PUBLIC HEALTH ASSESSMENT
U.S. DEFENSE GENERAL SUPPLY CENTER
RICHMOND, CHESTERFIELD COUNTY, VIRGINIA
Table 1: 1990 Census Data for DGSC Area
| Block Group 1 | Block Group 2 | Block Group 3 | |
|---|---|---|---|
| Total persons | 1,231 | 213 | 142 |
| % Male | 33.3 | 46.0 | 63.4 |
| % Female | 66.7 | 54.0 | 36.6 |
| % White | 51.7 | 94.4 | 69.7 |
| % Black | 47.3 | 4.2 | 26.1 |
| % Other races | 1.0 | 1.4 | 4.2 |
| % Younger than 10 | 44.9 | 9.4 | 21.8 |
| % Age 65 and over | 2.4 | 15.5 | 2.1 |
| Households* | 480 | 100 | 33 |
| Persons per household | 2.56 | 2.13 | 3.03 |
| % Owner occupied | 6.2 | 58.0 | 6.1 |
| % Renter occupied | 93.8 | 42.0 | 93.9 |
| Median value of owner- occupied units | $55,000 | $49,400 | $50,000 |
| Median monthly rent for renter- occupied units | $351 | $335 | $510 |
*= A household is defined as an occupied housing unit but doesnot include group quarters such as military barracks,prisons, and college dormitories.
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) |
|---|---|---|
| Groundwater | ||
| 1,1-Dichloroethylene | ||
| Tetrachloroethylene | ||
| Trichloroethylene |
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
*BDL= Below Detection Limit
a= Calculated from the Cancer Slope Factor
b= Maximum Contaminant Level Goal
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) |
|---|---|---|
| Benzene | ||
| Chlorobenzene | ||
| 1,2-Dichloroethane | ||
| 1,1-Dichloroethylene | ||
| T-1,2-Dichloroethylene | ||
| Tetrachloroethylene | ||
| Trichloroethylene | ||
| Vinyl Chloride | ||
| Benzo(a)anthracene | ||
| Benzo(k)fluoranthene | ||
| Chrysene |
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
*BDL= Below Detection Limit
**NT= Analysis for chemical not performed for all samples
a= Maximum Contaminant Level Goal
b= Calculated from the Reference Dose for ingestion by a child
c= Calculated from the Cancer Slope Factor
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) | ||
|---|---|---|---|---|
| Groundwater | Surface Water | |||
| Inside NGA* | Outside NGA | |||
| Arsenic | ||||
| Beryllium | ||||
| Lead | ||||
| Nickel | ||||
| Benzene | ||||
| 1,2-Dichloroethane | ||||
| 1,1-Dichloroethylene | ||||
| T-1,2-Dichloroethylene | ||||
| 1,2-Dichloropropane | ||||
| Tetrachloroethylene | ||||
| Trichloroethylene | ||||
| PAHs Chrysene | ||||
| Indeno(1,2,3)Pyrene | ||||
Reference: (Dames and Moore 1989b, CH2M Hill 1991)
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
| *NGA= National Guard Area **NT= Analysis for chemical not performed for samples ***BDL= Below Detection Limit ****NI= No information on the chemical for the medium | a= Ambient Water Quality Criteria--surface water b= Maximum Contaminant Level Goal--groundwater c= Calculated from the Cancer Slope Factor--groundwater |
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) | |||||||
|---|---|---|---|---|---|---|---|---|---|
| Groundwater | Soils | Soil Gas | |||||||
| 1982 | 1985 | 1987 | 1988 | Surface | Subsurface | October | November | ||
| Arsenic | 10,000 | 21,000 | |||||||
| Beryllium | |||||||||
| Chromium (hexavalent) | 20,000 | 19,000 | |||||||
| Lead | 102,000 | 52,000 | |||||||
| Carbon Tetrachloride | 2,600 | ||||||||
| 1,1-Dichloroethylene | 18,000 | 5,200 | 6,500 | 530+ | 245+ | ||||
| Methylene Chloride | 781,000 | 3,700 | 53,000 | ||||||
| Tetrachloroethylene | 21,000 | 19,000 | 1,500 | 16,000 | 130,000 | 15 | 2.4 | ||
| 1,1,1-Trichloroethane | 154,000 | 78,000 | 52,000 | 7,300 | |||||
| Trichloroethylene | 154,000 | 110,000 | 3,400 | 8,700 | 76,000 | 31 | 14 | ||
| Chlordane | 3,200 | ||||||||
Reference: (Dames and Moore 1989c)
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
*NT= Analysis for chemical not performed on all samples; **NI= No information on the chemical in the medium; ***B= Chemical present in all blanks
+= Chemical may have been 1,1-Dichloroethane; instrument cannot distinguish; @BDL= Below Detection Limit
a= Maximum Contaminant Level Goal--groundwater; b= Environmental Media Evaluation Guide--drinking water; c= Calculated from the Cancer Slope Factor--soil
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) | |
|---|---|---|---|
| 1987 | 1988 | Maximum Contaminant Level Goal | |
| Arsenic | |||
| Lead | |||
| 1,2-Dichloroethane | |||
| T-1,2-Dichloroethylene | |||
| Tetrachloroethylene | |||
| Trichloroethylene | |||
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
*NT= Analysis for chemical not performed for samples
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) |
|---|---|---|
| Total Lead | ||
| Total Beryllium | ||
| Total Chromium |
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
a= Maximum Contaminant Level--groundwater
b= Cancer Risk Evaluation Guide--groundwater
c= Reference Dose Media Evaluation Guide for children--groundwater
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) |
|---|---|---|
| 1,1,2-Trichloroethane | ||
| Tetrachloroethene | ||
| Trichloroethene | ||
| Vinyl Chloride | ||
| Trans-1,2-Dichloroethene | ||
| Benzene | ||
| 1,2-Dichlorobenzene | ||
| 1,4-Dichlorobenzene | ||
| Total Lead | ||
| Total Chromium |
Reference: (Law Environmental, Inc. 1993)
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
a= Cancer Risk Evaluation Guide--groundwater
b= Maximum Contaminant Level--groundwater
c= Reference Dose Media Evaluation Guide for children--groundwater
A= Estimated concentration due to the dilution factor being greater than 10x.
B= Estimated concentration; concentration detected in the samples exceeded the calibration range of the instrument. Other samples had concentrationsbelow the detection limit.
| Chemical | Concentration Ranges (ppb) | Comparison Values (ppb) |
|---|---|---|
| Benzene | ||
| 1,2-Dichloroethane | ||
| 1,1-Dichloroethylene | ||
| Tetrachloroethylene | ||
| 1,1,1-Trichloroethane | ||
| Trichloroethylene |
Reference: (Chesterfield Health District 1987)
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
a= Maximum Contaminant Level Goal--groundwater
b= Calculated from the Cancer Slope Factor--ingestion
| Chemical | Contaminant Ranges (ppb) | Comparison Values (ppb) |
|---|---|---|
| Ambient Water Quality Criteria | ||
| Tetrachloroethylene | ||
| Trichloroethylene |
Reference: (Dames and Moore 1989c)
Refer to the Beginning of the Environmental Contamination and Other Hazards section for a description of how contaminants of concern are selected.
*BDL= Below Detection Level
**J= Laboratory Estimated Value
APPENDIX B. COMPARISON VALUES, HEALTH GUIDELINES,
AND QUANTITATIVE UNITS
COMPARISON VALUES, HEALTH GUIDELINES, AND QUANTITATIVE UNITS
Comparison values for ATSDR public health assessments arecontaminant concentrations in specific media that are used as anaid to select contaminants for further evaluation. Those valuesusually appear in the Environmental Contamination and OtherHazards and the Public Health Implications section of thisdocument. Health guidelines, which usually appear in the PublicHealth Implications sections of this public health assessment,provide concentrations used to estimate a dose at which healtheffects might or might not be observed. Quantitative unitsexpress the amount of contaminant that has been detected inspecific media. Those units are usually first discussed in theEnvironmental Contamination and Other Hazards section; they aredescribed below.
| * AWQC | = Ambient Water Quality Criteria |
|---|---|
| * CREG | = Cancer Risk Evaluation Guides |
| * CSF | = Cancer Slope Factor |
| * EMEG | = Environmental Media Evaluation Guides |
| * LTHA | = Lifetime Health Advisory |
| * MCL | = Maximum Contaminant Level |
| * MCLG | = Maximum Contaminants Level Goal |
| * MRL | = Minimal Risk Level |
| * LOAEL | = Lowest Observed Adverse Effect Level |
| * NOAEL | = No Observed Adverse Effect Level |
| * RfC | = Reference Concentration |
| * RfD | = Reference Dose |
| * RMEG | = Reference Dose Media Evaluation Guide |
| Quantitative Units | |
| * ppm | = parts per million, (milligrams per liter, mg/L of water) |
| * ppb | = parts per billion, (micrograms per liter, µg/L water) |
| * mg/kg | = milligrams per kilogram (mg/kg; soil, sediment, or solid) |
| * µg/kg | = micrograms per kilogram (µg/kg soil; sediment, or solid) |
| * kg | = kilogram |
| * mg | = milligram |
| * µg | = microgram |
| * L | = liter |
Definition of Comparison Values and Health Guidelines
| AWQC | Ambient Water Quality Criteria are the recommended maximumpermissible pollutant concentrations protective of aquaticorganisms. They are federally enforceable. |
|---|---|
| CREG | Cancer Risk Evaluation Guides are derived by ATSDR fromthe EPA Cancer Slope Factor. They represent an estimatedconcentration in water, soil, or air that would beexpected to cause no more than one excess cancer in amillion (10E-6) persons exposed over a lifetime. |
| CSF | A Cancer Slope Factor is usually, but not always, the upper 95th percentile confidence limit of the slope for the dose-response curve. A CSF is developed for a probable or likely carcinogen and is expressed as (mg/kg/day)-1. When data permit, slope factors listed in IRIS are based on absorbed doses, although many of them are based on administered doses. |
| EMEG | Environmental Media Evaluation Guides are derived by ATSDRfrom ATSDR's Minimal Risk Levels (MRLs) and factor in bodyweight and ingestion rates. An EMEG is the concentrationof a particular contaminant in water, soil, or air atwhich daily human exposure is unlikely to result inadverse noncarcinogenic effects. |
| LTHA | A Lifetime Health Advisory represents contaminantconcentrations that EPA considers protective ofnoncarcinogenic health effects during a lifetime (70years) of exposure. Drinking water concentrations aredeveloped to predict acceptable exposure levels for bothadults and children when data on a NOAEL or LOAEL existfrom animal or human studies. LTHAs are not enforceablestandards. |
| MCL | Maximum Contaminant Levels represent contaminantconcentrations that EPA deems protective of public health(considering the availability and economics of watertreatment technology) over a lifetime (70 years) at anexposure rate of 2 liters of water per day. MCLs areenforceable standards. |
| MCLG | Maximum Contaminants Level Goal is a proposed,nonenforceable drinking water health goal recommended byEPA and set at a level at which no known or anticipatedadverse human health effects are expected to occur. |
| MRL | A Minimal Risk Level is an estimate of daily humanexposure to a chemical that is likely to be without anappreciable risk of adverse noncancerous effects over aspecified duration of exposure. MRLs are based on humanand animal studies and are reported for acute (< 14 days),intermediate (15-364 days), and chronic (> 365 days)exposures. MRLs are published in ATSDR ToxicologicalProfiles for specific chemicals. |
| LOAEL | Lowest Observed Adverse Effect Level is the lowestexposure level at which there are statistically orbiologically significant increases in frequency orseverity of adverse health effects between the exposedpopulation and its appropriate control group. LOAELs maybe used to estimate a dose at which people are notexpected to develop adverse health effects. LOAELs arepublished in ATSDR Toxicological Profiles for specificchemicals. |
| NOAEL | A No Observed Adverse Effect Level is an exposure level atwhich there are no statistically or biologicallysignificant increases in frequency or severity of adversehealth effects between the exposed population and itsappropriate control group. NOAELs may be used to estimatea dose at which people are not expected to develop adversehealth effects. NOAELs are published in ATSDRToxicological Profiles for specific chemicals. |
| RfC | EPA's Reference Concentration is an estimate of the dailyinhalation exposure to a contaminant (including sensitivesubpopulations) that is unlikely to cause noncanceroushealth effects during a lifetime exposure (chronic RfC) orduring a limited time interval (subchronic RfC). |
| RfD | EPA's Reference Dose is an estimate of the daily oralexposure to a contaminant (including sensitive subgroups)that is unlikely to cause noncancerous health effectsduring a lifetime exposure (chronic RfD) or during alimited time interval (subchronic RfD). |
| RMEG | Reference Dose Media Evaluation Guides are derived byATSDR from EPA's Reference Dose (RfD) and factor in bodyweight and ingestion rates. An RMEG is the concentrationof a particular contaminant in water, soil, or air atwhich daily human exposure is unlikely to result inadverse noncarcinogenic effects. |


