HEALTH CONSULTATION
FORMER RALLY'S RESTAURANT AND BRIARCLIFF STATION
ATLANTA, DEKALB COUNTY, GEORGIA
TABLE 1: SOIL VOLATILE ORGANIC SURVEY
ANALYTICAL SUMMARY*
BRIARCLIFF STATION SITE
| Sample Identification/ Sample Depth |
Constituents Detected Using EPA Analytical Method 8240 ppb | |
| Tetrachloroethene Detection Limit - 5 ppb) |
Acetone (Detection Limit = 50 ppb) |
|
| HA-01/20" | <5 | <50 |
| HA-01/78" | <5 | <50 |
| HA-02/9" | 29 | <50 |
| HA-03/23" | 6 | <50 |
| HA-03/27" | 14 | <50 |
| HA-04/12" | 41 | <50 |
| HA-04/76" | <5 | <50 |
| HA-06/120" | <5 | <50 |
| HA-07/24" | 6000J | <250** |
| HA-08/46" | 2630J | <250 |
| SB-01/18-20" | <5 | <50 |
| Field Blank | <5 | 111 |
| Equipment Blank | <5 | 116 |
ppb: parts per billion
HA: Sample taken with hand auger
J: Estimated concentration due to multiple dilution
SB: Sample taken from hollow stream auger boring
* Source: Professional Service Industries, Inc., Contamination Assessment, 11/94.
** Detection limit increased due to multiple dilution
TABLE 2: SOIL ANALYTICAL SUMMARY*
BRIARCLIFF STATION SITE
| LABORATORY SCREENING RESULTS for the AUGUST 23, 1994 SAMPLING EVENT | |
|
Sample Identification |
Tetrachloroethene ug/L |
|
1 |
17 |
|
2 |
109 |
| 3 | 11 |
| 4 | 154 |
| 5 | 120 |
| 6 | 99 |
| 7 | 137 |
| 8 | 72 |
| 9 | 285 |
| 10 | 19,937 |
ug/L: micrograms per liter
* Source: Professional Service Industries, Inc., Contamination Assessment, 11/94.
TABLE 3. GROUNDWATER ANALYTICAL SUMMARY*
|
Sample Identification |
||||||||||||
|
Former Rally's Restaurant |
Briarcliff Station |
School Board Property |
||||||||||
| Contaminant (ppm) | MW-01 | MW-02 | MW-03 | MW-04 | MW-05 | MW-06 | MW-06D** | MW-07 | MW-015 | MW-17 | MW-18 | MW-19 |
| Tetrachloroethane | nd | 0.153 | 0.499 | 0.010 | nd | 0.019 | 0.017 | 0.054 | 0.013 | nd | nd | nd |
| Lead | 0.107 | nd | nd | nd | 0.075 | nd | nd | nd | nd | 0.010 | nd | nd |
| 1,2-dichloroethane | 0.056 | nd | nd | nd | 1.15 | nd | nd | nd | nd | nd | nd | nd |
| Total BTEX | 3.149 | nd | nd | nd | 21.200 | 0.032 | 0.046 | nd | nd | nd | 4.099 | 0.178 |
ppm: parts per million
MW: Monitoring Well
BTEX: volatile petroleum constituents: Benzene, Toluene, Ethylbenzene, and Xylene
nd: not detected
* Source: Professional Service Industries, Inc., Contamination assessment, 11/94.
** Duplicate sample collected
TABLE 4. MAXIMUM SOIL CONCENTRATIONS AND SOIL COMPARISON VALUES
| Contaminant | Maximum Concentration (ppm) |
Comparison Values* | Estimated Dose and MRL** (mg/kg/day) |
|
| Concentration (ppm) |
Reference | |||
| Tetrachloroethene |
Pica Child: 20.0 |
Intermediate RMEG " " CREG |
Pica Child: 0.00012 | |
ppm: parts per million
mg/kg: milligrams per kilogram
EMEG: Environmental Media Evaluation Guide
RMEG: Reference Dose Media Evaluation Guide
CREG: Cancer Risk Evaluation Guide (1x10-6 excess cancer risk)
MRL: Minimal Risk Level
NA: Not Analyzed
* Source: ATSDR, Soil Comparison Values
** Source: ATSDR, Health Guidelines Comparison Values
Comparison Values
Comparison values are contaminant concentrations that are found in specific media and that are used to select contaminants for further evaluation. The values are derived from dose estimates at which health effects are not expected to be observed. Comparison values are listed and described below.
Cancer Risk Evaluation Guides (CREGs) are estimated contaminant concentrations that would be expected to cause no more than one excess cancer in one million (1 x 10') persons exposed over a lifetime. CREGs are calculated from EPAs cancer slope factors, which indicate the relative potency of a carcinogenic chemical.
Environmental Media Evaluation Guides (EMEGs) are based on ATSDR minimal risk levels and factor in body weight and ingestion rates. Reference Dose Media Evaluation Guides are the same as EMEGs only they are based on EPA reference doses (RfDs).
A Minimal Risk Level (MRL) is an estimate of daily human exposure to a chemical (in mg/kg/day) that is likely to be without an appreciable risk of deleterious effects (noncarcinogenic) over a specified duration of exposure. MRLs are based on human and animal studies and are reported for acute (14 days), intermediate (15-364 days), and chronic (365 days) exposures. MRLs are published in ATSDR Toxicological Profiles for specific chemicals.

Figure 2. Map of Sites and Assessment Area




