Appendix D continued
Table D-1. Exposure Doses for Chemicals Below the Oral Health Guideline in Fish
| Chemical |
Maximum Detected Concentration
(ppm) | Estimated Exposure Dose (mg/kg/day) |
Oral Health Guideline (mg/kg/day) | Basis for Health Guideline | |
| Adult | Child | ||||
| Aluminum | 13.5 | 0.0438 | 0.0958 | 1.0 | chronic RfD |
| Barium | 6.59 | 0.0214 | 0.0467 | 0.07 | chronic RfD |
| Beryllium | 0.02 | 0.00006 | 0.00014 | 0.001 | chronic MRL |
| Cadmium | 0.08 | 0.00026 | 0.00057 | 0.001 | chronic RfD (food) |
| Cobalt | 0.11 | 0.0004 | 0.0008 | 0.02 | chronic RfD |
| Manganese | 3.09 | 0.0100 | 0.0219 | 0.14 | chronic RfD (food) |
| Nickel | 1.28 | 0.0042 | 0.0091 | 0.02 | chronic RfD |
| Silver | 0.11 | 0.0004 | 0.0008 | 0.005 | chronic RfD |
| Vanadium | 0.09 | 0.0003 | 0.0006 | 0.007 | chronic RfD |
| Zinc | 24.7 | 0.0801 | 0.1752 | 0.3 | chronic MRL/RfD |
Notes: Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
Table D-2. Exposure Doses for Chemicals Below the Oral Health Guideline in Shellfish
| Metal |
Maximum Detected Concentration
(ppm) | Estimated Exposure Dose (mg/kg/day) |
Oral Health Guideline (mg/kg/day) | Basis for Health Guideline | |
| Adult | Child | ||||
| Aluminum | 43.9 | 0.1424 | 0.3114 | 1.0 | chronic RfD |
| Barium | 7.25 | 0.0235 | 0.0514 | 0.07 | chronic RfD |
| Beryllium | 0.02 | 0.00006 | 0.00014 | 0.001 | chronic MRL |
| Cobalt | 0.09 | 0.0003 | 0.0006 | 0.02 | chronic RfD |
| Manganese | 5.06 | 0.0164 | 0.0359 | 0.14 | chronic RfD (food) |
| Silver | 0.19 | 0.0006 | 0.0013 | 0.005 | chronic RfD |
| Vanadium | 0.27 | 0.0009 | 0.0019 | 0.007 | chronic RfD |
Table D-3. Estimated Exposure Doses from Ingestion of Fish
| Metal | Level of Exposure |
Maximum Detected Concentration
(ppm) | Estimated Exposure Dose (mg/kg/day) |
Oral Health Guideline (mg/kg/day) | Basis for Health Guideline | |
| Adult | Child | |||||
| Arsenic | 7 days/week | 29.25 | 0.095* | 0.207* | 0.0003 | chronic MRL/RfD |
| 5 days/week | 29.25 | 0.068* | 0.148* | 0.0003 | chronic MRL/RfD | |
| 4 days/week | 29.25 | 0.054* | 0.118* | 0.0003 | chronic MRL/RfD | |
| 2 days/week | 29.25 | 0.027* | 0.059* | 0.0003 | chronic MRL/RfD | |
| 1 day/week | 29.25 | 0.014* | 0.030* | 0.0003 | chronic MRL/RfD | |
| Chromium | 7 days/week | 1.99 | 0.0065* | 0.0141* | 0.003 | chronic RfD (CrVI) |
| 5 days/week | 1.99 | 0.0046* | 0.0101* | 0.003 | chronic RfD (CrVI) | |
| 4 days/week | 1.99 | 0.0037* | 0.0180* | 0.003 | chronic RfD (CrVI) | |
| 2 days/week | 1.99 | 0.0018 | 0.0040* | 0.003 | chronic RfD (CrVI) | |
| 1 day/week | 1.99 | 0.0009 | 0.0020* | 0.003 | chronic RfD (CrVI) | |
| Copper | 7 days/week | 8.21 | 0.027 | 0.058* | 0.04 | chronic RfD |
| 5 days/week | 8.21 | 0.019 | 0.041* | 0.04 | chronic RfD | |
| 4 days/week | 8.21 | 0.015 | 0.033 | 0.04 | chronic RfD | |
| 2 days/week | 8.21 | 0.008 | 0.017 | 0.04 | chronic RfD | |
| 1 day/week | 8.21 | 0.004 | 0.008 | 0.04 | chronic RfD | |
| Iron | 7 days/week | 57.78 | 0.19 | 0.41* | 0.3 | chronic RfD |
| 5 days/week | 57.78 | 0.13 | 0.29 | 0.3 | chronic RfD | |
| 4 days/week | 57.78 | 0.11 | 0.23 | 0.3 | chronic RfD | |
| 2 days/week | 57.78 | 0.05 | 0.12 | 0.3 | chronic RfD | |
| 1 day/week | 57.78 | 0.03 | 0.06 | 0.3 | chronic RfD | |
| Lead | 7 days/week | 1.94 | 0.0063 | 0.0138 | NA | NA |
| 5 days/week | 1.94 | 0.0045 | 0.0098 | NA | NA | |
| 4 days/week | 1.94 | 0.0036 | 0.0078 | NA | NA | |
| 2 days/week | 1.94 | 0.0018 | 0.0039 | NA | NA | |
| 1 day/week | 1.94 | 0.0009 | 0.0020 | NA | NA | |
| Mercury, total | 7 days/week | 0.33 | 0.00107* | 0.00234* | 0.0003 | chronic MRL (MeHg) |
| 5 days/week | 0.33 | 0.00076* | 0.00167* | 0.0003 | chronic MRL (MeHg) | |
| 4 days/week | 0.33 | 0.00061* | 0.00133* | 0.0003 | chronic MRL (MeHg) | |
| 2 days/week | 0.33 | 0.00030 | 0.00067* | 0.0003 | chronic MRL (MeHg) | |
| 1 day/week | 0.33 | 0.00015 | 0.00033* | 0.0003 | chronic MRL (MeHg) | |
| Methylmercury | 7 days/week | 0.082 | 0.00027 | 0.00058* | 0.0003 | chronic MRL |
| 5 days/week | 0.082 | 0.00019 | 0.00042* | 0.0003 | chronic MRL | |
| 4 days/week | 0.082 | 0.00015 | 0.00033* | 0.0003 | chronic MRL | |
| 2 days/week | 0.082 | 0.00008 | 0.00017 | 0.0003 | chronic MRL | |
| 1 day/week | 0.082 | 0.00004 | 0.00008 | 0.0003 | chronic MRL | |
| Selenium | 7 days/week | 2.48 | 0.0080* | 0.0176* | 0.005 | chronic MRL/RfD |
| 5 days/week | 2.48 | 0.0057* | 0.0125* | 0.005 | chronic MRL/RfD | |
| 4 days/week | 2.48 | 0.0046 | 0.0100* | 0.005 | chronic MRL/RfD | |
| 2 days/week | 2.48 | 0.0023 | 0.0050 | 0.005 | chronic MRL/RfD | |
| 1 day/week | 2.48 | 0.0011 | 0.0025 | 0.005 | chronic MRL/RfD | |
* Estimated exposure exceeds health guideline; however, an exposure dose that is higher than the MRL or RfD does not necessarily result in harmful health effects. These metals are further evaluated.
Note: Exposure doses were calculated using the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
Table D-4. Estimated Exposure Doses from Ingestion of Shellfish
| Metal | Level of Exposure |
Maximum Detected Concentration
(ppm) |
Estimated Exposure Dose (mg/kg/day) |
Oral Health Guideline (mg/kg/day) |
Basis for Health Guideline | |
| Adult | Child | |||||
| Arsenic | 7 days/week | 48.28 | 0.157* | 0.342* | 0.0003 | chronic MRL/RfD |
| 5 days/week | 48.28 | 0.112* | 0.244* | 0.0003 | chronic MRL/RfD | |
| 4 days/week | 48.28 | 0.0892* | 0.195* | 0.0003 | chronic MRL/RfD | |
| 2 days/week | 48.28 | 0.045* | 0.098* | 0.0003 | chronic MRL/RfD | |
| 1 day/week | 48.28 | 0.022* | 0.049* | 0.0003 | chronic MRL/RfD | |
| Cadmium | 7 days/week | 0.69 | 0.0022* | 0.0049* | 0.001 | chronic RfD (food) |
| 5 days/week | 0.69 | 0.0016* | 0.0035* | 0.001 | chronic RfD (food) | |
| 4 days/week | 0.69 | 0.0013* | 0.0028* | 0.001 | chronic RfD (food) | |
| 2 days/week | 0.69 | 0.0006 | 0.0014* | 0.001 | chronic RfD (food) | |
| 1 day/week | 0.69 | 0.0003 | 0.0007 | 0.001 | chronic RfD (food) | |
| Chromium | 7 days/week | 1.29 | 0.0042* | 0.0092* | 0.003 | chronic RfD (CrVI) |
| 5 days/week | 1.29 | 0.0030 | 0.0065* | 0.003 | chronic RfD (CrVI) | |
| 4 days/week | 1.29 | 0.0024 | 0.0052* | 0.003 | chronic RfD (CrVI) | |
| 2 days/week | 1.29 | 0.0012 | 0.0026 | 0.003 | chronic RfD (CrVI) | |
| 1 day/week | 1.29 | 0.0006 | 0.0013 | 0.003 | chronic RfD (CrVI) | |
| Copper | 7 days/week | 17.6 | 0.057* | 0.124* | 0.04 | chronic RfD |
| 5 days/week | 17.6 | 0.041* | 0.089* | 0.04 | chronic RfD | |
| 4 days/week | 17.6 | 0.032 | 0.071* | 0.04 | chronic RfD | |
| 2 days/week | 17.6 | 0.016 | 0.035 | 0.04 | chronic RfD | |
| 1 day/week | 17.6 | 0.008 | 0.018 | 0.04 | chronic RfD | |
| Iron | 7 days/week | 162 | 0.52* | 1.15* | 0.3 | chronic RfD |
| 5 days/week | 162 | 0.37* | 0.82* | 0.3 | chronic RfD | |
| 4 days/week | 162 | 0.30 | 0.65* | 0.3 | chronic RfD | |
| 2 days/week | 162 | 0.15 | 0.33* | 0.3 | chronic RfD | |
| 1 day/week | 162 | 0.07 | 0.16 | 0.3 | chronic RfD | |
| Lead | 7 days/week | 0.57 | 0.0018 | 0.0040 | NA | NA |
| 5 days/week | 0.57 | 0.0013 | 0.0029 | NA | NA | |
| 4 days/week | 0.57 | 0.0011 | 0.0023 | NA | NA | |
| 2 days/week | 0.57 | 0.0005 | 0.0012 | NA | NA | |
| 1 day/week | 0.57 | 0.0003 | 0.0006 | NA | NA | |
| Mercury, total | 7 days/week | 0.05 | 0.00016 | 0.00036* | 0.0003 | chronic MRL (MeHg) |
| 5 days/week | 0.05 | 0.00012 | 0.00025 | 0.0003 | chronic MRL (MeHg) | |
| 4 days/week | 0.05 | 0.00009 | 0.00020 | 0.0003 | chronic MRL (MeHg) | |
| 2 days/week | 0.05 | 0.00005 | 0.00010 | 0.0003 | chronic MRL (MeHg) | |
| 1 day/week | 0.05 | 0.00002 | 0.00005 | 0.0003 | chronic MRL (MeHg) | |
| Methylmercury | 7 days/week | 0.019 | 0.00006 | 0.00014 | 0.0003 | chronic MRL |
| 5 days/week | 0.019 | 0.00004 | 0.00010 | 0.0003 | chronic MRL | |
| 4 days/week | 0.019 | 0.00004 | 0.00008 | 0.0003 | chronic MRL | |
| 2 days/week | 0.019 | 0.00002 | 0.00004 | 0.0003 | chronic MRL | |
| 1 day/week | 0.019 | 0.00001 | 0.00002 | 0.0003 | chronic MRL | |
| Selenium | 7 days/week | 1.16 | 0.0038 | 0.0082* | 0.005 | chronic MRL/RfD |
| 5 days/week | 1.16 | 0.0027 | 0.0059* | 0.005 | chronic MRL/RfD | |
| 4 days/week | 1.16 | 0.0021 | 0.0047 | 0.005 | chronic MRL/RfD | |
| 2 days/week | 1.16 | 0.0011 | 0.0023 | 0.005 | chronic MRL/RfD | |
| 1 day/week | 1.16 | 0.0005 | 0.0012 | 0.005 | chronic MRL/RfD | |
| Zinc | 7 days/week | 96.6 | 0.31* | 0.69* | 0.3 | chronic MRL/RfD |
| 5 days/week | 96.6 | 0.22 | 0.49* | 0.3 | chronic MRL/RfD | |
| 4 days/week | 96.6 | 0.18 | 0.39* | 0.3 | chronic MRL/RfD | |
| 2 days/week | 96.6 | 0.09 | 0.20 | 0.3 | chronic MRL/RfD | |
| 1 day/week | 96.6 | 0.04 | 0.10 | 0.3 | chronic MRL/RfD | |
* Estimated exposure exceeds health guideline; however, an exposure dose that is higher than the MRL or RfD does not necessarily result in harmful health effects. These metals are further evaluated.
Note: Exposure doses were calculated using the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
Table D-5. Inorganic Arsenic Exposure Doses According to Location
| Location | Fish | Shellfish | ||||
|
Average
Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) |
Average Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) | |||
| Adult | Child | Adult | Child | |||
| 1 - North LIA | 3.8 | 0.0025 | 0.0054 | 9.9 | 0.0064 | 0.0140 |
| 2 - South LIA | 1.3 | 0.0008 | 0.0018 | 5.3 | 0.0034 | 0.0075 |
| 3 - Esperanza | 4.4 | 0.0029 | 0.0062 | 8.3 | 0.0054 | 0.0118 |
| 4 - Isabel Segunda | 1.9 | 0.0012 | 0.0027 | NS | NS | NS |
| 5 - Fish Market | 8.0 | 0.0052 | 0.0114 | 31.7 | 0.0206 | 0.0450 |
| 6 - West Vieques | 3.9 | 0.0025 | 0.0055 | 2.7 | 0.0018 | 0.0038 |
| All Locations | 4.0 | 0.0026 | 0.0057 | 11.1 | 0.0072 | 0.0157 |
Notes: Averages were calculated using detected values only.
Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED x 0.2) / (BW x AT).
The body metabolizes arsenic into a less harmful form at doses of 0.05 mg/kg/day.
Health effects were reported from exposure to 0.014 mg/kg/day.
Cancer effects were reported from exposures to 0.01-0.05 mg/kg/day.
NS = not sampled
Table D-6. Inorganic Arsenic Exposure Doses for Species of Shellfish
| Species | Level of Exposure |
Average Concentration
(ppm) |
Estimated Exposure Dose (mg/kg/day) | |
| Adult | Child | |||
| Lobster | 7 days/week | 32.9 | 0.0213 | 0.0467 |
| 5 days/week | 32.9 | 0.0152 | 0.0332 | |
| 4 days/week | 32.9 | 0.0122 | 0.0266 | |
| 2 days/week | 32.9 | 0.0061 | 0.0133 | |
| 1 day/week | 32.9 | 0.0030 | 0.0066 | |
| Conch | 7 days/week | 3.9 | 0.0025 | 0.0055 |
| Land Crab | 7 days/week | 2.6 | 0.0017 | 0.0037 |
Notes: Averages were calculated using detected values only.
Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED x 0.2) / (BW x AT).
The body metabolizes arsenic into a less harmful form at doses of 0.05 mg/kg/day.
Health effects were reported from exposure to 0.014 mg/kg/day.
Cancer effects were reported from exposures to 0.01-0.05 mg/kg/day.
Table D-7. Cadmium Exposure Doses According to Location
| Location | Shellfish | ||
|
Average
Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) | ||
| Adult | Child | ||
| 1 - North LIA | 0.34 | 0.0011 | 0.0024 |
| 2 - South LIA | 0.27 | 0.0009 | 0.0019 |
| 3 - Esperanza | 0.49 | 0.0016 | 0.0035 |
| 4 - Isabel Segunda | NS | NS | NS |
| 5 - Fish Market | ND | ND | ND |
| 6 - West Vieques | 0.34 | 0.0011 | 0.0024 |
| All Locations | 0.36 | 0.0012 | 0.0026 |
Notes: Averages were calculated using detected values only.
Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
No adverse health effects were reported from exposure to 0.01 mg/kg/day.
Cancer effects were reported from exposure to 3.5 mg/kg/day.
ND = not detected
NS = not sampled
Table D-8. Chromium Exposure Doses According to Location
| Location | Fish | Shellfish | ||||
|
Average
Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) |
Average Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) | |||
| Adult | Child | Adult | Child | |||
| 1 - North LIA | 0.14 | 0.0005 | 0.0010 | 0.16 | 0.0005 | 0.0011 |
| 2 - South LIA | 0.25 | 0.0008 | 0.0018 | 0.38 | 0.0012 | 0.0027 |
| 3 - Esperanza | 0.23 | 0.0007 | 0.0016 | 0.12 | 0.0004 | 0.0009 |
| 4 - Isabel Segunda | 0.10 | 0.0003 | 0.0007 | NS | NS | NS |
| 5 - Fish Market | 0.13 | 0.0004 | 0.0009 | 0.13 | 0.0004 | 0.0009 |
| 6 - West Vieques | 0.11 | 0.0003 | 0.0008 | 0.10 | 0.0003 | 0.0007 |
| All Locations | 0.16 | 0.0005 | 0.0011 | 0.19 | 0.0006 | 0.0013 |
Notes: Averages were calculated using detected values only.
Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
No adverse health effects were reported from exposure to 2.5 mg/kg/day.
NS = not sampled
Table D-9. Copper Daily Doses According to Location
| Location | Fish | Shellfish | ||||
|
Average
Concentration (ppm) |
Estimated Daily Dose (mg/day) |
Average Concentration (ppm) |
Estimated Daily Dose (mg/day) | |||
| Adult | Child | Adult | Child | |||
| 1 - North LIA | 0.45 | 0.10 | 0.05 | 9.5 | 2.16 | 1.08 |
| 2 - South LIA | 0.54 | 0.12 | 0.06 | 10.0 | 2.27 | 1.14 |
| 3 - Esperanza | 0.55 | 0.12 | 0.06 | 3.8 | 0.86 | 0.43 |
| 4 - Isabel Segunda | 0.46 | 0.10 | 0.05 | NS | NS | NS |
| 5 - Fish Market | 0.92 | 0.21 | 0.10 | 10.4 | 2.36 | 1.18 |
| 6 - West Vieques | 0.44 | 0.10 | 0.05 | 3.2 | 0.73 | 0.36 |
| All Locations | 0.56 | 0.13 | 0.06 | 7.8 | 1.77 | 0.89 |
Notes: Averages were calculated using detected values only.
Daily doses were calculated using the following formula: Dose = Conc. x IR.
No adverse health effects were reported from exposure to 10 mg/day.
NS = not sampled
Table D-10. Iron Exposure Doses According to Location
| Location | Fish | Shellfish | ||||
|
Average
Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) |
Average Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) | |||
| Adult | Child | Adult | Child | |||
| 1 - North LIA | 6.4 | 0.021 | 0.045 | 18.0 | 0.058 | 0.128 |
| 2 - South LIA | 10.3 | 0.033 | 0.073 | 52.1 | 0.169 | 0.370 |
| 3 - Esperanza | 4.8 | 0.016 | 0.034 | 1.6 | 0.005 | 0.011 |
| 4 - Isabel Segunda | 1.9 | 0.006 | 0.013 | NS | NS | NS |
| 5 - Fish Market | 5.0 | 0.016 | 0.035 | ND | ND | ND |
| 6 - West Vieques | 6.8 | 0.022 | 0.048 | NA | NA | NA |
| All Locations | 6.8 | 0.022 | 0.048 | 36.3 | 0.118 | 0.258 |
Notes: Averages were calculated using detected values only.
Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
No adverse health effects were reported from exposure to 0.15-0.27 mg/kg/day.
NA = not available
ND = not detected
NS = not sampled
Table D-11. Iron Daily Doses According to Location
| Location | Fish | Shellfish | ||||
|
Average
Concentration (ppm) |
Estimated Daily Dose (mg/day) |
Average Concentration (ppm) |
Estimated Daily Dose (mg/day) | |||
| Adult | Child | Adult | Child | |||
| 1 - North LIA | 6.4 | 1.5 | 0.7 | 18.0 | 4.1 | 2.0 |
| 2 - South LIA | 10.3 | 2.3 | 1.2 | 52.1 | 11.8 | 5.9 |
| 3 - Esperanza | 4.8 | 1.1 | 0.5 | 1.6 | 0.4 | 0.2 |
| 4 - Isabel Segunda | 1.9 | 0.4 | 0.2 | NS | NS | NS |
| 5 - Fish Market | 5.0 | 1.1 | 0.6 | ND | ND | ND |
| 6 - West Vieques | 6.8 | 1.5 | 0.8 | NA | NA | NA |
| All Locations | 6.8 | 1.5 | 0.8 | 36.3 | 8.2 | 4.1 |
Notes: Averages were calculated using detected values only.
Daily doses were calculated using the following formula: Dose = Conc. x IR.
Childhood poisoning was reported from exposure to 200 mg/event.
NA = not available
ND = not detected
NS = not sampled
Table D-12. Lead Exposure Doses According to Location
| Location | Fish | Shellfish | ||||
|
Average
Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) |
Average Concentration (ppm) |
Estimated Exposure Dose (mg/kg/day) | |||
| Adult | Child | Adult | Child | |||
| 1 - North LIA | 1.06 | 0.0034 | 0.0075 | ND | ND | ND |
| 2 - South LIA | 0.23 | 0.0007 | 0.0016 | 0.27 | 0.0009 | 0.0019 |
| 3 - Esperanza | 0.21 | 0.0007 | 0.0015 | 0.18 | 0.0006 | 0.0013 |
| 4 - Isabel Segunda | 0.17 | 0.0006 | 0.0012 | NS | NS | NS |
| 5 - Fish Market | 0.24 | 0.0008 | 0.0017 | 0.20 | 0.0006 | 0.0014 |
| 6 - West Vieques | ND | ND | ND | ND | ND | ND |
| All Locations | 0.27 | 0.0009 | 0.0019 | 0.25 | 0.0008 | 0.0018 |
Notes: Averages were calculated using detected values only.
Exposure doses were calculated using 365 days/year for EF in the formula described in the Deriving exposure doses section of this appendix: (Conc. x IR x EF x ED) / (BW x AT).
No adverse health effects were reported from exposure to 0.57-27 mg/kg/day.
Cancer health effects were reported from exposure to 27 to 371 mg/kg/day.
ND = not detected
NS = not sampled
Table D-13. Blood Lead Levels According to Location
| Location | Fish | Shellfish | ||
|
Average
Concentration (ppm) |
Estimated Blood Lead Level (mg/dl) |
Average Concentration (ppm) |
Estimated Blood Lead Level (mg/dl) | |
| 1 - North LIA | 1.06 | 0.25 | ND | ND |
| 2 - South LIA | 0.23 | 0.06 | 0.27 | 0.06 |
| 3 - Esperanza | 0.21 | 0.05 | 0.18 | 0.04 |
| 4 - Isabel Segunda | 0.17 | 0.04 | NS | NS |
| 5 - Fish Market | 0.24 | 0.06 | 0.20 | 0.05 |
| 6 - West Vieques | ND | ND | ND | ND |
| All Locations | 0.27 | 0.06 | 0.25 | 0.06 |
Notes: Averages were calculated using detected values only.
Blood lead levels were calculated by multiplying the concentration by a media-specific slope factor (0.24 mg/dl per ppm) as described in the Using other methods to evaluate potential health hazards section of this appendix.
CDC's blood lead level of concern is 10 mg/dl.
ND = not detected
NS = not sampled
Next Section Table of Contents