PUBLIC HEALTH ASSESSMENT
OUTBOARD MARINE CORPORATION
WAUKEGAN, LAKE COUNTY, ILLINOIS

Figure 1. General Location Map

Figure 2. Location of Outboard Marine Corporation
Plant and PCB Outfalls in Relation to Slip 3 and the
North Ditch

Figure 3. Waukegan Manufactured Gas and Coke Plant Site

Figure 4a. North Ditch Area Extent of PCB Contamination
Over 20 PPM

Figure 4b. North Ditch Area Extent of PCB Contamination
Over 50 PPM

Figure 4c. North Ditch Area Extent of PCB Contamination
Over 500 PPM

Figure 4d. North Ditch Area Extent of Contamination
Over 5000 PPM

Figure 5. Proposed remedial action

Figure 6. The vicinity around Waukegan

Figure 7. Extent of PCB Contamination in Waukegan
Harbor by Concentration

Figure 8. PCB Analysis of Slip No. 3 Core Borings B1-B6

Figure 9. Extent of PCB Contamination in Sediment in
Waukegan Harbor by Amount

Figure 10. Location of Stations Sampled in Waukegan Harbor.

Figure 11. Calculated water column total PCB
concentrations Present condition

Figure 12. Fatty areas of fish which should be
removed to minimize personal exposure to PCB's and
other contaminants
Table 1. PCB levels in fish from Waukegan Harbor (Harris, 1982).
| Year | Concentration (ppm) | |||
| Group | ||||
| A | B | C | D | |
| 1976 | -- | -- | -- | 7.0-8.0 |
| 1978 | -- | 3.5-38.8 | 1.8 | 3.6-29.0 |
| 1979 | -- | 18.9 | 7.0 | 8.2-38.5 |
| 1980 | 2.0-4.2 | 34.0-187 | -- | 131 |
| 1981 | 0.5 | trace-1.41 | 2.0 | 1.4-27.9 |
| Median | 2.0 | 18.9 | 2.0 | 18.2 |
| Health Criterion ---------------------------- |
0.02 | 0.02 | 0.02 | 0.02 |
-- = Data not available.
ppm = Parts per million, wet weight.
Group A = Coho salmon and rainbow trout.
Group B = Black and white crappie, largemouth bass, shiners,
sunfish, and yellow perch.
Group C = Alewife.
Group D = Brown and black bullhead, carp, and white suckers.
Table 2. Median PCB levels in Lake Michigan fish (Harris, 1982).
| Concentration (ppm) | |||
|
Group |
|||
|
Year |
A | E | F |
|
1972 |
4.6 | -- | -- |
|
1973 |
9.1 | -- | -- |
|
1974 |
4.85 | -- | 10.5 |
|
1975 |
3.7 | -- | 5.2 |
|
1976 |
6.5 | 2.5 | 6.0 |
|
1977 |
1.65 | 2.2 | 7.8 |
|
1978 |
5.5 | 2.0 | 3.9 |
|
1979 |
4.3 | 1.7 | 4.1 |
|
1980 |
4.4 | -- | 4.9 |
|
1981 |
2.3 | 1.7 | -- |
|
Health |
0.02 | 0.02 | 0.02 |
|
---------------------------- |
|||
Group A = Coho and chinook salmon, brown and rainbow trout.
Group E = Bloater chub, lake herring, whitefish.
Group F = Lake trout.
ppm = Parts per million, wet weight.
--
= Data not available.
Table 3. Concentrations of PCB's in whole fish from Waukegan Harbor (Clark,
1981).
|
Concentration |
Group | Percent Lipids (whole fish) |
PCB (ppm) |
| Rainbow trout |
A |
5.1 | 2.0 |
|
Carp |
D | 4.8 | 131 |
|
Largemouth bass |
B | 12.0 | 187 |
|
White Crappie |
B | 11.1 | 163 |
|
Yellow perch |
B | 5.8-8.2 | 20.2-34.0 |
|
Health Criterion |
0.02 | 0.02 |
------------------------
ppm = Parts per million.
| Location | Average PCB Concentration (ppm) |
Volume Contaminated (cubic yards) |
Total PCB's (pounds) |
|
Waukegan Harbor |
|||
|
A1 |
54,960 | 1,261 | 116,822a |
|
A2 |
54,796 | 789 | 79,359a |
|
A3 |
11,020 | 508 | 11,104a |
|
A4 |
2,028 | 553 | 2,173 |
|
A5 |
773 | 1,125 | 1,064 |
|
A6 |
341 | 2,939 | 1,299 |
|
Total A1-6 |
-- | 7,275 | 211,831 |
|
B1 |
256 | 5,510 | 1,672 |
|
B2 |
143 | 11,550 | 3,188 |
|
B3 |
100 | 14,825 | 1,529 |
| B4 | 103 | 3,792 | 470 |
| B5 | 47.1 | 1,897 | 122 |
|
Total B1-5 |
-- | 37,574 | 6,981 |
|
C1 |
16.4 | 11,855 | 169 |
| C2 | 15.7 | 15,219 | 354 |
| C3 | 12.2 | 25,253 | 454 |
|
C4 |
33.0 | 23,351b | 402 |
|
C5 |
19.4 | 34,958b | 589 |
|
C6 |
14.1 | 9,815b | 199 |
|
Total C1-6 |
-- | 120,451b | 2,167 |
|
D2 |
9.7 | 2,200b | 39 |
|
D2 |
7.5 | 7,637b | 102 |
|
D3 |
-- | 8,533b | 144 |
|
Total D1-3 |
-- | 18,370b | 255 |
|
Total for muck |
-- | 183,670b | 221,234a |
(continued)
aThe pounds of PCB's may
vary by an order of magnitude depending on how the core borings are grouped
and averaged.
bEstimated value.
ppm = Parts per million.
-- = Data
not available.
Table 4, continued. PCB contamination in the sediments of Waukegan Harbor, the
North Ditch, and the Parking Lot Area (Mason & Hanger-Silas Mason Company,
Inc., 1981). Locations are shown in Figures 2 and 9.
| Location | Average PCB Concentration (ppm) |
Volume Contaminated (cubic yards) |
Total PCB's (pounds) |
Waukegan Harbor Sand |
|||
|
A1 |
-- | 800-20000 | 20,0000- 50,000 |
|
North Ditch |
|||
|
Sediment, |
38,360 | -- | 184,591 |
|
Soil, 6.5-25 feet |
31,073 | -- | 183,658 |
| Soil, 6.5-25 feet deep, 13 feet wide, 340 foot section at two ends |
4,714 | -- | 34,448 |
| Soil around ditch 122,324 cubic feet |
90 | -- | 1,012 |
| Total Crescent Ditch |
-- |
28,900 |
403,709 |
|
Oval Lagoon |
|||
|
Sediments 0-5 feet |
26,207 | -- | 72,247 |
|
Sediments 5-27 |
-- | -- | -- |
|
Soil around |
688 | -- | 13,223 |
|
Total Oval |
-- | 14,600 | over 85,470 |
(continued)
aThe pounds of PCB's may
vary by an order of magnitude depending on how the core borings are grouped
and averaged.
bEstimated value.
ppm = Parts per million.
-- = Data
not available.
Table 4, continued. PCB contamination in the sediments of Waukegan Harbor, the
North Ditch, and the Parking Lot Area (Mason & Hanger-Silas Mason Company,
Inc., 1981). Locations are shown in Figures 2 and 9.
Location |
Average PCB Concentration (ppm) |
Volume |
Total |
|
North Ditch |
|||
|
Sediments 0-6 feet |
235 | 7,000 | 4,273 |
|
Die Storage Area |
|||
|
Soil 0-4 feet |
242 | -- | 1,992 |
| Soil 4 feet 3 inches to 24 feet 3 inches, 21,000 square feet |
1 | -- | 41 |
| Total Sediments | -- | -- | 261,111 |
|
Parking Lot |
|||
|
Bore hole 16 |
1,375 | 300 | 1,023 |
|
Bore hole B8, |
7,897 | -- | 75,881 |
|
Bore holes B4, |
900 | -- | 10,513 |
| Bore hole B9, 23,791 square feet, 9.5 feet deep |
82 | -- | 3,778 |
(continued)
aThe pounds of PCB's may
vary by an order of magnitude depending on how the core borings are grouped
and averaged.
bEstimated value.
ppm = Parts per million.
-- = Data
not available.
Table 4, continued. PCB contamination in the sediments of Waukegan Harbor, the
North Ditch, and the Parking Lot Area (Mason & Hanger-Silas Mason Company,
Inc., 1981). Locations are shown in Figures 2 and 9).
| Location | Average PCB Concentration (ppm) |
Volume Contaminated (cubic yards) |
Total PCB's (pounds) |
|
Parking Lot |
|||
|
Bore hole B18, |
17 | -- | 94 |
|
Bore holes 2, 2A, |
6,069 |
-- |
163,920 |
| Bore hole B15 21,120 square feet, 30 feet deep |
360 | -- | 20,950 |
| Total Parking Lot Area |
-- |
105,000 |
227,688 |
|
Total North Ditch |
-- | -- | 773,173 |
aThe pounds of PCB's may
vary by an order of magnitude depending on how the core borings are grouped
and averaged.
bEstimated value.
ppm = Parts per million.
-- = Data
not available.
Table 5. Concentrations of inorganic chemicals in the sediments of Waukegan
Harbor. Sample locations are shown in Figure 10 (Risatti et al., 1990).
| Concentration (ppm) | |||||
| Location |
Aluminum |
Barium | Beryllium | Calcium (%) |
Cadmium |
| WH-1 | 1.88 | 230 | 1.6 | 7.1 | N.D. |
|
WH-2 |
2.11 | 260 | 1.8 | 6.4 | N.D. |
|
WH-3 |
2.46 | 280 | 1.7 | 7.1 | N.D. |
|
WH-4 |
2.34 | 280 | 1.6 | 6.3 | N.D. |
|
WH-5 |
3.70 | 290 | 1.8 | 5.6 | 3.8 |
|
WH-6 |
3.54 | 290 | 1.8 | 5.5 | 4.0 |
|
WH-7 |
3.99 | 290 | 1.8 | 5.4 | 4.9 |
|
WH-8 |
3.87 | 290 | 1.7 | 5.7 | 4.9 |
|
WH-9 |
3.93 | 280 | 1.9 | 5.7 | 5.5 |
|
WH-10 |
3.59 | 290 | 1.8 | 6.1 | 4.0 |
|
WH-11 |
3.64 | 290 | 1.8 | 6.0 | 6.5 |
|
WH-12 |
3.04 | 280 | 1.8 | 6.6 | 23.0 |
|
WH-13 |
3.67 | 280 | 2.2 | 6.7 | 50.0 |
|
WH-14 |
3.56 | 290 | 1.8 | 6.9 | 38.0 |
|
WH-15 |
3.77 | 280 | 1.8 | 6.5 | 4.4 |
|
WH-16 |
3.92 | 280 | 1.8 | 6.4 | 2.1 |
|
WH-17 |
3.39 | 280 | 1.8 | 6.3 | 14.0 |
|
WH-18 |
2.67 | 290 | 1.8 | 6.9 | N.D. |
|
WH-19 |
3.69 | 280 | 1.8 | 6.7 | 2.2 |
|
WH-20 |
3.38 | 320 | 1.8 | 7.2 | 1.7 |
|
WH-21 |
2.68 | 270 | 1.7 | 8.7 | N.D. |
|
WH-22 |
2.85 | 280 | 1.8 | 8.2 | N.D. |
|
WH-23 |
3.30 | 300 | 1.8 | 8.0 | 5.7 |
|
All (range) |
1.88- 3.99 |
230- 300 |
1.6- 2.2 |
5.4- 8.7 |
N.D.- 50.0 |
|
Average |
3.26 | 283 | 1.8 | 6.6 | 8.0 |
|
Lake |
-- | -- | -- | -- | 0.9 |
| Criterion for heavily polluted1 |
-- | -- | -- | -- | over 6.0 |
(continued)
1Ecological critera and not
health-based.
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 5, continued. Concentrations of inorganic chemicals in the sediments of
Waukegan Harbor. Sample locations are shown in Figure 10 (Risatti et al., 1990).
| Concentration (ppm) | |||||
| Location | Cobalt | Chromium | Copper |
Iron |
Potassium (%) |
|
WH-1 |
10.0 | 9 | 120 | 4.0 | 1.0 |
|
WH-2 |
4.8 | 2 | 86 | 2.2 | 1.1 |
| WH-3 | 4.8 | 3 | 178 | 1.8 | 1.2 |
|
WH-4 |
3.1 | 1 | 57 | 1.3 | 1.2 |
|
WH-5 |
9.0 | 7 | 210 | 2.5 | 1.7 |
|
WH-6 |
6.2 | 6 | 230 | 2.4 | 1.7 |
|
WH-7 |
9.8 | 9 | 150 | 2.7 | 1.9 |
|
WH-8 |
9.4 | 8 | 120 | 2.4 | 1.7 |
|
WH-9 |
10.0 | 8 | 120 | 2.3 | 1.8 |
|
WH-10 |
7.1 | 6 | 100 | 2.1 | 1.7 |
|
WH-11 |
7.5 | 7 | 96 | 2.1 | 1.7 |
|
WH-12 |
7.5 | 1 | 76 | 1.9 | 1.4 |
|
WH-13 |
10.0 | 2 | 120 | 2.4 | 1.7 |
|
WH-14 |
9.2 | 2 | 100 | 2.2 | 1.6 |
|
WH-15 |
8.4 | 7 | 78 | 2.5 | 1.6 |
|
WH-16 |
7.6 | 6 | 86 | 2.1 | 1.8 |
|
WH-17 |
N.D. | 1 | 93 | 2.1 | 0.8 |
|
WH-18 |
N.D. | 9 | 48 | 1.6 | 0.6 |
|
WH-19 |
N.D. | 1 | 86 | 1.2 | 1.0 |
|
WH-20 |
N.D. | 1 | 72 | 1.8 | 0.9 |
|
WH-21 |
N.D. | 9 | 40 | 1.5 | 0.8 |
|
WH-22 |
N.D. | 9 | 45 | 1.5 | 0.8 |
|
WH-23 |
N.D. | 1 | 89 | 2.0 | 0.9 |
|
All (range) |
N.D.- 10.0 |
1-9 | 40- 230 |
1.3- 4.0 |
0.7- 1.9 |
|
Average |
5 | 5 | 104 | 2.2 | 1.3 |
| Lake Michigan (average) |
-- | 46.0 | 22.0 | 2.0 | -- |
| Criterion for heavily polluted1 |
-- | over 75.0 |
over 50.0 |
over 2.5 |
-- |
(continued)
1Ecological criteria and
not health-based.
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 5, continued. Concentrations of inorganic chemicals in the sediments of
Waukegan Harbor. Sample locations are shown in Figure 10 (Risatti et al., 1990).
| Concentration (ppm) | ||||
| Location | Lanthanum |
Magnesium |
Manganese | Molybdenum |
|
WH-1 |
27 | 4 | 840 | 24 |
|
WH-2 |
20 | 3 | 530 | 28 |
|
WH-3 |
21 | 4 | 460 | 18 |
|
WH-4 |
20 | 3 | 440 | 22 |
|
WH-5 |
30 | 3 | 460 | 18 |
|
WH-6 |
28 | 3 | 460 | 20 |
|
WH-7 |
32 | 4 | 470 | 17 |
|
WH-8 |
31 | 4 | 500 | 19 |
|
WH-9 |
32 | 4 | 490 | 15 |
|
WH-10 |
30 | 4 | 480 | 19 |
|
WH-11 |
30 | 4 | 510 | 18 |
|
WH-12 |
27 | 4 | 540 | 25 |
|
WH-13 |
32 | 4 | 580 | 20 |
|
WH-14 |
31 | 4 | 560 | 26 |
|
WH-15 |
32 | 4 | 610 | 18 |
|
WH-16 |
33 | 4 | 590 | 13 |
|
WH-17 |
31 | 4 | 480 | 22 |
|
WH-18 |
24 | 4 | 440 | 31 |
|
WH-19 |
32 | 4 | 550 | 17 |
|
WH-20 |
29 | 4 | 540 | 30 |
|
WH-21 |
28 | 5 | 570 | 32 |
|
WH-22 |
28 | 5 | 540 | 36 |
|
WH-23 |
31 | 5 | 580 | 24 |
|
All (range) |
20 -33 |
3-5 | 440- 840 |
13- 36 |
|
Average |
29 | 4 | 531 | 22 |
|
Lake |
-- | -- | -- | -- |
| Criterion for heavily polluted1 |
-- | -- | over 500 |
-- |
(continued)
1Ecological criteria and
not health-based.
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 5, continued. Concentrations of inorganic chemicals in the sediments of
Waukegan Harbor. Sample locations are shown in Figure 10 (Risatti et al., 1990).
| Concentration (ppm) | |||||
| Location | Sodium | Nickel | Lead |
Silicon |
Strontium |
| WH-1 | 5800 | 8 | 54 | 49 | 110 |
|
WH-2 |
3300 | 8 | 36 | 53 | 120 |
|
WH-3 |
3100 | 8 | 150 | 46 | 110 |
|
WH-4 |
3600 | 11 | 99 | 57 | 120 |
|
WH-5 |
3100 | 26 | 260 | 39 | 100 |
|
WH-6 |
3400 | 24 | 240 | 42 | 100 |
|
WH-7 |
1000 | 19 | 330 | 40 | 100 |
|
WH-8 |
7300 | 25 | 290 | 40 | 110 |
|
WH-9 |
1200 | 23 | 280 | 40 | 110 |
|
WH-10 |
1600 | 16 | 210 | 40 | 100 |
|
WH-11 |
1500 | 24 | 270 | 40 | 110 |
|
WH-12 |
2200 | 24 | 280 | 44 | 120 |
|
WH-13 |
1200 | 32 | 420 | 38 | 110 |
|
WH-14 |
2500 | 27 | 370 | 40 | 120 |
|
WH-15 |
2500 | 19 | 190 | 40 | 120 |
|
WH-16 |
2100 | 13 | 200 | 38 | 110 |
|
WH-17 |
2900 | 13 | 280 | 43 | 110 |
|
WH-18 |
3700 | 8 | 140 | 48 | 110 |
|
WH-19 |
3000 | 19 | 130 | 42 | 110 |
|
WH-20 |
3000 | 16 | 100 | 42 | 130 |
|
WH-21 |
3300 | 19 | 60 | 41 | 110 |
|
WH-22 |
2900 | 13 | 110 | 41 | 110 |
|
WH-23 |
2500 | 16 | 150 | 39 | 110 |
|
All (range) |
1000- 7300 |
8-32 | 36- 420 |
38- 53 |
100- 130 |
|
Average |
2900 | 17 | 202 | 43 | 111 |
|
Lake |
-- | 24.0 | 40.0 | -- | -- |
|
Criterion |
-- | over 50.0 |
over 60.0 |
-- | -- |
(continued)
1Ecological criteria and
not health-based.
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 5, continued. Concentrations of inorganic chemicals in the sediments of
Waukegan Harbor. Sample locations are shown in Figure 10 (Risatti et al., 1990).
| Concentration (ppm) | |||
|
Location |
Vanadium | Zinc | Titanium |
|
WH-1 |
180 | 210 | 5400 |
|
WH-2 |
83 | 130 | 2600 |
|
WH-3 |
45 | 300 | 2100 |
|
WH-4 |
42 | 81 | 1750 |
|
WH-5 |
90 | 270 | 2200 |
|
WH-6 |
85 | 260 | 2000 |
|
WH-7 |
83 | 330 | 2200 |
|
WH-8 |
82 | 280 | 2200 |
|
WH-9 |
43 | 270 | 2100 |
|
WH-10 |
83 | 210 | 2200 |
|
WH-11 |
41 | 210 | 2000 |
|
WH-12 |
83 | 200 | 2000 |
|
WH-13 |
84 | 370 | 2100 |
|
WH-14 |
73 | 290 | 2100 |
|
WH-15 |
84 | 200 | 2100 |
|
WH-16 |
73 | 200 | 2100 |
|
WH-17 |
77 | 240 | 2100 |
|
WH-18 |
63 | 110 | 1700 |
|
WH-19 |
94 | 200 | 2100 |
|
WH-20 |
52 | 160 | 1800 |
|
WH-21 |
58 | 90 | 1600 |
|
WH-22 |
52 | 98 | 1800 |
|
WH-23 |
74 | 220 | 1900 |
|
All (range) |
41- 180 |
81- 370 |
1600- 5400 |
|
Average |
75 | 214 | 2180 |
|
Lake |
-- | 97.0 | -- |
| Criterion for heavily polluted1 |
-- | over 200 |
-- |
1Ecological criteria and
not health-based.
-- = Data not available.
N.D. = Not detected.
ppm = Parts per million.
Table 6. Concentrations of organic priority pollutants in the sediments of Waukegan
Harbor. Sample locations are shown in Figure 10 (Risatti et al., 1990).
| Concentration (ppm) | ||
| Chemical | Station J | Station K |
|
Arochlor 1221 |
140 | 220.0 |
|
Arochlor 1248 |
36 | 44.0 |
|
Arochlor 1260 |
7 | 9.0 |
|
Benzo(a)anthracene |
23 | 0.4 |
|
Benzo(b)fluoranthene |
22 | N.D. |
|
Benzo(k)fluoranthene |
14 | N.D. |
|
Benzo(a)pyrene |
22 | N.D. |
|
Bis(2-ethylhexyl)phthalate |
1400 | N.D. |
|
Chrysene |
23 | 0.9 |
|
Di-m-octyl phthalate |
7 | N.D. |
|
Fluoranthrene |
64 | 1.0 |
|
Pentachlorophenol |
7 | N.D. |
|
Phenanthrene |
29 | N.D. |
|
Pyrene |
25 | 0.5 |
|
Total xylenes |
4.7 | N.D. |
N.D. = Not detected.
Table 7. Results of groundwater sampling at the New Slip (Barr Engineering Company, 1991).
| Concentration (ppb) | ||||
| Depth (feet) | Health Criteria | |||
|
Chemical |
12.5-17.5 | 23-28 | (ppb) | Source |
|
Acenaphylene |
N.D. | N.D. | -- | -- |
|
Acenaphthene |
N.D.-25 | N.D. | none | -- |
|
Anthracene |
N.D. | N.D. | 25 | RfD |
| Benzo(a)anthracene | N.D. |
N.D. |
-- | -- |
|
Benzo(b)fluoranthene |
N.D. | N.D. | -- | -- |
|
Benzo(k)fluoranthene |
N.D. | N.D. | -- | -- |
| Benzo(a)pyrene | N.D. | N.D. | -- | -- |
| Benzo(g,h,i)perylene | N.D. | N.D. | -- | -- |
| Benzoic acid | N.D. | N.D. | -- | -- |
| Bis(2-chlorodiisopropyl ether |
N.D. | N.D. | -- | -- |
| Bis(2-chloroethoxy) methane |
N.D. | N.D. | -- | -- |
| Bis(2-chloroethyl ether | N.D. | N.D. | -- | -- |
| Bis(2-ethylhexyl) phthalate |
N.D. | N.D. | -- | -- |
| 4-Bromophenyl phenyl ether |
N.D. | N.D. | -- | -- |
| Butyl alcohol | N.D. | N.D. | -- | -- |
| Butyl benzyl phthalate | N.D. | N.D. | -- | -- |
| 4-Chloroaniline | N.D. | N.D. | -- | -- |
| p-Chloro-m-cresol | N.D. | N.D. | -- | -- |
| 2-Chloronaphthene | N.D. | N.D. | -- | -- |
| 2-Chlorophenol | N.D. | N.D. | -- | -- |
| 4-Chlorophenyl phenyl ether |
N.D. | N.D. | -- | -- |
| Chrysene | N.D. | N.D. | -- | -- |
| Dibenzo(a,h)anthracene | N.D. | N.D. | -- | -- |
| Dibenzofuran | N.D. | N.D. | -- | -- |
| 1,2-Dichlorobenzene | N.D. | N.D. | -- | -- |
| 1,3-Dichlorobenzene | N.D. | N.D. | -- | -- |
| 1,4-Dichlorobenzene | N.D. | N.D. | -- | -- |
| 3,3'-Dichlorobenzidine | N.D. | N.D. | -- | -- |
| 2,4-Dichlorophenol | N.D. | N.D. | -- | -- |
| Diethyl phthalate | N.D. | N.D. | -- | -- |
| 2,4-Dimethylphenol | N.D. | N.D.-9,000 | 6 | RfD |
| Dimethyl phthalate | N.D. | N.D. | -- | -- |
| Di-N-butyl phthalate | N.D. | N.D. | -- | -- |
| Di-N-octyl phthalate | N.D. | N.D. | -- | -- |
| 4,6-dinitro-2-methyl phenol |
N.D. | N.D. | -- | -- |
(continued)
N.D. = Not detectable.
ppb = Parts per
billion.
Table 7, continued. Results of groundwater sampling at the New Slip (Barr Engineering
Company, 1991).
| Chemical | Concentration (ppb) | |||
| Depth (feet) | Health Criteria | |||
| 12.5-17.5 | 23-28 | (ppb) | Source | |
| 2,4-Dinitrophenol | N.D. | N.D. | -- | -- |
| 2,4-Dinitrotoluene | N.D. | N.D. | -- | -- |
| 2,6-Dinitrotoluene | N.D. | N.D. | -- | -- |
| Fluoranthene | N.D. | N.D. | -- | -- |
| Fluorene | N.D. | N.D. | -- | -- |
| Hexachlorobenzene | N.D. | N.D. | -- | -- |
| Hexachlorobutadiene | N.D. | N.D. | -- | -- |
| Hexachlorohexane | N.D. | N.D. | -- | -- |
| Hexachloropentadiene | N.D. | N.D. | -- | -- |
| Ideno(1,2,3-c,d)pyrene | N.D. | N.D. | -- | -- |
| Isophorone | N.D. | N.D. | -- | -- |
| 2-Methylnaphthalene | N.D.-52 | N.D. | none | -- |
| 2-Methylphenol | N.D. | 7,300-27,000 | 500 | RfD |
| 4-Methylphenol | N.D. | 44,000-100,000 | none | -- |
| Naphthalene | N.D.-1100 | N.D. | -- | -- |
| 2-Nitroaniline | N.D. | N.D. | -- | -- |
| 3-Nitroaniline | N.D. | N.D. | -- | -- |
| 4-Nitroaniline | N.D. | N.D. | -- | -- |
| Nitrobenzene | N.D. | N.D. | -- | -- |
| 2-Nitrophenol | N.D. | N.D. | -- | -- |
| 4-Nitrophenol | N.D. | N.D. | -- | -- |
| N-Nitrosodiphenylamine | N.D. | N.D. | -- | -- |
| N-Nitroso-di-N- propylamine |
N.D. | N.D. | -- | -- |
| Pentachlorophenol | N.D. | N.D. | -- | -- |
| Phenanthrene | N.D. | N.D. | -- | -- |
| Phenol | N.D. | 76,000-160,000 | 2100 | RfD |
| Pyrene | N.D. | N.D. | -- | -- |
| 1,2,3,4-Tetrachlorobenzene | N.D. | N.D. | -- | -- |
| 1,2,4-Trichlorobenzene | N.D. | N.D. | -- | -- |
| 2,4,6-Trichlorophenol | N.D. | N.D. | -- | -- |
| 2,4,5-Trichlorophenol | N.D. | N.D. | -- | -- |
N.D. = Not detectable.
ppb = Parts per
billion.
Table 8. Concentrations of organic compounds in the soil of the New Slip (Barr
Engineering Company, 1991).
| Chemical | Concentration (ppm) | ||
| Depth (feet) | |||
| 5 | 15-16 | 23.5-26 | |
| Acenaphthylene | N.D.-340 | N.D.-8.5 | N.D.-0.54 |
| Acenaphthene | N.D.-1100 | N.D.-460 | N.D.-3.3 |
| Anthracene | N.D.-880 | N.D.-210 | N.D.-0.82 |
| Beta-benzene hexachloride |
N.D.-0.15 | N.D. | N.D. |
| Benzo(a)anthracene | N.D.-770 | N.D.-0.42 | N.D.-0.96 |
| Benzo(b)fluoranthene | N.D.-770 | N.D. | N.D.-0.71 |
| Benzo(k)fluoranthene | N.D.-770 | N.D. | N.D.-0.69 |
| Benzo(g,h,i)perylene | N.D.-120 | N.D. | N.D. |
| Benzo(a)pyrene | N.D.-370 | N.D. | N.D. |
| Bis(2-ethylhexyl) phthalate |
N.D. | N.D.-0.6 | N.D.-0.43 |
| 4-Chloroaniline | N.D. | N.D. | N.D. |
| Chrysene | N.D.-800 | N.D. | N.D.-0.8 |
| Dibenzo(a,h)anthracene | N.D.-4.1 | N.D. | N.D. |
| Dibenzofuran | N.D.-960 | N.D.-360 | N.D.-2.5 |
| 2,4-Dimethylphenol | N.D. | N.D.-7.9 | N.D.-14 |
| Fluoranthene | N.D.-2900 | N.D.-680 | N.D.-4.4 |
| Fluorene | N.D.-1600 | N.D.-460 | N.D.-3.4 |
| Ideno(1,2,3-c,d) pyrene |
N.D.-130 | N.D. | N.D. |
| 2-Methylnaphthalene | N.D.-2300 | N.D.-510 | N.D.-3.3 |
| 2-Methylphenol | N.D. | N.D.-11 | N.D.-34 |
| 4-Methylphenol | N.D. | N.D.-42 | N.D.-79 |
| Naphthalene | N.D.-7600 | N.D.-1200 | N.D.-15 |
| Phenanthrene | N.D.-2900 | N.D.-1400 | N.D.-9 |
| Phenol | N.D. | N.D.-71 | 2.8-210 |
| Pyrene | N.D.-2200 | N.D.-420 | N.D.-2.5 |
N.D. = Not detected.
ppm = Parts per
million.
Table 9. Concentrations of inorganic and organic compounds in the soil of the
New Slip (Barr Engineering Company, 1991).
| Concentration (ppm) | |||||
| Depth (feet) | |||||
| Chemical Inorganic |
Boring S-39 3.0-4.5 |
Boring S-41 6.0-7.5 |
Boring S-36 8.0-9.5 |
Boring S-2 20-22 |
Boring S-41 23.5-25 |
| Arsenic | -- | -- | -- | 14 | -- |
| Barium | -- | -- | -- | 2.5 | -- |
| Cadmium | -- | -- | -- | 0.5 | -- |
| Chromium | -- | -- | -- | 2.1 | -- |
| Lead | -- | -- | -- | 2.9 | -- |
| Mercury | -- | -- | -- | N.D. | -- |
| Selenium | -- | -- | -- | N.D. | -- |
| Silver | -- | -- | -- | N.D. | -- |
| Organic | |||||
| Acenaphthene | N.D. | 840 | 9.5 | 200 | 1200 |
| Acenaphthylene | N.D. | 260 | N.D. | 65 | 440 |
| Aldrin | -- | -- | -- | N.D. | -- |
| Anthracene | N.D. | N.D. | N.D. | 120 | N.D. |
| Benzene | -- | -- | -- | 0.002 | -- |
| Benzene hexachloride, alpha |
-- | -- | -- | N.D. | -- |
| Benzene hexachloride, beta |
-- | -- | -- | 8.8 | -- |
|
Benzene hexachloride, |
-- | -- | -- | N.D. | -- |
| Benzene hexachloride, gamma (lindane) |
-- | -- | -- | 49 | -- |
| Benzidine | N.D. | N.D. | N.D. | -- | N.D. |
| Benzo(a)anthracene | N.D. | 610 | N.D. | 140 | 700 |
| Benzo(a)pyrene | N.D. | N.D. | N.D. | 760 | N.D. |
| Benzo(b) fluoranthene |
N.D. | 110 | N.D. | 85 | 110 |
| Benzo(g,h,i) perylene |
N.D. | N.D. | N.D. | 23 | N.D. |
| Benzyl alcohol | -- | -- | -- | N.D. | -- |
| Benzo(k)fluoranthene | N.D. | N.D. | N.D. | 74 | N.D. |
| Benzyl butyl phthalate |
N.D. | N.D. | N.D. | N.D. | N.D. |
| Bis(2)chloroethoxy methane |
N.D. | N.D. | N.D. | N.D. | N.D. |
(continued)
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 9, continued. Concentrations of inorganic and organic compounds in the
soil of the New Slip (Barr Engineering Company, 1991).
| Concentration (ppm) | |||||
| Depth (feet) | |||||
| Chemical Organic |
Boring S-39 3.0-4.5 |
Boring S-41 6.0-7.5 |
Boring S-36 8.0-9.5 |
Boring S-2 20-22 |
Boring S-41 23.5-25 |
| Bis(2-chloroethyl) ether |
N.D. | N.D. | N.D. | N.D. | N.D. |
| Bis(2-chloroisopropyl) ether |
N.D. | N.D. | N.D. | N.D. | N.D. |
| Bis(2-ethylhexyl) phthalate |
N.D. | 97 | N.D. | N.D. | 86 |
| Bromoform | -- | -- | -- | N.D. | -- |
| 4-Bromophenyl ether |
N.D. | 5.5 | N.D. | -- | N.D. |
| Carbon tetrachloride | -- | -- | -- | N.D. | -- |
| Chlordane, alpha | -- | -- | -- | N.D. | -- |
| Chlordane, gamma | -- | -- | -- | N.D. | -- |
| 4-Chloroaniline | -- | -- | -- | N.D. | -- |
| Chlorobenzene | -- | -- | -- | N.D. | -- |
| Chlorodibromomethane | -- | -- | -- | N.D. | -- |
| Chloroethane | -- | -- | -- | N.D. | -- |
| 2-Chloroethylvinyl ether |
-- | -- | -- | N.D. | -- |
| Chloroform | -- | -- | -- | N.D. | -- |
| 4-Chloro-3- methylphenol |
-- | -- | -- | N.D. | -- |
| 2-Chloronaphthalene | N.D. | N.D. | N.D. | -- | N.D. |
| 4-Chlorophenol | -- | -- | -- | N.D. | -- |
| 4-Chlorophenyl phenyl ether |
N.D. | 280 | N.D. | N.D. | 430 |
| Chrysene | N.D. | 520 | N.D. | 110 | 540 |
| 4,4'-DDD (p,p') | -- | -- | -- | N.D. | -- |
| 4,4'-DDE (p,p') | -- | -- | -- | N.D. | -- |
| 4,4'-DDT (p,p') | -- | -- | -- | N.D. | -- |
| Dibenzo(a,h) anthracene |
N.D. | N.D. | N.D. | 5.7 | N.D. |
| Dibenzofuran | -- | -- | -- | 190 | -- |
| 1,2-Dichlorobenzene | N.D. | N.D. | N.D. | N.D. | N.D. |
| 1,3-Dichlorobenzene | N.D. | N.D. | N.D. | N.D. | N.D. |
| 1,4-Dichlorobenzene | N.D. | 34 | N.D. | N.D. | N.D. |
| 3,3'-Dichlorobenzidine | N.D. | N.D. | N.D. | N.D. | N.D. |
| Dichlorobromomethane | -- | -- | -- | N.D. | -- |
(continued)
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 9, continued. Concentrations of inorganic and organic compounds in the
soil of the New Slip (Barr Engineering Company, 1991).
| Concentration (ppm) | |||||
| Depth (feet) | |||||
| Chemical
Organic |
Boring S-39 3.0-4.5 |
Boring S-41 6.0-7.5 |
Boring S-36 8.0-9.5 |
Boring S-2 20-22 |
Boring S-41 23.5-25 |
| Dichlorodifluoromethane | -- | -- | -- | N.D. | -- |
| 1,1-Dichloroethane |
-- |
-- | -- | N.D. | -- |
|
1,2-Dichloroethane |
-- | -- | -- | N.D. | -- |
|
1,1-Dichloroethylene |
-- | -- | -- | N.D. | -- |
|
1,2-trans- |
-- | -- | -- | N.D. | -- |
|
1,2-Dichloropropane |
-- | -- | -- | N.D. | -- |
| Dichloropropylene | -- | -- | -- | N.D. | -- |
|
Dieldrin |
-- | -- | -- | N.D. | -- |
|
Diethylphthalate |
N.D. | 55 | N.D. | N.D. | 100 |
|
2,4-Dimethylphenol |
-- | -- | -- | 6.9 | -- |
|
Dimethylphthalate |
N.D. | 95 | N.D. | N.D. | 120 |
|
2,4-Dinitro-2- |
-- | -- | -- | N.D. | -- |
|
2,4-Dinitrophenol |
-- | -- | -- | N.D. | -- |
|
2,4-Dinitrotoluene |
N.D. | N.D. | N.D. | 2.5 | N.D. |
|
2,6-Dinitrotoluene |
N.D. | N.D. | N.D. | N.D. | 200 |
|
Di-N-butylphthalate |
N.D. | 180 | N.D. | N.D. | 230 |
|
Di-N-octylphthalate |
N.D. | 380 | N.D. | N.D. | 400 |
|
1,2-Diphenylhydrazine |
N.D. | N.D. | N.D. | -- | N.D. |
|
Endosulfan I |
-- | -- | -- | N.D. | -- |
|
Endosulfan II |
-- | -- | -- | N.D. | -- |
|
Endosulfan sulfate |
-- | -- | -- | N.D. | -- |
|
Endrin |
-- | -- | -- | N.D. | -- |
|
Endrin aldehyde |
-- | -- | -- | N.D. | -- |
|
Endrin Keytone |
-- | -- | -- | N.D. | -- |
|
Ethylbenzene |
-- | -- | -- | 0.003 | -- |
|
Fluoranthene |
N.D. | 1900 | N.D. | 390 | 2200 |
|
Fluorene |
N.D. | 1200 | N.D. | 290 | 1700 |
|
Heptachlor |
-- | -- | -- | N.D. | -- |
|
Heptachlor epoxide |
-- | -- | -- | N.D. | -- |
|
Hexachlorobenzene |
N.D. | N.D. | N.D. | N.D. | N.D. |
|
Hexachloro- |
N.D. | 5700 | N.D. | N.D. | N.D. |
|
Hexachloroethane |
N.D. | N.D. | N.D. | N.D. | N.D. |
| Indeno(1,2,3,c,d) pyrene |
N.D. | N.D. | N.D. | 23 | N.D. |
(continued)
-- = Data not available.
N.D. = Not detected.
ppm = Parts per million.
Table 9, continued. Concentrations of inorganic and organic
compounds in the soil of the New Slip (Barr Engineering Company, 1991).
| Concentration (ppm) Depth (feet) |
|||||
|
Chemical |
Boring S-39 3.0-4.5 |
Boring S-41 6.0-7.5 |
Boring S-36 8.0-9.5 |
Boring S-2 20-22 |
Boring S-41 23.5-25 |
|
Isophorone |
N.D. | N.D. | N.D. | N.D. | N.D. |
|
Methoxychlor |
-- | -- | -- | 51 | -- |
|
Methyl bromide |
-- | -- | -- | N.D. | -- |
|
Methyl chloride |
-- | -- | -- | N.D. | -- |
|
2-Methylnaphthalene |
-- | -- | -- | 280 | -- |
|
2-Methylphenol |
-- | -- | -- | 16 | -- |
|
4-Methylphenol |
-- |
-- | -- | 61 | -- |
|
Methylene chloride |
-- | -- | -- | N.D. | -- |
|
Naphthalene |
N.D. | 8200 | N.D. | over 1000 |
12000 |
|
2-Nitroaniline |
-- | -- | -- | N.D. | -- |
|
3-Nitroaniline |
-- | -- | -- | N.D. | -- |
|
4-Nitroaniline |
-- | -- | -- | N.D. | -- |
|
Nitrobenzene |
N.D. | N.D. | N.D. | N.D. | N.D. |
|
2-Nitrophenol |
-- | -- | -- | N.D. | -- |
|
4-Nitrophenol |
-- | -- | -- | N.D. | -- |
|
N-Nitrosodiphenylamine |
N.D. | 200 | N.D. | N.D. | 270 |
|
N-Nitroso-Di-N- |
N.D. | N.D. | N.D. | N.D. | N.D. |
|
N-Nitrosodimethylamine |
N.D. | N.D. | N.D. | -- | N.D. |
|
Pentachlorophenol |
-- | -- | -- | N.D. | -- |
|
Phenanthrene |
N.D. | 5300 | N.D. | 710 | 6400 |
|
Phenol |
-- | -- | -- | 73 | -- |
|
Pyrene |
N.D. | 1500 | N.D. | 430 | 1700 |
|
1,1,2,2- |
-- | -- | -- | N.D. | -- |
|
Tetrachloroethylene |
-- | -- | -- | N.D. | -- |
|
Toluene |
-- | -- | -- | 0.008 | -- |
|
Toxaphene |
-- | -- | -- | N.D. | -- |
|
1,2,4-Trichlorobenzene |
N.D. | N.D. | N.D. | N.D. | N.D. |
|
1,1,1-Trichloroethane |
-- | -- | -- | N.D. | -- |
|
1,1,2-Trichloroethane |
-- | -- | -- | N.D. | -- |
|
Trichloroethylene |
-- | -- | -- | N.D. | -- |
|
Trichlorofluoromethane |
-- | -- | -- | N.D. | -- |
|
2,4,5-Trichlorophenol |
-- | -- | -- | N.D. | -- |
|
2,4,6-Trichlorophenol |
-- | -- | -- | N.D. | -- |
|
Vinyl chloride |
-- | -- | -- | 0.055 | -- |
-- = Data not available.
N.D. = Not detected.
ppm = Parts
per million.
Table 10. Compounds emitted by the OMC facility in reportable quantities (TRI,
1991).
| Compound |
Emitted |
Pounds Per Year | ||
|
1987 |
1988 | 1989 | ||
|
Aluminum oxide |
air | 250 | 250 | -- |
|
Aluminum (fumes or |
air | 5800 | 3850 | 3870 |
|
1,1,1-Trichloroethane |
air | 5700 | 1546 | 32,570 |
|
Trichloroethane |
air | 356,000 | 143,340 | 103,435 |
|
water |
87 | 21 | 116 | |
-- = Data not available.
Table 11. Concentrations of PCBs in the filets of Lake Michigan Fish, 1989 (Flentge, 1991).
| PCB Concentration (ppm) | |||||
| Area | Brown Trout |
Rainbow Trout |
Lake Trout |
Alewife | Coho Salmon |
|
"Harbor areas" |
0.92- 2.5 |
0.44- 1.6 |
-- | -- | -- |
|
S. Waukegan |
-- | 0.13 | -- | -- | -- |
|
Lake Michigan off |
-- | -- | 0.66- 3.4 |
-- | -- |
| S. Waukegan1 + Great Lakes Harbors |
-- | -- | -- | -- | 0.39- 0.66 |
|
S. Waukegan1 + |
-- | -- | -- | -- | -- |
|
Lake Michigan off |
-- | -- | -- | 0.52 | -- |
|
S. Waukegan1 + |
-- | -- | -- | -- | 0.78 |
|
Group |
A | A | F | C | A |
|
Health Criterion |
0.02 | 0.02 | 0.02 | 0.02 | 0.02 |
-- = Data not available.
ppm = parts per million
1New
harbor.
Table 12. Off-site chemicals emitted into the air in reportable quantities,
Waukegan zip code 60085, 1987-9 (TRI, 1991).
| Chemical | Number of Sources |
Pounds Per Year | ||
|
1987 |
1988 | 1989 | ||
| Acetone | 1 | 114,898 | 32,690 | 11,360 |
|
Ammonia |
1 | -- | -- | 750 |
|
Butyl acrylate |
1 | 500 | 1500 | -- |
|
N-Butyl alcohol |
1 | 7800 | 7600 | 6300 |
|
Chromium compounds |
1 | -- | -- | 500 |
|
Cresols (mixed isomers) |
1 | -- | 500 | 1000 |
|
1,2-Dichloroethane |
1 | 40,453 | 3350 | 11,965 |
|
Dimethyl phthalate |
1 | -- | 250 | -- |
|
Ethyl acrylate |
1 | 500 | 500 | -- |
|
Formaldehyde |
1 | -- | 500 | -- |
|
Freon-113 |
1 | -- | 87,000 | 58,800 |
|
Glycol ethers |
2 | 43,700 | 24,700 | 20,500 |
|
Hydrochloric acid |
3 | -- | 500 | 1000 |
|
Hydrogen fluoride |
1 | 500 | 500 | 500 |
|
4,4'-Isopropylidenediphenol |
1 | 500 | 3900 | 500 |
|
Methyl alcohol |
2 | 822,988 | 306,833 | 46,984 |
|
Methyl ethyl keytone |
1 | 31,200 | 9000 | 2500 |
|
Methyl isobutyl keytone |
1 | 6600 | -- | 5000 |
|
Methyl methacrylate |
1 | 500 | 500 | -- |
|
Methylene bis |
1 | -- | -- | 500 |
|
Methylene chloride |
2 | 15,100 | 233,760 | 91,446 |
|
Nitric acid |
1 | 500 | 500 | 500 |
|
Phenol |
1 | 500 | 3800 | 3700 |
|
Phosphoric acid |
1 | 500 | 500 | 500 |
|
Phthalic anhydride |
1 | -- | -- | 1000 |
|
Sodium hydroxide |
3 | 505 | 755 | -- |
|
Styrene |
1 | 500 | -- | -- |
|
Sulfuric acid |
3 | 500 | 750 | 1000 |
|
Terephthalic acid |
1 | -- | 250 | 1000 |
|
Toluene |
3 | 8200 | 14,320 | 6600 |
|
1,1,1-Trichloroethane |
3 | -- | 30,500 | 30,250 |
|
Xylenes |
1 | 44,000 | 22,500 | 9000 |
|
Zinc compounds |
2 | 500 | 500 | 500 |
-- = Data not available.
Table 13. Chemicals of concern, contaminated media, exposure pathways1,
and possible receptors for the various OMC/Waukegan Harbor areas.
| Chemical of Concern |
Contaminated Media |
Exposure Pathways |
Possible Receptors |
Time |
|
1. Waukegan Harbor |
||||
|
PCB's |
Air | Inhalation | Boaters Fisherpersons Children On-site workers |
Past Present Future |
|
(Ingestion) |
Boaters Fisherpersons Children On-site workers |
Past Present Future |
||
|
Fish |
Ingestion | Fisherpersons and their families |
Past Present Future |
|
|
Sediments |
Dermal contact | Remediation workers Anglers |
Past Present Future |
|
|
|
Ingestion |
Remediation workers Anglers |
Past Present Future |
|
|
Surface Water |
Dermal contact | Boaters Fisherpersons Children |
Past Present Future |
|
|
Ingestion |
Boaters Fisherpersons Children |
Past Present Future |
||
|
2. North Ditch |
||||
|
PCB's |
(Air) (possible) |
(Inhalation) | Beach-goers Trespassers On-site workers |
Past Present Future |
|
(Ingestion) |
Beach-goers Trespassers On-site workers |
Past Present Future |
||
|
(Groundwater) |
(Dermal (contact) |
Remediation workers |
Future | |
|
Soil |
Dermal contact | Trespassers On-site workers Beach-goers |
Past Present Future |
|
|
Ingestion |
Trespassers On-site workers Beach-goers |
Past Present Future |
(continued)
1Potential pathways in parentheses.
Table 13, continued. Chemicals of concern, contaminated media, exposure pathways1,
and possible receptors for the various OMC/Waukegan Harbor areas.
| Chemical of Concern |
Contaminated Media |
Exposure Pathways |
Possible Receptors |
Time |
|
2. North Ditch |
||||
|
PCB's |
Surface Water | Dermal contact | Beach-goers On-site workers |
Past Present Future |
|
Ingestion |
Beach-goers On-site workers |
Past Present Future |
||
|
3. Parking Lot Area |
||||
|
PCB's |
(Air) (possible) |
(Inhalation) | Trespassers On-site workers |
Past Present Future |
|
(Groundwater) |
(Dermal contact) |
Remediation workers |
Future | |
|
Soil |
Ingestion (primarily children) |
Trespassers On-site workers |
(Past) (Present) Future |
|
|
Dermal |
Trespassers On-site workers |
(Past) (Present) Future |
||
|
(Vegetation) |
(Dermal contact) |
On-site workers Trespassers |
Past Present Future |
|
|
4. New Slip |
||||
|
Phenol |
(Air) (possible) |
(Inhalation) | On-site workers Trespassers |
Past Present Future |
|
(Ingestion) |
On-site workers Trespassers |
Past Present Future |
||
|
Groundwater |
Dermal contact | Remediation workers |
Future | |
|
Soil |
Ingestion (primarily children) |
Trespassers On-site workers |
(Past) (Present) Future |
|
|
Dermal |
Trespassers On-site workers |
(Past) (Present) Future |
(continued)
1Potential pathways in parentheses.
Table 13, continued. Chemicals of concern, contaminated media, exposure pathways1,
and possible receptors for the various OMC/Waukegan Harbor areas.
| Chemical of Concern |
Contaminated Media |
Exposure Pathways |
Possible Receptors |
Time |
|
4. New Slip |
||||
|
PAH's |
(Air) (possible) |
(Inhalation) | On-site workers Trespassers |
Past Present Future |
|
(Ingestion) |
On-site workers Trespassers |
Past Present Future |
||
|
Groundwater |
Dermal contact |
Remediation workers |
Future | |
|
Soil |
Ingestion (primarily children) |
Trespassers On-site workers |
Past Present Future |
|
|
Dermal |
Trespassers On-site workers |
(Past) (Present) Future |
||
|
5. Off-site Contamination |
||||
| PCB's | (Air) (possible) |
(Inhalation) | Boaters Beach-goers Fisherpersons |
Past Present Future |
| (Ingestion) (possible for aerosols) |
Boaters Beach-goers Fisherpersons |
Past Present Future |
||
|
Fish |
Ingestion | Fisherpersons and their families |
Past Present Future |
|
|
(Surface |
(Ingestion) | Boaters Beach-goers (including swimmers) Fisherpersons |
Past Present Future |
|
|
(Dermal |
Boaters Beach-goers (including swimmers) Fisherpersons |
Past Present Future |
||
(continued)
1Potential pathways are in parentheses.
Table 13, continued. Chemicals of concern, contaminated media, exposure pathways1,
and possible receptors for the various OMC/Waukegan Harbor areas.
| Chemical of Concern |
Contaminated Media |
Exposure Pathways |
Possible Receptors |
Time |
|
      b. Waukegan |
||||
|
PCB's |
(Air) (possible) |
(Inhalation) | People in Waukegan |
Past Present Future |
|
(Ingestion) |
People in Waukegan |
Past Present Future |
||
|
(Surface |
(Dermal contact) |
People in Waukegan |
Past Present Future |
|
|
(Inhalation) |
People in Waukegan |
Past Present Future |
||
|
(Ingestion) |
People in Waukegan |
Past Present Future |
||
|
      c. North Ditch |
||||
| (Air) | (Inhalation) | Beach-goers Maintenance workers Remediation workers |
Past Present Future |
|
|
Sediments |
Dermal contact | Beach-goers Maintenance workers Remediation workers |
Past Present Future |
|
|
Ingestion |
Beach-goers Maintenance workers Remediation workers |
Past Present Future |
||
|
Soil |
Dermal contact | Beach-goers Maintenance workers Remediation workers |
Past Present Future |
(continued)
1Potential pathways are in parentheses.
Table 13, continued. Chemicals of concern, contaminated media, exposure pathways1,
and possible receptors for the various OMC/Waukegan Harbor areas.
| Chemical of Concern |
Contaminated Media |
Exposure Pathways |
Possible Receptors |
Time |
|
      c. North Ditch |
||||
|
PCB's |
Soil | Ingestion | Beach-goers Maintenance workers Remediation workers |
Past Present Future |
|
Surface |
Dermal contact | Beach-goers Maintenance workers Remediation workers |
Past Present Future |
|
|
Ingestion |
Beach-goers | Past Present Future |
1Potential pathways are in parentheses.
Table 14. Bioconcentration and depuration studies of Group B fish exposed to
the water or suspended sediment of Waukegan Harbor or the North Ditch (Harris,
1982).
| Fish PCB Concentration (ppm) |
||||
|
Study conditions |
Species | Day | Control | Experimental |
|
Waukegan Harbor Water |
||||
|
7 Day laboratory |
Yellow| perch |
7 | 0.48 | 2.04 |
| 28 Day exposure to water in Waukegan Harbor Slip 3, October- November, 1978. |
Yellow perch |
0 28 |
-- -- |
0.156 29.9 |
| Bluegill | 0 28 |
-- -- |
0.207 19.7 |
|
|
30 Day exposure to water |
Yellow perch |
0 30 114 |
-- 0.26 0.46 |
0.14 12.1 8.6 |
| Bluegill | 0 30 114 |
-- 0.35 0.64 |
0.11 21.6 8.3 |
|
|
North Ditch Water |
||||
|
28 Day laboratory |
Flathead minnow (adults) |
28 | 1.82 | 419 |
|
Flathead |
28 | 0.79 | 183 | |
|
Health Criterion |
0.02 | .02 | ||
-- = Data not available.
Table 15. Chemicals monitored in fish from Lake Michigan by the State of Illinois
(Modified from IEPA, 1992).
| Chemical | Status | USDA Standard (ppm) |
|
Aldrin |
Pesticide, most uses cancelled since 1975 |
0.3 |
|
Benzene hexachloride |
Pesticide, all uses cancelled in 1978 |
0.5 |
|
Chlordane |
Pesticide, voluntarily withdrawn in 1989 by the manufacturer |
0.3 |
|
DDT & similar chemicals |
Pesticide, most uses cancelled since 1971 |
5.0 |
|
Dieldrin |
Pesticide, most uses cancelled since 1975 |
0.3 |
|
Endrin |
Pesticide, uses are restricted |
0.3 |
|
Heptachlor |
Pesticide, most uses cancelled in 1983 |
0.3 |
|
Heptachlor epoxide |
One degradation product of heptachlor |
0.3 |
|
Hexachlorobenzene |
Pesticide, still in use | -- |
|
Lindane |
Pesticide, uses are restricted |
-- |
|
Methoxychlor |
Pesticide, still in use | -- |
|
Methyl mercury |
Heavy metal | 1.0 |
|
Mirex |
Pesticide and component of a fire retardant, most uses cancelled in 1977 |
0.1 |
|
PCB's |
Industrial lubricant, hydraulic fluid, cooling fluid, electrical insulator, production halted in 1970. |
2.0 |
|
Toxaphene |
Pesticide, most uses cancelled in 1982 |
5.0 |
-- = Not available.
Table 16. Fish advisories for sport fish from Lake Michigan (IEPA, 1992). Fish
not listed are not under any advisory.
| Qualitative Level of Contamination | ||
|
Group 1-Low |
Group 2-Moderate | Group 3-High |
|
Lake trout |
Lake trout 20 to 23 inches |
Lake trout over 23 inches |
|
Coho salmon |
Coho salmon over 26 inches |
Chinook salmon over 32 inches |
|
Chinook salmon |
Chinook salmon 21 to 32 inches |
Brown trout over 23 inches |
|
Brook trout |
Brown trout up to 23 inches |
Carp Catfish |
|
Rainbow trout |
||
|
Pink salmon |
||
|
Smelt |
||
|
Perch |
||
Group 1 = Lowest level of contaminants.
Group 2 = Moderate levels of contamination; children,
pregnant women, women who may become pregnant, and nursing
mothers should not eat Group 2 fish; all others should
limit their consumption of these fish to one meal per
week.
Group 3 = High levels of contamination; no one should
eat Group 3 fish.
(3) possible dioxin formation during
remediation by the high temperature extraction process proposed for removing
PCBs from the most contaminated sediments and soils, (4) the lack of incentives
to more efficiently dispose of the wastes in the future, (5) the off-site transportation
of wastes, and (6) Slip 2 (nature of concern unknown).