PUBLIC HEALTH ASSESSMENT
SANGAMO ELECTRIC DUMP/CRAB ORCHARD NATIONAL WILDLIFE REFUGE
(a/k/a CRAB ORCHARD NATIONAL WILDLIFE REFUGE)
CARTERVILLE, WILLIAMSON COUNTY, ILLINOIS
Table 1. Site Descriptions - Crab Orchard Refuge
| SITE NO. | ||
| 17 | Job Corps Landfill | |
| 28 | Water Tower Landfill | |
| 32 | Area 9 Landfill | |
| 33 | Area 9 Building Complex | |
| 15 | Area 7 Plating Pond | |
| 22 | Old Refuge Shop Drainage Pool | |
| 29 | Fire Station Landfill | |
| COC-3 | Crab Orchard Cemetery -wooded area and wastepile | |
| COC-6 | Crab Orchard Cemetery -fenced, triangular shaped area pitted with several depressions | |
| COC-9 | Crab Orchard Cemetery -wooded area with several pits surrounded by cropland | |
| COP-1 | Previous Ordnance Plant area -man-made impoundment | |
| COP-2 | Previous Ordnance Plant area -old lagoon area | |
| COP-4 | Previous Ordnance Plant area -former land mine disposal area; old railroad bed | |
| 10 | Drainage Channel North of Refuge Waterworks Facility | |
| 14 | Area 14 Solvent Storage Drainage Channel | |
| 16 | Area 7 Industrial Site | |
| 22A | Post Treating Facility at the Old Refuge Shop Site | |
| 36 | Refuge Waste-Water Treatment Plant |
Table 2. Maximum Concentrations of Subsurface Soil Contaminants
- Crab Orchard Refuge (mg/kg)
| CONTAMINANT
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| 171 | 281 | 321 | 331 | 221 | 291 | 142 | 162 | 22A2 | 362 | COC33 | COP43 |
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| PCBs | 50,000 | 8,900 | 88,000 | 120,000 | ND | 2.57 | ND | 0.16 | 0.14 | 0.25 | ND | ND |
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CREG |
| Lead | 17,414 | 4300 | 20,500 | 66 | 410 | 85,900 | 150 | ND | 26 | 20.7 | 4,250 | 421 |
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IDPH |
| Cadmium | 57 | 8 | 18 | ND | 136 | 10 | ND | 4.2 | ND | 0.02 | 9.98 | 5.10 | 40(child)/500(adult) | EMEG |
| Arsenic | 28 | 90 | 12 | 84 | ND | 60 | ND | ND | ND | 15.1 | 9.86 | ND |
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CREG |
| Manganese | 1650 | 1270 | 461 | 232 | ND | 1030 | ND | ND | 1600 | ND | 4030 | ND |
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RMEG |
| Antimony | 300 | ND | 61 | 3.6 | ND | ND | ND | ND | ND | ND | 596 | ND |
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RMEG |
| Dioxin/Furan (TEFs) | ND | ND | 0.006 | 0.022 | ND | ND | ND | ND | 0.0004 | 0.00002 | ND | ND |
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ATSDR |
| PAHs (TEFs) | ND | ND | 0.03 | ND | ND | ND | ND | ND | 0.53 | 0.0003 | ND | ND |
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CREG |
| 2-Chloronaphthalene | ND | ND | ND | 6820 | ND | ND | ND | ND | ND | ND | ND | ND |
NONE
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NONE |
Reference: 1-1(1988); 2-17(1995); 3-18(1994);
4-21(July 1995)
ND = Not Detected
mg/kg = milligrams of contaminant per kilogram of soil
Table 3. Maximum Concentrations of Explosives in Subsurface
Soil Samples - Crab Orchard Refuge (mg/kg)
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| 2,4,6-trinitrotoluene (TNT) |
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| 1,3,5-trinitrobenzene (TNB) |
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| 2,Amino-4,6-DNT |
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| HMX |
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| RDX |
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mg/kg = milligrams per kilogram
Reference - 18 (1994)
ND = Not Detected
Table 4. Maximum Concentrations of Contaminants selected
for evaluation Identified in Sediments - Crab Orchard Refuge (mg/kg)
| CONTAMINANT |
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| PCBs |
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| Lead |
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| Cadmium |
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| Chromium |
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| Arsenic |
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| Cyanide |
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| Manganese |
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| Antimony |
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| Dioxin/Furan (TEFs) |
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.000022 |
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| PAHs (TEFs) |
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| 2,4,6-TNT |
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CREG |
mg/kg = milligram per kilogram
- = not analyzed
Reference: 1=1(1988); 2=20(1994);
3=17(1995); 4=18(1994); 5=21(July 1995)
ND = Not Detected; (-) = Not Reported; COL = Crab Orchard
Lake
* = Comparison Value for Chromium VI
Table 5. Maximum Concentrations of Contaminants Selected
for Evaluation Identified in Groundwater Crab Orchard Refuge (µg/L)
| CONTAMINANT |
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COC-33 | COP-43 |
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Source | |
| PCBs | 11.0 | ND | .044 | .114 | .01 | ND | ND | ND | .0005 |
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| Lead | 55 | 76 | 12 | 11 | 22 | 6.6 | 8.2 | ND | ND |
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| Cadmium | ND | 7.4 | ND | ND | ND | 25 | ND | ND | ND |
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| Chromium | 139 | 165 | 92 | 113 | 15 | 21 | 8.2 | ND | ND |
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| Arsenic | 4.7 | 30 | 5.9 | 10 | 7.6 | ND | 8.9 | ND | ND |
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| Manganese | ND | 2,780 | ND | ND | ND | ND | 1,790 | ND | ND |
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19,300 |
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| Antimony | ND | ND | ND | ND | ND | ND | ND | 71.1 | ND |
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| Dioxin/Furan (TEFs) | ND | ND | ND | ND | ND | ND | ND | ND | 0.006 |
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| PCP | 19 | ND | ND | ND | ND | ND | ND | ND | ND |
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| Ethylbenzene | ND | ND | ND | ND | ND | ND | ND | 3500 | ND |
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| 1,2-Dichloroethene | ND | ND | ND | 404 | ND | ND | ND | ND | ND |
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| Trichloroethene | ND | ND | ND | 906 | ND | ND | ND | ND | ND |
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| Nitrobenzene | 11.4 | ND | ND | ND | ND | ND | ND | ND | ND |
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| 1,3,5-TNB | ND | ND | ND | ND | ND | ND | ND | ND | ND |
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| 2,4,6-TNT | ND | ND | ND | ND | ND | ND | ND | ND | ND |
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| 2-Amino-4-6-DNT | ND | ND | ND | ND | ND | ND | ND | ND | ND |
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| RDX | ND | ND | ND | ND | ND | ND | ND | ND | ND |
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µg/L = micrograms per liter
Reference: 1=1(1988); 2=17(1995);
3=18(1994); 4=21(July 1995). ND = Not Detected. * = Comparison
Value for Chromium VI.
Table 6. Maximum Concentrations of Contaminants Selected
for Evaluation Identified in Surface Water - Crab Orchard Refuge (µg/L)
| CONTAMINANT |
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| COL1 | 171 | 102 | 142 | 362 | COP-13 | COC-33 | COC-93 |
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| PCBs | 28 | 0.06 | ND | ND | 0.31 |
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| Cadmium | 3.4 | ND | ND | ND | 14.4 |
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| Arsenic | 3.4 | ND | ND | ND | 6.2 |
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| Manganese | 280 | 20 | 287 | 461 | 673 |
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50(child) |
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| Trichloroethene | ND | ND | 46 | ND | ND |
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| RDX | ND | ND | ND | ND | ND |
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µg/L = micrograms per liter
Reference: 1=1(1988); 2=17(1995);
3=18(1994); 4=21(July 1995)
ND = Not Detected; COL = Crab Orchard Lake
Table 7. Airborne Concentrations of PCBs and Metals Measured
at Selected Sites - Crab Orchard Refuge (µg/me)
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| Contaminant |
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| Lead | .0064 | .0021 | .004 | .0018 | .015 | .0019 | .0046 | .0013 |
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| Cadmium | .0031 | .0033 | ND | ND | ND | ND | ND | ND |
0.0006
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| Chromium | .0005 | .0007 | .0004 | .0004 | ND | .0006 | ND | .0005 |
0.00008
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| Arsenic | .0007 | .0004 | .0013 | .0003 | .0008 | ND | .0004 | ND |
0.0002
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| PCBs |
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NA |
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NONE |
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µg/ me = micrograms per cubic meter
Reference: 12
ND = Not Detected (Below Detection Level)
NA = Not analyzed
Table 8. Range of Contaminant Concentrations Detected at
Perimeter Ambient Air Monitoring Stations - Crab Orchard Refuge (µg/me)
| CONTAMINANT |
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| Lead |
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| Cadmium |
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| PCBs |
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| Dioxins/Furans |
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µg/me = micrograms per cubic meter
Reference: 34
ND = Not Detected (Below Detection Level); NA = Not Analyzed
For
Table 9. Fish Monitoring Data Summary - Crab Orchard Lake
| Species | Date Collected | Yearly Avg. PCB Concentration (Fillet) mg/kg (ppm) | Number of Samples | Average Sample Weight (lb) |
| WEST OF RT. 148 | ||||
| Catfish |
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2.00
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0.44
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0.45
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| Carp |
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0.91
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<0.05
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| Large Mouth Bass |
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| Bullhead |
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| Bluegill Sunfish |
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| EAST OF RT. 148 | ||||
| Catfish |
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| Carp |
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| Large Mouth Bass |
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| Bullhead |
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| Bluegill Sunfish |
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| Crappie |
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Reference: Illinois Interagency Program by IDNR, IEPA & IDPH in (1).
Table 10. Completed and Potential Exposure Pathways
| Completed Exposure Pathway | |||||||||
| Pathway Name: | Source | Medium | Exposure Point | Exposure Route | Receptor Population | Time of Exposure | Exposure Activities | Estimated Number Exposed | Chemicals (identify by name or reference to tables in document) |
| Consumption of PCB-Contaminated Fish | Crab Orchard Refuge Site 9--Landfill | Fish | Meal | Ingestion | Individuals eating contaminated fish | Past | Eating fish caught in Crab Orchard Lake | About 300 people | PCBs |
| Potential Exposure Pathways | |||||||||
| Contaminated Surface Soil | Site | Surface Soil | Site Soils | Ingestion Dermal Contact Inhalation |
Refuge Employees, Site Workers Hunters/Hikers, Site Trespassers | Past Present |
Inhalation of contaminated dusts; skin contact with contaminated soils; incidential ingestion by smoking/eating | N/A | PCBs, Lead, Explosives |
| Surface Water/
Sediment |
Site | Surface Water/
Sediment |
Crab Orchard Lake & Drainage Areas | Ingestion Dermal Contact Inhalation |
Refuge Recreational Users, Refuge Employees, Industrial Workers, Marion Penitentiary | Past Present Future |
Ingestion or inhalation by past Crab Orchard water users; dermal exposure/incidential ingestion by swimmers/boaters | N/A | PCBs |
| Private Well | Site | Groundwater | Residences tap | Ingestion Inhalation Dermal Contact |
Occupants utilizing groundwater from a private well | Future | Ingestion; Inhalation/Dermal Contact from showering/bathing | N/A | PCBs, VOCs |
| Ambient Air | Site | Air | On-Site; Downwind of Incinerator | Inhalation | Refuge Employees, Site Workers, Hunters/Hikers, Site Trespassers, Nearby Residents | Past Present Future |
Working near contaminated sites, Living near Refuge Downwind of Incinerator | N/A | PCBs, Lead, Cadmium, Dioxin |

Figure 3. Approximate Sampling Locations

Figure 4. Cemetery and Plant Sites

Figure 6. Approximate Locations of Refuge Area Wells

Figure 7. Fish Sampling Locations

Figure 8. Air Monitoring Stations