PUBLIC HEALTH ASSESSMENT
EASTERN SURPLUS COMPANY SITE
MEDDYBEMPS, WASHINGTON COUNTY, MAINE

Figure 1. Eastern Surplus Vicinity Map

Figure 2. Eastern Surplus Site Layout

Figure 3. Eastern Surplus Demographics Information

Figure 4. Private Well Sample Locations

Figure 5. Monitoring Well Sample Locations

Figure 6. Surface Soil Sample Locations

Figure 7. On-site Surface Water and Sediment Sample Locations

Figure 8. Off-site Surface Water and Sediment Sample Locations
| Site area | ZIP code 04567 | Washington County | ||||
|---|---|---|---|---|---|---|
| Total population | 24* | - | 62* | - | 35,308 | -- |
| White | 24 | 100% | 62 | 100% | 33,704 | 95.5% |
| Black | 0 | 0% | 0 | 0% | 54 | 0.2% |
| American Indian, Eskimo, Aleut | 0 | 0% | 0 | 0% | 1,442 | 4.1% |
| Asian or Pacific Islander | 0 | 0% | 0 | 0% | 88 | 0.2% |
| Other | 0 | 0% | 0 | 0% | 20 | 0.1% |
| Hispanic Origin | 0 | 0% | 0 | 0% | 164 | 0.5% |
| Less than 18 Years of Age | -- | -- | 7 | 11.3% | 9,040 | 25.6% |
| 18 Years of Age or Greater | -- | -- | 55 | 88.7% | 26,268 | 74.4% |
| Children Aged 6and Younger | 2 | 8.3% | 0 | 0% | 2,250† | 5.3% |
| Females Aged 15-44 | 4 | 16.7% | 8 | 12.9% | 7,382 | 20.4% |
| Adults Aged 65 and Older | 4 | 16.7% | 15 | 24.2% | 5,694 | 17.3% |
| Total Housing Units | 93 | -- | 207 | -- | 19,124 | -- |
| Occupied | -- | -- | 24 | 11.6% | 13,418 | 70.2% |
| Owner Occupied | -- | -- | 24 | 11.6% | 10,568 | 55.3% |
| Median Housing Value | -- | -- | 125,000 | -- | 53,100 | -- |
Source: 1, 5
Notes:
* the town of Meddybemps has a population of 142 which is said to approximately triple in the summer (1)
† under 5 years
Site area statistics from 1990 census
ZIP code from 1990 census
County statistics from 1990 census
| Pathway Name | Exposure Pathway Elements | Time | Comments | ||||
|---|---|---|---|---|---|---|---|
| Source | Media | Point of Exposure | Route of Exposure | Exposed Population | |||
| Ground-water as Drinking Water | Eastern Surplus | Groundwater | Private Wells | Ingestion, Dermal contact | Year-round residents with private wells (approximately 142 in Meddybemps, Maine) | Past, Current, Future | No past, current, or future public health hazards are likely because contaminants were detected below levels likely to result in adverse health effects and groundwater remediation is underway at the site. No on-site use of groundwater has been identified, therefore contact with on-site groundwater is an incomplete exposure pathway. |
| Surface Soil | Eastern Surplus | Surface Soil | Contaminated on-site areas , including VOC and PCB hot spots | Incidental ingestion, Dermal contact | Trespassers, Past on-site residents and workers | Past, Current, Future | The site is fenced to prevent site access; therefore, no exposures are expected. Remedial actions have removed areas of soil contamination and no adverse health effects are expected from exposures to surface soil. Past exposures to on-site residents, workers, or trespassers cannot be evaluated because data to characterize surface soil contamination before MEDEP, EPA, and DOD conducted remedial actions in the 1980s and 1990s are unavailable. |
| Surface water and sediment in Meddy-bemps Lake and Dennys River | Eastern Surplus | Surface water, Sediment | Meddybemps Lake, Dennys River (including Mill Pond) | Incidental ingestion, Dermal contact | Recreational users | Past, Current, Future | Contact with contaminants in surface water and sediment in Meddybemps Lake and Dennys River (including Mill Pond) is unlikely to result in adverse health effects. Contaminants are present below levels likely to result in health effects, exposures are infrequent, and remedial actions have been conducted to prevent contaminant migration. |
| Surface water from Meddy-bemps Lake as drinking water | Eastern Surplus | Surface water | Meddybemps Lake | Ingestion, Dermal Contact | Summer residents | Past, Current, Future | Some summer residents are reported to use surface water from Meddybemps Lake as a drinking water source. Only antimony was found slightly above comparison values in a background sample from Meddybemps Lake. Ingestion of antimony at the maximum detected concentration for 3 to 4 months a year is unlikely to result in adverse health effects. Ongoing remediation at the site will further prevent site impacts to the lake. No past, current, of future use of lake water for drinking water by summer residents is likely to result in adverse health effects. |
| Air | Eastern Surplus | Air | Site vicinity | Inhalation | Nearby residents, Trespassers | Past, Current, Future | No air contaminants were detected off site, even during remedial activities. No data, however, are available to assess past airborne contamination when the site was active. |
| Biota | Eastern Surplus | Plants, Animals, Fish, Shellfish | Plants and animals from the site, Fish and shellfish from Meddybemps Lake and Dennys River | Ingestion | Recreational users, including the Passamaquoddy Tribe | Past, Current, Future | Current and future use of biota from Meddybemps Lake and Denny's River is unlikely to result in adverse health effects when following the state-wide fish consumption advisory. EPA and the Passamaquoddy tribe plan to meet to identify any plants they may use for medicinal or other purposes on the site. Remedial actions were implemented to reduce site contamination and prevent contaminant migration. Potential health hazards from former (prior to 1970) tribal subsistence gathering, hunting, and fishing are unknown because no data were collected to characterize site conditions before remediation in the 1980s and 1990s. |
| Physical hazards | Eastern Surplus | Physical hazard | Former hydroelectric power unit | Physical hazard | Trespassers | Past, Current, Future | A dilapidated hydroelectric unit spans Dennys River along the southern site shoreline. Access from the west is restricted by a fence surround the site, but access from the east is unrestricted. |
| Chemical | Max. Conc. In parts per billion (ppb) | Date | CV | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|---|
| Benzene | 2 | 12/11/96 | 0.6 | CREG | 3 / 3 / 279 | MW-1B, MW-16S |
| Chloromethane | 55 | 6/17/98 | 2.1 | RBC-C | 2 / 6 / 277 | AP-06 |
| 1,1-Dichloroethene | 3 | 6/14/98 | 0.06 90 | CREG C-EMEG-child | 6 / 6 / 279 0 / 6 / 279 | MW-8B |
| 1,2-Dichloroethene (total) | 440 | 11/6/98 | 55 | RBC-N | 4 / 15 / 137 | MW-23M |
| Methylene chloride | 6,300 | 11/6/98 | 5 600 | CREG RMEG-child | 12 / 61 / 279 2 / 61 / 279 | AP-06 |
| Tetrachloroethylene (PCE) | 7,900 | 11/5/98 | 5 100 | MCL RMEG-child | 68 / 132 / 279 | MW-20B |
| Toluene | 650 | 12/4/97 | 200 | I-EMEG-child | 2 / 42 / 279 | MW-8B |
| 1,1,2-Trichloroethane | 11 | 12/4/97 | 0.6 40 | CREG RMEG-child | 1 / 1 / 278 0 / 1 / 278 | MW-3B |
| Trichloroethylene (TCE) | 380 | 11/19/97 | 5 | MCL | 51 / 61 / 279 | MW-23M |
| Vinyl chloride | 0.9 | 11/5/98 | 0.02 0.2 | CREG C-EMEG-child | 1 / 1 / 279 1 / 1 / 279 | MW-23M |
| Xylenes, total | 2,700 | 11/6/98 | 2,000 | I-EMEG-child | 1 / 12 / 246 | AP-06 |
| Bis(2-ethylhexyl)phthalate | 330 | 12/12/96 | 3 200 | CREG RMEG-child | 8 / 21 / 134 1 / 21 / 134 | MW-4B |
| Carbazole | 5 | 9/4/96 | 3.3 | RBC-C | 1 / 1 / 134 | MW-1B |
| Naphthalene | 32 | 9/4/96 | 20 | LTHA | 1 / 2 / 166 | MW-1B |
| PAHs, total | 33 | 6/4/96 | -- | No CV | -- / 2 / 110 | MW-1B |
| Aldrin | 0.0024 | 11/18/97 | 0.002 0.3 | CREG C-EMEG-child | 1 / 2 / 37 0 / 2 / 37 | MW-24B |
| PCBs, total | 4,120.6 | 6/8/99 | 20 | CREG | 12 / 18 / 49 | MW-17S |
| Aluminum | 20,100 | 11/20/97 | 20,000 | I-EMEG-child | 1 / 140 / 227 | MW-25S |
| Antimony | 30 | 11/19/97 | 4 | RMEG-child | 7 / 15 / 222 | MW-23M |
| Arsenic | 65 | 6/11/99 | 0.02 3 | CREG C-EMEG-child | 62 / 62 / 227 54 / 62 / 227 | AP-06 |
| Cadmium | 15.6 | 6/14/98 | 2 | C-EMEG-child | 4 / 28 / 226 | MW-8S |
| Chromium | 713 | 6/7/97 | 30 | RMEG-child | 21 / 120 / 225 | AP-05 |
| Iron | 51,600 | 12/11/96 | 11,000 | RBC-N | 13 / 185 / 227 | AP-06 |
| Lead | 90 | 6/14/98 | 15 | MCL Action Level | 12 / 103 / 227 | MW-8S |
| Manganese | 26,800 | 11/19/97 | 500 | RMEG-child | 29 / 103 / 227 | AP-06 |
| Nickel | 576 | 6/7/97 | 200 | I-EMEG-child | 3 / 146 / 225 | AP-05 |
| Silver | 83.7 | 6/14/98 | 50 | RMEG-child | 1 / 15 / 222 | MW-TB-08 |
| Thallium | 53.2 | 11/5/98 | 2.6 | RBC-N | 6 / 6 / 222 | MW-8B |
| Vanadium | 36.3 | 12/11/96 | 30 | I-EMEG-child | 1 / 69 / 225 | MW-11S |
| Zinc | 7,680 | 6/14/98 | 3,000 | C-EMEG-child | 3 / 153 / 227 | MW-8S |
Key:
C-EMEG-child = Environmental Media Evaluation Guide for chronic exposure to a child (ATSDR)
CREG = Cancer Risk Evaluation Guide (ATSDR)
CV = Comparison Value
Max. Conc. = maximum concentration
MCL = Maximum Contaminant Level
PCBs = polychlorinated biphenyls
ppb = parts per billion
RBC-C = Risk-Based Concentration for cancer effects (EPA)
RBC-N = Risk-Based Concentration for non-cancer effects (EPA)
RMEG-child = Reference Dose Media Evaluation Guide for a child (ATSDR)
Source: 1
| Chemical | Max. Conc. | Date | CV | Type | Exceedences / Detections / Samples | Drinking well (DW-) numbers with exceedences (number of exceedences) |
|---|---|---|---|---|---|---|
| Tetrachloroethylene (PCE) | 8.6 | 6/5/97 | 5 | MCL | 1 / 3 / 55 | 38* |
| Bis(2-ethylhexyl)phthalate | 6 | 9/30/96 | 3 200 | CREG RMEG-child | 1 / 4 / 46 0 / 4 / 46 | 27* -- |
| Arsenic | 40.8 | 9/5/96 | 0.02 3 | CREG C-EMEG-child | 30 / 30 / 55 27 / 30 / 55 | 01 (4), 06, 11, 13, 17 (6), 20, 21 (2), 24, 25*, 26, 27, 28, 29 (9) 01, 06, 11, 13, 17 (6), 20, 21 (2), 24, 25*, 26, 27, 28, 29 (9) |
| Manganese | 836 | 9/4/96 | 500 | RMEG-child | 4 / 37 / 55 | 01 (4)* |
| Thallium | 6.2 | 9/4/96 | 2.6 | RBC-N | 2 / 2 / 55 | 02*, 03* |
| Zinc | 3,600 | 9/4/96 | 3,000 | C-EMEG-child | 1 / 17 / 55 | 03* |
All units are ppb
Key:
C-EMEG-child = Environmental Media Evaluation Guide for Chronic exposure to a child (ATSDR)
CREG = Cancer Risk Evaluation Guide (ATSDR)
CV = Comparison Value
Max. Conc. = Maximum concentration
MCL = Maximum Contaminant Level
ppb = parts per billion
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
* = maximum detection occurred at this location.
Source: 1
| Chemical | Max. Conc. | Date | CV | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|---|
| Methylene chloride | 40,000 | 10/21/96 | 90 10,000 | CREG C-EMEG-child | 4 / 12 / 419 | SS096 |
| 4-Methyl-2-pentanone | 23 | 10/21/96 | -- | none | -- / 6 / 40 | SS096 |
| Benzo(a)pyrene | 0.4 | 10/8/97 | 0.1 | CREG | 2 / 4 / 26 | SS108 |
| Benzo(g,h,i)perylene | 0.19 | 10/8/97 | -- | none | -- / 4 / 26 | SS108 |
| Bis(2-ethylhexyl)phthalate | 60 | 11/8/97 | 50 1,000 | CREG RMEG-child | 1 / 10 / 26 0 / 10 / 26 | ES-GS-BII07-0001 |
| Dibenzo(a,h)anthracene | 0.18 | 10/8/97 | 0.087 | RBC-C | 3 / 3 / 26 | SS108 |
| PAHs, total | 7.068 | 10/8/97 | -- | none | -- / 8 / 26 | SS108 |
| Phenanthrene | 0.21 | 10/8/97 | -- | none | -- / 5 / 26 | SS108 |
| Dieldrin | 0.061 | 11/8/97 | 0.04 3 | CREG C-EMEG-child | 1 / 7 / 37 0 / 7 /37 | ES-GS-BII06-0001 |
| Endosulfan sulfate | 0.0041 | 11/11/97 | -- | none | -- / 1 / 37 | ES-GS-BIV07-0001 |
| Aroclor-1248 | 6.4 | 9/23/98 | 0.32 | RBC-C | 1 / 1 / 412 | ES-SS-15-0001 |
| Aroclor-1254 | 8 | 9/23/98 | 1 | RMEG-child | 6 / 18 / 412 | ES-SS-15-0001 |
| Aroclor-1260 | 560 | 10/8/97 | 0.32 | RBC-C | 78 / 111 / 412 | SS114 |
| PCBs, total | 560 | 10/8/97 | 0.4 | CREG | 90 / 120 / 412 | SS114 |
| Antimony | 64.5 | 10/21/96 | 20 | RMEG-child | 4 / 45 / 102 | SS096 |
| Arsenic | 105 | 10/21/98 | 0.5 20 | CREG C-EMEG-child | 114 / 114 / 477 34 / 114 / 477 | ES-SS-154-0001 |
| Cadmium | 270 | 9/23/98 | 10 | C-EMEG-child | 11 / 47 / 478 | ES-DP-41-0002 |
| Chromium | 13,800 | 10/21/96 | 200 | RMEG-child | 51 / 143 / 477 | SS096 |
| Iron | 180,000 | 10/8/97 | 23,000 | RBC-N | 56 / 102 / 102 | SS108 |
| Lead | 1,500 | 10/13/98 | 400 | EPA SSL | 10 / 170 / 477 | ES-SS-113-0001 |
All units are ppm.
Key:
C-EMEG-child = Environmental Media Evaluation Guide for Chronic exposure to a child (ATSDR)
CREG = Cancer Risk Evaluation Guide (ATSDR)
CV = Comparison Value
Max. Conc. = Maximum Concentration
PAHs = Polynuclear aromatic hydrocarbons
PCBs = Polychlorinated biphenyls
ppm = parts per million
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
RMEG-child = Reference Dose Media Evaluation Guide for a child (ATSDR)
SSL = Soil Screening Level (EPA)
Source: 1
| Chemical | Max. Conc. | Date | CV | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|---|
| Arsenic | 63 | 10/22/98 | 0.5 20 | CREG C-EMEG-child | 5 / 5 / 5 1 / 5 / 5 | DP-120 (south of site) |
| Aroclor-1260 | 0.46 | 10/8/97 | 0.32 | RBC-C | 1 / 2 / 4 | SS116 (west of site) |
| PCBs, total | 0.46 | 10/8/97 | 0.4 | CREG | 1 / 2 / 4 | SS116 (west of site) |
All units are ppm.
Key:
C-EMEG-child = Environmental Media Evaluation Guide for Chronic exposure to a child (ATSDR)
CV = Comparison Value
Max. Conc. = Maximum Concentration
PAHs = Polynuclear aromatic hydrocarbons
PCBs = Polychlorinated biphenyls
ppm = part per million
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
Source: 1
| Chemical | Max. Conc. | Date | CV | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|---|
| Tetrachloroethylene (PCE) | 270 | 6/17/99 | 5 100 | MCL RMEG-child | 5 / 5 / 37 2 / 5 / 37 | SW-406 |
| Trichloroethylene (TCE) | 76 | 6/17/99 | 5 | MCL | 6 / 6 / 37 | SW-406 |
| Bis(2-ethylhexyl)phthalate | 480 | 10/6/97 | 3 200 | CREG RMEG-child | 2 / 5 / 38 1 / 5 / 38 | SW-118 |
| Antimony | 7.4 | 10/6/97 | 4 | RMEG-child | 3 / 4 / 44 | SW-122 |
| Arsenic | 3.8 | 10/6/97 | 0.02 3 | CREG C-EMEG-child | 2 / 2 / 44 1 / 2 / 44 | SW-119 |
| Manganese | 1,410 | 6/17/99 | 500 | RMEG-child | 1 / 43 / 44 | SW-406 |
| Thallium | 5.7 | 10/2/96 | 2.6 | RBC-N | 1 / 1 / 44 | SW-108 |
All units are ppb.
Key:
C-EMEG-child = Environmental Media Evaluation Guide for Chronic exposure to a child (ATSDR)
CREG = Cancer Risk Evaluation Guide (ATSDR)
CV = Comparison Value
Max. Conc. = Maximum Concentration
ppb = parts per billion
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
RBC-N = Risk-Based Concentration for Non-cancer effects (EPA)
RMEG-child = Reference Dose Media Evaluation Guide for a child (ATSDR)
Source: 1
| Chemical | Max. Conc. | Date | CV | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|---|
| Benzo(a)anthracene | 5.8 | 10/3/96 | 0.87 | RBC-C | 1 / 19 / 73 | SD-131 |
| Benzo(b)fluoranthene | 6.6 | 10/3/96 | 0.87 | RBC-C | 1 / 23 / 73 | SD-131 |
| Benzo(g,h,i)perylene | 3.5 | 10/3/96 | -- | none | -- / 7 / 73 | SD-131 |
| Benzo(a)pyrene | 5.6 | 10/3/96 | 0.1 | CREG | 18 / 19 / 73 | SD-131 |
| Dibenzo(a,h)anthracene | 1 | 10/3/96 | 0.087 | RBC-C | 1 / 1 / 73 | SD-131 |
| Indeno(1,2,3-cd)pyrene | 3.7 | 10/3/96 | 0.87 | RBC-C | 1 / 10 / 73 | SD-131 |
| Phenanthrene | 5.2 | 10/3/96 | -- | none | -- / 16 / 73 | SD-131 |
| Endosulfan sulfate | 0.0031 | 6/16/99 | -- | none | -- / 1 / 81 | ES-SD-409-03 |
| Endrin aldehyde | 0.0034 | 6/16/99 | -- | none | -- / 4 / 81 | ES-SD-406-03 |
| Aroclor-1260 | 1.6 | 6/16/99 | 0.32 | RBC-C | 6 / 16 / 38 | ES-SD-406-03 |
| Total PCBs | 7.89 | 6/17/98 | 0.4 | CREG | 9 / 74 / 81 | ES-SD-303-01 |
| Arsenic | 31.9 | 10/7/97 | 0.5 20 | CREG C-EMEG-child | 76 / 76 / 81 6 / 76 / 81 | SD-151 |
| Iron | 43,900 | 10/1/96 | 23,000 | RBC-N | 16 / 79 / 81 | SD-107 |
All units are ppm.
Key:
C-EMEG-child = Environmental Media Evaluation Guide for Chronic exposure to a child (ATSDR)
CREG = Cancer Risk Evaluation Guide (ATSDR)
CV = Comparison Value
Max. Conc. = Maximum Concentration
PCBs = Polychlorinated biphenyls
ppm = parts per million
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
RBC-N = Risk-Based Concentration for Non-cancer effects (EPA)
RMEG-child = Reference Dose Media Evaluation Guide for a child (ATSDR)
Source: 1
| Chemical | Max. Conc. | RBC | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|
| 4,4'-DDE | 0.0119 | 0.0093 | C | 2 / 13 / 36 | DS02BT |
| Dieldrin | 0.00381 | 0.0002 | C | 2 / 2 / 36 | DS01BT |
| PCBs, total | 0.062 | 0.0016 | C | 36 / 36 / 36 | ES02SM |
| Arsenic | 4.13 | 0.0021 | C | 30 / 30 / 36 | MS04SM |
| Chromium | 12.2 | 4.1 | N | 1 / 16 / 36 | ES01SM |
| Lead | 1.01 | -- | 2 / 2 / 36 | SC05SM | |
| Mercury | 3.94 | 0.14 | N* | 35 / 35 / 36 | DW01SM |
All units are ppm.
Notes:
- All samples were taken on September 22 and 27, 1997.
- Five fish samples, representing different ages and sizes, were collected from each of seven different sampling locations. The fillets from each fish were analyzed individually. The maximum concentrations, therefore, represents the concentration found in an individual fish.
- Analysis results were normalized for lipid and moisture content using statistical models to allow for data comparisons across results.
- Smallmouth bass were collected from each sampling location, except DS01BT and DS02BT, where brook trout were collected.
Key:
Max. Conc. = Maximum Concentration
PCBs = Polychlorinated biphenyls
ppm = parts per million
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
RBC-N = Risk-Based Concentration for Non-cancer effects (EPA)
* for methylmercury
Source: 1
| Chemical | Max. Conc. | RBC | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|
| 4,4'-DDE | 0.021 | 0.0093 | C | 8 / 64 / 71 | DS02BT |
| Dieldrin | 0.00711 | 0.0002 | C | 11 / 11 / 71 | DS02BT |
| PCBs, total | 0.330 | 0.0016 | C | 71 / 71 / 71 | DW05SM |
| Arsenic | 3.05 | 0.0021 | C | 34 / 34 / 71 | MS06PS |
| Chromium | 16.5 | 4.1 | N | 3 / 70 / 71 | FP04SM |
| Lead | 0.65 | -- | -- / 7 / 71 | ES08WS | |
| Mercury | 1.91 | 0.14 | N* | 65 / 65 / 71 | EM06SM |
All units are ppm.
Notes:
- All samples were taken on September 22 and 27, 1997.
- Whole body results were generated either through analysis of the whole body fish sample or the combined results from separate analyses of the fish fillet and carcass samples.
- Ten fish samples, representing different ages and sizes, were collected from each of seven different sampling locations and analyzed individually. Of the ten samples collected from each location, five samples were analyzed as whole body and five samples were analyzed separately as a fillet (see Table 9) and carcass. The maximum concentrations represents the concentration found in an individual fish.
- Analysis results were normalized for lipid and moisture content using statistical models to allow for data comparisons across results.
- Four fish species were collected for analysis: smallmouth bass (fillet and carcass), brook trout (fillet and carcass), pumpkinseed (whole body), and white sucker (whole body). Maximum concentrations of PCBs, chromium, and mercury were found in smallmouth bass; 4,4'-DDE and dieldrin in brown trout; arsenic in pumpkinseed; and lead in white sucker.
Key:
Max. Conc. = Maximum Concentration
PCBs = Polychlorinated biphenyls
ppm = parts per million
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
RBC-N = Risk-Based Concentration for Non-cancer effects (EPA)
* for methylmercury
Source: 1
| Chemical | Max. Conc. | RBC | Type | Exceedences / Detections / Samples | Location of maximum |
|---|---|---|---|---|---|
| PCBs, total | 0.0099 | 0.0016 | C | 5 / 6 / 6 | ES02AF |
| Arsenic | 8.41 | 0.0021 | C | 6 / 6 / 6 | FP01EC |
| Barium | 452 | 95 | N | 6 / 6 / 6 | EM01EC |
| Cadmium | 5.8 | 1.4 | N | 6 / 6 / 6 | ES01AF |
| Chromium | 6.43 | 4.1 | N | 1 / 6 / 6 | ES02AF |
| Iron | 2,758 | 410 | N | 6 / 6 / 6 | EM01EC |
| Lead | 5.91 | -- | -- / 6 / 6 | EM01EC | |
| Manganese | 4,262 | 190 | N | 6 / 6 / 6 | EM01EC |
| Mercury | 0.78 | 0.14 | N* | 3 / 3 / 6 | EM01EC |
All units are ppm.
Notes:
- All samples were taken on September 22 and 27, 1997.
- Each sample represents a composite of five mussels of similar size and species collected from one sampling location.
- Analysis results were normalized for lipid and moisture content using statistical models to allow for data comparisons across results.
- Two mussel species were collected for analysis: eastern elliptio and alewife floater. Maximum concentrations of arsenic, barium, iron, lead, manganese, and mercury were found in eastern elliptio; and maximum concentrations of PCBs, cadmium, and chromium were found in alewife floater.
Key:
Max. Conc. = Maximum Concentration
PCBs = Polychlorinated biphenyls
ppm = parts per million
RBC-C = Risk-Based Concentration for Cancer effects (EPA)
RBC-N = Risk-Based Concentration for Non-cancer effects (EPA)
* for methylmercury
Source: 1


