-16 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 18,900.00 6.80 BNJ 11.60 39.90 B 0.22 U 0.99 B 68,800.00 * 36.40 NJ 19.00 72.10 NJ 30,600.00 45.60 N*J 16,300.00 599.00 0.57 15.70 506.00 B 0.44 UWJ 1.30 B 396.00 B 0.67 U 79.70 NJ 459.00 0.55 U eL-02-015 06/06/89 SOIL 0.25'-1.0' V.SV.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eL-02-02S 06/06/89 SOIL O.O'-O.S' V,SV,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eL-02-035 06/06/89 SOIL 0.25'-1.0' V.SV.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA -ic o KJ 0- -i Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Inorganic Analytes 07/29/1994 7:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE. TOTAL dig/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MUS-16 04/04/94 SOIL 0.0' - 2.0' V.SV,I,T 25,700.00 5.00 UJ 2.10 41.30 B 0.28 B 0.84 U 22,800.00 39.10 J 27.40 J 135.00 35,300.00 3.20 22,000.00 927.00 0.05 U 21.50 151.00 U 0.42 U 0.63 U 384.00 U 0.42 U 120.00 51.70 0.52 U MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 29,000.00 5.20 UJ 0.77 B 26.50 B 0.25 B 0.97 B 54,400.00 45.30 J 23.70 J 82.40 36,900.00 3.00 25,100.00 818.00 0.05 U 21.90 175.00 B 0.43 U 0.65 U 396.00 U 0.43 U 109.00 52.30 0.54 U MUS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V,SV,!,T 27,350.00 5.10 UJ 2.10 33.90 B 0.27 B 0.70 B 38.600.00 42.20 J 25.55 J 108.70 36,100.00 3.10 23,550.00 872.50 0.05 U 21.70 125.25 B 0.43 U 0.64 U 390.00 U 0.43 U 114.50 52.00 0.53 U b -•4 Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg SS-3 08/19/92 SOIL 0.0'-2.0' V.SV.l NA SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I NA SS-3-AVS 08/19/92 SOIL 0.0--2.0' V.SV.I NA SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I NA SS-4-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I NA 07/29/1994 9:14 AM SS-4-AVS 08/19/92 SOIL 0.0'-2.0' v.sv.i NA QO K.I i-5 Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg B-14 08/14/92 SOIL 0.0'-2.0« V.SV.I.T 250.00 DJ B-15 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 24.00 U B-16 08/14/92 SOIL 0.0'-2.0' V.SV,I,T 82.00 J MWS-16 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 37.00 J MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 53.00 J 07/29/1994 9:14 AM MWS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 45.00 J -f I™1 two-f oo M W Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Present - Surface Soil Total Petroleum Hydrocarbons 07/29/1994 9:14 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS ug/g TOTAL PETROLEUM HYDROCARBONS ug/g eL-02-018 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 3,470.00 NA eL-02-02S 06/06/89 SOIL O.O'-O.S' V,SV.P,T 1,730.00 NA eL-02-035 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 544.00 NA Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:43 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organ ics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1 -D 1 CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-0 1 CHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOO I CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1 , 3-DICHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1 , 1 , 2-TRICHLOROETHANE BENZENE Trans-1, 3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1,1,2,2- TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL O.O'-Z.O' v.sv.i 13.00 U 13.00 U 13.00 U 13.00 U 22.00 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 35.00 13.00 U 13.00 U NA 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 4.00 J 13.00 U 3.00 J 13.00 U 19.00 6.40 U 13.00 UJ 6.40 UJ NA SS-3-CDM 08/19/92 SOIL 0.0'-2.0' v,sv,i 65.00 U 65.00 U 65.00 U 65.00 U 84.00 UJ 91.00 UJ 65.00 U 65.00 U 65.00 U 65.00 U 7.00 J 65.00 UJ 54.00 J 65.00 U 65.00 U NA 65.00 U 65.00 U 65.00 U 65.00 J 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U 65.00 U NA NA NA NA SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 39.00 U 39.00 U 39.00 U 39.00 U 22.00 52.00 UJ 39.00 U 39.00 U 39.00 U 39.00 U 6.75 J 39.00 UJ 44.50 J 39.00 U 39.00 U NA 39.00 U 39.00 U 39.00 U 65.00 J 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 39.00 U 4.00 J 39.00 U 3.00 J 39.00 U 19.00 6.40 U 13.00 UJ 6.40 UJ NA SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 8.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ NA SS-4-CDM 08/19/92 SOIL O.O'-Z.O' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 22.00 UJ 14.00 UJ 11.00U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA NA NA NA SS-4-AVS 08/19/92 SOIL 0.0'-2.0' V,SV,I 11.00 U 11.00 U 11.00 U 11.00 U 8.00 J 125.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 UJ 11.00 U 11.00 U 11.00 UJ NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 u 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U n.oou 11.00 U 5.50 U 11.00 UJ 5.50 UJ NA HC Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:43 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULF1DE 1,1-DICHLOROETHENE 1,1-0 1 CHLOROETHANE 1,2-DlCHLOROETHENE (TOTAL) CHLOROFORM 1,2-OICHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROHOO I CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1, 3-D I CHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans- 1 ,3-D I CHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-OIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg .ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eL-02-OlS 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 57.00 UJ 57.00 UJ 57.00 UJ 57.00 UJ R 250.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 57.00 U 28.00 UJ 28.00 UJ 57.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 57.00 UJ 57.00 UJ 28.00 UJ 28.00 UJ 200.00 NJ 28.00 UJ 420.00 J 28.00 UJ 1,400.00 J NA NA NA NA eL-02-02S 06/06/89 SOIL 0.0'-0.5' V.SV.P.T 58.00 UJ 58.00 UJ 58.00 UJ 58.00 UJ R 58.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 58.00 UJ 29.00 UJ 29.00 UJ 58.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 58.00 UJ 58.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 29.00 UJ 1,600.00 J NA NA NA NA eL-02-03S 06/06/89 SOIL 0.25--1.0' V.SV.P.T 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ R 14.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 12.00 UJ 6.00 UJ 6.00 UJ 12.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ '6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 12.00 UJ 12.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ 6.00 UJ NA NA NA NA MUS-16 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 72.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 55.00 U R R MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 11.00 UJ 11.00 U 11.00 U 11.00 U 1.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 35.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 55.00 U R R MWS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 11.00 UJ 11.00 U 11.00 U 11.00 U 1.00 J 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 53.50 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 55.00 U R R c —; —Ic OO Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:45 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL, ALCOHOL 1,2-OICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-OICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2 , 4 , 5 - TR I CHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0« V.SV, I R R R R R NA R R R R R R R R R R NA R R R R R R R R R R R R R R R R SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I R 13000.0 UJ R 13000.0 UJ 13000.0 UJ NA 13000.0 UJ R 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R R NA 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ R R 13000.0 UJ 32000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I R 13000.0 UJ R 13000.0 UJ 13000.0 UJ NA 13000.0 UJ R 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ R R NA 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13dOO.O UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ R R 13000.0 UJ 32000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I R R R R R NA R R R R R R R R R R NA R R R R R R R R R R R R R R R R SS-4-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ SS-4-AVS 08/19/92 SOIL 0.0--2.01 v.sv.i 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ NA 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ W HI C. Oo Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:45 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAM1NE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHEMOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOR08UTAD IENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2.4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eL-02-015 06/06/89 SOIL 0.25'-1.0' V,SV,P,T 900000.0 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 320000.0 78000.0 U 1300000.0 J 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 42000.0 J 380000.0 U 78000.0 U 78000.0 U 78000.0 U 7700.0 J 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 78000.0 U 380000.0 U 78000.0 U 380000.0 U 78000.0 U 78000.0 U 78000.0 U eL-02'02S 06/06/89 SOIL O.O'-O.S1 V,SV,P,T 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 3900.0 U 19000.0 U 3900.0 U 3900.0 U 3900.0 U 4100.0 3900.0 U 3900.0 U 3900.0 U 750.0 J 3900.0 U 3900.0 U 19000.0 U 3900.0 U 19000.0 U 3900.0 U 3900.0 U 3900.0 U eL-02-035 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 4100.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 850.0 U 4100.0 U 850.0 U 4100.0 U 850.0 U 850.0 U 850.0 U MUS-16 04/04/94 SOIL O.O1 - 2.0' V.SV.t.T 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U NA 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U NA 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 U 360.0 UJ 360.0 U 880.0 U 360.0 U 880.0 U 360.0 U 360.0 U 360.0 U MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U NA 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U NA 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 340.0 U 810.0 U 340.0 U 810.0 U 340.0 U 340.0 U 340.0 U MWS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U NA 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U NA 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 U 350.0 UJ 350.0 U 845.0 U 350.0 U 845.0 U 350.0 U 350.0 U 350.0 U K1 H ,--, KJ Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:45 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semtvolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DlNITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-OINITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4,6-DINITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROHOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE Dl-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0' V.SV.l R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,I 32000.0 UJ 13000.0 UJ R R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 32000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 9400.0 J 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V,SV,I 32000.0 UJ 13000.0 UJ R R 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 32000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ R 13000.0 UJ 13000.0 UJ 13000.0 UJ 9400.0 J 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ 13000.0 UJ SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R SS-4-CDM 08/19/92 SOIL 0.0'-2.0' V,SV,I 28000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 uj 1800.0 J 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ SS-4-AVS 08/19/92 SOIL 0.0«-2.0' V.SV.I 28000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 28000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 1800.0 J 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ 11000.0 UJ cn a S-o in st 01 • • o> oo aa. 01 (/) U ID t. at v> £ « at L. «> <- 3TJ ~- *J C > 3 3 u. O co i e" => O)U ill 5 5 D> jz m i- -,.0 * 0> <M 4-» <"§ 3 3 3 U 3 U § s» _l - I— O> —O » •oo > *-^v I tfi 05 O - > 0=* o> o _i - i— OO — O » M . . i -o cn «- > rjo i > o v. - (/> ' ^ in » -10 <M > 01 •o at o —i - t- ry oo — in - o *xO • o. i <o too - rvj o i > o «•«. - v> i -O O - -10 • > 01 O wo> — i - t- r-eo —o - O. ii??S ) </> <n t/»- inoinmoooooinmoo i =>=5 = =>33-> = 3 = =3333=)=l = 333 ooooooooooooooo O l X o O O f M O O O O O O O O O O O O O O ooooooooooooooooooooooooooooooooo oooooo'oooooooo'o'oooooooooooooooooo «r->»r-«—^sd-^^t**^-*— > * « 4 ' ' ^ t — > ' - - > ' - ' ' p ' ooooooooooooooooooooooooooooooooo !§§ OOOO vO'C'O'O O O O O O O O O < ooooooooooooooo goooooooooooooooo<oooooopop •*»»••* «»•* *» oooooo ooooooooooooooooo ooooooooooooooo >oooooc3o'oooooo'o'oo«oooooooppppoo ^ o o o o o o o o o o zoooo o N* ooo oc* oc . ooo oo ooooooooooo oooooooo oo<ooo o o< gg? tO oooo "ggg o oooooo o oooo ~ ~ = =>=>=>=J oooo oooo gggg! !gggggg • -i UJ ui o : z a. ui ui .yj '.BJ-F 1%, UI I— UI UI UI X K UI Of U Z UI **^ Uf AB ' UI Z ^ ^t UI 52£ 2"!? ^£S <»« ^*?£iu'"1~" UI UI ~ i Iff? I UI HI —J < -J UI toaf ar _i o ~J >- z CM a= QlMMUIAOgEI—^CSB » - « » Q . _ _ _ _ _ _ _ _ _ _ _ —'-jzozvcozuj _i o — at m a: z O.3B _j o < >-a.a«ia.oj-- .v-MMiuoctiJocoei^sr * M W O U J O O U J U J «J LLJ >- " — ~ "" """ — *i^«^Z = ^Zar..ZH.81=«^«zu,g| go<u,uih^-<- 094CUI TUT 007 0236 -i o Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:46 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides \Pcbs ALPHA-BHC BETA-BHC DELTA-BNC LINDANE, TOTAL HEPTACHLOR ALDRIN HEPTACHLOR EPOXIDE ENOOSULFAN I DIELDRIN 4.4-DDE ENDRIN, TOTAL ENDOSULFAN II 4,4-DDD ENDOSULFAN SULFATE 4,4-DDT METHOXYCHLOR ENDRIN KETONE ALPHA-CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-3 08/19/92 SOIL 0.0'-2.0' V,SV,I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-3-CDM 08/19/92 SOIL 0.0'-2.0' v.sv.i NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA SS-4 08/19/92 SOIL 0.0'-2.0' v,sv,i NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-4-CDM 08/19/92 SOIL 0.0--2.0' V,SV,I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-4-AVS 08/19/92 SOIL .0'-2.0' V.SV.I Xt Ww CD Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Organic Compounds 07/29/1994 8:46 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides\Pcbs ALPHA- BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDRIN HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4,4-DDE ENDRIN, TOTAL ENDOSULFAN II 4,4-DDD ENDOSULFAN SULFATE 4,4-DDT METHOXYCHLOR ENDRIN KETONE ALPHA- CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eL-02-015 06/06/89 SOIL 0.25'-1.0' V,SV,P,T 47.00 U 47.00 U 47.00 U 47.00 U 47.00 U 47.00 U 47.00 U 92.00 94.00 U 94.00 U 94.00 U 94.00 U 94.00 U 94.00 U 94.00 U 470.00 U 94.00 U 470.00 U 470.00 U 940.00 U 470.00 U 470.00 U 470.00 U 470.00 U 470.00 U 940.00 U 940.00 U eL-02-02S 06/06/89 SOIL 0.0'-0.5' V.SV.P.T 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 75.00 U 75.00 U 75.00 U 75.00 U 75.00 U 75.00 U 75.00 U 380.00 U 75.00 U 380.00 U 380.00 U 750.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 750.00 U 750.00 U eL-02-03S 06/06/89 SOIL 0.25'-1.0» V.SV.P.T 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 100.00 U 20.00 U 100.00 U 100.00 U 200.00 U 100.00 U 160.00 u 100.00 U 100.00 U 100.00 U 200.00 U 200.00 U MWS-16 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-16-AVD 04/04/94 SOIL 0.0« - 2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA H C.H Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Inorganic Analytes 07/29/1994 8:47 AM SAMPLE MAKE SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg . mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg eL-02-015 06/06/89 SOIL 0.25'-1.0' V.SV.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eL-02-025 06/06/89 SOIL O.O'-O.S' V,SV,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eL-02-03S 06/06/89 SOIL 0.25--1.0' V.SV.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA MWS-16 04/04/94 SOIL 0.0' - 2.0' V.SV.I.T 25.700.00 5.00 UJ 2.10 41.30 B 0.28 B 0.84 U 22.800.00 39.10 J 27.40 J 135.00 35,300.00 3.20 22,000.00 927.00 0.05 U 21.50 151.00 U 0.42 U 0.63 U 384.00 U 0.42 U 120.00 51.70 0.52 U MWS-16-FR 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 29,000.00 5.20 UJ 0.77 B 26.50 B 0.25 B 0.97 B 54,400.00 45.30 J 23.70 J 82.40 36,900.00 3.00 25,100.00 818.00 0.05 U 21.90 175.00 B 0.43 U 0.65 U 396.00 U 0.43 U 109.00 52.30 0.54 U HWS-16-AVO 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 27,350.00 5.10 UJ 2.10 33.90 B 0.27 B 0.70 B 38,600.00 42.20 J 25.55 J 108.70 36,100.00 3.10 23,550.00 872.50 0.05 U 21.70 125.25 B 0.43 U 0.64 U 390.00 U 0.43 U 114.50 52.00 0.53 U O K3 Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Future - Surface Soil Inorganic Analytes 07/29/1994 8:47 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg SS-3 08/19/92 SOIL 0.0'-2.0' V.SV.I 23,100.00 7.20 BNJ 1.70 B 94.20 0.26 U 0.77 U 56,500.00 33.80 NJ 22.10 J 72.80 NJ 55,400.00 12.20 J 18,700.00 886.00 0.06 U 19.20 7,140.00 0.51 U 2.10 B 476.00 B 0.77 U 88.30 NJ 258.00 0.96 SS-3-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I 26,900.00 4.10 U 2.90 98.30 0.25 B 0.37 U 49,600.00 34.10 23.40 75.00 42,200.00 27.70 18,700.00 841.00 0.12 U 17.10 8,110.00 J 0.88 UJ 1.70 B 501.00 B 0.22 UJ 102.00 313.00 0.62 U SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 25,000.00 4.63 BNJ 2.30 B 96.25 0.19 B 0.57 U 53,050.00 33.95 NJ 22.75 J 73.90 NJ 48,800.00 19.95 J 18,700.00 863.50 0.09 U 18.15 7,625.00 J 0.70 UJ 1.90 B 488.50 B 0.50 UJ 95.15 NJ 285.50 0.64 SS-4 08/19/92 SOIL 0.0'-2.0' V.SV.I 23,000.00 6.50 BNJ 0.92 BWJ 39.40 B 0.22 U 0.66 U 61,100.00 25.10 NJ 20.90 J 62.90 NJ 29,800.00 9.10 J 19,300.00 634.00 0.05 U 16.80 673.00 B 0.44 U 0.93 B 352.00 B 0.66 U 86.00 NJ 265.00 0.57 U SS-4-COM 08/19/92 SOIL 0.0'-2.0' V.SV.I 30,900.00 3.30 U 2.00 B 49.00 0.14 U 0.30 U 51,000.00 31.80 21.30 71.50 35,100.00 13.50 18,500.00 719.00 0.10 U 16.10 1,150.00 J 0.73 U 1.40 B 453.00 B 0.18 UJ 107.00 371.00 0.50 U SS-4-AVS 08/19/92 SOIL 0.0'-2.0' V,SV,I 26,950.00 4.08 BNJ 1.46 BUJ 44.20 B 0.18 U 0.48 U 56,050.00 28.45 NJ 21.10 J 67.20 NJ 32.450.00 11.30 J 18,900.00 676.50 0.08 U 16.45 911.50 BJ 0.59 U 1.17 B 402.50 B 0.42 UJ 96.50 NJ 318.00 0.54 U HC Oo X! Ow Tutu, St. Thomas, U.S. Virgin Islands 07/29/1994 Curriculum Center Building - Future - Surface Soil •, 8:55 AM Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS ing/ kg SS-3-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I NA SS-4-AVS 08/19/92 SOIL O.O'-Z.O1 V,SV,I NA MWS-16-AVD 04/04/94 SOIL 0.0' - 2.0' V,SV,I,T 45.00 J M Tutu, St. Thomas, U.S. Virgin Islands 07/29/1994 Curriculum Center Building - Future - Surface Soil ; 8:56 AM Total Petroleum Hydrocarbons ' SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS ug/g TOTAL PETROLEUM HYDROCARBONS ug/g eL-02-OIS 06/06/89 SOIL 0.25'-1.0' V.SV.P.T 3,470.00 NA eL-02-02S 06/06/89 SOIL 0.0--0.5' V,SV,P,T 1,730.00 NA eL-02-03S 06/06/89 SOIL 0.25--1.0- V.SV.P.T 544.00 NA *— •H KJ Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Surface Soil Organic Compounds 06/16/1994 11:25 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHL0RIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1-D I CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-DICHLOROETHANE 2-BUTANONE 1,1,1-TR I CHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOO I CHLOROMETHANE 1,2-DICHLOROPROPANE cis 1,3-DICHLOROPROPENE TRICHLOROETHYLENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans 1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHYLENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZNE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-2 08/03/92 SOIL 0.0' - 2.0' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 17.00 J 14.00 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.00 U 10.00 UJ 5.00 UJ eC-09S 09/12/88 SOIL 0.0'-2.0' V,P,T 1,800.00 U 1,800.00 U 1,800.00 U 1.800.00 U 12,000.00 U 2,700.00 UJ 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U R 880.00 U 880.00 U 1,800.00 U 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U 880.00 U 1,800.00 UJ 1,800.00 UJ 880.00 U 880.00 U 560.00 J 880.00 U 1,300.00 880.00 U 2,500.00 NA NA NA eC-IOS 09/12/88 SOIL 0.5'-1.0' V,P,T 13.00 U 13.00 U 13.00 U 13.00 U 29.00 U 54.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 13.00 U 6.00 U 6.00 U 13.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U '6.00 U 45.00 J 6.00 U 6.00 U 33.00 J 13.00 UJ 6.00 U 6.00 U 1,300.00 6.00 U 2,100.00 6.00 U 5,600.00 NA NA NA eR-078 09/12/88 SOIL 0.3'-1.0' V,P,T 12.00 U 12.00 U 12.00 U 12.00 U 26.00 U 17.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 12.00 U 6.00 U 6.00 U 12.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 8.00 J 55.00 J 6.00 U 6.00 U 2.00 J 6.00 U 6.00 U 6.00 U 1.00 J NA NA NA eR-OSS 09/12/88 SOIL 0.25'-0.75' V.P.T 13.00 U 13.00 U 13.00 U 13.00 U 26.00 U 33.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 13.00 U 6.00 U 6.00 U 13.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 J 6.00 U 6.00 U 13.00 UJ 13.00 UJ 6.00 U 6.00 U 6.00 U 6.00 U 18.00 B 6.00 U 7.00 NA NA NA eR-02-025 06/08/89 SOIL 0.17--1.01 V.SV.P 60.00 UJ 60.00 UJ 60.00 UJ 60.00 UJ 200.00 60.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 60.00 UJ 30.00 UJ 30.00 UJ 60.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 60.00 UJ 60.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 30.00 UJ 490.00 J NA NA NA _ -5 o ow 4s. Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Co. Organic Compounds - Surface Soil 06/16/1994 11:24 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZEHE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-MITROSO-D1 -N-PROPYLAM1NE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DtCHLOROPHENOL 1,2, 4- TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPEHTAD I ENE 2.4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-2 08/03/92 SOIL 0.0' - 2.0' V.SV.I.T 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U NA 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U NA 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 UJ 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 3,400.00 U 1,400.00 U 3,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U eC-095 09/12/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eC-10S 09/12/88 SOIL 0.5--1.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA ,NA NA NA NA NA NA NA NA NA NA NA NA NA eR-07S 09/12/88 SOIL 0.3'-1.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eR-08S 09/12/88 SOIL 0.25'-0.75' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eR-02-025 06/08/89 SOIL 0.17'-1.0' V.SV.P 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 7,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 4,400.00 1,600.00 U 1,600.00 U 1,600.00 U 6,100.00 1,600.00 U 1,600.00 U 7,600.00 U 1,600.00 U 7,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U c CH OO Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Surface Soil Organic Compounds 06/16/1994 11:24 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Sefliivolatiles-2 3-NITROAN1LINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DlNITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4.6-D1NITRO-2-METHYLPHENOL N - N I TROSOO I PHENYLAM I NE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYL8ENZYLPHTHALATE 3,3'-DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE D I BENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ' ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-2 08/03/92 SOIL 0.0' - 2.0' V.SV.l.T 3,400.00 UJ 1,400.00 U 3,400.00 U ,400.00 U ,400.00 U ,400.00 U ,400.00 U ,400.00 U ,400.00 U 3,400.00 U 3,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 3,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 220.00 J 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 U 1,400.00 UJ 270.00 J 1,400.00 U 1,400.00 U 290.00 J eC-09S 09/12/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eC-10S 09/12/88 SOIL 0.5'-1.0- V.P/T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA NA NA NA NA NA NA eR-07S 09/12/88 SOIL 0.3'-1.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eR-OSS 09/12/88 SOIL 0.25--0.75' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eR-02-025 06/08/89 SOIL 0.17'-1.0' V.SV.P 7,600.00 U 190.00 J 7,600.00 U 7,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 420.00 J 7,600.00 U 7,600.00 U 1,600.00 U 1,600.00 U 1,600.00 U 7,600.00 U 1,600.00 U 1,600.00 U NA 1,600.00 U 740.00 J 2,000.00 1,600.00 U 3,100.00 U 1,600.00 U 1,600.00 U 5,400.00 1,600.00 U 870.00 J 1,600.00 U 770.00 J 1,600.00 U 1,600.00 U 430.00 J w Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Surface Soil Organic Compounds 06/16/1994 11:24 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides ALPHA- BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDRIN HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4,4' -DDE ENDRIN, TOTAL ENDOSULFAN II 4, 4' -ODD ENDOSULFAN SULFATE 4, 4 '-DOT METHOXYCHLOR ENDRIN KETONE ALPHA- CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-2 08/03/92 SOIL 0.0' - 2.0' V,SV,I,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eC-09S 09/12/88 SOIL 0.0'-2.0' V,P,T 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 230.00 UJ 230.00 UJ 230.00 UJ 230.00 UJ 230.00 UJ 230.00 UJ 230.00 UJ 1,100.00 UJ 230.00 UJ 1,100.00 UJ 1,100.00 UJ 2,300.00 UJ 1,100.00 UJ 1,100.00 UJ 1,100.00 UJ 1,100.00 UJ 1,100.00 UJ 2,300.00 UJ 2,300.00 UJ eC-10S 09/12/88 SOIL 0.5'-1.0' V.P.T 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 1,000.00 UJ 200.00 UJ ,000.00 UJ ,000.00 UJ 2,000.00 UJ ,000.00 UJ ,060.00 uj ,000.00 UJ ,000.00 UJ 1,000.00 UJ 2,000.00 UJ 2,000.00 UJ eR-075 09/12/88 SOIL 0.3'-1.0' V.P.T 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 10.00 UJ 19.00 UJ 19.00 UJ 19.00 UJ 19.00 UJ 19.00 UJ 19.00 UJ 19.00 UJ 96.00 UJ 19.00 UJ 96.00 UJ 96.00 UJ 190.00 UJ 96.00 UJ 96.00 UJ 96.00 UJ 470.00 UJ 96.00 UJ 190.00 UJ 190.00 UJ eR-08S 09/12/88 SOIL 0.25--0.75' V,P,T 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 100.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 200.00 UJ 1,000.00 UJ 200.00 UJ 1,000.00 UJ 1,000.00 UJ 2,000.00 UJ 1,000.00 UJ 1,000.00 UJ 1,000.00 UJ 1,000.00 UJ 1,000.00 UJ 2,000.00 UJ 2,000.00 UJ eR-02-025 06/08/89 SOIL 0.17'-1.0' V,SV,P 37.00 U 37.00 U 37.00 U 37.00 U 37.00 U 37.00 U 37.00 U 37.00 U 74.00 U 74.00 U 74.00 U 74.00 U 74.00 U 74.00 U 74.00 U 370.00 U 74.00 U 370.00 U 370.00 U 740.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 740.00 U 740.00 U o "M Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Surface Soil Total Petroleum Hydrocarbons 06/20/1994 7:32 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg B-2 08/03/92 SOIL 0.0' - 2.0' V.SV.I.T 110.00 eC-09S 09/12/88 SOIL 0.0'-2.0' V.P.T 0.90 J eC-IOS 09/12/88 SOIL 0.5'-1.0' V.P.T 15.70 J eR-07S 09/12/88 SOIL 0.3'-1.0' V,P,T 0.57 J eR-OSS 09/12/88 SOIL 0.25'-0.75- V.P.T 1.93 J £j S! Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Surface Soil Inorganic Analytes 06/16/1994 11:23 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, total mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-2 08/03/92 SOIL 0.0' - 2.0« V.SV.I.T 26,000.00 5.90 BJ 2.10 U 67.20 0.26 B 0.64 U 47,200.00 31.70 21.90 79.10 38,400.00 26.00 SJ 17,100.00 834.00 0.06 U 17.50 1,170.00 0.42 U 2.20 J 319.00 B 0.64 U 119.00 108.00 1.10 eC-09S 09/12/88 SOIL 0.0'-2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eC-10S 09/12/88 SOIL V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA ..NA NA NA NA eR-07S 09/12/88 SOIL V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eR-08S 09/12/88 SOIL 0.25'-0.75» V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eR-02-02S 06/08/89 SOIL V,SV,P NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA H q K": s Tutu, St. Thomas, U.S. Virgin Islands 06/20/1994 Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Surface Soil ; 7:32 AH Total Petroleum Hydrocarbons SAMPLE NAME eR-02-02S SAMPLE DATE 06/08/89 SAMPLE TYPE SOIL SAMPLE DEPTH 0.17'-1.0' TEXT 004 V,SV,P TOTAL PETROLEUM HYDROCARBONS ug/g 23,400.00 TOTAL PETROLEUM HYDROCARBONS ug/g NA O hJ 4i -0 -I !—H O X! Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Organic Compounds 06/24/1994 12:11 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON OISULFIDE 1,1-DICHLOROETHEME 1,1-D I CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-DICHlOROETHANE 2-BUTANONE 1,1.1 -TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMODICHLOROMETHANE 1,2-DICHLOROPROPANE cts 1,3-DICHLOROPROPENE TRICHLOROETHYLENE 0 1 BROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans 1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHYLENE 1 , 1 ,2, 2- TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZNE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-6 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.00 U 11.00 U 11.00 U 11.00 U 22.00 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.70 U 11.00 UJ 5.70 UJ SS-6-FR 08/19/92 SOIL 0.0--2.0' V,SV,I 12.00 U 12.00 U 12.00 U 12.00 U 20.00 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA NA NA SS-6-CDM 08/19/92 SOIL 0.0--2.0' v.sv.i 12.00 U 12.00 U 12.00 U 12.00 U 26.00 UJ 12.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA NA NA SS-6-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 11.75 U 11.75 U 11.75 U 11.75 U 16.50 11.75 UJ 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 UJ 11.75 U 11.75 U 11.75 U NA 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 11.75 U 5.70 U 11.00 UJ 5.70 UJ B-13A 08/12/92 SOIL 0.0'-2.0' v,sv,i 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 15.00 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.40 U 11.00 UJ 5.40 UJ e-01 09/08/88 SOIL 0.0'-2.0' V P T " ir i ' 27,000.00 U 27,000.00 U 27,000.00 U 27,000.00 U 14,000.00 BU 27,000.00 BU 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U R 14,000.00 U 14,000.00 U 27,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 U 14,000.00 UJ 14,000.00 U 14,000.00 U 27,000.00 U 27,000.00 U 440,000.00 14,000.00 U 14,000.00 UJ 14,000.00 UJ 14,000.00 UJ 14,000.00 UJ 14,000.00 UJ NA NA NA w OSO c —5 Tutu, St. Thomas, U.S. Virgin islands 0'Henry Dry Cleaners & Liquor Barn - Surface Soil Organic Compounds 06/24/1994 12:11 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1.1-DICHLOROETHENE 1,1-0 I CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-DICHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DlCHLOROPROPANE CIS 1,3-01CHLOROPROPENE TRICHLOROETHYLENE D I BROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans 1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHYLENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZNE STYRENE XYLENES (TOTAL) 1,2-DlBROMOETHANE (EDB) tert -butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eO-02-01 06/05/89 SOIL 0.5--1.251 V.SV.P.T 11,000.00 U 11,000.00 U 11,000.00 U 11,000.00 U 5,300.00 U 11,000.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 11,000.00 U 5,300.00 U - 5,300.00 U 11,000.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5.300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 11,000.00 U 11,000.00 U 170,000.00 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U 5,300.00 U NA NA NA eO-02-02 06/05/89 SOIL 1.25'-2.0' V.SV.P 62.00 U 62.00 U 62.00 U 62.00 U 150.00 J 84.00 J 31.00 U 31.00 U 31.00 U 20.00 J 12.00 J 31.00 U 62.00 U 31.00 U 31.00 U 62.00 U 31.00 0 31.00 U 31.00 U 75.00 31.00 U 31.00 U 31.00 U 31.00 U 31.00 U 62.00 U 62.00 U 180,000.00 D 31.00 U 31.00 U 31.00 U 31.00 U 31.00 U 31.00 U NA NA NA eO- 02-03 06/05/89 SOIL 0.5'-1.25' V,SV,P,T 11.00 U 11.00 U 11.00 U 11.00 U 27.00 U 80.00 U 6.00 U 6.00 U 6.00 U 6.00 U 2.00 J 6.00 U 11.00 U 6.00 U 6.00 U 11.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U <R 6.00 U 6.00 U 6.00 U 11.00 U 11.00 U 58.00 J 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U 6.00 U NA NA NA o Q "j ssso zoo in± l — . T J » > ~ m . - . I T l i M . 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Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Organic Compounds 06/24/1994 11:27 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 SemivotatHes-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DlCHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DlCHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BtS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-NETHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2 , 4 , 6- TR I CHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eO-02-01 06/05/89 SOIL 0.5'-1.25' V,SV,P,T 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U R 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 2,000.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 2,000.00 U 420.00 U 2,000.00 U 420.00 U 420.00 U 420.00 U eO-02-02 06/05/89 SOIL 1.25'-2.0' V.SV.P 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 2,000.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 2,000.00 U 410.00 U 2,000.00 U 410.00 U 410.00 U 410.00 U eO-02-03 06/05/89 SOIL 0.5'-1.25' V,SV,P,T 39.00 NJ 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 1,800.00 U 370.00 U 370.00 U 370.00 U 370.00 U 3TO.OO U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 1,800.00 U 370.00 U 1,800.00 U 370.00 U 370.00 U 370.00 U M CJtw —.H Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners and Liquor Barn - Surface Soil Organic Compounds 06/24/1994 12:12 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semi vot at iles- 2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE D1ETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4,6-DIMITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCNLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DlCHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDEHO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg SS-6 08/19/92 SOIL 0.0--2.0' V.SV.l R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R SS-6-FR 08/19/92 SOIL 0.0«-2.0' V,SV,I 910.00 U 370.00 U 910.00 U 910.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 910.00 U 910.00 U 370.00 U 370.00 U 370.00 U 910.00 U 370.00 U 370.00 U 370.00 U 62.00 J 370.00 U 370.00 U 75.00 J 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 370.00 U 370.00 U 370.00 U SS-6-CDM 08/19/92 SOIL 0.0--2.0' v,sv,i 940.00 UJ 390.00 U 940.00 U 940.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 940.00 UJ 940.00 U 390.00 U 390.00 U 390.00 U 940.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 64.00 J 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U SS-6-AVS . 08/19/92 SOIL 0.0'-2.0' V,SV,I 475.00 UJ 380.00 U 475.00 U 475.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 475.00 UJ 475.00 U 380.00 U 380.00 U 380.00 U 475.00 UJ 380.00 U 380.00 U 380.00 U 62.00 J 380.00 U 380.00 U 69.50 J 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 UJ 380.00 U 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U B-13A 08/12/92 SOIL 0.0'-2.0' V.SV.I 840.00 U 350.00 U 840.00 U 840.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 840.00 U 840.00 U 350.00 U 350.00 U 350.00 U 840.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U e-01 09/08/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA - •*••! C -i Q 0 i Tutu, St. Thomas, U.S. Virgin Islands 0'Henry Dry Cleaners and Liquor Barn - Surface Soil Organic Compounds 06/24/1994 12:12 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DlNITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DlNITROTOLUENE DIETHYLPHTHALATE 4- CHLOROPHEM YL - PHENYLETHER FLUORENE 4-NITROAN1LINE 4.6-DINITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTNRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZlDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE Dt-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE D I BENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eO- 02-01 06/05/89 SOIL 0.5'-1.25' V,SV,P,T 2,000.00 U 420.00 U 2,000.00 U 2,000.00 UJ 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 2,000.00 U 2,000.00 U 420.00 U 420.00 U 420.00 UJ 2,000.00 U 420.00 U 420.00 U NA 420.00 U 420.00 U 420.00 U 420.00 U 840.00 UJ 420.00 U 420.00 U 510.00 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U eO-02-02 06/05/89 SOIL 1.25'-2.0' V,SV,P 2,000.00 U 410.00 U 2,000.00 U 2,000.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 2,000.00 U 2,000.00 U 410.00 U 410.00 U 410.00 U 2,000.00 U 410.00 U 410.00 U NA 410.00 U 410.00 U 410.00 U 410.00 U 820.00 U 410.00 U 410.00 U 390.00 J 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U eO-02-03 06/05/89 SOIL 0.5'-1.25' V.SV.P.T 1,800.00 U 370.00 U 1,800.00 U 1,800.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 1,800.00 U 1,800.00 U 370.00 U 370.00 U 370.00 U 1,800.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 740.00 U 370.00 U 370.00 U 280.00 J 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U en xj Tutu, St. Thomas, U.S. Virgin Islands O1Henry Dry Cleaners & Liquor Barn - Surface Soil Organic Compounds 06/24/1994 11:26 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides\Pcbs ALPHA-BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDRIN HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4, 4' -DDE ENDRIN, TOTAL ENDOSULFAN II 4,4 '-DDD ENDOSULFAN SULFATE 4,4'-DDT METHOXYCHLOR ENDRIN KETONE ALPHA- CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ss-6 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-6-FR 08/19/92 SOIL 0.0'-2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA SS-6- COM 08/19/92 SOIL 0.0--2.0' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA SS-6-AVS 08/19/92 SOIL 0.0'-2.0' V,SV,I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA B-13A 08/12/92 SOIL 0.0'-2.0' V,SV,I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA e-01 09/08/88 SOIL 0.0'-2.0' V.P.T 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 24.00 U 24.00 U 24.00 U 24.00 U 24.00 U 24.00 U 24.00 U 120.00 U 24.00 U 120.00 U 120.00 U 240.00 U 120.00 U 120.00 U 120.00 U 120.00 U 120.00 U 240.00 U 240.00 U ui Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Organic Compounds 06/24/1994 11:26 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides\Pcbs ALPHA-BHC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDRtN HEPTACHLOR EPOXIDE ENDOSULFAN I DIELDRIN 4, 4' -DDE ENDRIN, TOTAL ENDOSULFAN II 4,4'-DDD ENDOSULFAN SULFATE 4,4'-DDT METHOXYCHLOR ENDRIN KETONE ALPHA-CHLORDANE GAMMA -CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg eO-02-01 06/05/89 SOIL 0.5'-1.25' V,SV,P,T 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 100.00 U 20.00 U 100.00 U 100.00 U 200.00 U 100.00 U 100.00 U 100.00 U 100.00 U 100.00 U 200.00 U 200.00 U eO-02-02 06/05/89 SOIL 1.25'-2.0' V,SV,P 9.90 U 9.90 U 9.90 U 9.90 U 9.90 U 9.90 U 9.90 U 9.90 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 99.00 U 20.00 U 99.00 U 99.00 U 200.00 U 99.00 U 99.00 U 99.00 U 99.00 U 99.00 U 200.00 U 200.00 U eO-02-03 06/05/89 SOIL 0.5'-1.25' V.SV.P.T 9.00 U 9.00 U 9.00 U 9.00 U 9.00 U 9.00 U 9.00 U 9.00 U 18.00 U 18.00 U 18.00 U 18.00 U 18.00 U 18.00 U 18.00 U 90.00 U 18.00 U 90.00 U 90.00 U 180.00 U 90.00 U 90.00 U 90.00 U 90.00 U 90.00 U 180.00 U 180.00 U oo Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Inorganic Analytes 06/24/1994 12:12 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, total mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg SS-6 08/19/92 SOIL 0.0'-2.0' V.SV.I 14,300.00 J 7.40 BNJ 17.30 J 89.00 J 0.23 UJ 0.68 UJ 59,200.00 J 23.30 NJ 14.00 J 55.40 NJ 39,500.00 J 14.40 J 9,960.00 J 662.00 J 0.06 U 14.10 J 1,910.00 J 0.46 UJ 1.60 BJ 340.00 BJ 0.68 UJ 71.30 NJ 91.70 J 0.57 U SS-6-FR 08/19/92 SOIL 0.0--2.0' V.SV.I 13,800.00 J 6.00 BNJ 19.10 J 90.90 J 0.23 UJ 0.70 UJ 30,700.00 J 18.80 NJ 13.80 J 54.80 NJ 23,800.00 J 11.40 J 9,670.00 J 672.00 J 0.06 U 10.70 J 2,070.00 J 0.47 UJ 0.93 UJ 251.00 BJ 0.70 UJ 73.10 NJ 97.10 J 1.30 SS-6-CDM 08/19/92 SOIL 0.0'-2.0' V.SV.I 30,800.00 3.80 U 8.20 84.90 0.52 B 2.00 34,100.00 21.50 22.70 96.20 42,300.00 75.20 17,700.00 817.00 0.25 10.50 4,540.00 J R 3.20 368.00 B 0.20 UJ 131.00 170.00 0.59 U SS-6-AVS 08/19/92 SOIL 0.0'-2.0' V.SV.I 22,425.00 J 6.35 BNJ 18.65 J 90.43 J 0.23 UJ 0.65 UJ 37,825.00 J 19.93 NJ 13.85 J 54.95 J 27,725.00 J 12.15 J 9,742.50 J 669.50 J 0.06 U 11.50 J 2,030.00 J 0.47 UJ 0.75 BJ 273.25 BJ 0.70 UJ 72.65 NJ 95.75 J 1.05 B-13A 08/12/92 SOIL 0.0'-2.0' V.SV.I 21,100.00 4.30 UNJ 13.70 59.30 0.22 U 0.65 U 73,200.00 * 23.60 16.30 52.00 29,400.00 4.80 J 18,300.00 870.00 0.05 U 14.70 841.00 B 0.43 U 1.60 BNJ 474.00 B 0.65 U 83.10 63.10 0.54 U 0 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA e-01 09/08/88 SOIL ,0'-2.0' V,P,T H O '•••i OM 03 Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Inorganic Analytes 06,724/1994 12:12 PH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, total mg/kg ing/kg mg/kg mg/kg ing/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg eO-02-01 06/05/89 SOIL 0.5'-1.25' V,SV,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eO-02-02 06/05/89 SOIL 1.25--2.0' V,SV,P NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eO-02-03 06/05/89 SOIL 0.5'-1.25' V.SV,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA •S3m -o Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS ug/g TOTAL PETROLEUM HYDROCARBONS ug/g eO-02-01 06/05/89 SOIL 0.5'-1.25' V.SV.P.T 379.00 224.00 eO-02-02 06/05/89 SOIL 1.25--2.0' V.SV.P 998.00 732.00 eO-02-03 06/05/89 SOIL 0.5'-1.25' V.SV.P.T 42.00 33.00 06/24/1994 12:02 PM —i :—' !—— —i Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Surface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg SS-6 08/19/92 SOIL 0.0'-2.0' V.SV.I NA SS-6-FR 08/19/92 SOIL 0.0'-2.0' V.SV.I NA SS-6-CDM 08/19/92 SOIL 0.0--2.01 V.SV.I NA SS-6-AVS 08/19/92 SOIL 0.0--2.0' V.SV.I NA B-13A 08/12/92 SOIL 0.0'-2.0' V.SV.I NA 06/24/1994 12:01 PM e-01 09/08/88 SOIL 0.0--2.0' V.P.T 0.17 J H L~ •H f: w0" Tutu, St. Thomas, U.S. Virgin Islands Surface Soil - Background Inorganic Analytes SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg SS-1 08/19/92 SOIL 0.0'-2.0' I 23,600.00 6.10 BNJ 0.44 U 41.90 B 0.22 U 0.66 U 75,100.00 23.40 NJ 25.70 J 55.30 NJ 31,300.00 2.10 SJ 20,500.00 763.00 0.05 U 18.90 412.00 B 0.44 U 0.98 B 557.00 B 0.66 U 109.00 NJ 50.60 1.20 SS-1 -COM 08/19/92 SOIL 0.0'-2.0' I 35,600.00 3.40 U 1.20 B 47.00 0.20 B 0.31 U 74,700.00 29.90 28.60 73.90 43,400.00 2.50 22,400.00 814.00 0.10 U 19.60 723.00 B 0.78 UJ 1.90 B 577.00 B 0.19 UJ 151.00 54.80 0.54 U SS-1-AVS 08/19/92 SOIL 0.0'-2.0' I 29,600.00 3.90 BNJ 0.71 B 44.45 B 0.16 B 0.49 U 74,900.00 26.65 NJ 27.15 J 64.60 NJ 37,350.00 2.30 SJ 21,450.00 788.50 0.08 U 19.25 567.50 B 0.61 UJ 1.44 B 567.00 B u 0.43 UJ 130.00 NJ 52.70 0.74 SS-2 08/19/92 SOIL 0.0'-2.0' I 16,100.00 4.20 UNJ 0.42 U 30.10 B 0.21 U 0.62 U 9,630.00 25.80 NJ 18.00 J 40.30 NJ 22,600.00 1.70 J 13,200.00 535.00 0.05 U 15.50 568.00 B 0.42 U 0.99 B 157.00 B 0.62 U 74.90 NJ 40.10 0.52 U SS-2- COM 08/19/92 SOIL 0.0'-2.0' I 33,100.00 3.40 U 1.30 B 43.60 0.34 B 0.32 U 18,700.00 30.60 27.40 70.00 40,900.00 4.00 19,700.00 810.00 0.10 U 18.80 1,090.00 J 0.76 U 2.20 257.00 B 0.19 UJ 139.00 56.80 0.52 U 08/18/1994 8:56 AM SS-2-AVS 08/19/92 SOIL O.O'-Z.O1 I 24,600.00 3.80 UNJ 0.76 B 36.85 B 0.22 B 0.47 U 14,165.00 28.20 NJ 22.70 J 55.15 NJ 31,750.00 2.85 J 16,450.00 672.50 0.08 U 17.15 829.00 BJ 0.59 U 1.60 B 207.00 B 0.41 UJ 106.95 NJ 48.45 0.52 U C O KT ?: KJ Tutu, St. Thomas, U.S. Virgin Islands 08/18/1994 Surface Soil - Background . 8:56 AM Inorganic Analytes ' SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Anatytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg ing/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg SS-8 08/19/92 SOIL O.O'-Z.O' I 21.500.00 J 14.70 BNJ 0.99 BJ 29.30 BJ 0.41 UJ 1.20 UJ 144,000.00 J 16.20 NJ 16.90 BJ 43.10 NJ 25,400.00 J 2.50 SJ 21,400.00 J 888.00 J 0.05 U 12.90 BJ 325.00 BJ 0.41 UJ 1.70 UJ 187.00 BJ 0.62 UJ 82.10 NJ 43.80 J 1.10 SS-8-CDM 08/19/92 SOIL 0.0'-2.0- I 31,000.00 3.20 U 0.67 BJ 30.40 B 0.27 B 0.30 U 100,000.00 20.40 20.00 56.10 33,100.00 R 23,800.00 911.00 0.09 U 10.30 520.00 B 0.70 UJ 0.95 U 184.00 B 0.18 UJ 108.00 51.30 0.51 U SS-8-AVS 08/19/92 SOIL 0.0'-2.0' I 26,250.00 J 8.15 BNJ 0.83 BJ 29.85 BJ 0.24 B 0.75 UJ 122,000.00 J 18.30 NJ 18.45 BJ 49.60 NJ 29,250.00 J 2.50 SJ 22,600.00 J 899.50 J 0.07 U 11.60 BJ 422.50 BJ 0.56 UJ 1 .33 UJ 185.50 BJ 0.40 UJ ^95.05 NJ 47.55 J 0.68 c H -••1 0" Tutu, St. Thomas, U.S. Virgin Islands Tillett Garden Area - Subsurface Soil Organic Compounds 06/17/1994 10:11 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETKANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1 -DI CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-0 I CHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DICHLOROPROPANE cis 1,3-DICHLOROPROPENE TRICHLOROETHYLENE D I BROMOCHLOROMETHANE 1,1, 2- TR I CHLOROETHANE BENZENE Trans 1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHYLENE 1 , 1 ,2, 2- TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZNE STYRENE XYLENES (TOTAL) 1,2-D!BROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-8 08/12/92 SOIL 0.0--2.0- V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 2.00 J 11.00 U 4.00 J 11.00 U 2.00 J 11.00 U 11.00 U 5.80 U 12.00 UJ 5.80 UJ B-8-FR 08/12/92 SOIL 0.0'-2.0' V.SV.l.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 1.1.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 5.00 J 11.00 U 4.00 J 11.00 U 3.00 J 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ B-8-AVD 08/12/92 SOIL 0.0--2.0' V.SV.l.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 3.50 J 11.00 u 4.00 J 11.00 U 2.50 J 11.00 U 11.00 U 5.65 U 11.50 UJ 5.65 UJ MUS-5 08/11/92 SOIL 0.0 ' - 4.0' V.SV.l.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.30 U 11.00 UJ 5.30 UJ MWS-5-CDM 08/11/92 SOIL 0.0'-4.0' V.SV.l.T 10.00 U 10.00 U 10.00 U 10.00 U 27.00 UJ 31.00 UJ 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U NA 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 11.00 U 11.00 U 11.00 U MWS-5-AVS 08/11/92 SOIL 0.0'-4.0' V.SV.l.T 10.50 U 10.50 U 10.50 U 10.50 U 19.00 UJ 21.00 UJ 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 UJ 10.50 U 10.50 U NA 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 UJ 10.50 UJ 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 8.15 U 11.00 UJ 8.15 UJ X.-' to :5- ^°«, (s. .• tn en rvj — i - 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UJ UJ I UJ UJ _!<_! U J I U I i l M X « z x —i o -i >- z IM 3: —i z a. a> — uja.ozt«tz — • a. >- LLI o uj —<_izoz<cOaeui —< o — z CD oe z .— — uja:ujaeo£i—or —QJQUJOOUJUJ TUT 007 0266 y Tutu, St. Thomas, U.S. Virgin Islands Tillett Garden Area - Subsurface Soil Inorganic Analytes 06/17/1994 9:49 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, total mg/kg rag/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 8-8 08/12/92 SOIL 0.0'-2.0' V.SV.I.T 23,600.00 4.60 UNJ 4.30 98.40 0.37 B 0.69 U 72,800.00 * 29.70 20.50 157.00 J 31,500.00 R 18,000.00 700.00 0.12 14.90 3,320.00 J 0.46 U 3.90 NJ 465.00 B 0.69 U 79.10 149.00 0.58 U B-8-FR 08/12/92 SOIL 0.0'-2.0' V.SV.I.T 19,700.00 5.00 BNJ 94.00 J 53.00 0.35 B 0.66 U 65,200.00 * 22.30 16.30 49.80 J 29,100.00 10.00 J 16,100.00 791 .00 0.06 U 14.10 870.00 BJ 0.44 U 1.60 BNJ 453.00 B 0.66 U 76.20 63.80 2.70 B-8-AVO 08/12/92 SOIL 0.0'-2.0' V.SV.I.T 21,650.00 3.65 BNJ 49.15 J 75.70 0.36 B 0.68 U 69,000.00 * 26.00 18.40 103.40 J 30,300.00 10.00 J 17,050.00 745.50 0.06 14.50 2,095.00 BJ 0.45 U 2.75 BNJ 459.00 B ,.0.68 U 157.30 106.40 1.50 MUS-5 08/11/92 SOIL 0.0 ' - 4.0' V.SV.I.T 27,400.00 5.10 BNJ 0.77 B 50.70 0.46 B 0.64 U 54,400.00 * 24.20 24.30 115.00 37,700.00 R 26,200.00 763.00 0.05 U 15.30 1,180.00 0.43 UU 2.20 NJ 381.00 B 0.64 U 108.00 164.00 0.53 U MWS-5-CDM 08/11/92 SOIL 0.0'-4.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.50 U MUS-5 -AVS 08/11/92 SOIL 0.0'-4.0' V.SV.I.T 27.400.00 5.10 BNJ 0.77 B 50.70 0.46 B 0.64 U 54,400.00 * 24.20 24.30 115.00 37,700.00 R 26,200.00 763.00 0.05 U 15.30 1,180.00 0.43 UW 2.20 NJ 381.00 B 0.64 U 108.00 164.00 0.52 U —ic 0- xi ) Tutu, St. Thomas, U.S. Virgin Islands Tillett Garden Area - Subsurface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS ntg/kg B-8 08/12/92 SOIL 0.0'-2.0' V.SV.I.T 23.00 U B-8-FR 08/12/92 SOIL 0.0'-2.0' V,SV,I,T 77.00 B-8-AVD 08/12/92 SOIL 0.0'-2.0' V.SV.I.T 44.25 MWS-5 08/11/92 SOIL 0.0 ' - 4.0' V.SV.I.T 590.00 D MWS-5-CDM 08/11/92 SOIL 0.0'-4.0' V.SV.I.T 1,210.00 06/17/1994 9:51 AM MUS-5-AVS 08/11/92 SOIL 0.0'-4.0' V.SV.I.T 900.00 D Cr- 00 c oo" Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:05 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organ ics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1-D I CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-D I CHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-OICHLOROPROPENE TRICHLOROETHENE D I BROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans-1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-7 07/31/92 SOIL 2.0'-4.0' V,SV,I,T 10.00 U 10.00 U 10.00 U 10.00 UJ 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U NA 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 5.20 U 10.00 UJ 5.20 UJ NA MUS-3 06/10/92 SOIL 0.4--2.0' V.SV.I.T 12.00 U 12.00 U 12.00 U 12.00 U 1.00 J 11.00 J 12.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 2.00 J 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 5.90 U 12.00 UJ 5.90 UJ NA B-4 06/09/92 SOIL S.O'-IO.O' V.SV.I.T 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 55.00 J 12.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 6.00 U 12.00 UJ 6.00 UJ NA MWS-4 06/16/92 SOIL 2.7--4.71 V.SV.I.T 13.00 U 13.00 U 13.00 U 13.00 U 2.00 J 190.00 B 13.00 UJ 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 48.00 13.00 U 13.00 U NA 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 1.00 J 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 13.00 U 6.30 U 13.00 U 6.30 UJ NA MUS-4D 06/04/92 SOIL 8.7'-10.7' v.sv,r R R R R 1.00 J 81.00 J R R R R R R R R R NA R R R R R R R R R R R R R R R R R R R R R NA B-3 08/03/92 SOIL 2.0--4.0' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 26.00 J 6.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 6.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.00 U 10.00 UJ 5.00 UJ NA -0 Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:05 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE B80MOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULF1DE 1,1-DICHLOROETHENE 1,1 -D I CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-OICHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-DICHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans- 1 , 3-D I CHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DlBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-5 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 9.00 J 92.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 18.00 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 U 11.00U 11.00 U 11.00 U 5.70 U 1.30 J 5.70 UJ NA eT-025 09/14/88 SOIL 0.0'-2.0' V.P.T 14.00 UJ 2.00 J 14.00 UJ 14.00 UJ 28.00 UBJ 220.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 75.00 J 7.00 UJ 7.00 UJ 14.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 7.00 UJ 4.00 J 7.00 UJ 7.00 UJ 25.00 J 14.00 UJ 7.00 UJ 7.00 UJ 18.00 J 7.00 UJ 10.00 J 7.00 UJ 88.00 J NA NA NA NA 6T-02SD 09/14/88 SOIL 0.0'-2.0' V,P,T 18.00 UJ 18.00 UJ 18.00 UJ 18.00 UJ 16.00 UJ 18.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ R 9.00 UJ 9.00 UJ 18.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ '9.00 UJ 9.00 UJ 9.00 UJ 9.00 UJ 18.00 UJ 18.00 UJ 9.00 UJ 9.00 UJ 32.00 J 9.00 UJ 8.00 J 9.00 UJ 1,700.00 J NA NA NA NA eT-02S-AVD 09/14/88 SOIL 0.0'-2.0' V.P.T 16.00 UJ 2.00 J 16.00 UJ 16.00 UJ 22.00 UBJ 119.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 75.00 J 8.00 UJ 8.00 UJ 16.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 8.00 UJ 4.25 J 8.00 UJ 8.00 UJ 17.00 J 16.00 UJ 8.00 UJ 8.00 UJ 25.00 J 8.00 UJ 9.00 J 8.00 UJ 1,700.00 J NA NA NA NA MWS-15 03/28/94 SOIL 4.0' - 6.0- V,SV,I,T 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 4.00 J 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 20.00 J R R MWS-17 03/28/94 SOIL 6.0' - 8.0' V.SV.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 3.00 J 11.00 U 11.00 U 11.00 U 2.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00U 11.00 U 11.00U 11.00 U 11.00 U NA 55.00 U R R HC Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:06 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DtCHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4- CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-7 07/31/92 SOIL 2.0'-4.0' V.SV.I.T 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U NA 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U NA 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 830.00 U 340.00 U 830.00 U 340.00 U 340.00 U 340.00 U MUS-3 06/10/92 SOIL 0.4'-2.0' V,SV,I,T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 950.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U B-4 06/09/92 SOIL 8.0'-10.0' V.SV.I.T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 950.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U MWS-4 06/16/92 SOIL 2.7'-4.7' V.SV.I.T 420.00 U 13.00 J 420.00 U 420.00 U 420.00 U NA 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U NA 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 UJ 420.00 U 1,000.00 U 420.00 U 1,000.00 U 420.00 U 420.00 U 420.00 U MUS-4D 06/04/92 SOIL 8.7'-10.7' V.SV.I 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 950.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U B-3 08/03/92 SOIL 2.0'-4.0' V.SV.I.T 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 910.00 U 380.00 U 910.00 U 380.00 U 380.00 U 380.00 U o K2 '••4W Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:06 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatites-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-OICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 NETHYLPHENOL N-NITROSO-D1-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-OIMETHYLPHENOL BENZ01C ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE KEXACHLOROCYCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-5 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 UJ 370.00 U 370.00 U 370.00 UJ 370.00 U 910.00 UJ 370.00 U 910.00 U 370.00 U 370.00 U 370.00 U eT-02S 09/14/88 SOIL 0.0--2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eT-02SD 09/14/88 SOIL 0.0'-2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA NA NA NA NA NA NA eT-025-AVD 09/14/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-15 03/28/94 SOIL 4.0' - 6.0' V.SV.I.T 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U NA 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U NA 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 UJ 410.00 U 980.00 U 410.00 U 980.00 U 410.00 U 410.00 U 410.00 U MWS-17 03/28/94 SOIL 6.0' - 8.0' V.SV.T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 900.00 U 370.00 U 900.00 U 370.00 U 370.00 U 370.00 U Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:07 PH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINlTROTOLUENE DIETNYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4,6-DINITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBEHZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3, 3 '-DICHLOROBENZID I ME BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G.H.I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-7 07/31/92 SOIL 2.0'-4.0' V,SV,I,T 830.00 U 340.00 U 830.00 U 830.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 830.00 U 830.00 U 340.00 U 340.00 U 340.00 U 830.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 UJ 340.00 U 340.00 U 340.00 U 340.00 U MWS-3 06/10/92 SOIL 0.4'-2.0' V.SV.I.T 950.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 950.00 UJ 950.00 U 390.00 U 390.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U 170.00 J 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U B-4 06/09/92 SOIL 8.0'-10.0' V.SV.I.T 950.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U R 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U MUS-4 06/16/92 SOIL 2.7'-4.7' V,SV,I,T 1,000.00 U 420.00 U 1,000.00 U 1,000.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 1,000.00 UJ 1,000.00 U 420.00 U 420.00 U 420.00 U 1,000.00 U 420.00 U 420.00 U 420.00 U 1,900.00 U 420.00 U 420.00 U 420.00 U 420.00 UJ 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 420.00 U 140.00 J 420.00 U 420.00 U 420.00 U MUS-4D 06/04/92 SOIL 8.7'-10.7' V,SV,I 950.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 950.00 U 950.00 U 390.00 U 390.00 U 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U R 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U B-3 08/03/92 SOIL 2.0'-4.0' V.SV.I.T 910.00 U 380.00 U 910.00 U 910.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 910.00 UJ 910.00 U 380.00 U 380.00 UJ 380.00 UJ 910.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U oo Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:07 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROAN1LINE ACENAPHTHENE 2,4-DlNITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINlTROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4,6-DINiTRO-2-METHYLPHENOL N-NITROS001PHENYLAHINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PNENANTHRENE ANTHRACENE CARBAZOLE OI-M-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3.3'-DICHLOROBENZlDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B)FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE ItlDENO (1.2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,1) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-5 08/13/92 SOIL 0.0'-2,0' V,SV,l,T 910.00 UJ 370.00 U 910.00 U 910.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 910.00 U 910.00 U 370.00 U 370.00 U 370.00 UJ 910.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 370.00 U 370.00 U 370.00 U eT-02S 09/14/88 SOIL 0.0--2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA CT-02SD 09/14/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA NA NA NA NA NA NA CT-02S-AVD 09/14/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-15 03/28/94 SOIL 4.0' - 6.0' V,SV,1,T 980.00 UJ 410.00 U R 980.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 980.00 U 980.00 UJ 410.00 U 410.00 U 410.00 U 980.00 UJ 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U 410.00 U MUS-17 03/28/94 SOIL 6.0- - 8.0' V,SV,T 900.00 U 370.00 U 900.00 UJ 900.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 900.00 U 900.00 U 370.00 U 370.00 U 370.00 U 900.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 J 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U OO "s. o •--j :-.4 rn Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:19 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 PesticidesXPcbs ALPHA-BHC BETA-BHC DELTA-BHC LINDANE, TOTAL NEPTACHLOR ALDRIN HEPTACHLOR EPOXIDE ENDOSt/LFAN I DIELDRIN 4,4-DDE ENDR1N, TOTAL ENDOSULFAN 11 4,4-DDD ENDOSULFAN SULFATE 4,4-DDT HETHOXYCHLOR ENDRIN KETONE ALPHA- CHLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-7 07/31/92 SOIL 2.0'-4.0' V.SV.l.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-3 06/10/92 SOIL 0.4'-2.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA B-4 06/09/92 SOIL 8.0'-10.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 'NA NA NA NA NA NA MWS-4 06/16/92 SOIL 2. 7' -4. 7' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-4D 06/04/92 SOIL 8.7'-10.7' V.SV.I NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA B-3 08/03/92 SOIL 2.0'-4.0- V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Organic Compounds 07/29/1994 12:19 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Pesticides\Pcbs ALPHA-8HC BETA-BHC DELTA-BHC LINDANE, TOTAL HEPTACHLOR ALDRIN NEPTACHLOR EPOXIDE ENDOSULFAN I D1ELDR1N 4,4-DDE ENDRIN, TOTAL ENDOSULFAN II 4,4-DDD ENDOSULFAN SULFATE 4,4-DDT METHOXYCHLOR ENDRIN KETONE ALPHA-CNLORDANE GAMMA-CHLORDANE TOXAPHENE AROCLOR-1016 AROCLOR-1221 AROCLOR-1232 AROCLOR-1242 AROCLOR-1248 AROCLOR-1254 AROCLOR-1260 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-5 08/13/92 SOIL 0.0'-2.0' V,SV,I,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eT-02S 09/14/88 SOIL 0.0'-2.0' V,P,T 11.00 UJ 11.00 UJ 11.00 UJ 11.00 UJ 11.00 UJ 11.00 UJ 11.00 UJ 11.00 UJ 22.00 UJ 22.00 UJ 22.00 UJ 22.00 UJ 22.00 UJ 22.00 UJ 22.00 UJ 110.00 UJ 22.00 UJ 130.00 J 120.00 J 220.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 110.00 UJ 220.00 UJ 220.00 UJ eT-02SD 09/14/88 SOIL 0.0'-2.0' V,P,T 14.00 UJ 14.00 UJ 14.00 UJ 14.00 UJ 14.00 UJ 14.00 UJ 14.00 UJ 14.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 28.00 UJ 140.00 UJ 28.00 UJ 140.00 UJ 140.00 UJ 280.00 UJ 140.00 UJ 140.00 UJ 140.00 UJ 140.00 UJ 140.00 UJ 280.00 UJ 280.00 UJ eT-02S-AVD 09/14/88 SOIL 0.0'-2.0' V,P,T 12.50 UJ 12.50 UJ 12.50 UJ 12.50 UJ 12.50 UJ 12.50 UJ 12.50 UJ 12.50 UJ 25.00 UJ 25.00 UJ 25.00 UJ 25.00 UJ 25.00 UJ 25.00 UJ 25.00 UJ 125.00 UJ 25.00 UJ 135.00 UJ 130.00 UJ 250.00 UJ 125.00 UJ 125.00 UJ 125.00 UJ 125.00 UJ 125.00 UJ 250.00 UJ 250.00 UJ MWS-15 03/28/94 SOIL 4.0' - 6.0' V,SV,I,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-17 03/28/94 SOIL 6.0' - 8.0' V,SV,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA —! f— oo x! Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Inorganic Analytes 07/29/1994 12:20 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-5 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 22,900.00 7.90 BNJ 0.46 U 38.40 B 0.23 U 0.69 U 67,200.00 * 33.60 NJ 18.90 47.30 NJ 29/800.00 3.60 J 19,400.00 861.00 0.06 U 19.40 386.00 B 0.46 UUJ 0.92 U 271.00 B 0.69 U 94.90 NJ 49.90 . 0.58 U eT-028 09/14/88 SOIL 0.0'-2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA eT-02SD 09/14/88 SOIL 0.0--2.0' V.P.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA ''NA NA NA 6T-02S-AVD 09/14/88 SOIL 0.0'-2.0' V,P,T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MUS-15 03/28/94 SOIL 4.0' - 6.0' V.SV.I.T 21,100.00 6.00 UJ 0.82 B 81.10 0.34 1.10 B 5,730.00 33.20 J 21.30 94.90 38,600.00 4.90 11,100.00 622.00 0.08 B 18.40 773.00 B 0.50 U 0.75 U 1,550.00 0.50 U 112.00 51.40 0.79 U 6.0 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA MWS-17 03/28/94 SOIL ' - 8.0' V.SV.T O to c —! Si Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Inorganic Analytes 07/29/1994 12:20 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-7 07/31/92 SOIL 2.0'-4.0' V,SV,I,T 28,400.00 5.90 BJ 1.00 B 36.90 B 0.21 U 0.62 U 51,600.00 28.60 23.40 73.10 35,400.00 19.80 J 21,500.00 828.00 0.05 U 17.80 460.00 B 0.41 UUJ 0.83 U 561.00 B 0.62 U 94.80 62.40 0.52 U MUS-3 06/10/92 SOIL 0.4'-2.0' V,SV,I,T 25,800.00 J 3.00 U R 59.80 J 0.23 U 0.68 U 57,300.00 J 31.80 J 21.60 J 57.40 J 31,500.00 J 3.90 J 15,000.00 J 725.00 J 0.06 U 16.70 J 919.00 B 0.46 UUJ 1.40 BJ 665.00 B 0.68 UW 93.40 J 42.60 J 0.57 U B-4 06/09/92 SOIL 8.0'-10.0' V.SV.I.T 32,200.00 J 3.00 U 0.54 BUJ 42.90 BJ 0.27 BJ 0.70 U 7,360.00 J 31.30 J 28.20 J 74.70 J 41,500.00 J 1.50 J 23,600.00 J 941.00 J 0.12 BJ 18.60 J 569.00 B 0.47 U 2.10 BJ 217.00 BJ 0.70 UU 137.00 J 53.10 J 0.59 U MUS-4 06/16/92 SOIL 2.7'-4.7' V.SV.I.T 22,800.00 J 6.20 BJ 1.80 BJ 55.00 J 0.24 U 0.73 BJ 9,810.00 J 38.00 EJ 32.70 J 73.90 EJ 39,400.00 EJ 3.60 BJ 14,000.00 EJ 947.00 EJ 0.06 U 18.80 J 1,270.00 J 0.55 BWJ 0.72 U 274.00 B 0.72 U 121.00 EJ 49,00 EJ 0.65 MWS-4D 06/04/92 SOIL 8.7'-10.7' V.SV.l 21,700.00 J 3.50 BJ 0.46 U 59.40 J 0.23 U 0.69 U 7,790.00 J 27.00 J 28.50 J 75.30 J 38,000.00 J 2.80 J 17,800.00 J 717.00 J 0.06 U 19.10 J 505.00 B 0.53 BWJ 2.00 BJ 318.00 B 0.69 UU 120.00 J 46.80 J 0.57 U B-3 08/03/92 SOIL 2.0'-4.0' V,SV,I,T 24,200.00 4.70 UJ 1.20 B 184.00 0.42 B 0.70 U 65,900.00 35.80 22.80 104.00 42,500.00 4.50 J 12,700.00 506.00 0.06 U 17.10 471.00 B 0.47 U 2.10 BJ 2,040.00 0.70 U 157.00 42.60 0.58 U x! •(0 SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg Fire Dept., Texaco B-7 07/31/92 SOIL 2.0--4.0' V.SV.I.T 28.00 Tutu, St. Thomas, U.S. Virgin Islands Gas Station, Antilles Auto Parts, Ramsay Motor Total Petroleum Hydrocarbons MUS-3 06/10/92 SOIL 0.4'-2.0' V,SV,I,T 24.00 U B-4 06/09/92 SOIL 8.0'-10.0' V,SV,I,T 24.00 U Co. - Subsurface Soil MWS-4 06/16/92 SOIL 2.7"-4.7' V,SV,I,T 130.00 • MWS-4D 06/04/92 SOIL 8.7--10.71 V.SV.I NA 07/29/1994 12:38 PM B-3 08/03/92 SOIL 2.0'-4.0' V,SV,I,T 23.00 U oo wx! -G Tutu, St. Thomas, U.S. Virgin Islands Fire Dept., Texaco Gas Station, Antilles Auto Parts, Ramsay Motor Co. - Subsurface Soil Total Petroleum Hydrocarbons 07/29/1994 12:38 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS dig/kg B-5 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 53.00 eT-025 09/14/88 SOIL 0.0--2.0' V.P.T 66.10 J eT-0250 09/14/88 SOIL 0.0'-2.0' V.P.T 47.60 J eT-02S-AVD 09/14/88 SOIL 0.0--2.0' V,P,T 56.85 J MWS-15 03/28/94 SOIL 4.0' - 6.0' V,SV,I,T 25.00 U MUS-17 03/28/94 SOIL 6.0' - 8.0' V.SV.T 21.00 U —!C K.1 IBO H O Xi O * Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROHOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1-D I CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-DICHLOROETHANE 2-BUTANONE 1,1,1-TR I CHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMODI CHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-DICHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans-1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1,1,2 , 2- TETR ACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert -butyl methyl ether (MTBE) n-PROPYLBENZENE OIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-H 08/14/92 SOIL 0.0«-2.0' V.SV.l.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 72.00 J 11.00 U 2.00 J 11.00 U 11.00 U 11.00 U 11.00 U 5.70 U 11.00 UJ 5.70 UJ NA B-14-FR 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 100.00 J 11.00 U 3.00 J 11.00 U 11.00 U 11.00 U 11.00 U 5.70 U 11.00 UJ 5.70 UJ NA B-14-AVD 08/14/92 SOIL 0.0'-2.0' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 86.00 J 11.00 U 2.50 J 11.00 U 11.00 U 11.00 U 11.00 U 5.70 U 11.00 UJ 5.70 U NA B-15 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 6.00 J 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 170.00 12.00 U 12.00 12.00 U 12.00 U 12.00 U 12.00 U 6.00 U 12.00 UJ 6.00 UJ NA B-16 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 u NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 23.00 11.00 U 11.00 J 11.00 U 11.00 U 11.00 U 11.00 U 5.60 U 11.00 UJ 5.60 UJ NA B-1 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 38.00 U 38.00 U 38.00 U 38.00 UJ 38.00 U 16.00 J 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U NA 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 38.00 U 19.00 U 38.00 UJ 19.00 UJ NA 03 I-i Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:13 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1 -DICHLOROETHENE 1,1-DICHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-D I CHLOROETHANE 2-BUTANONE 1,1,1 -TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMODICHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-DICHLOROPROPENE TRICHLOROETHENE D 1 BROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans- 1 , 3-D I CHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-D IBROHOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-1-CDM 07/30/92 SOIL 4.0'-8.0' V,SV,T 11.00 U 11.00 U 11.00 U 11.00 U 18.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 1.00 J 11.00 U 11.00 U 11.00 u 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA B-1-AVS 07/30/92 SOIL 4.0'-8.0' V,SV,I,T 24.50 U 24.50 U 24.50 U 24.50 UJ 28.00 UJ 10.75 J 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 UJ 24.50 U 24.50 U NA 24.50 U 24.50 U 24.50 U 1.00 J 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 24.50 U 15.00 U 24.50 UJ 15.00 UJ NA B-6 07/30/92 SOIL 4.0' - 8.0' V.SV.I.T 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 370.00 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 59.00 29.00 U 29.00 U NA 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 29.00 U 15.00 U 30.00 UJ 15.00 UJ NA B-6-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 11.00 U 11.00 U 11.00 U 11.00 U 17.00 UJ 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA B-6-AVS 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 20.00 U 20.00 U 20.00 U 20.00 U 23.00 UJ 370.00 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 59.00 20.00 U 20.00 U NA 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 20.00 U 13.00 U 20.50 UJ 13.00 UJ NA MWS-1 06/30/92 SOIL 0.0'-2.0' V.SV.I.T 11.00 UJ 11.00 U 11.00U 11.00 U 2.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.80 U 12.00 U 5.80 UJ NA .. X! Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:13 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organ ics CHLOROMETHANE BROMONETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1-D I CHLOROETHANE 1,2-DlCHLOROETHENE (TOTAL) CHLOROFORM 1,2-D I CHLOROETHANE 2-BUTANONE 1,1,1 -TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMODICHLOROMETHANE 1,2-DICHLOROPROPANE cis-1 ,3-DICHLOROPROPENE TRICHLOROETHENE D I BROMOCHLOROMETHANE 1,1, 2- TRICHLOROETHANE BENZENE Trans-1 ,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 ,2, 2- TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DlBROMOETHANE (EDB) tert -butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-1D 06/05/92 SOIL 1.0'-2.5' V,SV,1,T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 49.00 J 11.00 UJ 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.60 U 11.00 UJ 5.60 UJ NA MUS-13 03/29/94 SOIL 2.0' - 3.5' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 u 11.00 U 11.00 U 11.00 U NA 55.00 U R R MUS-13D 06/19/92 SOIL 4.0'-6.0' v.sv.i 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.40 U 11.00 U 5.40 U NA MWS-14 07/01/92 SOIL 0.0'-2.0« V.SV.I 12.00 U 12.00 U 12.00 U 12.00 U 34.00 B 16.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 2.00 J 12.00 U 12.00 U 12.00 U 1.00 J 5.90 U 12.00 U 5.90 U NA CO HCH Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:14 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL B ! S(2-CHLOROI SOPROPYL )ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE 1SOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOfC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTADIENE 2, 4 , 6- TR I CHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-14 08/14/92 SOIL 0.0--2.0' V.SV.I.T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 UJ 370.00 U 370.00 U 370.00 UJ 370.00 U 910.00 UJ 370.00 U 910.00 U 370.00 U 370.00 U 370.00 U B-14-FR 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 UJ 380.00 U 380.00 U 380.00 UJ 380.00 U 920.00 UJ 380.00 U 920.00 U 380.00 U 380.00 U 380.00 U B-14-AVD 08/14/92 SOIL 0.0'-2.0l V,SV,I,T 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U NA 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U 375.00 U NA 375.00 U 375.00 U 375.00 U 3,75.00 U 375.00 UJ 375.00 UJ 375.00 U 375.00 U 375.00 UJ 375.00 U 915.00 UJ 375.00 U 915.00 U 375.00 U 375.00 U 375.00 U B-15 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 UJ 390.00 U 390.00 U 390.00 UJ 390.00 U 950.00 UJ 390.00 U 950.00 U 390.00 U 390.00 U 390.00 U B-16 08/14/92 SOIL 0.0'-2.0' V,SV,I,T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 UJ 370.00 U 370.00 U 370.00 UJ 370.00 U 890.00 UJ 370.00 U 890.00 U 370.00 U 370.00 U 370.00 U B-1 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 1,300.00 U ,300.00 U ,300.00 U ,300.00 U .300.00 U NA ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U NA ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U ,300.00 U 1,300.00 U 1,300.00 U 1,300.00 U 3,100.00 U 1,300.00 U 3,100.00 U 1,300.00 U 1,300.00 U 1,300.00 U OO xj Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:14 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DlCHLOROBENZENE BENZYL ALCOHOL 1,2-DlCHLOROBENZEME 2-METHYLPHEMOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-N1TROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1 ,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTAD1ENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2,4,6- TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-1-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 860.00 U 350.00 U 860.00 UJ 350.00 U 350.00 U 350.00 U B-1-AVS 07/30/92 SOIL 4.0--8.01 V.SV.I.T 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U NA 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U NA 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 1,980.00 U 825.00 U 1,980.00 UJ 825.00 U 825.00 U 825.00 U B-6 07/30/92 SOIL 4.0' - 8.0' V,SV,I,T 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U NA 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U NA 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 2,000.00 U 820.00 U 2,000.00 U 820.00 U 820.00 U 820.00 U B-6-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ NA 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ NA 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 870.00 UJ 360.00 UJ 870.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ B-6-AVS 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ NA 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ NA 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 1,435.00 UJ 590.00 UJ 1,435.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ MUS-1 06/30/92 SOIL 0.0'-2.0' V,SV,I,T 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 U 920.00 U 380.00 U 920.00 U 380.00 U 380.00 U 380.00 U HC o Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:14 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Senrivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DiCHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-N1TROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTADIENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINlTROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg . ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-1D 06/05/92 SOIL 1.0--2.5' V.SV.I.T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 890.00 U 370.00 U 890.00 U 370.00 U 370.00 U 370.00 U MWS-13 03/29/94 SOIL 2.0' - 3.5' V,SV,I,T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 890.00 U 370.00 U 890.00 U 370.00 U 370.00 U 370.00 U MWS-13D 06/19/92 SOIL 4.0'-6.0' v.sv.i 350.00 U 350.00 U 350.00 U 350.00 'U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 390.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 UJ 350.00 U 860.00 U 350.00 U 860.00 U 350.00 U 350.00 U 350.00 U MUS-14 07/01/92 SOIL 0.0'-2.0' V.SV.I 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 940.00 U 390.00 U 940.00 U 390.00 U 390.00 U 390.00 U 02 :•>> «- in ^r- •& </><v'~* ^f «— i > «- -V, - </) i eo o > coo • > o OffM-l- H- u-O^ — O • O • — V> CM « V CO0 - 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O: — 1 z >. ->i— a: iou = £§5 S-1 — — o —i s- Ul O. O Z I- « Z Z O Z < O Z UJ _ _ ___ ui oe ui ex. ee. i— z — at o tu O O _ _ _ z t- a: 3 i-; x o. z t-Ozg-ioezui >• Z Z O O Z _ l o e z O Z O O — • o ui ee *~ac a>z—i z <rsim «tui m o lunjo-^^-' o M — - i - o i - O < J « ^ i O O O z z o - - — • — — — T r O U I > - - N > - Z M N I M U I U I I M w t z z z a aa z — — — z i »ui i i— 3>- -x — — 10.01 - - u- -<t z TUT O07 0287 Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:15 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROAN1L1NE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DtMITROTOLUEME DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4.6-DIN1TRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE 1NDENO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-1-CDM 07/30/92 SOIL 4.0'-8.0' V,SV,T 860.00 U 350.00 U 860.00 UJ 860.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 860.00 UJ 860.00 U 350.00 U 350.00 U 350.00 U 860.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 UJ 350.00 U 350.00 U 350.00 U 49.00 J 350.00 UJ 350.00 U 350.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U B-1-AVS 07/30/92 SOIL 4.0'-8.0' V,SV,I,T 1,980.00 U 825.00 U 1.980.00 UJ 1,980.00 UJ 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 1,980.00 UJ 1,980.00 UJ 825.00 U 825.00 U 825.00 U 1,980.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 U 825.00 UJ 825.00 U 825.00 U 825.00 U 49.00 J 825.00 UJ 825.00 UJ 825.00 UJ 825.00 U 825.00 U 825.00 U 825.00 U B-6 07/30/92 SOIL 4.0' - 8.0' V,SV,I,T 2,000.00 U 820.00 U 2,000.00 U 2,000.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 2,000.00 U 2,000.00 U 820.00 U 820.00 U 820.00 U 2,000.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 U 820.00 UJ 820.00 U 820.00 U 820.00 U 820.00 U B-6-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 870.00 UJ 360.00 UJ 870.00 UJ 870.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 870.00 UJ 870.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 870.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ 360.00 UJ B-6-AVS 07/30/92 SOIL 4.0'-8.0' V,SV,I,T 1,435.00 UJ 590.00 UJ 1,435.00 UJ 1,435.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 1,435.00 UJ 1,435.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 1,435.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ 590.00 UJ MUS-1 06/30/92 SOIL 0.0'-2.0' V.SV.I.T 920.00 U 380.00 U 920.00 U 920.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 920.00 U 920.00 U 380.00 U 380.00 U 380.00 U 920.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 03 CO —! ow CO -G Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Organic Compounds 07/29/1994 11:15 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semi vo tat iles- 2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4.6-DINITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4-BROHOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-OICHLOROBENZ!D!NE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B)FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE D I BENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-1D 06/05/92 SOIL 1.0'-2.5' V,SV,I,T 890.00 U 370.00 U 890.00 U 890.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 890.00 U 890.00 U 370.00 U 370.00 U 370.00 U 890.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U R 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U MUS-13 03/29/94 SOIL 2.0' - 3.5' V,SV,I,T 890.00 U 370.00 U 890.00 UJ 890.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 890.00 U 890.00 U 370.00 U 370.00 U 370.00 U 890.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 210.00 J 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U MWS-13D 06/19/92 SOIL 4.0'-6.0- V,SV,I 860.00 U 350.00 U 860.00 U 860.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 860.00 UJ 860.00 U 350.00 U 350.00 U 350.00 U 860.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U MUS-14 07/01/92 SOIL 0.0--2.01 V,SV,I 940.00 U 390.00 U 940.00 U 940.00 UJ 390.00 U 390.00 U 40.00 J 390.00 U 390.00 U 940.00 U 940.00 U 390.00 U 390.00 U 390.00 U 940.00 U 390.00 U 390.00 U 390.00 U 890.00 B 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Inorganic Analytes 07/29/1994 11:16 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg ing/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-14 08/14/92 SOIL 0.0'-2.0' V,SV,I,T 25,300.00 7.30 BNJ 0.46 U 34. SO B 0.23 U 0.70 U 120,000.00 * 13.80 NJ 20.00 48.30 NJ 28,000.00 2.90 J 26,200.00 757.00 0.06 U 11.10 161.00 B 0.46 UWJ 0.93 B 181.00 B 0.70 U 95.80 NJ 50.90 0.58 U B-14-FR 08/14/92 SOIL 0.0--2.0' V,SV,I,T 19,000.00 4.60 UNJ 0.46 U 33.60 B 0.23 U 0.69 U 73,000.00 * 17.40 NJ 18.20 77.60 NJ 23,100.00 2.00 J 17,800.00 640.00 0.06 U 13.10 201.00 B 0.46 U 0.92 U 191.00 B 0.69 U 69.30 NJ 60.10 0.58 U B-14-AVD 08/14/92 SOIL 0.0'-2.0« V.SV.I.T 22,150.00 4.80 BNJ 0.46 U 34.05 B 0.23 U 0.70 U 96,500.00 * 15.60 NJ 19.10 62.95 NJ 25,550.00 2.45 J 22,000.00 698.50 0.06 U 12.10 181.00 B 0.46 UWJ 0.70 B 186.00 B ,0.70 U $2.55 NJ 55.50 0.58 U B-15 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 26,400.00 6.40 BNJ 1.30 B 32.10 B 0.23 U 0.70 U 89,400.00 * 27.30 NJ 23.20 65.90 NJ 32,600.00 12.20 J 22,900.00 809.00 0.06 U 16.50 389.00 B 0.46 UWJ 1.10 B 281.00 B 0.70 U 98.80 NJ 206.00 0.75 B-16 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 18,900.00 6.80 BNJ 11.60 39.90 B 0.22 U 0.99 B 68,800.00 * 36.40 NJ 19.00 72.10 NJ 30,600.00 45.60 N*J 16,300.00 599.00 0.57 15.70 506.00 B 0.44 UWJ 1.30 B 396.00 B 0.67 U 79.70 NJ 459.00 0.55 U B-1 07/30/92 SOIL 4.0--8.0' V.SV.I.T 25,100.00 7.40 BJ 0.96 B 42.10 B 0.23 U 0.68 U 39,600.00 29.20 23.00 85.60 35,700.00 31.00 SJ 17,600.00 757.00 0.06 U 18.90 634.00 B 0.46 U 0.91 U 472.00 B 0.68 U 102.00 56.50 0.57 U to -0o —! r-j •-J. Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Inorganic Analytes 07/29/1994 11:16 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg rag/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-1-CDM 07/30/92 SOIL 4.0--8.0' V.SV.T 29,800.00 16.00 0.65 53.00 0.60 U 5.20 43.300.00 33.00 29.00 100.00 43,200.00 11.20 J 17,700.00 849.00 0.20 U 19.00 572.00 U 0.57 U 1.10 U 572.00 U 0.57 U 115.00 59.00 10.00 U B-1-AVS 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 27,450.00 11.70 BJ 0.81 B 47.55 B 0.42 U 2.77 41,450.00 31.10 26.00 92.80 39,450.00 31.00 SJ 17,650.00 803.00 0.13 U 18.95 460.00 B 0.52 U 1.01 U 379.00 B 0.63 U 108.50 57.75 5.29 U B-6 07/30/92 SOIL 4.0« - 8.0' V,SV,I,T 35,700.00 4.50 BJ 0.74 B 41.00 B 0.22 U 0.67 U 6,490.00 36.00 30.30 67.60 42,700.00 6.20 SJ 21,300.00 895.00 0.06 U 19.00 833.00 B 0.45 U 0.98 BJ 274.00 B ,0.67 U 119.00 51.00 0.56 U B-6-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 40,100.00 19.00 0.57 U 40.00 0.60 U 5.40 6,590.00 37.00 35.00 70.00 50,100.00 7.20 J 23,100.00 1,050.00 0.20 U 20.00 778.00 0.57 U 1.20 U 579.00 U 0.57 U 131.00 59.00 10.00 U B-6-AVS 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 37,900.00 19.00 0.51 B 40.50 B 0.41 U 2.87 6,540.00 36.50 32.65 68.80 46,400.00 6.70 SJ 22,200.00 972.50 0.13 U 19.50 805.50 B 0.51 U 0.79 BJ 274.00 B 0.62 U 125.00 55.00 5.28 U MWS-1 06/30/92 SOIL 0.0'-2.0' V.SV.I.T 26,700.00 J 5.70 BJ 0.45 BJ 59.10 J 0.23 U 0.68 U 48,300.00 J 18.60 J 22.60 J 47.80 J 37,100.00 EJ 3.00 J 24,600.00 J 734.00 J 0.06 U 12.80 J 278.00 B 0.45 UW 0.68 U 305.00 B 0.68 U 132.00 J 56.00 EJ 0.88 C Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Inorganic Analytes 07/29/1994 11:16 AH SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL fflg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MWS-1D 06/05/92 SOIL 1.0--2.5' V,SV,I,T 37.000.00 J 8.10 BJ 0.46 UU 23.10 BJ 0.23 BJ 0.68 U 41,200.00 J 28.70 J 28.80 J 75.20 J 39,900.00 J 9.20 J 23,600.00 J 833.00 J 0.06 U 19.90 J 655.00 B 0.46 UWJ 2.30 J 632.00 B 0.68 UU 113.00 J 52.10 J 0.57 U MUS-13 03/29/94 SOIL 2.0' - 3.5' V,SV,I,T 23,000.00 5.20 UJ 0.71 B 40.50 B 0.22 B 0.86 U 67,400.00 23.80 J 17.10 77.90 29,100.00 33.60 18,700.00 705.00 0.05 U 27.30 492.00 B 0.43 UJ 0.64 U 393.00 U 0.43 U 84.50 585.00 0.58 U MUS-13D 06/19/92 SOIL 4.0--6.0' V.SV.I 23,400.00 EJ 3.70 BJ 1.70 BJ 17.90 BJ 0.21 U 0.63 U 37,900.00 EJ 20.00 J 26.30 J 102.00 EJ 39,000.00 EJ 3.40 J 17,400.00 EJ 820.00 EJ 0.05 U 17.20 J 205.00 B 0.42 U 0.63 U 581.00 B 0.63 U $5.10 EJ 59.50 EJ 0.52 U MUS-14 07/01/92 SOIL 0.0'-2.0' V.SV.I 28,700.00 EJ 3.40 BJ 0.67 BJ 40.20 BEJ 0.22 U 0.67 U 29,900.00 J 36.00 EJ 28.30 J 86.40 EJ 40,000.00 EJ 3.20 J 20,300.00 EJ 883.00 EJ 0.06 U 18.90 J 689.00 B 0.45 U 0.67 U 500.00 B 0.67 U 113.00 EJ 57.40 EJ 0.56 U KJ •43 Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg B-14 08/14/92 SOIL 0.0'-2.0' V,SV,I,T 250.00 DJ B-14-FR . 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 56.00 J B-14-AVD 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 153.00 DJ B-15 08/14/92 SOIL 0.0.'-2.0' V.SV.I.T 24.00 U B-16 08/14/92 SOIL 0.0'-2.0' V.SV.I.T 82.00 J 07/29/1994 11:17 AM B-1 07/30/92 SOIL 4.0'-8.0' V,SV,I,T 77.00 U -"•i Tutu, St. Thomas, U.S. Virgin Islands Curriculum Center Building - Subsurface Soil Total Petroleum Hydrocarbons SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg B-1-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 60.20 B-1-AVS 07/30/92 SOIL 4.0'-8.0' V.SV.I.T 49.35 B-6 07/30/92 SOIL 4.0' - 8.0' V.SV.l.T 170.00 B-6-CDM 07/30/92 SOIL 4.0'-8.0' V.SV.T 69.60 B-6-AVS 07/30/92 SOIL 4.0'-8.0' V.SV.l.T 119.80 07/29/1994 11:17 AM MUS-1 06/30/92 SOIL 0.0'-2.0' V,SV,I,T 140.00 -.4c ow •-0 Tutu, St. Thomas, U.S. Virgin Islands 07/29/1994 Curriculum Center Building - Subsurface Soil . 11:17 AM Total Petroleum Hydrocarbons ' SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg MWS-1D 06/05/92 SOIL 1.0'-2.5« V.SV.I.T 84.00 MWS-13 03/29/94 SOIL 2.0' - 3.5' V,SV,I,T 230.00 MUS-13D 06/19/92 SOIL 4.0'-6.0' V.SV.I 21.00 U MUS-14 07/01/92 SOIL 0.0'-2.0' V.SV.I 220.00 D _I !~ H " Ui Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Organic Compounds 07/29/1994 10:42 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROHETHANE BROHOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1 -D I CHLOROETHANE 1,2-OICHLOROETHENE (TOTAL) CHLOROFORM 1,2-D I CHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOOICHLOROMETHANE 1,2-DICHLOROPROPANE cis-1,3-DICHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE T rans- 1 , 3 -D I CHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 , 2, 2- TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE DIBROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-9 07/29/92 SOIL 2.0'-6.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.30 U 11.00 UJ 5.30 UJ NA MWS-8 07/20/92 SOIL 0.0--4.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 25.00 27.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 2.00 J 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 5.60 U 11.00 UJ 5.60 UJ NA MWS-8-CDM 07/20/92 SOIL 0.0'-4.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 25.00 UJ 53.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA MWS-8-AVS 07/20/92 SOIL 0.0>-4.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 18.75 40.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 UJ 11.00 U 11.00 U 2.00 J 11.00 U 1.00 J 11.00 U 11.00 U 11.00 U 11.00 U 8.30 U 11.00 UJ 8.30 UJ NA MUS-9 07/24/92 SOIL 0.0' - 4.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 18.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.00 U 10.00 U 5.00 U NA MUS-9- COM 07/24/92 SOIL 0.0'-4.0' V.SV.I.T 10.00 U 10.00 U 10.00 U 10.00 U 25.00 UJ 70.00 UJ 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U NA 10.00 U 10.00 U 10.00 U 10.00 J 10.00 U 10.00 U 10.00 U 10.00 U 10.00 UJ 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 10.00 U 11.00 U 11.00 U 11.00 U NA ("*t KJ c H .o Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Organic Compounds 07/29/1994 10:43 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolati tes-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI -N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DlCHLOROPHENOL 1 , 2 , 4 - TR I CHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROCYCLOPENTAD I ENE 2 , 4 , 6- TR I CHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-9 07/29/92 SOIL 2.0'-6.0' V.SV.I.T 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 840.00 U 350.00 U 840.00 U 350.00 U 350.00 U 350.00 U MUS-8 07/20/92 SOIL 0.0'-4.0' V,SV,I,T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 900.00 U 370.00 U 900.00 U 370.00 U 370.00 U 370.00 U MWS-8-CDM 07/20/92 SOIL 0.0'-4.0' V.SV.I.T 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ NA 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ NA 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 890.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ HUS-8-AVS 07/20/92 SOIL 0.0'-4.0' V.SV.I.T 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ NA 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ NA 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 635.00 UJ 370.00 UJ 895.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ MWS-9 07/24/92 SOIL 0.0' - 4.0' V.SV.I.T 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U NA 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 UJ 350.00 U 860.00 U 350.00 U 860.00 U 350.00 U 350.00 U 350.00 U MWS-9-CDM 07/24/92 SOIL 0.0'-4.0' V.SV.I.T 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U NA 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U NA 340.00 U 340.00 U 340.00 U 340.00 U 340.00 UJ 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 830.00 U 340.00 U 830.00 U 340.00 U 340.00 U 340.00 U K3 -•O X! Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Organic Compounds 07/29/1994 10:42 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DlCHLOROETHENE 1,1-DICHLOROETHAME 1,2-DlCHLOROETHENE (TOTAL) CHLOROFORM 1,2-DtCHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DlCHLOROPROPANE c i s - 1 , 3 -D I CHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans- 1 ,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1 , 1 , 2, 2- TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZENE STYREME XYLENES (TOTAL) 1,2-DlBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE D I BROMOMETHANE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg . ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MWS-9-AVS 07/24/92 SOIL 0.0'-4.0' V.SV.I.T 10.50 U 10.50 U 10.50 U 10.50 U 21.50 UJ 40.50 UJ 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U NA 10.50 U 10.50 U 10.50 U 7.75 J 10.50 U 10.50 U 10.50 U 10.50 U 10.50 UJ 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 10.50 U 8.00 U 10.50 U 8.00 U NA MWS-10 08/04/92 SOIL 2.0--4.0' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 17.00 J 35.00 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.00 J 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.00 U 10.00 UJ 5.00 UJ NA MWS-10D 08/04/92 SOIL 0.0'-2.0' V,SV,I,T 11.00 U 11.00 U 11.00 U 11.00 U 20.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U ,11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 1.00 J 11.00U 11.00 U 11.00 U 11.00 U 5.50 U 11.00 UJ 5.50 UJ NA MWS-18 03/26/94 SOIL 12.0' - 14.0' V.SV.I.T 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 50.00 BJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 13.00 BJ 12.00 UJ 12.00 UJ NA 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ 12.00 UJ NA 60.00 UJ R R MUS-25 03/31/94 SOIL 12.0' - 14.0' V,SV,I,T 12.00 U 12.00 U 12.00 U 12.00 U 3.00 J 33.00 J 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 60.00 U R R KJ CO Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Organic Compounds 07/29/1994 10:43 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivotatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1.4-D1CHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLANINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2.4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHtOROC YCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MWS-9-AVS 07/24/92 SOIL 0.0'-4.0' V.SV.I.T 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U NA 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U NA 345.00 U 345.00 U 345.00 U 345.00 U 345.00 UJ 345.00 U 345.00 U 345.00 U 345.00 UJ 345.00 U 845.00 U 345.00 U 845.00 U 345.00 U 345.00 U 345.00 U MUS-10 08/04/92 SOIL 2.0'-4.0' V,SV,!,T 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U NA 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U NA 360.00 u 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 880.00 U 360.00 U 880.00 U 360.00 U 360.00 U 360.00 U MWS-10D 08/04/92 SOIL 0.0'-2.0' V,SV,I,T 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U NA 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 890.00 U 370.00 U 890.00 U 370.00 U 370.00 U 370.00 U MUS-18 03/26/94 SOIL 12.0' - 14.0' V,SV,I,T 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U NA 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U NA 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 1.800.00 U 750.00 U 1,800.00 U 750.00 U 750.00 U 750.00 U MUS-25 03/31/94 SOIL 12.0' - 14.0' V,SV,I,T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 930.00 U 390.00 U 930.00 U 390.00 U 390.00 U 390.00 U M -C C Tutu, St. Thomas, U.S. Virgin islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Organic Compounds 07/29/1994 10:44 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Seniivolatiles-2 3-NITROAN1LINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE OIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4.6-D1NITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4 - BROMOPHENYL - PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PNENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INOENO (1,2,3-CD) PYRENE 0 I BENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-9 07/29/92 SOIL 2.0--6.0' V.SV.I.T 840.00 U 350.00 U 840.00 U 840.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 840.00 U 840.00 U 350.00 U 350.00 U 350.00 U 840.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 220.00 J 350.00 U 350.00 U 350.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U MWS-8 07/20/92 SOIL 0.0'-4.0« V.SV.I.T 900.00 U 370.00 U 900.00 UJ 900.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 900.00 U 900.00 UJ 370.00 U 370.00 U 370.00 U 900.00 U 370.00 U 370.00 U 370.00 U 730.00 B 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U MUS-8-CDM 07/20/92 SOIL 0.0'-4.0' V.SV.I.T R 370.00 UJ 890.00 UJ 890.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 890.00 UJ 890.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 890.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ R 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ MWS-8-AVS 07/20/92 SOIL 0.0'-4.0' V,SV,I,T 900.00 U 370.00 UJ 895.00 UJ 895.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 895.00 UJ 895.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 895.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 457.50 B 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ 370.00 UJ MUS-9 07/24/92 SOIL, 0.0' - 4.0' V.SV.I.T 860.00 U 350.00 U 860.00 UJ 860.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 860.00 U 860.00 UJ 350.00 U 350.00 U 350.00 U 860.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 UJ 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U 350.00 U MUS-9-CDM 07/24/92 SOIL 0.0'-4.0' V.SV.I.T R 340.00 U 830.00 U 830.00 UJ 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 830.00 U 830.00 UJ 340.00 UJ 340.00 UJ 340.00 UJ 830.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 UJ R 340.00 U 340.00 U 340.00 UJ 340.00 UJ 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U 340.00 U OO Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Organic Compounds 07/29/1994 10:44 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DINlTROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-NITROANILINE 4.6-DINITRO-2-METHYLPHENOL M-NITROSOOIPHENYLAHINE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZID!N£ BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MWS-9-AVS 07/24/92 SOIL 0.0'-4.0' V,SV,I,T 860.00 U 345.00 U 845.00 UJ 845.00 UJ 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 845.00 U 845.00 UJ 345.00 UJ 345.00 UJ 345.00 UJ 845.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 UJ 350.00 UJ 345.00 U 345.00 U 345.00 UJ 345.00 UJ 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U 345.00 U MUS-10 08/04/92 SOIL 2.0'-4.0' V.SV.I.T 880.00 U 360.00 U 880.00 U 880.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 880.00 UJ 880.00 U 360.00 U 360.00 UJ 360.00 UJ 880.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 U 360.00 UJ 360.00 U 360.00 U 360.00 U 360'. 00 U MWS-10D 08/04/92 SOIL 0.0'-2.0' V.SV.I.T 890.00 U 370.00 U 890.00 U 890.00 U 370.00 U 370. 00. U 370.00 U 370.00 U 370.00 U 890.00 UJ 890.00 U 370.00 U 370.00 UJ 370.00 UJ 890.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 U 370.00 UJ 370.00 U 370.00 U 370.00 U 370.00 U MUS-18 03/26/94 SOIL 12.0' - 14.0' V.SV.I.T 1,800.00 U 750.00 U 1,800.00 UJ 1,800.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 1,800.00 U 1,800.00 U 750.00 U 750.00 U 750.00 U 1,800.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 130.00 J 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U 750.00 U MUS-25 03/31/94 SOIL 12.0' - 14.0' V.SV.I.T 930.00 U 390.00 U 930.00 UJ 930.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 930.00 U 930.00 U 390.00 U 390.00 U 390.00 U 930.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 140.00 J 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U xi Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Inorganic Analytes 07/29/1994 10:44 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL MUS-9-AVS 07/24/92 SOIL 0.0'-4.0' V,SV,I,T mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 28,000.00 3.85 0.47 21.85 0.18 0.48 37,750.00 20.50 22.85 58.85 32,450.00 3.80 18,550.00 775.50 0.05 15.65 234.50 0.43 4.12 832.00 0.77 73.45 42.05 0.53 J BJ BJ BJ U U J J J J J J J J U J B U B B U J J U MWS-10 08/04/92 SOIL 2.0'-4.0' V.SV.l.T 14,900.00 4.70 2.40 120.00 0.27 0.71 3,480.00 5.70 8.80 42.20 30,000.00 3.40 5,770.00 480.00 0.06 3.20 621.00 0.47 2.20 413.00 0.71 57.90 57.70 0.59 UJ U B U B J U B B U BJ BJ U U MWS-10D 08/04/92 SOIL 0.0'-2.0' V.SV.I.T 14,100.00 4.30 2.20 199.00 0.28 0.65 5,260.00 4.50 7.90 40.20 33,600.00 3.20 5,770.00 435.00 0.05 3.50 529.00 0.43 2.00 373.00 .0.65 69.50 58.20 0.54 UJ U B U B J U B B U BJ BJ U U MWS-18 03/26/94 SOIL 12.0' - 14.0' V.SV.I.T 22.200.00 5.50 1.30 37.90 0.28 0.91 10,800.00 27.50 20.10 62.60 34,300.00 8.50 15,600.00 472.00 0.06 17.00 1,440.00 0.46 0.68 511.00 0.46 130.00 65.20 0.57 UJ B B B U J U U U B U U MWS-25 03/31/94 SOIL 12.0' - 14.0' V,SV,I,T 17,000.00 5.60 0.94 114.00 0.35 0.95 2,340.00 13.50 18.40 56.50 39,300.00 11.70 6,280.00 1,250.00 0.06 8.30 1,130.00 1.10 0.82 430.00 0.47 89.60 87.20 0.59 UJ B B B J U B B B B U U U oo Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Inorganic Analytes 07/29/1994 10:44 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, TOTAL mg/kg ing/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-9 07/29/92 SOIL 2.0'-6.0' V.SV.I.T 20,800.00 J 4.40 BJ 1.60 BJ 33.80 BJ 0.23 BJ 0.64 U 15,400.00 J 35.20 J 23.70 J 105.00 J 33,100.00 J 5.50 J 16,300.00 J 760.00 J 0.05 U 21.80 J 528.00 B 0.43 U 0.85 U 248.00 B 0.64 U 85.80 J 58.40 J 0.53 U MWS-8 07/20/92 SOIL 0.0'-4.0' V,SV,I,T 22,500.00 J 5.60 BJ 0.44 U 21.70 BJ 0.22 U 0.65 U 28,400.00 J 15.30 J 19.00 J 49.70 J 26,500.00 J 0.48 BJ 15,400.00 J 688.00 J 0.05 U 11.30 J 204.00 B 0.44 UWJ 0.65 U 491.00 B 0.65 U 59.50 J 31.80 J 0.55 MUS-8-CDM 07/20/92 SOIL 0.0'-4.0' V,SV,I,T 33,000.00 3.40 UJ 0.46 UJ 23.80 B 0.21 B 0.32 U 39,000.00 20.80 24.50 J 57.10 37,500.00 1.90 J 20,600.00 859.00 0.05 U 15.70 J 201.00 B R 1.70 B 843.00 B 0.90 U 85.60 45.10 0.55 U MWS-8-AVS 07/20/92 SOIL 0.0'-4.0' V,SV,I,T 27,750.00 J 3.65 BJ 0.45 UJ 22.75 BJ 0.16 B 0.49 U 33,700.00 J 18.05 J 21.75 J 53.40 J 32,000.00 J 1.19 BJ 18,000.00 J 773.50 J 0.05 U 13.50 J 202.50 B 0.44 UUJ 1.01 B 667.00 B 0.78 U 72.55 J 38.45 J 0.41 MUS-9 07/24/92 SOIL 0.0' - 4.0' V.SV.I.T 22,400.00 J 6.00 BJ 0.70 BJ 18.70 BJ 0.21 U 0.64 U 31,600.00 J 15.60 J 18.90 J 50.70 J 25,700.00 J 3.20 J 15,100.00 J 631.00 J 0.05 U 12.40 J 205.00 B 0.43 U 0.64 U 654.00 B 0.64 U 56.30 J 32.40 J 0.53 U MWS-9-CDM 07/24/92 SOIL 0.0'-4.0' V.SV.I.T 33,600.00 3.40 UJ 0.46 UJ 25.00 B 0.15 U 0.31 U 43,900.00 25.40 26.80 J 67.00 39,200.00 4.40 J 22,000.00 920.00 0.05 U 18.90 J 264.00 B R 1.80 B 1,010.00 B 0.90 U 90.60 51.70 0.52 U SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg Esso B-9 07/29/92 SOIL 2.0--6.0' V.SV.I.T 160.00 Tutu, St. Thomas, U.S. Virgin Islands Gas Station and Splash & Dash Car Wash-Subsurface Soil Total Petroleum Hydrocarbons MWS-8 07/20/92 SOIL 0.0'-4.0' V.SV.I.T 22.00 U MWS-8-CDM 07/20/92 SOIL 0.0'-4.0' V.SV.I.T 69.30 MWS-8-AVS 07/20/92 SOIL 0.0'-4.0« V.SV.I.T 69.30 MWS-9 07/24/92 SOIL 0.0' - 4.0' V.SV.I.T 230.00 D 07/29/1994 10:45 AM MUS-9-CDM 07/24/92 SOIL 0.0'-4.0' V.SV.I.T 163.00 Tutu, St. Thomas, U.S. Virgin Islands Esso Gas Station and Splash & Dash Car Wash-Subsurface Soil Total Petroleum Hydrocarbons 07/29/1994 10:45 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg MWS-9-AVS 07/24/92 SOIL 0.0'-4.0' V,SV,I,T 196.50 D MWS-10 08/04/92 SOIL 2.0'-4.0' V,SV,I,T 22.00 U MUS-10D 08/04/92 SOIL 0.0'-2.0' V,SV,I,T 22.00 U MWS-18 03/26/94 SOIL 12.0' - 14.0' V.SV.I.T 23.00 U MUS-25 03/31/94 SOIL 12.0' - 14.0' V.SV,I,T 23.00 U '„' MO Tutu, St. Thomas, U.S. Virgin Islands 0'Henry Dry Cleaners & Liquor Barn - Subsurface Soil Organic Compounds 06/21/1994 2:10 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON D1SULFIDE 1,1-DICHLOROETHENE 1,1 -01 CHLOROETHANE 1,2-DICHLOROETHENE (TOTAL) CHLOROFORM 1,2-D I CHLOROETHANE 2-BUTANONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROMOD I CHLOROMETHANE 1,2-DICHLOROPROPANE cis 1,3-DICHLOROPROPENE TRICHLOROETHYLENE DIBROMOCHLOROMETHANE 1,1,2-TRICHLOROETHANE BENZENE Trans 1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHYLENE 1 , 1 ,2,2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYLBENZNE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert- butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-10 08/10/92 SOIL 6.0'-8.0' V,SV,I,T 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 5.90 U 12.00 UJ 5.90 UJ B-11 08/10/92 SOIL 0.0'-2.0' V.SV.I.T 12.00 U 12.00 U 12.00 U 12.00 U 3.00 J 26.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 UJ 12.00 UJ 29.00 12.00 U 3.00 J 12.00 U 12.00 U 12.00 U 12.00 U 6.10 U 12.00 UJ 6.10 UJ B-12 08/11/92 SOIL 6.0« - 8.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 13.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.70 U 11.00 UJ 5.70 UJ B-12-CDM 08/11/92 SOIL 6.0'-8.0' V.SV.I.T 12.00 U 12.00 U 12.00 U 12.00 U 28.00 UJ 25.00 UJ 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 11.00 U 11.00 U 11.00 U B-12-AVS 08/11/92 SOIL 6.0'-8.0' V.SV.T 11.50 U 11.50 U 11.50 U 11.50 U 19.50 UJ 19.00 UJ 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 UJ 11.50 U 11.50 U NA 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 UJ 11.50 UJ 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 8.35 U 11.00 UJ 8.35 UJ B-13 08/10/92 SOIL 4.0'-6.0- V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 UJ 11.00 UJ 200.00 D 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 5.70 U 11.00 UJ 5.70 UJ NJ Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Subsurface Soil Organic Compounds 06/21/1994 2:07 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-0!CHLOROBENZENE 1.4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DIMETHYLPHENOL BENZOlC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHLOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROC YCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-10 08/10/92 SOIL 6.0--8.0' V.SV.I.T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 940.00 U 390.00 U 940.00 U 390.00 U 390.00 U 390.00 U B-11 08/10/92 SOIL 0.0--2.0' V.SV.I.T 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U NA 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U NA 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 980.00 U 400.00 U 980.00 U 400.00 U 400.00 U 400.00 U B-12 08/11/92 SOIL 6.0' - 8.0' V.SV.I.T 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 920.00 U 380.00 U 920.00 U 380.00 U 380.00 U 380.00 U B-12-CDM 08/11/92 SOIL 6.0'-8.0' V.SV.I.T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 940.00 U 390.00 U 940.00 U 390.00 U 390.00 U 390.00 U B-12-AVS 08/11/92 SOIL 6.0'-8.0' V.SV.T 385.00 UJ 385.00 U 385.00 U 385.00 U 385.00 U NA 385.00 U 385.00 U 385.00 U 385.00 UJ 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U NA 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 930.00 U 385.00 U 930.00 U 385.00 U 385.00 U 385.00 U 8-13 08/10/92 SOIL 4.0'-6.0' V.SV.I.T 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 910.00 U 380.00 U 910.00 U 380.00 U 380.00 U 380.00 U c —! o o Tutu, St. Thomas, U.S. Virgin Islands 0'Henry Dry Cleaners and Liquor Barn - Subsurface Soil Organic Compounds 06/21/1994 1:46 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Serai volatites-2 3-NITROANILINE ACENAPHTHENE 2,4-DlNITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE D1ETHYLPHTHALATE 4- CHLOROPHEHYL -PHENYLETHER FLUORENE 4-NITROANILINE 4.6-DINITRO-2-METHYLPHENOL N-NITROSODIPHENYLAMINE 4 -BROMOPHEN YL - PHENYLETHER HEXACHLOROBENZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZOLE Dl-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3,3'-DICHLOROBENZIOINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE DI-N-OCTYLPHTHALATE BENZO(B) FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE DIBENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg B-10 08/10/92 SOIL 6.0'-8.0' V,SV,I,T 940.00 U 390.00 U 940.00 UJ 940.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 940.00 U 940.00 U 390.00 U 390.00 U 390.00 U 940.00 U 390.00 U 390.00 U 390.00 U 160.00 J 390.00 U 390.00 U 220.00 J 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 390.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U B-11 08/10/92 SOIL 0.0'-2.0- V,SV,I,T 980.00 U 400.00 U 980.00 UJ 980.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 980.00 U 980.00 U 400.00 U 400.00 U 400.00 U 980.00 U . 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 UJ 400.00 U 400.00 UJ 400.00 U 400.00 U 400.00 U 400.00 U B-12 08/11/92 SOIL 6.0' - 8.0' V.SV.I.T 920.00 U 380.00 U 920.00 U 920.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 920.00 U 920.00 U 380.00 U 380.00 U 380.00 U 920.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 3^0.00 UJ 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U B-12-CDM 08/11/92 SOIL 6.0'-8.0' V.SV.I.T 940.00 U 390.00 U 940.00 U 940.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 940.00 U 940.00 U 390.00 U 390.00 U 390.00 U 940.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U B-12-AVS 08/11/92 SOIL 6.0'-8.0' V,SV,T 930.00 U 385.00 U 930.00 U 930.00 UJ 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 930.00 U 930.00 U 385.00 U 385.00 U 385.00 U 930.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 UJ 385.00 UJ 385.00 U 385.00 U 385.00 U 385.00 UJ 385.00 UJ 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U 385.00 U B-13 08/10/92 SOIL 4.0--6.0' V,SV,I,T 910.00 U 380.00 U 910.00 U 910.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 910.00 UJ 910.00 U 380.00 U 380.00 UJ 380.00 UJ 910.00 U 380.00 U 380.00 U 380.00 U 380.00 U 42.00 J 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U o <B Tutu, St. Thomas, U.S. Virgin Islands O'Henry Dry Cleaners & Liquor Barn - Subsurface Soil Inorganic Analytes 07/05/1994 2:02 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Inorganic Analytes ALUMINUM ANTIMONY ARSENIC BARIUM BERYLLIUM CADMIUM CALCIUM CHROMIUM COBALT COPPER IRON LEAD MAGNESIUM MANGANESE MERCURY NICKEL POTASSIUM SELENIUM SILVER SODIUM THALLIUM VANADIUM ZINC CYANIDE, total rag/kg ing/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ma/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg B-10 08/10/92 SOIL 6.0'-8.0' V.SV.I.T 14,300.00 5.20 BJ 2.20 U 498.00 0.22 U 0.65 U 14.400.00 13.00 17.20 88.70 33,600.00 EJ 5.20 J 9,970.00 2,200.00 0.05 U 4.70 B 1,900.00 0.43 U 2.00 BJ 352.00 B 0.65 U 119.00 68.20 EJ 0.54 U B-11 08/10/92 SOIL 0.0'-2.0' V,SV,I,T 19,200.00 4.70 UJ 5.00 124.00 0.33 B 0.70 U 5,150.00 19.50 15.10 76.60 34,100.00 EJ 6.90 SJ 5,920.00 768.00 0.08 B 12.80 2,830.00 0.47 U 1.90 BJ 270.00 B 0.70 U 88.80 99.50 EJ 0.58 U B-12 08/11/92 SOIL 6.0' - 8.0' V,SV,I,T 15,300.00 4.40 UJ 18.30 172.00 0.29 B 0.65 U 6,060.00 21.20 18.20 74.20 28,100.00 EJ 5.40 SJ 5.570.00 2,070.00 0.05 U 16.40 2,280.00 0.44 U 1.80 BJ 297.00 B . 0.65 U V.80 89.10 EJ 0.57U B-12-CDM 08/11/92 SOIL 6.0'-8.0' V.SV.I.T NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0.56 U B-12-AVS 08/11/92 SOIL 6.0'-8.0' V.SV.T 15,300.00 4.40 UJ 18.30 172.00 0.29 B 0.65 U 6,060.00 21.20 18.20 74.20 28,100.00 EJ 5.40 SJ 5,570.00 2,070.00 0.05 U 16.40 2,280.00 0.44 U 1.80 BJ 297.00 B 0.65 U 87.80 89.10 EJ 0.57 U B-13 08/10/92 SOIL 4.0--6.0' V.SV.I.T 18,000.00 4.90 BJ 185.00 J 29.00 B 0.22 U 0.67 U 12,800.00 20.10 15.20 46.40 26,800.00 EJ 1.20 J 14.600.00 430.00 0.06 U 12.30 591.00 B 0.44 U 1.60 BJ 133.00 B 0.67 U 83.90 45.70 EJ 0.56 U £••! '—•' ••0 Tutu, St. Thomas, U.S. Virgin Islands Subsurface Soil - Background Organic Compounds 08/18/1994 9:18 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Volatile Organics CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE 1,1-DICHLOROETHENE 1,1 -DICHLOROETHANE 1 , 2 -D I CHLOROETHENE ( TOTAL ) CHLOROFORM 1,2-DICHLOROETHANE 2-BUTANONE 1,1,1-TR I CHLOROETHANE CARBON TETRACHLORIDE VINYL ACETATE BROHOD I CHLOROMETHANE 1,2-DICHLOROPROPANE CJS-1.3-DICHLOROPROPENE TRICHLOROETHENE DIBROMOCHLOROHETHANE 1 ,1, 2- TR I CHLOROETHANE BENZENE Trans-1,3-DICHLOROPROPENE BROMOFORM 4-METHYL-2-PENTANONE 2-HEXANONE TETRACHLOROETHENE 1,1,2.2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYL8ENZENE STYRENE XYLENES (TOTAL) 1,2-DIBROMOETHANE (EDB) tert-butyl methyl ether (MTBE) n-PROPYLBENZENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-2 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 11.00 U 11.00 U 11.00 U 11.00 U 10.00 J 58.00 J 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U NA 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 U 11.00 u 11 .00 U 5.70 U 11.00 UJ 5.70 UJ MWS-2-FR 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 12.00 U 12.00 U 12.00 U 12.00 U 10.00 J 130.00 J 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 25.00 12.00 U 12.00 U NA 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 12.00 U 6.00 U 12.00 UJ 6.00 UJ MWS-2-AVD 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 11.50 U 11.50 U 11.50 U 11.50 U 10.00 J 94.00 J 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 15.25 11.50 U 11.50 U NA 11.50 U 11.50 U 11. SOU 11.50 U 11.50 U J1.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11.50 U 11. SOU 11.50 U 11.50 U 11.50 U 11. SOU 11.50 U 11.50 U 5.85 U 11.50 UJ 5.85 UJ o '•vi Tutu, St. Thomas, U.S. Virgin Islands O1Henry Dry Cleaners & Liquor Barn - Subsurface Soil Total Petroleum Hydrocarbons 06/21/1994 1:47 PM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 TOTAL PETROLEUM HYDROCARBONS mg/kg 8-10 08/10/92 SOIL 6.0'-8.0' V.SV.I.T 27.00 B-11 08/10/92 SOIL 0.0'-2.0' V.SV.I.T 41.00 B-12 08/1 V92 SOIL 6.0' - 8.0' V.SV.I.T 25.00 B-12-CDM 08/11/92 SOIL 6.0'-8.0' V.SV.I.T 26.40 B-12-AVS 08/11/92 SOIL 6.0'-8.0' V.SV.T 25.70 B-13 08/10/92 SOIL 4.0'-6.0' V.SV.I.T 28.00 o si t_ —I Tutu, St. Thomas, U.S. Virgin Islands Subsurface SoiI - Background Organic Compounds 08/18/1994 9:17 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-1 PHENOL BIS (2-CHLOROETHYL) ETHER 2-CHLOROPHENOL 1,3-DICHLOROBENZENE 1,4-DICHLOROBENZENE BENZYL ALCOHOL 1,2-DICHLOROBENZENE 2-METHYLPHENOL BIS(2-CHLOROISOPROPYL)ETHER 4 METHYLPHENOL N-NITROSO-DI-N-PROPYLAMINE HEXACHLOROETHANE NITROBENZENE ISOPHORONE 2-NITROPHENOL 2,4-DlMETHYLPHENOL BENZOIC ACID BIS (2-CHLOROETHOXY) METHANE 2,4-DICHLOROPHENOL 1,2,4-TRICHLOROBENZENE NAPHTHALENE 4-CHLOROANILINE HEXACHIOROBUTADIENE 4-CHLORO-3-METHYLPHENOL 2-METHYLNAPHTHALENE HEXACHLOROC YCLOPENTAD I ENE 2,4,6-TRICHLOROPHENOL 2,4,5-TRICHLOROPHENOL 2-CHLORONAPHTHALENE 2-NITROANILINE DIMETHYLPHTHALALTE ACENAPHTHYLENE 2,6-DINITROTOLUENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MWS-2 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U NA 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 UJ 380.00 U 380.00 U 380.00 UJ 380.00 U 910.00 UJ 380.00 U 910.00 U 380.00 U 380.00 U 380.00 U MUS-2-FR 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U NA 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U NA 400.00 U 400.00 U 400.00 U 400.00 U 400.00 UJ 400.00 UJ 400.00 U 400.00 U 400.00 UJ 400.00 U 960.00 UJ 400.00 U 960.00 U 400.00 U 400.00 U 400.00 U MWS-2- AVD 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U NA 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 UJ 390.00 U 390.00 U 390.00 UJ 390.00 U 935.00 UJ 390.00 U 935.00 U 390.00 U 390.00 U 390.00 U CM H-w c H Tutu, St. Thomas, U.S. Virgin Islands Subsurface Soil - Background Organic Compounds 08/18/1994 9:17 AM SAMPLE NAME SAMPLE DATE SAMPLE TYPE SAMPLE DEPTH TEXT 004 Semivolatiles-2 3-NITROANILINE ACENAPHTHENE 2,4-DINITROPHENOL 4-NITROPHENOL DIBENZOFURAN 2,4-DINITROTOLUENE DIETHYLPHTHALATE 4-CHLOROPHENYL-PHENYLETHER FLUORENE 4-HITROANiLINE 4.6-DINITRO-2-METHYLPHENOL N - N I TROSOO I PHENYL AMI NE 4-BROMOPHENYL-PHENYLETHER HEXACHLOROBEMZENE PENTALCHLOROPHENOL PHENANTHRENE ANTHRACENE CARBAZdLE DI-N-BUTYLPHTHALATE FLUORANTHENE PYRENE BUTYLBENZYLPHTHALATE 3.3--DICHLOROBENZIDINE BENZO (A) ANTHRACENE CHRYSENE BIS (2-ETHYLHEXYL) PHTHALATE Dl-N-OCTYLPHTHALATE BENZO(B)FLUORANTHENE BENZO(K) FLUORANTHENE BENZO (A) PYRENE INDENO (1,2,3-CD) PYRENE D I BENZO (A,H) ANTHRACENE BENZO (G,H,I) PERYLENE ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MUS-2 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 910.00 UJ 380.00 U 910.00 U 910.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 910.00 U 910.00 U 380.00 U 380.00 U 380.00 UJ 910.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 U 380.00 UJ 380.00 U 380.00 U 380.00 U 380.00 U MUS-2-FR 08/13/92 SOIL 0.0'-2.0' V,SV,I,T 960.00 UJ 400.00 U 960.00 U 960.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 960.00 U 960.00 U 400.00 U 400.00 U 400.00 UJ 960.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 U 400.00 UJ 400.00 U .400.00 U 400.00 U 400.00 U HWS-2-AVD 08/13/92 SOIL 0.0'-2.0' V.SV.I.T 935.00 UJ 390.00 U 935.00 U 935.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 935.00 U 935.00 U 390.00 U 390.00 U 390.00 UJ 935.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 U 390.00 UJ 390.00 U 390.00 U 390.00 U 390.00 U O