HomeMy WebLinkAboutNCD986175644_19960214_Davis Park Road TCE Site_SERB HRS_HRS Document Package-OCRI
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State of North Carolina
Department of Environment,
Health and Natural Resources
Division of Solid Waste Management
James B. Hunt, Jr., Governor
Jonathan B, Howes, Secretary
William L Meyer, Director
Ms. Cindy Gurley
NC CERCLA Project Officer
EPA Region IV Waste Division
345 Courtland Street, NE
Atlanta, Georgia 30365
February 14, 1996
AVA
DEHNR
I RE: Davis Park Road TCE Site
NCD 986 175 644
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Gastonia, Gaston County, North Carolina
HRS Documentation Package
Dear Ms. Gurley:
Please find enclosed the HRS Documentation Package for the subjeG't site. The
preliminary HRS score calculated here is 34.1. The documents enclosed here for your review are
listed below:
•
•
•
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Narrative (Site) Summary •
PREScore scoresheets and copy on disk
HRS Documentation Records including a List of References
Complete copies of documents referenced in the HRS Documentation Records
(except the HRS Final Rule, SCDM, and Expanded Site Inspection Report)
NPL Characteristics Data Collection Form
If you have any questions, please contact me at (919) 733-2801.
HZ
enclosures
P.O. Box 27687,
Roleigh, North Carolina 27611-7687
Voice 919-733-4996
Sincerely,
'},?-_.-r-,).--::-
Harry Zinn
Environmental Engineer
Federal Contracts Branch
NC Superfund Section
f#MJdlj, $£41il
FAX 919-715-3605
An Equal Opportunity Affirmative Action Employer
50% recycled/10% post-consumer paper
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January 29, 1996
Ms. Cindy Gurley
NC CERCLA Project Officer
EPA Region IV Waste Division
345 Courtland Street, NE
Atlanta, Georgia 30365
RE: Davis Park Road TCE Site
NCO 986 175 644
Gastonia, Gaston County, North Carolina
HRS Documentation Package
Dear Ms. Gurley:
Please find enclosed the HRS Documentation Package for the subject site. The
preliminary HRS score calculated here is 34.1. The docwnents enclosed here for your review
are listed below:
• Narrative (Site) Swnmary
• PREScore scoresheets and copy on disk
• HRS Documentation Records including a List of References
•
•
Complete copies of documents referenced in the HRS Docwnentation Records
( except the HRS Final Rule, SCDtvf, and Expanded Site Inspection Report)
NPLCharacteristics Data Collection Fonn
If you have any questions, please contact me at (919) 733-2801.
HZ
enclosures
Sincerely,
?/~;;.-:.-..
Harry Zinn
Environmental Engineer
Federal Contracts Branch
NC Superfund Section
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STATE OF
NORTH CAROLINA
Department of Environment, Health,
and Natural Resources
Division of Solid Waste Management
Superfund Section
NARRATIVE SITE SUMMARY
Davis Park Road TCE Site
NCD 986 175 644
Gastonia, Gaston County, North Carolina
HRS Documentation Package
February 1996
Harry Zinn
Environmental Engineer
Federal Contracts Branch
NCSuperfund Section
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NARRATIVE SITE SUMMARY
Davis Park Road TCE Site
NCD 986 175 644
Gastonia, Gaston County, NC
The Davis Park Road TCE Site (DPR) is located on Davis Park Road between Hudson
Boulevard and Dogwood Avenue west of the city of Gastonia within the Gastonia Extra
Territorial Jurisdiction (ETJ) area. The site consists of an area of contaminated soil behind the Moore's Transmission and Auto Repair Shop (Moore's). The site can be found on the Gastonia
South, North Carolina USGS 7.5' Quadrangle Map at latitude 35· 13' 56" N and 81 ° 13' 08" ; W.
Prior to 1960, the site was owned by Mr. John Birch of Gastonia, who operated a service
station on-site. Mr. Carl Bell, 2916 Burnt Mill Road, Charlotte, purchased the property in about 1960. During the time period from 1960 to 1979 a service station was operated on the premises; however, the identity of the actual operator is unclear. In 1979 or 1980, he leased the property
to Mr. Roy Moore, who currently operates a transmission rebuild and repair facility on-site. The property is now part of Mr. Bells estate. ·
Several samples were collected from soils behind the Moore's operation close to a drain
line which exits the rear of the building. These soils were highly contaminated with PCE and TCE. The drain line was installed when Acme Petroleum installed service bays in the shop
portion of the service station. A holding tank was to be installed, but, when bedrock was
encountered at 2-3 feet, the tank was not installed. Based on this information, the North
Carolina Superfund Section believes discharges from the drain line have contaminated the soils
and subsequently the groundwater behind the Moore's operation. The area of soils
contamination has not been fully delineated; however, sampling has shown that the area is approximately 0.6 square foot and the area of stained soils appears to be approximately 5 square
feet.
In March of 1990 during routine sampling of the community well at the Cedar Oak Park
Subdivision, and again in April 1990, high levels of trichloroethylene (TCE) and
tetrachloroethylene (PCE)were detected in the groundwater. During follow-up sampling by the Gaston County Health Department (GCH), three other private residential wells were also found to be contaminated. The North Carolina Division of Environmental Management (DEM)
performed extensive sampling of the private wells in the vicinity of the site from May 1990 to August 1992.
Most of the domestic water supplies, industrial supplies, and several municipal supplies
in Gaston County are obtained from wells. Dug wells, usually found in older, rural areas, derive their water from the saprolite which is the weathered and disintegrated zone between the soil and
the unweathered bedrock. Drilled wells, used for higher yields for industry and municipal use, obtain their water from either granite or schist formations. According to Mr. Mark Durway, the
former hydrogeologist for the Gaston County Health Department, the saprolite and the fractun;d
bedrock act as a single hydrologic unit.
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PREScore 4.0
NPL Characteristics Data Collection Form
Record Information
l. Site Name: Davis Park Road TCE Site
(as entered in CERCLIS)
2. Site CERCLIS Number: NCD986175644
3. Site Reviewer: H. Zinn
4. Date: 02/14/96
5. Site Location: Gastonia/Gaston County, North Carolina
(City/County,State)
6. Congressional District: 12
7. Site Coordinates: Single
Latitude: 35°15'56.0 11 Longitude: 081°13'08.0"
Site Description
I l. Setting: Suburban
2. Current Owner: Private -Industrial II 3. Current Site Status: Inactive
4. Years of Operation: Inactive Site,from and to dates: 1960 to Present I 5. How Initially Identified: Other -Contaminated Community Well
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6. Entity Responsible for Waste Generation:
Retail Activities
7. Site Activities/Waste Deposition:
-Illegal Dumping
Waste Description
8. Wastes Deposited or Detected Onsite:
-Solvents
-Oily Waste
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PREScore 4.0
NPL Characteristics Data Collection Form
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Response Actions
9. Response/Removal Actions:
-Drinking Water Well Has Been Closed
-Alternative Water Supply Provided
RCRA Information
10. For All Active Facilities, RCRA Site Status:
-Not Applicable
Demographic Information
11. Workers Present Onsite: Yes
12. Distance to Nearest Non-Worker Individual: > 10
13. Residential Population Within 1 Mile: unknown
14. Residential Population Within 4 Miles: Unknown
Water Use Information
• 15. Local Drinking Water Supply Source:
Feet -1/4 Mile
I -Ground Water (within 4 mile distance limit)
16. Total Population Served by Local Drinking Water Supply Source:
II 17. Drinking Water Supply System Type for Local Drinking ■ Water Supply Sources:
-Municipal (Services over 25 People) -Private
18. Surface Water Adjacent to/Draining Site: II -Stream
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12070.0
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PREScore 4.0
HRS DOCUMENTATION RECORD
1. Site Name: Davis Park Road TCE Site
(as entered in CERCLIS)
2. Site CERCLIS Number: NCD986175644
3. Site Reviewer: H. Zinn
4. Date: 02/14/96
5. Site Location: Gastonia/Gaston County, North Carolina (City/County,State)
6. Congressional District: 12
7. Site Coordinates: Single
Latitude: 35°15'56.0" Longitude: 081°13'08.0"
Score
Ground Water Migration Pathway Score (Sgw) 68.20
surface Water Migration Pathway Score (Ssw) 0.00
Soil Exposure Pathway Score (Ss) 0.00
Air Migration Pathway Score (Sa) 0.00
Site Score 34.10
NOTE
Site names, and references to specific parcels or properties, are provided for general identification purposes only. Knowledge regarding the extent of sites will be refined as more information is developed during the RI/FS and even during implementation of the remedy.
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PREScore 4.0 GROUND WATER MIGRATION PATHWAY SCORESHEET
GROUND WATER MIGRATION PATHWAY
Factor Categories & Factors Maximum
Value
Likelihood of Release to an Aquifer Aquifer: Saprolite/Bedrock
1. Observed Release 550 2. Potential to Release
2a. Containment 10 2b. Net Precipitation 10 2c. Depth to Aquifer 5 2d. Travel Time 35 2e. Potential to Release
[lines 2a (2b+2c+2d) J 500 3. Likelihood of Release 550
Waste Characteristics
4. Toxicity/Mobility * 5. Hazardous Waste Quantity * 6. Waste Characteristics 100
Targets
7. Nearest Well 50 8. Population
Ba. Level I Concentrations ** Bb. Level II Concentrations ** Be. Potential Contamination ** Bd. Population (lines aa+Bb+Bc) ** 9. Resources 5 10. Wellhead Protection Area 20 11. Targets (lines 7+8d+9+10) .. ** 12. Targets (including overlaying aquifers) ** 13. Aquifer Score 100
GROUND WATER MIGRATION PATHWAY SCORE (Sgw) 100
* Maximum value applies to waste characteristics category. ** Maximum value not applicable.
Value
Assigned
550
10
6
3
25
340
550
l.00E+02
100
10
5.00E+0l
7. 80E+02
0.00E+00
l.93E+02
9.73E+02
0.00E+00
0.00E+00
l.02E+03
l.02E+03
68.20
68.20
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PREScore 4.0 SURFACE WATER OVERLAND/FLOOD MIGRATION COMPONENT SCORESHEET
u 1. WASTESTREAM QUANTITY SUMMARY TABLE, SOURCE, Contaminated Soils
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a.
b.
c.
d.
e.
f.
Wastestream ID
Hazardous Constituent Quantity (C) ( lbs . )
Data Complete?
Hazardous Wastestream Quantity (W) (lbs.)
Data Complete?
Wastestream Quantity Value (W/5, 000)
0.00
NO
0.00
NO
0.00E+00
Page, S
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PREScore 4.0 SURFACE WATER OVERLAND/FLOOD MIGRATION COMPONENT SCORESHEET
2. SOURCE HAZARDOUS WASTE QUANTITY FACTOR TABLE
a. Source ID Contaminated Soils
b. Source Type Contaminated Soil
C. Secondary Source Type N.A.
d. Source Vol. (yd3/gal) I Source Area (ft2) 0.00 I
e. Source Volume/Area Value 2.06E-05
f. Source Hazardous Constituent Quantity O.OOE+OO (HCQ) Value (sum of lb)
g. Data Complete? NO
h. Source Hazardous Wastestream Quantity O.OOE+OO (WSQ) Value (sum of lf)
i. Data Complete?· NO
k. Source Hazardous Waste Quantity (HWQ) 2.06E-05 Value (2e, 2f, or 2h)
Source Depth Liquid Concent. Units Hazardous Substances (feet)
Dichloroethylene, trans-1,2-< 2 YES 2.6E-01 ppm Toluene < 2 YES 2.3E-01 ppm Trichloroethylene < 2 YES 2.0E-02 ppm Xylene, m-< 2 YES 3:3E-01 ppm Xylene, o-< 2 YES 3.3E-Ol ppm Xylene, p-< 2 YES 3.3E-01 ppm
Documentation for Source Type:
Contaminated soils are located behind the Moore facility.
References: Figure 2, Table 1
Documentation for Source Hazardous Substances:
0.70
Source samples were collected on January 25, 1994 following US EPA CLP protocol. Sample locations are shown on Figure 2. The analytical results for these samples are listed on Table 1.
References: 4, Figure 2, Table 1
Documentation for Source Area:
The area of contaminated soils enclosed within the samples calculates to 0.73 square feet. The intent at the ESI sampling event was to document.an area of contamination. These samples did not attempt to delineate the full extent of soil contamination.
References: 7
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PREScore 4.0
SURFACE WATER OVERLAND/FLOOD MIGRATION COMPONENT SCORESHEET
3. SITE HAZARDOUS WASTE QUANTITY SUMMARY
No. Source ID
1 Contaminated Soils
Migration
Pathways
GW
Vol. or Area
Value (2e)
2.06E-05
Constituent or
Wastestream
Value (2f, 2h)
0.00E+00
Hazardous
Waste Qty.
Value (2k)
2.06E-05
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PREScore 4.0 SURFACE WATER OVERLAND/FLOOD MIGRATION COMPONENT SCORESHEET
4. PATHWAY HAZARDOUS WASTE QUANTITY AND WASTE CHARACTERISTICS SUMMARY TABLE
Migration Pathway Contaminant Values
Ground Water Toxicity/Mobility
SW: Overland Flow, DW Tox./Persistence
SW: Overland Flow, HFC Tox./Persis./Bioacc.
SW: Overland Flow, Env Etox./Persis./Bioacc.
SW: GW to SW, DW Tox./Persistence
SW: GW to SW, HFC Tox./Persis./Bioacc.
.
SW: GW to SW, Env Etox .'/Persis. /Bioacc.
Soil Exposure:Resident Toxicity
Soil Exposure: Nearby Toxicity
Air Toxicity/Mobility
* Hazardous Waste Quantity Factor Values ** Waste Characteristics Factor Category Values
Note: SW Surface Water
GW Ground Water
DW = Drinking Water Threat -HFC Human Food Chain Threat
.Env = Environmental Threat
l.00E+02
0.00E+00
0.00E+00
0.00E+00
4.00E+0l
2.00E+03
2.00E+04
1.00E+02
0.00E+00
0.00E+00
HWQVs* WCVs**
100 10
0 0
0 0
0 0
10 3
10 10
10 18
10 6
0 0
0 0
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PREScore 4.0
GROUND WATER PATHWAY AQUIFER SUMMARY
No. Aquifer ID
1 Saprolite/Bedrock
Containment
Type Overlaying
No.
Non K o
Inter-
connected
with
0
No. Source ID HWQ Value Containment Value
1 Contaminated Soils 2.06E-05 10
=====================================================
Containment Factor 10
Likelihood Targets
of Release
550 l.02E+03
Documentation for Ground Water Contain~ent, Source Contaminated Soils:
Contaminated private wells have documented the migration of contaminants from the site.
References: 6, pp. 10-19
Net Precipitation
Net Precipitation (inches) N.A.
I Documentation for Net Precipitation:
Figure 3-2
I References: 1
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PREScore 4.0
GROUND WATER PATHWAY LIKELIHOOD OF RELEASE Saprolite/Bedrock AQUIFER
n Aquifer: Saprolite/Bedrock
Type of Aquifer: Non Karst n Overlaying Aquifer: 0
Interconnected with: 0
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Documentation for Saprolite/Bedrock Aquifer:
Saprolite is the weathered and disintegrated zone between soil and unweathered
bedrock. Wells in the Piedmont Physiographic Province obtain their water from
the saprolite and from fractures in the bedrock formations. According to Mark
Duraway, the saprolite and bedrock are a single hYdological unit.
References: 12, 13
OBSERVED RELEASE
No. Well ID
1 Corella Well
2 May Well
3 Tompkins Well
4 Cedar Oak Park
Well
Well Type
Drinking
Drinking
Drinking
Drinking
No. Hazardous Substance
1 Trichloroethylene
2 Trichloroethylene
3 Trichloroethylene
4 Tetrachloroethylene
4 Trichloroethylene
Distance
(miles) Level of Contamination
Water 0.030 Level I
Water 0.660 Level I
Water 0.080 Level I
Water 0.200 Level I
Concent. MCL Cancer RFD Units
1.0E+0l 5.0E+00 7.7E+00 0.0E+00 ppb
3.BE+0l 5.0E+00 7.7E+00 0.0E+00 ppb
1. lE+0l 5.0E+00 7.7E+00 0.0E+00 ppb
l.BE+0l 5.0E+00 1. 6E+00 3.7E+02 ppb
5.lE+0l 5.0E+00 7.7E+00 0.0E+00 ppb
=============================================================================
Observed Release Factor 550
D Documentation for Well Corella Well:
The well at the residence of Doris Corella was sampled on 1/25/94 according to
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US EPA CLP protocol. No well data was available and Mrs. Corella had no
knowledge of the well construction. Sample results, validated by the US EPA ESD,
indicate 10 ppb of trichloroethene in the well water. 3 people currently occupy
the Corella residence.
References: 5, 6, 9
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PREScore 4.0
GROUND WATER PATHWAY LIKELIHOOD OF RELEASE Saprolite/Bedrock AQUIFER
Documentation for Well May Well:
The well at the residence of Charles May, 2419 Davis Park Road, was sampled on
1/25/94 according to US EPA CLP protocol. Mr. May has stated that his well is
6" in diameter, 187' deep and about 12 years old. Sample results, validated by
the US EPA ESD, indicate 38 ppb of trichloroethene in the well water. 4 people
currently occupy the May residence.
References: 5, 6, 9
Documentation for Well Tompkins Well:
The well at the residence of Orlin Tompkins, 2425 Davis Park Road, was sampled
on 1/25/94 according to the US EPA CLP protocol. No well data was available and
Mr. Tompkins had no knowledge of the well construction. Sample results,
validated by the US EPA ESD, indicate 11 ppb of trichloroethene in the well
water. 2 people currently occupy the Tompkin~ residence.
References: 5, 6
Documentation for Well Cedar Oak Park:
The well at the Cedar Oak Park Subdivision was sampled on 1/25/94 according to
the US EPA CLP protocol. According to Mr. Cregg Bess the well is 6" in diameter,
cased to 71' deep, is a total of 150' deep and currently supplies 26 hook-ups.
Based on the 1990 US Census data of 2.64 persons per household for Gaston County,
a total of 68 persons are supplied by this well. Sample results, validated by
the US EPA ESD, indicate 18 ppb tetrachloroethene and 51 ppb trichloroethene.
References: 5, 6, 9
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PREScore 4.0
GROUND WATER PATHWAY LIKELIHOOD OF RELEASE Saprolite/Bedrock AQUIFER
POTENTIAL TO RELEASE
Containment
Containment Factor 10
Net Precipitation
Net Precipitation Factor 6
Depth to Aquifer
A. Depth of Hazardous Substances 1. 66 feet
Documentation for Depth of Hazardous Substances:
The top of the lowest source sample which was contaminated was at 20 11 bls.
References: s
B. Depth to Aquifer from Surface 45.00 feet
Documentation for Depth to Aquifer from Surface :
The water table was never encountered during the ESI sampling event. Most of the
well logs listed for the area southwest of Gastonia have recorded the water table
as 15 to 45 feet bls.
References: 12, pp. 56
C. Depth to Aquifer (B -A)
Depth to Aquifer Factor
Travel Time
Are All Layers Karst?
Thickness of Layer(s) with Lowest Conductivity
43.34
3
NO
35.00
Documentation for Thickness of Layers with Lowest Conductivity:
feet
feet
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PREScore 4.0 GROUND WATER PATHWAY LIKELIHOOD OF RELEASE Saprolite/Bedrock AQUIFER
The distance from ten feet below the land surface, since this is lower than the contaminated soils, to the water table at 45 feet is 35.0 feet. This material is a weathered bedrock material and would be most compatible to the sands listed on Table 3-6. This would give us a Hydraulic Conductivity of l.0EE-4.
References: 1, pp. 55, 57; 12, pp. 49, 56
Hydraulic Conductivity (cm/sec) l.0E-04
Documentation for Hydraulic Conductivity:
The weathered bedrock would be most similar to the sandy silts and sediments that are predominantly sand listed in Table 3-6.
References: 1, pp. 57
Travel Time Factor 25
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Potential to Release Factor 340
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D PREScore 4.0
GROUND WATER PATHWAY WASTE CHARACTERISTICS
D
, I Source: 1 Contaminated Soils
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Source Hazardous Waste Quantity Value: 0.00
Hazardous Substance
Dichloroethylene, trans-1,2-
Toluene
Trichloroethylene
Xylene, m-
Xylene, o-
Xylene, p-
Toxicity
Value
100
10
10
1
1
10
Mobility Toxicity/
Value Mobility
Value
1. 00E+00 l.00E+02
l.00E+00 l.00E+0l
1. 00E+00 l.00E+0l
l.00E+00 l.00E+00
l.00E+00 l.00E+00
l.00E+00 l.00E+0l
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PREScore 4.0
GROUND WATER PATHWAY WASTE CHARACTERISTICS
Hazardous Substances Found in an Observed Release
Well Observed Release Toxicity Mobility Toxicity/
No. Hazardous Substance Value Value Mobility
Value
1 Trichloroethylene 10 1.00E+00 1.00E+01
2 Trichloroethylene 10 1.00E+00 1.00E+01
3 Trichloroethylene 10 1.00E+00 1.00E+01
4 Tetrachloroethylene 100 1.00E+00 1.00E+02
4 Trichloroethylene 10 1.00E+00 1.00E+01
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PREScore 4.0
GROUND WATER PATHWAY TARGETS FOR AQUIFER S~prolite/Bedrock
Toxicity/Mobility Value from Source Hazardous Substances:
Toxicity/Mobility Value from Observed Release Hazardous Substances:
Toxicity/Mobility Factor:
Sum of Source Hazardous Waste Quantity Values:
Hazardous Waste Quantity Factor:
Waste Characteristics Factor Category:
l.00E+02
l. 00E+00
l.00E+02
2.06E-05
100
10
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PREScore 4.0 GROUND WATER PATHWAY TARGETS FOR AQUIFER Saprolite/Bedrock
Population by Well
Distance Level of No. Well ID Sample Type (miles) Contamination Population
1 Corella Well Drinking Water 0.030 Level I 3.00 2 May Well Drinking Water 0.660 Level I 4.00 3 Tompkins Well Drinking Water 0.080 Level I 2.00 4 Cedar Oak Park Drinking Water 0.200 Level I 69.00
Well
No. Hazardous Substance Concent. MCL Cancer RFD Units
1 Trichloroethylene l.0E+0l 5.0E+00 7.7E+00 0.0E+00 ppb 2 Trichloroethylene 3.8E+0l 5.0E+00 7.7E+00 0.0E+00 ppb 3 Trichloroethylene l.lE+0l 5.0E+00 7.7E+00 0.0E+00 ppb 4 Tetrachloroethylene 1. 8E+0l 5.0E+00 1. 6E+00 3.7E+02 ppb 4 Trichloroethylene 5.lE+0l 5.0E+00 7.7E+00 0.0E+00 ppb
Documentation for Well Corella Well:
The well at the residence of Doris Corella was sampled on 1/25/94 according to US EPA CLP protocol. No well data was available and Mrs. Corella had no knowledge of the well construction. Sample results, validated by the US EPA ESD, indicate 10 ppb of trichloroethene in the well water. 3 people currently occupy the Corella residence.
References: 5, 6, 9
Documentation for Well May Well:
The well at the residence of Charles May, 2419 Davis Park Road, was sampled on 1/25/94 according to US EPA CLP protocol. Mr. May has stated that his well is 6" in diameter, 187' deep and about 12 years old. Sample results, validated by the US EPA ESD, indicate 38 ppb of trichloroethene in the well water. 4 people currently occupy the May residence.
References: S, 6, 9
Documentation for Well Tompkins Well:
The well at the residence of Orlin Tompkins, 2425 Davis Park Road, was sampled on 1/25/94 according to the US EPA CLP protocol. No well data was available and Mr. Tompkins had no knowledge of the well construction. Sample results, validated by the US EPA ESD, indicate 11 ppb of trichloroethene in the well water. 2 people currently occupy the Tompkins residence.
References: 5, 6
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PREScore 4.0
GROUND WATER PATHWAY TARGETS FOR AQUIFER Saprolite/Bedrock
Documentation for Well Cedar Oak Park:
The well at the Cedar Oak Park Subdivision was sampled on 1/25/94 according to
the US EPA CLP protocol. According to Mr. Cregg Bess the well is 6" in diameter,
cased to 71' deep, is a total of 150' deep and currently supplies 26 hook-ups.
Based on the 1990 us. Census data of 2.64 persons per household for Gaston County,
a total of 68 persons are supplied by this well. Sample results, validated by
the US EPA ESD, indicate 18 ppb tetrachloroethene and 51 ppb trichloroethene.
References: 5, 6, 9
Level I Population Factor:
Level II Population Factor:
780.00
0.00
Page: 18
R
I PREScore 4.0
GROUND WATER PATHWAY TARGETS FOR AQUIFER Saprolite/Bedrock
II Potential Contamination by Distance Category
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Distance Category
(miles)
> 0 to 1/4
> 1/4 to 1/2
> 1/2 to l
> l to 2
> 2 to 3
> 3 to 4
Potential Contamination Factor:
Population
162.0
415.0
299.0
1952.0
5808.0
3357.0
Value
l.64E+0l
3.24E+0l
5.20E+00
2.94E+0l
6.78E+0l
4.17E+0l
193.000
Documentation for Target Population> Oto 1/4 mile Distance Category:
The total population utilizing groundwater as potable water within the 0-1/4 mile
area was determined to be 162. This number does not include the 77 people which
are listed as being on contaminated wells.
References: S; 10
Documentation for Target Population> 1/4 to 1/2 mile Distance Category:
References: 10
Nearest Well
Well: l Corella Well
Level of Contamination: Level I
Distance in miles: 0.03
Nearest Well Factor: 5.00E+0l
Documentation for Nearest Well:
The nearest contaminated private well is the Corella Well located 150 feet south
of the site.
References: Figure 2
Page: 19
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PREScore 4.0 GROUND WATER PATHWAY TARGETS FOR AQUIFER Saprolite/Bedrock
Resources
Resource Use: NO
Resource Factor: 0.00E+00
Documentation for Resources:
No resource use has been identified.
References:
Wellhead Protection Area
No wellhead protection area
Wellhead Protection Area Factor: 0.00E+00
Documentation for Wellhead Protection Area:
No wellhead protection areas exist in North Carolina.
References: 11
Page: 20
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HRS DOCUMENTATION RECORD--REVIEW COVER SHEET
Name of Site: Davis Park Road TCE Site
Contact Persons
Site Investigation:
Documentation Record:
Harry Zinn (Name)
Harry Zinn (Name)
Pathways. Components, or Threats Not Evaluated
919-733-2801
(Telephone)
919-733-2801
(Telephone)
Only the Groundwater Pathway was evaluated for this site. The groundwater to surface water interface and the surface water pathway were not evaluated based on the low toxicity/rrobility/bioaccumulation values of the contaminants and the distance (over 1/2 mile) to the site Probable Point of Entry. The soil exposure pathway was not evaluated based on the lack of targets. The air pathway wsa not evaluated based on the low number of targets in the area and the belief that no release to the air has occurred.
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HRS DOCUMENTATION RECORD
Name of Site: Davis Park Road TCE site
EPA Region:IV Date Prepared:01/29/96
Street Address of Site: 2703 Davis Park Road
County and State: Gaston, North Carolina
General Location in the State: Southcentral North Carolina
Topographic Map: Gastonia South, North Carolina
Latitude:35 13 56.0
Scores
Air Pathway
Ground Water Pathway Soil Exposure Pathway Surface Water Pathway
HRS SITE SCORE
l
Longitude:081 13 09.5
NA
68.20
NA
NA
34.10
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WORKSHEET FOR COMPUTING HRS SITE SCORE
1. Ground Water Migration Pathway Score (Sgw) (from Table 3-1, line 13)
2a. Surface Water Overland/Flood Migration Component (from Table 4-1, line 30)
2b. Ground Water to Surface Water Migration Component (from Table 4-25, line 28)
2c. Surface Water Migration Pathway Score (S_) Enter the larger of lines 2a and 2b as the pathway
3. Soil Exposure Pathway Score (S.) (from Table 5-1, line 22)
4. Air Migration Pathway Score (S.) (from Table 6-1, line 12)
6. HRS Site Score Divide the value on line 5 by 4 and take the square root
2
s
68.20
Not
Not
Not
score.
Not
Not
34.10
S'
4651.2
Evaluated
Evaluated
Evaluated
Evaluated
Evaluated
4651.2
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REFERENCES
Reference
Number Description of the Reference
1 U.S. Environmental Protection Agency, 1990 . Hazard Ranking System; Final Rule. 55 FR 51532, December 14, 1990.
2 U.S. Environmental Protection Agency, 1994. Superfund O:lemical
3
4
5
6
7
8
9
10
11
12
13
14
Data Matrix (SCDM) . Office of Solid Waste and Emergency Response. Directive 9345.1-13 Revised Semi-annually.
Latitude and Longitude Coordinate Worksheets from Guidance for Performing Preliminary Assessments Under CERCIA U.S. ·EPA Publication 9345. 0-0.lA September 1991 Appendix E
Zinn, Harry. 1994 memo to file RE: Field Notes from Sampling Trip on January 25, 1994. January 27.
Zinn, Harry. Field Log for Sampling Trip on January 25, 1994.
U.S. EPA Region IV Environmental Services Division Results of Purgable Organic Analysis; 94-0244 Davis Park Road TCE Site 3/15/94.
Sample Area Laycut Calculation Worksheet
John E. Matthews, Handbook of Bioremediation Ada, Oklahoma Pg. 206
Zinn, Harry. memo to file RE: Private Well Data for Davis Park Road TCE Site May 11, 1994
Zinn, Harry. 1996 memo to file RE: Groundwater Population for Davis Park Road TCE Site. January 24, 1996.
Stanley, Jeanette. 1996 memo to Superfund Section Staff RE: Update on Status of Wellhead Protection Programs in N.C. January 2, 1996.
N.C. Department of Conservation and Development, Bulletin No. 63 Geology and Ground Water in the Charlotte Area, North Carolina 1952 pgs 47-57
Zinn, Harry. 1993 memo to file RE: Hydrogeology of Gastonia Area, Davis Park Road TCE Site. December 23, 1993.
N.C. Superfund Section Expanded Site Inspection, May 1994
3
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SD-Oiaracterization and Containment
SOURCE DESCRIPTION
2.2 Source Characterization
Number of the source: 1
Name and description of the source: Contaminated Soils -located at the discharge end of a pipe originating in a service bay inside the Moore:' s Transmission Shop and terminating approximately 3 inches outside the rear of the shop (Ref. 4).
Location of the source, with reference to a map of the site: The contaminated soil area confirmed by sampling at the site is approximately 0.67 sq. ft. (Ref. 4; 7).
The pipe is located approximately 18 feet north of the southwest corner of the building along the west wall of the building (Ref. 5, pg. 2).
Containment
Gas release to air
NA
Particulate release to air NA
Release to ground water An observed release to the groundwater has been documented (Ref.6, pp. 10-15) .
Release via overland migration and/or flood NA
4
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2.4.1 Hazardous Substances
Hazardous substance
1,2-Dichloroethene (Total) Trichloroethylene
Toluene
Total Xylenes
SD-Hazardous Substances
Source No. : 1
Evidence
Sarrple 002-SB,003-SB,004-SB
Sarrple 002-SB,003-SB
Sarrple 002-SB,003-SB,004-SB
Sarrple 002-SB,003-SB,004-SB
5
Reference
6, HJ. 4-6
6, pp. 4,5
6, pp. 4-6 6, pp. 4-6
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SD-Hazardous Constituent Quantity Source No. : 1
2.4.2. Hazardous Waste Quantity
2.4.2.1.1. Hazardous Constituent Quantity
Hazardous Substance NA
Constituent
Quantity (pounds)
(Mass -S)
sum:
Reference
(pounds)
Hazardous Constituent Quantity Value (S) : NA
6
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2.4.2.1.2.
Hazardous
Wastestream
NA
SD-Hazardous Wastestream Quantity NA Source No.: 1
Hazardous Wastestream Quantity
Quantity
(pounds)
sum:
Reference
(pounds)
Hazardous Wastestream Quantity Value (W) :NA
7
0
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2.4.2.1.3. Volume
2.4.2.1.4. Area
SD-Volume Source No. : 1
Dimension of source (yd' or gallons) : NA
References(s):
8
Volume Assigned Value: NA
Area of source (ft'): 0.625
Reference(s): 4; 7
Area.Assigned Value: >0
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SD-Source Hazardous Waste Quantity Value >0
Source No.:· 1
2.4.2.1.5. Source Hazardous Waste Quantity Value
Source Hazardous Waste Quantity Value: >0
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Source
No.
1
SD-Surrmary
SITE SUMMARY OF SOURCE DESCRIPTIONS
Source Hazardous
Waste Quantity Value
Containment
>0
Ground
Water
10
10
Surface
Water
NA
Air
Gas Particulate
NA NA
U
GW-General
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3 • 0 GROUND WATER MrGRATION PATHWAY
3.0.l GENERAL CONSIDERATIONS
Aquifer/Stratum l (shallowest)
Aquifer/Stratum Name: Saprolite/Bedrock
Description: Most of the domestic water supplies in Gaston County are obtained by wells. Dug wells, usually found in older, rural areas, derive their water from the saprolite, which is the weathered and disintegrated zone between the soil and the unweathered bedrock. Drilled wells, used for higher yields for industry and municipal use, obtain their water from either granite or schist fonrations.
The saprolite and the bedrock act as a single hydrological unit in this area.
References: 12, pp. 49, 51; 13
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3 .1 LIKELIHOOD OF RELEASE
3.1.1 OBSERVED RELEASE
Aquifer Being Evaluated: Saprolite/Bedrock
Olemical Analysis:
Background Concentration
Sample ID Depth DP-001-PW 70 feet
GW-Observed Release
Date Reference 1-25-94 5, pp. 5
DP-001-PW is a grcundwater sample collected from the well of Mr. Godwin,at 2231 Davis Park Road. This well is located topographically upgradient from the site (Fig. 1).
Sample ID DP-001-PW
Hazardous
Substance
PCE
TCE
Contaminated Samples
Sample ID
DP-003-PW
DP-004-PW
DP-005-PW
DR-006-PW
Concentration
ND
ND
Depth
Not Known
187 Feet
Not Known 150 Feet
Sample
Quantitation
Limit
10 ug/1
10 ug/1
Date
1/25/94
1/25/94
1/25/94
1/25/94
Reference
6, pp. ,10
Reference
5, pp. 3
5, pp. 6
5, pp. 6
5, pp. 4
The aoove samples were collected from three private wells and a conmunity well located topographically downgradient, from the site, which have been shown by past sampling events to be contaminated with PCE and TCE (Ref. 14, Table 2-1) .
Sample ID DP-003-PW
DP-004-PW
DP-005-PW
DP-006-PW
Hazardous
Substance
TCE
TCE
TCE
PCE
TCE
-Level I Sa~les
Sample ID:
DP-003-PW
DP-004-PW
DP-005-PW
DP-006-PW
• Hazardous
Substance
TCE
TCE
TCE
PCE
TCE Reference for Benchmarks: 2
Concentration
10 ug/kg
38 ug/kg
11 ug/kg 18 ug/kg
51 ug/kg
Sample
Quantitation
Limit
10 ug/1
10 ug/1
10 ug/1
10 ug/1 10 ug/1
Hazardous Substance Concentration
10 ug/1
38 ug/1
11 ug/1.
18 ug/1
51 ug/1
12
Reference
6, pp. 12
6, pp. 13
6, pp. 14
6, pp. 15
Benchmark
MCL, CRSC
MCL, CRSC
MCL, CRSC
MCL, CRSC
MCL, CRSC
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GW-Observed Release
Attribution:
Soil sarrples around the drain pipe which exits the transmission shop are contaminated with TCE and its. degradation product 1,2-DCE (Ref. 6, pp. 3-6) . The private wells are contaminated with TCE and the farthest downgradient well, the corrmunity well, has a high level of TCE and a low level of PCE in it (Ref. 6, pp. 12-15). Since PCE degrades into TCE and 1,2-DCE, the transmission shop is suspected of being the origin of the groundwater contamination (Ref 8, pp. 206).
Hazardous Substances Released PCE (tetrachloroethylene)
TCE (trichloroethylene)
=======================================================================
Ground Water Observed Release Factor Value: 550
13
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3.2 WASTE CHARACTERISTICS
3.2.1 Toxicity/Mobility
Hazardous
Substance
cis 1,2-DCE
trans 1, 2-DCE Ethyl benzene
PCE
Toluene
TCE
Source
No.
1
1
1
1
1
1
Toxicity
Factor Value
100
100
10
100
10
10
Mobility
Factor Value
1
1
0.01
1
0.01
1
GW-Toxicity/Mobility
Toxicity/
Mobility
100
100
0.1
100
0.1
10
Ref.
2
2
2
2
2
2
========================================================================== Toxicity/Mobility Factor Value: 100
14
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0
0
GW-Hazardous Waste Quantity
3.2.2 Hazardous Waste Quantity
Source Hazardous Is source hazardous constituent quantity
data complete? (yes/no)
Waste Quantity Source Number Value (Section 2.4.2.1.5) 1 >0 no
Sum of Values: >0 Hazardous Waste Quantity Value= 100 based on Level I target concentrations(Ref. 1, pp. 27)
3.2.3 Waste Characteristics Factor Category Value
Toxicity/Mobility Factor Value X Hazardous Waste Quantity Factor Value: 10,000
' ==========================================================================
Hazardous Waste Quantity Factor Value: 100 Waste Characteristics Factor Category Value: 10
15
•::11 .~.1 II .
<!
-1.11 -:: II
1 '·
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3 .3 TARGETS
Distance
Well From Source ifer 1 0.030 S B 2 0.066 S/B 3 0.080 S/B 4 0.200 S/B
GW-Targets
Level I Level II Potential Contam. Contam. Contam.
YN YN YN Ref. y N N 6, pp. :12 y N N 6, pp. '13 y N N 6, pp. 14 y N N 6, pp. 15
16
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GW-Nearest Well
3.3.1 Nearest Well
Well: 1
Level of Contamination (I, II, or potential): I If potential contamination, distance from source in miles: NA
' ==-==-=============-=====-================================================
Nearest Well Factor Value: 50
17
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I 3.3.2 Population
3.3.2.1 Level of Contamination
3.3.2.2 Level I Concentrations
Level I Well
1
2
3
4
Population
3
4
2
69
GW-Level I Concentrations
Reference
5, pp. 7
5, pp .. 7
5 ,pp. 7
9; 10
========================================================================== Population Served by Level I Wells:78 Level I Concentrations Factor Value: 780
18
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GW-Level II Concentrations
3.3.2.3 Level II Concentrations
Level II Well Population Reference NA
==========================================================================
Level II Concentrations Factor Value: NA
19
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3.3.2.4 Potential Contamination
Distance
Category
0 -1/4 mi. 1/4 -1/2 mi.
1/2 -
1
mi.
1 -
2
mi.
2 -
3
mi.
3 -
4
mi.
Population
162
415
299
1952
5808
3357
Sum of
GW-Potential Contamination
Reference
10
10
10
10
10
10
Distance-Weighted
Distance-Weighted
Population Value
164
324
52
294
678
417 Population Values: 1929
Potential Contamination· Factor Value: 1929
20
I GW-Resources
I 3.3.3 RESOURCES
No Resource use of the groundwater has been identified.
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D
Resources Factor Value: O D
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GW-Wellhead Protection Area
3 .3 .4 WELLHEAD PROTECTION AREA
No Well Head Protection Program cu=ently is in place in North Carolina (Ref. 11) .
Wellhead Protection Area Factor Value: 0
22
:+ 'f
f ,, .. ,
! . ,, , __ .-·
f , •••
'.f-' .
·.i,."·,···
, ·.
'
f-
==-== ~~ --------n--~;=:=
-----------------===--=== ,.§ -==::: -::=_ .. ~-__ ...__ --------.... ,. _., ,,_ --~-~
---------~~
!:;') ::::
-·---_:=:,
Friday
December 14, 1990
Part II.
Enviror1rnentai
Protection Agency
40 CFR P:irt 300
Hazard Ranking System; Final Ru!e
. ------, ----
Reference 2
Handout -kG
SUPJ~llFUNJ) CJIEMIC1-\L DA1'A lY[Al'llIX
l\1larch 1993
' Reference 3
..
L,\';_' I-:l'UDE -A,j,':)_·' LC/JC! TUC2 .c.::,.I~CUL.l·.T .1.0!1 · ',•iO?.::sr:2:..:r. /2
TO'n'USHIP: !i/S RAEGS:
KAP DATE: S:SCTIOU:
1983 (CIRCLE OtJE}
COORDI/i,\T::::s FHOH. LOWr:R RIGHT (SOUT!~E>.ST) COR.HER OF 7.5' !-'.AP (attach phot.OCO?Y):
LONGITUDE: 5U_o ....Lll_' ~" LATITUDS: ]<; 0 Ol '
COORDI:t,'AT?.:S E'RO.u; LO',i"::H RIGHT ( SOUT:~EAST) CO?J'1ER OF 2. 5' Gi"lID CELL:
LOt1GITUDS: _KJ._0 11.. ' 3c)_
CALCULATIO!{S: LATITUDE (7.5' QUADRANGLE !-:1\?)
A) t{U~B2R OF ?.ULE?. GR.tc.DUATIONS ?ROM SATITUDE GRID LIN::: TO SITE RE? POINT: :J..(.j_
3) ~ULTI?L:' (,\) E':" 0.330!, TO COtrVE?,T TO sscorrns:
A:-: 0.330'/
C) EX?RESS IN l-':INUTES NiD sr:cot~DS (l'= 60''): , _M_ . --2:l_"
D) ,,OD TO STARTillG LATITUD2: ..:lI_o_il'_}Q_._Q_ ·• __ 1_'__2:i_.~;,_ =
CA..LCULi\TIO!~S: LONGITUDE ( 7. 5' QUi\DRAilGLE l-':.l\P)
,\) f'jU~3S?. o: P.UL?.:H GRJ..DUATIOtlS ~-HO:-': RIGHT LONGITUDE LINE TO SITS REF' ?OINT: lLL .·
B) MULTIPLY (A) BY 0. J~O•: TO COt,'VER'l' TO S?.:COND.'3:
A.:-:0.230!,
D) A.DD TO s-r;,..P.'!'Ih'G LONcr1uo:;: ~0 _l~'_J_Q_ o T _O_'~_-..}J_
I SFO: LOtlGITUD2: -~_J_0 _J_:',_._Q}l_._ji_" • L_-__________ _
:S--l0
j COOR.D!NATE..S o;: LOWE!\ PJGH"] -!i.•\t'iD COR.'<Er: OF
LATITUDE, 35_0 o7 '3a . !.OHGiTUDE, .1.!_·, 01
2-ll
' ' ~ DATE:
TO:
FROM:
RE:
:ranuary 27, 1994
File
Harry Zinn, Environmental Engineer
North Carolina DEHNR, Superfund Section
Field notes from Sampling Trip on January 25, 1994
Davis Park Road TCE Site
Gastonia, Gaston County, North Carolina
NCD 986 175 644
Reference 4
On January 25, 1994 Bob Gandley, NC Superfund Section, and I
went to the Davis Park Road site to sample soils on-site and the
surrounding private wells to determine if contamination had
occurred and to what extent it may have migrated off-site. We
arrived at the site at 9:30. Mr. Roy Moore, owner of Moore's
Automatic Transmission and Auto Repair Shop (Moore's) met with us
and discussed our sampling plan. We proceeded to an area behind
the shop an prepared to collect the first source sample. We used
the Hnu 970165 with probe R721, calibrated at a span of 6.66. The
calibration reading was 50 ppm.
We proceeded to sample in a depression area where we suspected
the drain pipe terminated. After hand augering to approximately
2'-0" with no indication of-any contamination, we asked .Mr. Moore
to verify the location of the end of the drain pipe. Mr. Moore
showed us an approximately 2" diameter pipe coming through the,wall
of the shop at ground level, and projecting 3" from the wall.' We
relocated an collected sample DR-002-SB from 1 1 south of the pipe.
The soil was oil stained to 18" deep. We collected the soil sample
from 18" to 24" deep. The sample was collected_ at 10: 10 and no
reading was detected on the Hnu.
Sample DR-003-SB was collected 2' west of the pipe. Red sandy
clay was encountered to a depth of 20". The sample was collected
from 20'' to 26'' depth, and again was oil stained. The sample was
collected at 10:25 and no reading was detected on the Hnu.
After trying to sample 18" northwest of the pipe'. and
encountering rock at about 1" depth, Sample DR-004-SB was collected
from 9 11 west of the pipe. Clean looking soil was removed to a
depth of 18". Oil stained soil was removed to a depth.of 24" where
rock was again encountered. The sample was collected from the 18"
to 24" depth, however not enough soil was available to collect a
duplicate sample. The sample was collected at 10:45 and no reading
was detected on the Hnu.
We obtained the background soil sample, DR-001-SB, from the
southeast corner of the property, approximately 8" southwest of the
water meter, at a depth of 6". The sample was collected at 11:05
and no reading was detected on the HNu.
~
;111
ill)
i ' .II
Ill
,Ill
II
The residence of Mrs. Doris Corella is located at 2403 Davis Park Road. Nobody was home at the time, however, Mrs. Corella had given us prior approval to sample her well. Upon initial inspection no well could be located. We suspected that the wellhead may be buried, since the water supply lines located in the crawlspace under the house just appeared and could not be traced to any area. We proceeded to purge-the well at a tap on the southeast corner of the house. We checked the Ph, temperature, and specific conductivity at 5 minute intervals to determine if the groundwater has stabilized. During the purging, we investigated an old wooden shed located approximately 135 feet south of the house, and next to an abandoned house. The well supplying the Corella residence is housed in this shed. A tap was located after a holding tank but before a filter system on the line feeding the· house. · The parameters were checked on water obtained at the tap and were found to have stabilized after 25 minutes of purging. A sample was collected at 12:10.
The Cedar Oak Subdivision community well was located on the south side of the subdivision. The pump was connected to an open two inch line with a tap prior to the end. A four inch diameter piece of flexible pvc piping was placed over the open end of the pipe to carry the purge water · outside the wellhouse. Mr. Doc Thompson, Gaston County Health Department, had told us earlier in the day that the secondary. well supplying the subdivision with water had been pumped dry the-day before. When the pump was turned on a significant flow of water, approximately 25 to 30 gallons of water per minute was being discharged. Because of the fear. of pumping the well dry, we sampled the well after ten minutes' of purging, since the parameters had stabilized at this time. The sample was collected at 12: 40 and a duplicate was collected at 12:50.
Mr. Godwin, 2231 Davis Park Road, directed us to a tap on the northeast corner of his house. This tap is the closest to the wellhead that does not go through the filtering system which treats the water used in the house. The well was purged for .15 minutes until the parameters stabilized. The sample was collected· at 14:45.
Nobody was home at the Philbeck residence, 2301 Davis Park Road, however, Mrs. Philbeck had previously given us permission'to sample the weli. A tap was located at the wellhead. The well was purged for 10 minutes until the parameters stabilized. The sample was collected at 15:40.
Mr. Charles May, 2419 Davis Park Road, was summoned to his fence due to the presence of a somewhat friendly Malamute. Mr. May introduced us to his dog and proceeded to show us to the wellhead. A new galvanized tap had been placed between the wellhead and the waterline running underground to the house that morning. We purged the well for 15 minutes until the parameters stabilized. The sample was collected at 16:00.
Mr. Orlin Tompkins, 2425 Davis Park Road, was home the second
time we attempted to sample his well. We had a lengthy discussion
concerning the contamination of the groundwater, the responsibility
of the former owner to inform Mr. Tompkins about the contamination,
and several other matters. Mr. Tompkins then proceeded to show us
an accumulation of what appeared to be blue ·green algae growing in
the tank on his toilet. Mr. Tompkins requested that we take a
sample of his water inside the house at his sink tap as well as a
sample outside at the wellhead. I informed Mr. Tompkins that we
are limited to the number of samples authorized on the approved
sampling plan, however, I would recommend to the NC DEM and the
Gaston County Health Department that this sampling could be done by
them. We proceeded to the wellhead in the back yard. The
parameters stabilized after 15 minutes, and we collected the sample
at 16:50.
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UNITED STATES ENVIR(>l,tcJ:;,111,~ PRO'.:EC';ION. AGENCY
RE:;1i,,:·1 ~:-✓
En·Ji rocrnerLtaJ Si! :·v::.,:E s ·D:·_vi sion
College Stacic,n !:,,acl, /1tt.e1s, Ca. 30613
DATE: 03/ l5/'l4
S JE.J EC'!: Resul·:s
9L--Q2-f4
of :?urgeable C>::ganic Aualysi i;;
DAVIS PARK RD 1•1:E SJ
GASTONcA NC
CASE NO: 21:,'59
F'l\•JM:~h~rles H. Hooper ~\v('.,. LS
Chie~, :Jabora:ory Eva~u&tic111/()ual.it:1 Ass~.rance Section
TO: PAT DEROSA (NC)
Att.a~h.ed are tl-11~, results c-f 2nalysi3 of :i.3111pLEs collected as part of
the s~bject projec:c.
As 11 resu~t of :he Qu,ility Assu1·anc:•~ I<0v~e~, ct!rt.ain data qualifiers
may have been p.Lac:ed ,,n tr.e data. At 1. aclt,ad is a DATA QUALIFIER
R3P0RT which explains the reas•)fLS t.hat th,:;~e qu9.l :~fiers were required.
If y,u ~ave any qt1estior1s please cc,11te1ct me.
ATTACHMllNT
Reference 6
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ORGANIC DATA QUALIFIER REPORT
Case Number 21559 Project Number 911-0211/1 SAS Number
Site ID. Davis Park Rd TCE Site, Gastonia, NC
Affected Sample
Volatiles
82565
82566
82566,82567
82567
82568
82571, 82572
82575
Compound or Fraction
Flag .
UsedReason
chloroform J
acetone J
1,1,1-trichloroethane J
benzene J
trichloroethene J
1,1,1-trichloroethane J
1,2-dichloroethene,total J
<quantitation lin1it
er~atic response factor
<quantitation limit
<quantitation limit
<quantitation li,nit
<quantitation limit
<quantitation limit
:l
__ : IIIRJ ---.: --~ -----J __ , l!!!l!!!!!I
PURGEABLE ORGANICS DATA REPORT
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM
EPA-REGION IV ESD. ATHENS, GA. ... .. .. .. .. ..
• * * * * * * * * * * * * * * * * * * * * * * * * * * * * * • • • * • * * * * * * * * * * * * * * * * * *
PROJECT NO. 94-0244 SAMPLE NO. 82569 SAMPLE TYPE: SOIL
SOURCE: DAVIS PARK RD TCE SI
STATION ID: 001-SB
CASE NO.: 21559 SAS NO.:
PROG ELEM: SSF CITY: GASTONIA
COLLECTION START:
D. NO.· FC81
COLLECTED BY: H ZINN ST: NC
01 /25/94 1105 STOP: 00/00/00
03/14/94
• • • ... .. .. .. .. ..
Tt* * * * * * * * * * * * * * * * * * * * * * * * * * * * * T * * * * * * * * *TS T * * * * T T T * T * * * * * * * T * T T * TTT
UG/KG ANALYTICAL RESULTS UG/KG ANALYTICAL RESULTS
12U CHLOROMETHANE
12U BROMOMETHANE
12U VINYL CHLORIDE
12U CHLOROETHANE
12U METHYLENE CHLORIDE
12U ACETONE
12U CARBON DISULFIDE
12U 1,1-D!CHLOROETHENE(1,1-D!CHLOROETHYLENE)
12U 1 ,1-DICHLOROETHANE
12U 1,2-D!CHLOROETHENE (TOTAL)
12U CHLOROFORM
12U 1 ,2-DICHLOROETHANE
12U METHYL ETHYL KETONE
12U 1,1,1-TRICHLOROETHANE
12U CARBON TETRACHLORIDE
12U BROMOD!CHLOROMETHANE
•••FOOTNOTES***
12U 1,2-DICHLOROPROPANE
12U CIS-1 .3-DICHLOROPROPENE
12U TRICHLOROETHENE(TR!CHLOROETHYLENE)
12U DIBROMOCHLOROMETHANE
12U 1, 1 ,2-TRICHLOROETHANE
12U BENZENE
12U TRANS-1 ,3-DICHLOROPROPENE
12U BROMOFORM
12U METHYL ISOBUTYL KETONE
12U METHYL BUTYL KETONE
12U TETRACHLOROETHENE(TETRACHLOROETHYLENE)
12U 1.1 .2.2-TETRACHLOROETHANE
12U TOLUENE 12U CHLOROBENZENE
12U ETHYL BENZENE
12U STYRENE 12U TOTAL XYLENES
15 PERCENT MOISTURE
•A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL
•K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN
•U-MATER!AL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT.
•R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM
EPA-REGION IV ESD, ATHENS, GA.
PURGEABLE ORGANICS DATA REPORT • • • • • • • • • • * • • • * • • • • •
PROJECT NO. 94-0244 SAMPLE NO. 82566
SOURCE: DAVIS PARK RD TCE SJ
STATION ID: 002-SB
CASE NO.: 21559
UG/KG
12U 12U 12U 12U 12U
CHLOROMETHANE
BROMOMETHANE
ANALYTICAL RESULTS
VINYL CHLORIDE
CHLOROETHANE
METHYLENE CHLORIDE ACETONE CARBON DISULFIDE ~
• • • • • • • • * *
SAMPLE TYPE: SOIL
120J 12U 12U
12U
1,1-DJCHLOROETHENE(l .1-DICHLOROETHYLENEJ
1 ,1-DICHLOROETHANE
38 12U 12U 12U
BJ 12U 12U
1.2-DICHLOROETHENE (TOTAL)
CHLOROFORM 1 .2-DICHLOROETHANE
METHYL ETHYL KETONE
1,1,1-TRICHLOROETHANE
CARBON TETRACHLORIDE
BROMODICHLOROMETHANE
* :n: FOOTNOTES•*•
PROG ELEM: SSF CITY: GASTONIA
COLLECTION START:
COLLECTED BY: H ZINN ST: NC
01/25/94 1010 STOP: 00/00/00
D.NO.:FC78
UG/KG
12U 12U 20 12U 12U
12U 12U 12U 12U 12U 20U 12U 79 12U 20U 12U 210 14
ANALYTICAL RESULTS
1,2-DICHLOROPROPANE
CIS-1 .3-DICHLOROPROPENE
TRICHLOROETHENE(TRICHLOROETHYLENE)
DIBROMOCHLOROMETHANE
1 .1 ,2-TRICHLOROETHANE
BENZENE TRANS-1 .3-DICHLOROPROPENE
BROMOFORM METHYL JSOBUTYL KETONE
METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENEJ
1 , 1 . 2, 2-TETRACHLOROETHANE
TOLUENE
CHLOROBENZENE ETHYL BENZENE
STYRENE
TOTAL XYLENES PERCENT MOISTURE
03/14/94 . ..
" .. ..
•• ••
•A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL
•K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN
•U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT.
•R-QC INDICATES THAT DATA UNUSABLE.-COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPL!NG AND REANALYSIS IS NECESSARY FOR VERIFICATION.
1111111..; 1iii;;;J 1111111,; ... ;.,
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA.
PURGEABLE ORGANICS DATA REPORT
" " " ••
PROJECT NO. 94-0244 SAMPLE NO. 82567 SOURCE: DAVIS PARK RD TCE SI STATION ID: 003-SB
•• CASE NO.: 21559
UG/KG
12U 12U 12U 12U 12U
ANALYTICAL RESULTS
CHLOROMETHANE BROMOMETHANE
VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE
ACETONE CARBON DISULFIDE
SAMPLE TYPE: SOIL
SAS NO.
lOOU 12U 12U 12U 260 12U 12U 12U
1 , 1-DI CHLOROETHENE ( 1 . 1-DICHLOROETHYLENE)
1 .1-DICHLOROETHANE
7J 12U 12U_
1 .2-DICHLOROETHENE (TOTAL) CHLOROFORM 1 .2-DICHLOROETHANE METHYL ETHYL KETONE 1.1.1-TRICHLOROETHANE CARBON TETRACHLORIDE BROMODICHLOROMETHANE
PROG ELEM: SSF COLLECTED CITY: GASTONIA
BY: H ZINN ST: NC
COLLECTION START: 01/25/94 1025 STOP: 00/00/00
D. NO.· FC79
UG/KG
12U 12U 17 12U 12U 2J 12U 12U 12U 12U 12U 12U 230 12U
45 12U 330 19
ANALYTICAL RESULTS
1.2-DICHLOROPROPANE CIS-1 .3-DICHLOROPROPENE TRICHLOROETHENE(TRICHLOROETHYLENE)
DIBROMOCHLOROMETHANE 1 .1.2-TRICHLOROETHANE BENZENE TRANS-1 .3-DICHLOROPROPENE BROMOFORM . METHYL ISOBUTYL KETONE METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENE)
1. 1 .2.2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYL BENZENE STYRENE TOTAL XYLENES PERCENT MOISTURE
***REMARKS***
03/14/94 ..
" •• •• ••
***FOOTNOTES*** •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT. •R-QC·INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR•MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA.
PURGEABLE ORGANICS DATA REPORT .. .. .. .. ..
PROJECT NO. 94-0244 SAMPLE SOURCE: DAVIS PARK RD TCE SI STATION JD: 004-SB
CASE NO.: 21559
NO. 82568
ANALYTICAL RESULTS
CHLOROMETHMJE
BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE
SAMPLE TYPE: SOIL
SAS NO.
UG/KG
12U 12U 12U 12U 12U 12U 12U 12U 12U
?~f~8~c~rn~~~rn~NE ( 1 , 1-DICHLOROETHYLENE) 1.l~DICHLOROETHANE 38 12U 12U 12U 12U 12U
12U
1.2-DICHLOROETHENE (TOTAL)
CHLOROFORM 1.2-DICHLOROETHANE METHYL ETHYL KETONE 1,1.1-TRICHLOROETHANE CARBON TETRACHLORIDE BROMODICHLOROMETHANE
PROG ELEM: SSF COLLECTED
CITY: GASTONIA
BY: H ZINN ST: NC COLLECTION START: 01/25/94 1045 STOP: OD/00/00
D. NO.: FC80
UG/KG
12U 12U 4J
12U 12U 12U 12U 12U
1 2ll
12U 12U 12U 46
12U 12U 12U
100 18
ANALYTICAL RESULTS
1,2-DICHLOROPROPANE CIS-1 .3-DICHLOROPROPENE TRICHLOROETHENE(TRICHLOROETHYLENE) DIBROMOCHLOROMETHANE 1.1.2-TRICHLOROETHANE BENZENE TRANS-1 ,3-DICHLOROPROPENE
BROMOFORM METHYL ISOBUTYL KETONE METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENEJ 1 .1 .2.2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYL BENZENE STYRENE TOTAL XYLENES PERCENT MOISTURE
03/14/94
.. .. .. ..
••
***FOOTNOTES••• •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL
•K-ACTUAL VALUE JS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TD BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM OUANTITATJON LIMIT. •.R~QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPL!NG. AND REANALYSIS IS NECESSARY FOR VERIFICATION.
r
_J
. SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION JV ESD. ATHENS. GA.
MISCELLANEOUS PURGEABLE ORGANICS -DATA REPORT
"' .. * * * • * • * * * * • * • • * * * * * • ~ • • * * • * * * * * * * * * * * * * * * * * .. ..
" "
PROJECT NO. 94-0244 SAMPLE NO. 82566 SOURCE: DAVIS PARK RD TCE SJ
SAMPLE TYPE: SOIL
STATION ID: 002-SB CASE.NO.· 21559 SAS NO.:
400JN lDDOJN 60DJN 50DJN BOOJN 300JN 400JN 2DOOJ
ANALYTICAL RESULTS UG/KG
TRJMETHYLHEXANE DECANE ETHYLMETHYLHEPTANE TRIMETHYLBENZENE UNDECANE ·•METHYL(METHYLETHYL)BENZENE
ETHYLD!METHYLBENZENE 3 UNIDENTIFIED COMPOUNDS
PROG ELEM: SSF CITY: GASTONIA COLLECTION START: D. NO.· FC78
COLLECTED BY: H ZINN ST: NC 01/25/94 1010 STOP: 00/00/00 MD NO:
03/14/94
' ' '
..
"
***FOOTNOTES*** •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE JS KNOWN TO BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
--SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA. 03/14/94
MISCELLANEOUS PURGEABLE ORGANICS -DATA REPORT .. .. .. ..
"
* * • * • * * * * * * * • * * * * • * * * • * • * * * * • * * PROJECT NO. 94-0244 SAMPLE NO. 82567 SOURCE: DAVIS PARK RD TCE SI SAMPLE TYPE: SOIL
STATION ID: 003-SB CASE.NO.: 21559 SAS NO.
4000J 600JN 2000JN 700JN 500JN
ANALYTICAL RESULTS UG/KG
5 UNIDENTIFIED COMPOUNDS
ETHYLMETHYLBENZENE TRIMETHYLBENZENE (2 ISOMERS) UNDECANE ~METHYLIMETHYLETHYL)BENZENE
• • ~ROG ELEM: SSF COLLECTED CITY: GASTONIA COLLECTION START: 01/25/94 D. NO.· FC79
BY: H ZINN ST: NC 1025 STOP: 00/00/00
MD NO:
•••FOOTNOTES••* •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN
•U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
!!!!!-. ·--~ I!!!!..: -;;;;
_Q
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA.
MISCELLANEOUS PURGEABLE ORGANICS -DATA REPORT
* * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * *
PROJECT NO. 94-0244 SAMPLE NO. 82568 SOURCE: DAVIS PARK RD TCE SI
SAMPLE TYPE: SOIL
STATION ID: 004-SB CASE.NO.: 21559 SAS NO.
200JN 600JN 200JN 400JN 600J
ANALYTICAL RESULTS UG/KG
ETHYLMETHYLBENZENE TRIMETHYLBENZENE (3 !SOMERSJ DIETHYLBENZENE ETHYLDIMETHYLBENZENE (2 ISOMERS) ... 3 UNINDENTIFIED COMPOUNDS
. PROG ELEM: SSF CITY: GASTONIA COLLECTED
COLLECTION START: 01/25/94 D. NO.· FC80
BY: H ZINN ST: NC 1045 STOP: 00/00/00
MD NO:
03/14/94
• * * ... ..
** •• .. .,
***FOOTNOTES*** •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •LI-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
C,
iiiiiiii
PURGEABLE ORGANICS DATA REPORT
•• •• •• •• ..
PROJECT NO. 94-0244 SAMPLE NO. 82573 SOURCE: DAVIS PARK RD TCE SI STATION ID: 001-PW
CASE NO.: 21559
ANALYTICAL RESULTS
CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA.
SAMPLE TYPE: GROUND\'/A
SAS NO.·
PROG ELEM: SSF COLLECTED
CITY: GASTONIA COLLECTION START: 01/25/94
D. NO.· FC85
BY: H ZINN ST: NC 1445 STOP: 00/00/00
UG/L ANALYTICAL RESULTS
,au 1,2-DICHLOROPROPANE 10U CIS-1 .3-DICHLOROPROPENE 10U TRICHLOROETHENE(TRICHLOROETHYLENE) 10U DIBROMOCHLOROMETHANE 10U 1,1 .2-TRICHLOROETHANE 10U BENZENE
UG/L
10U 10U ,au ,au ,au ,au ,au ,au ,au ,au ,au 10U ,au ,au ,ou
1 OU
?Af ~g~ cSC6~6HS~NE c, . 1-1i'rcHLOROETHYLENE J 1. 1-DICHLOROETHANE
,au TRANS-1 .3-DICHLOROPROPENE 10U BROMOFORM 10U. METHYL ISOBUTYL KETONE ,au METHYL BUTYL KETONE 1 .2-DICHLOROETHENE (TOTAL)
CHLOROFORM 1.2-DICHLOROETHANE METHYL ETHYL KETONE 1, 1. 1-TRICHLOROETHANE
CARBON TETRACHLORIDE BROMODICHLOROMETHANE
•••FOOTNOTES•••
10U TETRACHLOROETHENE(TETRACHLOROETHYLENE) 10U 1 .1 .2.2-TETRACHLOROETHANE 10U TOLUENE 10U CHLOROBENZENE 10U ETHYL BENZENE 10U STYRENE ,au TOTAL XYLENES
03/14/94
.. .. ..
• • ..
•A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATEO VALUE ·•N-PRESUM0 TIVE EVIDENCE OF PRESENCE OF ~ATERIAL •K~ACTUAL_VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •LI-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING ANO REANALYSIS IS NECESSARY FOR VERIFICATION.
r.--iiiii iiii iii -·-·'"; ---; iiiiil_
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA. PURGEABLE ORGANICS DATA REPORT • • • • • • • • • • • • • • • • • • • • PROJECT NO. 94-0244 SAMPLE NO. 82574 SOURCE.: DAVIS PARK RD TCE SI STATION ID: 002-PW
CASE NO.: 21559
CHLOROMETHANE BROMOMETHANE
ANALYTICAL RESULTS
VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE
SAMPLE TYPE: GROUNDWA
SAS NO.:
UG/L
10U 10U 10U 10U 10U 10U 10U· 10U 10U 10U 10U 10U 10U 10U
10U 10U
?~~~81c8C6~6H 8~NE c 1 . 1-01 CHLOROETHYLENE J 1,1-DICHLOROETHANE 1,2-DICHLOROETHENE (TOTAL)
CHLOROFORM 1 .2-DICHLOROETHANE METHYL ETHYL KETONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE BROMODICHLOROMETHANE
PROG ELEM: SSF COLLECTED CITY: GASTONIA BY: H ZINN ST: NC COLLECTION START: 01/25/94 1540 STOP: 00/00/00
D. NO.: FC86
UG/L
1 OU 10U
1 OU
10U
1 OU 10U 10U 10U
1 OU 10U 10U 10U 10U 10U 10U
1 OU 10U
ANALYTICAL RESULTS
1,2-DICHLOROPROPANE
CIS-1 .3-DICHLOROPROPENE TRICHLOROETHENE(TRICHLOROETHYLENE) DIBROMOCHLOROMETHANE 1 ,1 ,2-TRICHLOROETHANE
BENZENE TRANS-1 .3-DICHLOROPROPENE BROMOFORM METHYL ISOBUTYL KETONE
METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENE) 1, 1 .2.2-TETRACHLOROETHANE
TOLUENE CHLOROBENZENE ETHYL BENZENE STYRENE TOTAL XYLENES
03/14/94
•*•FOOTNOTES••• •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-EST!MATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE. IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FDR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPL!NG AND REANALYSIS IS NECESSARY FOR VERIFICATION.
-----; SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD. ATHENS, GA.
PURGEABLE ORGANICS DATA REPORT •••••••••••••••••••••••••••••••••••• •• PROJECT NO. 94-0244 SAMPLE NO. 82570 SAMPLE TYPE: GROUNDWA •• SOURCE: DAVIS PARK RD TCE SI •• STATION ID: 003-PW •• .. CASE NO.: 21559
UG/L ANALYTICAL RESULTS
1 OU CHLOROMETHA.NE lOU BROMOMETHANE lOU VINYL CHLORIDE lOU CHLOROETHANE 10U METHYLENE CHLORIDE lOU ACETONE 10U CARBON DISULFIDE
SAS NO.·
10U 1 .1-DICHLOROETHENE(l .1-DICHLOROETHYLENE)
lOU 1 .1-DICHLDROETHANE 10U 1 .2-DICHLOROETHENE (TOTAL)
10U CHLOROFORM lOU 1 .2-DICHLOROETHANE 10U METHYL ETHYL KETONE
10U 1. 1. 1-TRICHLOROETHANE 10U CARBON TETRACHLORIDE 10U BROMODICHLOROMETHANE
PROG ELEM: SSF CITY: GASTONIA COLLECTION START:
D. NO.: FC82
COLLECTED BY: H ZINN ST: NC 01/25/94 1210 STOP: 00/00/00
UG/L ANALYTICAL RESULTS
10U 1,2-DICHLOROPROPANE 10U CIS-1.3-DICHLOROPROPENE 10 TRICHLOROETHENE(TRICHLOROETHYLENE)
lOU DIBROMOCHLOROMETHANE lOU 1 .1.2-TRICHLOROETHANE lOU BENZENE 10U TRANS-1 .3-DICHLOROPROPENE lOU BROMOFORM lOU METHYL ISOBUTYL KETONE 10U METHYL BUTYL KETONE 10U TETRACHLOROETHENE(TETRACHLOROETHYLENE) 1 OU 1 . 1 . 2. 2-TETRACHLOROETHANE 10U TOLUENE . 10U CHLOROBENZENE lOU ETHYL BENZENE 10U STYRENE 10U TOTAL XYLENES
03/14/94
.. ..
"**FOOTNOTES*** •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL
•K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS. THE MINIMUM QUANTITATION LIMIT. . _ . . . •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
iii --SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA.
-· 1!!!!!!!1-!Bl f!!I!!! 1111111
03/14/94
PURGEABLE ORGANICS DATA REPORT ..
** ** ..
PROJECT NO. 94-0244· SAMPLE NO. 82575 SOURCE: DAVIS PARK RD TCE SJ STATION JD: 004-PW
PROG ELEM: SSF COLLECTED CITY: GASTONIA COLLECTION START: 01/25/94
D. NO.: FC87
BY: H ZINN ST: NC 1600 STOP: 00/00/00
.,
** " •• •• " CASE NO.: 21559 *** * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * ' * * * * * * * * * ' * * * * * * * * * * * *** UG/L ANALYTICAL RESULTS UG/L ANALYTICAL RESULTS
SAS NO.:
lOU CHLOROMETHANE lOU BROMOMETHANE lOU VINYL CHLORIDE lOU CHLOROETHANE lOU METHYLENE CHLORIDE lOU ACETONE 10U CARBON DISULFIDE _ 10U 1, 1-DJCHLOROETHENE( 1.1-D.ICHLOROETHYLENE) 10U 1 ,1-DICHLOROETHANE 2J 1 ,2-DICHLOROETHENE (TOTAL) 10U CHLOROFORM 10U 1 ,2-DICHLOROETHANE
10U METHYL ETHYL KETONE 10U 1,1,1-TRICHLOROETHANE 10U CARBON TETRACHLORIDE lOU BROMODICHLOROMETHANE
lOU 1 ,2-DICHLOROPROPANE lOU CIS-1 .3-DICHLOROPROPENE 38 TRICHLOROETHENE(TRICHLOROETHYLENE) lOU DIBROMOCHLOROMETHANE lOU 1 .1.2-TRICHLOROETHANE lOU BENZENE lOU TRANS-1 .3-DICHLOROPROPENE lOU BROMOFORM lOU METHYL ISOBUTYL ~ETONE lOU METHYL BUTYL KETO,!E lOU TETRACHLOROETHENE(TETRACHLOROETHYLENE) lOU 1.1 .2.2-TETRACHLOROETHANE lOU TOLUENE lOU CHLOROBENZENE 10U ETHYL BENZENE
lOU STYRENE 10U TOTAL XYLENES
•••FOOTNOTES••• •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATJON LIMIT. •R~QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS JS NECESSARY FOR VERIFICATION.
==
PURGEABLE ORGANICS DATA REPORT
., ..
*' .. ..
• * * • • * • • * * • * * • * * • • * •
PROJECT NO. 94-0244 SAMPLE NO. 82576
SOURCE: DAVIS PARK RD TCE SI
STATION ID: 005-PW
CASE NO.· 21559
UG/L ANALYTICAL RESULTS
10U CHLOROMETHANE
10U BROMOMETHANE
10U VINYL CHLORIDE
10U CHLOROETHANE
10U METHYLENE CHLORIDE
10U ACETONE
10U CARBON-DISULFIDE ...
--
-
--l!!!!!!!I
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM
EPA-REGION IV ESD. ATHENS, GA.
• • . * • * • * • * • • *
SAMPLE TYPE: GROUNDWA
SAS NO.:
PROG ELEM: SSF
CITY: GASTONIA
COLLECTION START:
D. NO.: FC88
COLLECTED BY: H ZINN ST: NC
01/25/94 1650 STOP: 00/00/00
UG/L ANALYTICAL RESULTS
10U 1.2-DICHLOROPROPANE
10U CIS-1 .3-DICHLOROPROPENE
11 TRICHLOROETHENE(TRICHLOROETHYLENE)
lOU DJBROMOCHLOROMETHANE
lOU 1 .1 .2-TRICHLOROETHANE
10U BENZENE
10U 1.1-D!CHLOROETHENE(1 ,1-DICHLOROETHYLENE)
10U 1 .1-DICHLOROETHANE
10U TRANS-1 .3-DICHLOROPROPENE
1QU BROMOFORM
10U METHYL ISOBUTYL KETONE
10U METHYL BUTYL KETONE 10U 1.2-D!CHLOROETHENE (TOTAL)
10U CHLOROFORM 10U 1 .2-D!CHLOROETHANE
10U METHYL ETHYL KETONE
10U 1,1.1-TRICHLOROETHANE
10U CARBON TETRACHLORIDE
10U BROMOD!CHLOROMETHANE
•••FOOTNOTES•*"'
10U TETRACHLOROETHENE(TETRACHLOROETHYLENE)
10U 1 .1 .2.2-TETRACHLOROETHANE
10U TOLUENE
10U CHLOROBENZENE
10U ETHYL BENZENE
10U STYRENE
10U TOTAL XYLENES
03/14/94 ...
*' ** ** •• ..
•A-AVERAGE VALUE. •NA-NOT ANALYZED •NAI-JNTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL
•K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE JS KNOWN TO BE GREATER THAN VALUE GIVEN
•U-MATER!AL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTJTATJON LIMIT.
•R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
!-liiilllil -iiii -~ __ I __ :== -liiiiiiiil ----
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD. ATHENS. GA.
PURGEABLE ORGANICS DATA REPORT_
.. ..
PROJECT NO. 94-0244 SAMPLE NO. 82571 SOURCE: DAVIS PARK RD TCE SJ STATION ID: 006-PW
CASE NO.: 21559
-ANALYTICAL RESULTS
CHLOROMETHAfJE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE CARBON DISULFIDE .
SAMPLE TYPE: GROUNDWA
SAS NO .
UG/L
IOU lOU lOU !OU lOU
lOU lOU lOU lOU
lOU lOU lOU
lOU
5J
1,1-DICHLOROETHENE(l.1-DICHLOROETHYLENE) 1,1-DICHLOROETHANE
lOU lOU
1 .2-DICHLOROETHENE (TOTAL) CHLOROFORM 1 .2-DJCHLOROETHANE METHYL ETHYL KETONE 1,1 ,1-TRICHLOROETHANE CARBON TETRACHLORIDE BROMODICHLOROMETHANE
PROG ELEM: SSF COLLECTED CITY: GASTONIA
BY: H ZINN
ST: NC
COLLECTION START: 01/25/94 1240 STOP: 00/00/00
D. NO.: FC83
UG/L
lOU lOU 51 lOU lOU lOU lOU lOU lOU _ lOU 18 lOU lOU lOU lOU lOU
lOU
ANALYTICAL RESULTS
1 .2-DICHLOROPROPANE CJS-1 .3-D!CHLOROPROPENE TRICHLOROETHENE(TRICHLOROETHYLENE) DIBROMOCHLOROMETHANE 1,1,2-TRJCHLOROETHANE BENZENE TRANS-1 .3-DICHLOROPROPENE
BROMOFORM METHYL JSOBUTYL KETONE METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENE) 1 .1 .2.2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYL BENZENE STYRENE TOTAL XYLENES
03/14/94
.. .. .. ..
•••FOOTNOTES••* •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL -•K-ACTUAL VALUE JS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE JS KNOWN TO BE GREATER THAN VALUE GIVEN •II-MATERIAL .WAS ANALYZED FOR BUT NOT DETECTED. THE 'NUMBER IS THE MINIMUM OUANTITATJON LIMIT. _ _ _ •R-OC INDICATES THAT DATA UNUSABLE. COMPOUND-MAY OR MAY NOT BE PRESENT. RESAMPllNG AND REANALYSIS JS NECESSARY FOR VERIFICATION.
----PURGEABLE ORGANICS DATA REPORT ••••••••••••••••.• * • *
PROJECT NO. 94-0244 SAMPLE NO. 82577
SOURCE: DAVIS PARK RD TCE SI
STATION ID: 101-PW
CASE NO.: 21559
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM
EPA-REGION IV ESD, ATHENS. GA.
• • • * * • • • • • • • •
SAMPLE TYPE: GROUNDWA
SAS NO.·
PRDG ELEM: SSF COLLECTED
CITY: GASTONIA
COLLECTION START: 01/25/94
D. NO.· FC89
BY: H ZINN ST: NC
0725 STOP: 00/00/00
03/14/94 ... ,, .. ..
•• ••
:l°'fc•-"T"f••••:rT
UG/L
10U 10U 10U 10U
10U
10U
10u·
10U 10U
10U
10U
10U 10U 10U 10U 10U
CHLOROME THANE BROMOMETHANE
ANALYTICAL RESULTS
VINYL CHLORIDE
CHLOROETHANE METHYLENE CHLORIDE
ACETONE CARBON DISULFIDE _
1.1-DICHLOROETHENE( 1 .1-D.ICHLOROETHYLENEJ
1, 1-DICHLOROETHANE
1,2-D!CHLOROETHENE (TOTAL)
CHLOROFORM .
1 .2-D!CHLOROETHANE
METHYL ETHYL KETONE
1,1 .1-TRICHLOROETHANE
CARBON TETRACHLORIDE
BROMOD!CHLOROMETHANE
***FOOTNOTES••*
UG/L
10U 10U. 10U 10U 10U 10U 10U 1 OU 10U 10U 10U 10U 10U 10U 10U 10U 10U
ANALYTICAL RESULTS
1,2-DICHLOROPROPANE
CIS-1 .3-DICHLOROPROPENE
TR!CHLOROETHENE(TR!CHLOROETHYLENEJ
D!BROMOCHLOROMETHANE
1 .1.2-TR!CHLOROETHANE r
BENZENE TRANS-1 .3-DICHLOROPROPENE
BROMOFORM
METHYL !SOBUTYL KETONE
METHYL BUTYL KETONE
TETRACHLOROETHENE(TETRACHLOROETHYLENEJ
1,1.2.2-TETRACHLOROETHANE
TOLUENE CHLOROBENZENE
ETHYL BENZENE
STYRENE TOTAL XYLENES
•••REMARKS•••
•A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL
•K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN
•U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATION LIMIT.
•R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
PURGEABLE ORGANICS DATA REPORT
* * * * * * * * * * * * * * * * * * * * PROJECT NO. 94-0244 SAMPLE NO. 82578 SOURCE: DAVIS PARK RD TCE SI STATION ID: 104-PW
-SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD. ATHENS. GA.
* * * * * * * * * * * * * SAMPLE TYPE: GROUNDWA PROG ELEM: SSF COLLECTED
CITY: GASTONIA COLLECTION START: 01/25/94
BY: H ZINN
ST: NC 1700 STOP: 00/00/00
03/14/94 ...
" .. .. ..
.. .. ..
•• •• CASE NO. · 21559 *** * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * .• * * *** UG/L ANALYTICAL RESULTS UG/L ANALYTICAL RESULTS
SAS NO. D. NO.: FC90
10U 10U 10U 10U 10U
10U 10U 10U 10U
10U
1 1 10U 10U 10U 10U ,OU
CHLOROMETHANE BROMOMETHANE VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE ACETONE
~~~~81c8C6~~~rn~NE ( 1 . 1-DI CHLOROETHYLENE l 1.1-DICHLOROETHANE 1.2-DICHLOROETHENE (TOTAL) CHLOROFORM 1 .2-DICHLOROETHANE METHYL ETHYL KETONE 1.1.1-TRICHLOROETHANE CARBON TETRACHLORIDE BROMODICHLOROMETHANE
10U
10U
10U 10U 10U
10U 10U 10U 10U.
10U 10U 10U 10U 10U 10U 10U 10U
1,2-DICHLOROPROPANE CIS-1 .3-DICHLOROPROPENE TRICHLOROETHENE(TRICHLOROETHYLENEJ DIBROMOCHLOROMETHANE
1.1 .2-TRICHLOROETHANE BENZENE TRANS-1 .3-DICHLOROPROPENE
BROMOFORM METHYL ISOBUTYL KETONE METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENE) 1 .1 .2.2-TETRACHLOROETHANE
TOLUENE CHLOROBENZENE ETHYL BENZENE STYRENE TOTAL XYLENES
***REMARKS***
**•FOOTNOTES••• •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTJVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GRE.'.TtR THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATIDN LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
liilii ,_ - - ---__ : l!!l!!!!I: !!!Ii -. -,..._._ ==i_ ==i 1 ===:I~ lliiliiL -
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD. ATHENS. GA. 03/14/94
PURGEABLE ORGANICS DATA REPORT .. .. ..
" ..
* * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * PROJECT NO. 94-0244 SAMPLE NO. 82565 SAMPLE TYPE: GROUNDWA SOURCE: DAVIS PARK RD TCE SI STATION ID: 105-PW
CASE NO.: 21559 SAS NO.
* * * * * * * * * * * * * * * * * * * * * PROG ELEM: SSF CITY: GASTONIA COLLECTED
COLLECTION START: 01/25/94
D. NO.: FC77
BY: H ZINN ST: NC 0730 STOP: 00/00/00
...
" ..
" .. ..
*** * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * * ~ * * * * * * * * * *** UG/L ANALYTICAL RESULTS UG/L ANALYTICAL RESULTS
10U 10U 10U ,ou
10U 10U 10U 10U 10U
10U 3J 10U 10U ,ou
10U 10U
CHLOROMETHANE BROMOMETHANE
VINYL CHLORIDE CHLOROETHANE METHYLENE CHLORIDE
ACETONE CARBON DISULFIDE _ 1 ,1-DICHLOROETHENE(1 ,1-D!CHLOROETHYLENE) 1,1-DICHLOROETHANE 1.2-DICHLOROETHENE (TOTAL) CHLOROFORM 1 .2-DICHLOROETHANE METHYL ETHYL KETONE 1,1,1-TRICHLOROETHANE CARBON TETRACHLORIDE BROMODICHLOROMETHANE
10U 10U 10U ,ou ,ou 10U 10U 10U ,au. 10U 10U 10U
10U 10U 10U
10U 10U
1 ,2-DJCHLOROPROPANE CIS-1 .3-DICHLOROPROPENE TRICHLOROETHENE(TRICHLOROETHYLENE)
DIBROMOCHLOROMETHANE 1. 1 ,2-TRICHLOROETHANE BENZENE TRANS-1 .3-DICHLOROPROPENE
BROMOFORM METHYL ISOBUTYL KETONE METHYL BUTYL KETONE TETRACHLOROETHENE(TETRACHLOROETHYLENE) 1. 1 .2.2-TETRACHLOROETHANE TOLUENE CHLOROBENZENE ETHYL BENZENE STYRENE TOTAL XYLENES
***FOOTNOTES*"* •A-AVERAGE VALUE •NA-NOT ANALYZED •NAI-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE OF MATERIAL •K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L-ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN •U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITAT!ON LIMIT. · •R~oc INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS JS NECESSARY FOR VERIFICATION.
c::iiil ~ ~ ~ ~ Uiiiill Uliil Lliiiiil tliiiiil ;liiiiil :liiiiiil liiii liiii liiiii'I
SAMPLE AND ANALYSIS MANAGEMENT SYSTEM EPA-REGION IV ESD, ATHENS, GA:
PURGEABLE ORGANICS DATA REPORT •-•··• ...... * •• * * * *. *. * •• * * ••• * * •• * * * PROJECT, NO. ·94-0244 SAMPLE NO, 82572 SAMPLE TYPE: GR0UNDWA
SOURCE:! DAVIS PARK RD TCE SI STATION Ip: 106-PW
PR0G ELEM: SSF COLLECTED CITY: GASTONIA COLLECTION START: 01/25/94
D. NO.: FC84
BY: H ZINN ST: NC 1250 STOP: 00/00/00
03/14/94 ... .. .. .. .. .. *** * * *. * .• * * * • * * * * * * * •• * * * * *. * * * * * * * * * * * * * * * * * * * * * * • * • * * * *. * * * * * * * *** UG/L ANALYTICAL RESULTS UG/L ANALYTICAL RESULTS
CASE NO.: 21559 SAS NO.:
l0U CHL0R0METHANE 10U BR0M0METHANE 10U VINYL'CHL0RIDE 10U CHL0R0ETHANE 10U METHYLENE CHLORIDE 10U ACETONE l0U CARB0N·DISULFIDE ~ 1 OU 1 , 1-DI CHL0R0ETHENE ( 1 , 1-DI CHL0R0ETHYLENE) 10U 1,1-DICHL0R0ETHANE l0U 1,2-DICHL0R0ETHENE (TOTAL) l0U CHLOROFORM 10U 1.2-DICHL0R0ETHANE 10U METHYL ETHYL KETONE SJ 1,1,1-TRICHL0R0ETHANE 10U CARBON TETRACHLORIDE l0U BR0M0DICHL0R0METHANE_
***REMARKS•••
10U 1,2-DICHL0R0PR0PANE 10U CIS-1,3-DICHL0R0PR0PENE 50 TRICHL0R0ETHENE(TRICHL0R0ETHYLENE) 10U DIBR0M0CHL0R0METHANE l0U 1 ,1 ,2-TRICHL0R0ETHANE 10U BENZENE l0U TRANS-1 ,3-DICHL0R0PR0PENE
10U BR0M0F0RM l0U METHYL IS0BUTYL KETONE l0U METHYL BUTYL KETONE 17 TETRACHL0R0ETHENE(TETRACHL0R0ETHYLENE) l0U 1 .1 ,2,2-TETRACHL0R0ETHANE
10U TOLUENE 10U CHL0R0BENZENE l0U ETHYL BENZENE 10U STYRENE l0U TOTAL XYLENES
•••FOOTNOTES*** •A-AVERAGE VALUE •NA-NOT ANALYZED •NA!-INTERFERENCES •J-ESTIMATED VALUE •N-PRESUMPTIVE EVIDENCE OF PRESENCE Of MATERIAL
•K-ACTUAL VALUE IS KNOWN TO BE LESS THAN VALUE GIVEN •L~ACTUAL VALUE IS KNOWN TO BE GREATER THAN VALUE GIVEN
•U-MATERIAL WAS ANALYZED FOR BUT NOT DETECTED. THE NUMBER IS THE MINIMUM QUANTITATIDN LIMIT. •R-QC INDICATES THAT DATA UNUSABLE. COMPOUND MAY OR MAY NOT BE PRESENT. RESAMPLING AND REANALYSIS IS NECESSARY FOR VERIFICATION.
a,
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NORRIS • HINCHEE • BROWN • MCCARTY
SEMPRINI • WILSON • KAMPBELL
REINHARD• BOUWER • BORDEN• VOGEL
THOMAS • WARD
Project Officer
John E. Matthews
Chief, Applications and Assistance Branch
Robert S. Kerr Environmental Research Laboratory
Ada, Oklahoma
Reference 8
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Handbook of Bioremediation .,:./: :: .. · -1:.;r~~ .
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been observ_ed to undergo epo_xidation, and. hexachlorobenzene, which hav;, all cai:bons~fi1f/; :
occupied • With 'chlorme substituents, allowmg no· site for hydroxylatwn. . l hese high!,: .\;,:~\iillr I
chlorinated organic compounds are not, •however, resista?t to anaerobic b10degradat10n}~~· l
(Vogel and McCarty, 1985; Gibson and Suflita, 1986; TiedJe et al., 1987; Vogel and',<~~••• I
McCarty, 1987a; Vogel, 1988; Freedman and Gossett, 1989; Bagley and Gossett, 1990; Nies .;,,%( I
and Vogel, 1990; Bhatnagar and Fathepure, 1991). 'l,;,..'' i
: _:,~~;"\,1 •:
10.4.2. Anaerobic ·,: !·:'.,;t::~11
.• ~,·,,l1f'i_..,,
'. ' .,, ... ~~;',I'
Under different anaerobic conditions, both in laboratory studies and in the,;¥~l-
environment, highly chlorinated organics, such as tetrachloroethylene (Vogel arid·::-,i:~r
McCarty, 1985), hexachlorobenzene (Gibson and Suflita, 1986), and polychlorinated;i}/h
biphenyls (Nies and Vogel, 1990), have been shown to undergo reductive dechlorination. ·_~;".f'.:
Reductions of chlorinated solvents normally involve the removal of a chlorine substituenL\J.l;~~
and either its replacement with a hydrogen or removal of a second chlorine substituent·.,;;~il*ii
'from alkanes and formation of an alkene. The first mechanism, commonly called :-~i,:~,
reductive dechlorination, can occur with both alkanes and alkcneS. Reductive_t-~4]%~}
dechlorination has been described for the sequence of ethylenes from letrachloroethylene ·.:l:!f;::
to vinyl chloride (Vogel and McCarty, 1985) (Figure 10.l) and to ethylene (Freedman and :j11(·
Gossett, 1989), and for TCA to chloroethane (Vogel and McCarty, 1987a) (Figure 10.2). -/fe 1 :,
under methanogenic conditions in laboratory studies. In the case of TCA, potential ':"'!r:.~·t
products are co_mplicated by the chemic?!· reactions (denoted by A) that _co-occur '."ith,1_)@.,!J.
b10logical react10ns. Relative rate studies on the reductive dechlonnat10n of vanou~i.,&:if',J
chlorinated ethanes and ethenes have shown a general decrease in rate with decreasing0:{i::t.'1,;(·
number of chlorine substituents, opposite to the trend shown for oxidation reactions,'.;ii¥"i
under aerobic conditions: The relative rates of reduction under methanogenic condition·s.,:)~J;~
have been quantified in two cases (Table 10.2) (Bouwer and McCgrty, 1988; Vogel, 1988)'. ',i1 · •
From these data and that for the chemical reactivity described above, the disappearance:\';:
of an initial chlorinated solvent and the appearance of its products under favorablii'fi~
anaerobic conditions might be derived, as will be discussed later. · .,"
CClz~CCJi -CHCl~CClz
lrcEI ITcaj
1,2-DCE
H Cl
C~C
Cl H
H H
C~C
Cl Cl
1.2-DCE
Figure 10.L PCE anaerobic transformations.
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CHrCHCI -CHt=CHz -2COz + HCI :;~~lt . .: •:]~. 1~ ~ •\\j+>i'if
!vinyl Chlori<lcl I Ethylene I ::i'.j'i
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,f
DATE:
TO:
FROM:
RE:
May 11,· 1994
File
Harry Zinn, Environmental Engineer
North Carolina DEHNR, Superfund Section
Private Well Data for Davis Park Road TCE Site
Gastonia/ Gaston County, North Carolina
NCO 986 175 ·544
Reference 9
On October 14, 1993 I talked to Mr. W.L. Godwin, 2231 Davis Park Road about
the construction of his well. Mr. Godwin stated that his well is 6 inches in
diameter and is approximately 70 feet deep.
about
about
On October 14, 1993 I talked to
the construction of her well.
her well.
Mrs. Pauline Philbeck, 2301 Davis Park Road
Mrs. Phi°ibeck did not know any information
On October 14, 1993 I talked to Mrs. Doris Corella, 2403 Davis Park Road
about the construction of her well. Mrs. Corella did not know any information
about her well.
On October 14, 1993 I talked to Mr. Charles May, 2419 Davis Park Road about
the construction of his well. Mr. May stated that his well is 6 inches in
diameter and is approximately 18T feet deep.
On October 14, 1993 I talked to Mr. Cregg Bess about the contaminated well
which previously served the Cedar Oak Park Subdivision. Mr. Bess stated that the
well is 6 inches in diameter and is approximately 150 feet deep. The system the
well supplied has 26 hook-ups.
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DATE:
TO:
FROM:
RE:
January 24, 1996
File
Harry Zinn, Environmental Engineer
North Carolina DEHNR, Superfund Section
Groundwater Population Calculations for Davis Park Road TCE Site
Gastonia/ Gaston County, North Carolina
NCO 986 175 644
Reference I 0
On September 11, 1995 I calculated the population inside the Target Distance
Limits (TDL's) for the Davis Park Road TCE site. First I located the community
wells supplied by the N.C. Public Water Supply Section on the topographic maps and
delineated those houses associated with them. Several community wells which do not
serve over 30 people are identified on Figure 2. These wells and the Cedar Oak Park
Subdivision population was determined by house counts on Figure 2. Next I delineated
the area of Gastonia served by the Gaston Water Supply System.
Several areas depicted as urban areas on the topographic maps, pink with no
individual houses shown, are located within the TDL's and are not served by the
Gaston Water Supply System. These areas were planimetered and the area (sq. mi.)
was multiplied by the population density (315.3 people/sq. mi.) for South Gastonia.
TDL AREA (sq.mi.) DENSITY POPULATION
(people/sq.mi.)
0 -l< 0.0533 315.3 17
l< -½ 0.0333 315.3 10
½ -1 0. 2 02 315.3 64
1 -2 0.956 315.3 301
2 -3 0.105 315.3 33
3 -4 0.000 315.3 0
Finally those houses not included in any of the above areas were counted. All of
the house counts were multiplied by the population density (2.64 people/house) for
Gaston County.
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GROUNDWATER POPULATION
DAVIS PARK ROAD TCE SITE
Urban Areas not Supplied by the Gaston Water District
TDL Area (sa. mi.) Densitv
0 - ¼ mile 0.0533 315.3
¼-½mile 0.0333 315.3
½-1 mile 0.202 315.3
1 - 2 miles 0.956 315.3
2 - 3 miles 0.105 315.3
3 -4 miles 0.00 315.3
Density Is based on 1990 US Census Data
House Count from Topographic Maps
TDL Houses Density
o - ¼ mile 30 2.64
¼-½mile 20 2.64
½ - 1 mile 17 2.64
1 - 2 miles 249 2.64
2 - 3 miles 544 2.64
3 - 4 miles 462.00 2.64
Density Is based on 1990 US Census Data
Total Groundwater Population
TDL House Count Urban Areas
0 - ¼ mile 79 17
¼-½ mile 53 10
½-1 mile 45 64
1 - 2 miles 657 301
2 - 3 miles 1436 33
3 - 4 miles 1220 0
Population
17
10
64
301
33
0
Population
79
53
45
657
1436
1220
Comm. Wells Total Pop.
66 162
352 415
190 299
994 1952
4339 5808
2137 3357
•
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GROUNDWATER POPULATION
DAVIS PARK ROAD TCE SITE
COMMUNITY WELLS
Well ID ari.j Name
B -Hedaewood Circle (C0-11
NA -Moore Community Well ( CO-22)
NA -Puritan Community Well CO-4)
I Subtotal
A -Jenkins Community Well (CO-3)
3 -Cedar Oak Park S/D
6 -Penny Park Dr. S/D
9 -Skvland Dr. SID
12 -Valleydale SID
!Subtotal
126 -Old Providence S/D
128 -Silverstone SID
Subtotal
15 -King Grant S/D
21 -Mountain Villaoe MHP
23 -Brimer Rental Prooertv
25 -Oakley Park #2
I Subtotal
1 -Alan Acres
2 -Beverlv Acres
11 -Sunset Park S/D
13 -Lamar Acres
14 -Park Place
16 -Maolecrest SID
17 -Hickory Village MHP
19 -Brenvwood MHP
24 -Northwoods MHP
27 -Raby's MHP
29 -South Lane SID
30 -Suburban MHP
32 -Woodland Acres
34 -Windwood Acres S/0
35 -Raintree SID
39 -Fallscrest II SID
40 -South Forest SID
41 -Amy Acres
42 -Castlewood S/D ---
45 -Shadv Rest MHP
47 -Chapel Acres MHP
48 -Scarrow MHP
50 - D M Rentals
51 -Hickorv Creek S/D
52 -Robinwood Lake
53 -Chapel Grove Elem. School
I Subtotal
5 -Lakewood SID
7 -Pines MHP
8 -Robinbrook Place
10 -Suburban Heights S/D
18-Jack -A -Shell MHP
22 -Fairfax S/D
31 -Wesley Acres #2
36 -Southamoton SID
37 -South Hills Estate Ill
38 -Woodleioh SID
43 -Stoney Uaks s;o .
44 -Bethanv MHP
46 -Snowshoe MHP
49 -Covinqton MHP
I Subtotal
• These population figures are based on house
counts from Figure 2 multiplied by the density
for Gaston County
Pop,
42 .
-~ [; "
16 .
66
29
69
34
60
160
352
30
160
190
519
135
40
300
994
417
147
344
159
135
240
160
70
75
84
48
186
128
88
256
240
124
60
135
65
150
81
65
25
100
757
4339
144
210
84
200
80
240
183
140
76
353
3C
75
56
260
2137
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MEMO
TO:
FROM:
DATE:
SUBJECT:
Superfund Section Staff
Jeanette Stanleyr / \
Environmental Chemist LA
NC Superfund Section
January 2, 1996
Update on Status of Wellhead Protection Programs in N.C.
Reference 11
I spoke with Mr. Randy Prillaman, Hydrogeologist, NC DEM (919) 715-6187. He said that
the Wellhead Protection Area implementation plan written by him and submitted to US EPA in late
December 1994 has been approved. This plan calls for prntection of a whole area based on a
calculation using recharge rate and pumping rate as variables.
North Carolina now has primacy in approval of wellhead protection areas. None have yet
been implemented. The Rural Water Association is preparing to submit several applications for
wellhead proptection, but none have yet been received or approved.
Some areas he expects to be the first to have wellhead protection areas are Gaston County,
the Town of Black Mountain, and numerous small communities affiliated with the North Carolina
Rural Water Association. Gaston County has delineated wells and completed a contaminant source
inventory.
.
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Reference 12
NORTH CAROLINA
DEPARTMENT OF CONSERVATION AND DEVELOPMENT
. -DIVISION_ OF ~HNER_AL RESOU_RCES -i .:·_, ','. ·: -·,./ ,_,0 ,,,;,
\),jj/lfU1ff'ffi'i~~;~fiiiljf ~if ?lf II il~f
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0t· EPARED 'cooPERATIYELY,111'v~=r11?GroLoG1cA ,suRvEt{>-,::
~.;~ ;•,;,·~",':-:;,I •:.~\7:.-t.8.'l,;,it;.,'i"'~,•~.,:,i9."£~1.;,, ~J.7' ;,-\·:·.~~),.,'f:~t~1f-~i<W~~~rl~~"W!:.'!;::W,~~~t~,., • ., ,,.~-~~ :·• ;, '
~~:,·~':!rH ~~tuHIT·Eo'·STAT·Es~·o~ePARTMENT:~oF·,"THtr~Tt~·,ct:~i~~.;~;}~t~~J~lf~·;.; ~:·t:::
' p.:._;~tt;{:~ 1fr?:~R ;;~~:V:t:C..."'5-":;,~),I , .. )1,~,r-.:.~\j•\f••"'S:."C.if't£$:1;.~~~.,.1~~"t-R~~~";-}fit.~1'~~,:~;-7;f (sl~l~.i:~'$~ . '"-~tt~I..{• ~ ~~~·1~i;~~--;-iJ$t~,;-~r~1~'r·.t~~;~ir?R,?i~·l!·:~-;~:~t?b1J::½:t--.~;':it~)~~~trl.i:,~~}f:1~:~.::,~·.\;;,_::}-:~g~-;tr~,. ~1:;:,t.'r•,!
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1i(~1i~,, ~1r-~,~~~ -::.!,,. t , ':'4", $r1Jf~>•<!n-~~--:5:~{t ... -:--+1.7, ~Jft~:t.tt.n;1'.'.t--' '":-";i,-_:.i.:~ i;-:,:-.7'>1 '7'.,'i:'~~ ... -;:~f~~~Kl;~\'l.~!~':"-1?:~~;~~1:,'j,_;:,.:-~ ~'-::1·:--: .. :, .. ~,?~, .. ~·.?,~;.:;i,;~~,-.; -"~ ,.,.,_,,,,,,, ,:.-.', ,"~ , •' r,,''''-''·'"-~-':;,,-.,.·t,,,..,~.,, .~ .. ,,. I !,_..,.s.;,""' ,,..,, ,-•••· , j'D-;,,.-')<,.. ,,.,...,.,.,_ • .,..__\,.""'"•"''-.i:•~.,. --.... ~~~,;,¥:,,:_;;.1•1~~ · •·•-~;.\.=,l::)o.:1?;-,,,.,,..s•}:.-._~~~ • ,._,~'l,:f__.,,,._ ,,..-• .,,~~"-~1-,,._..,.\,(!, .•• .,,;, ~ -,,, .. ~-~--.. -~-..,,,.._-,,.,,,.2'1,f,_.,,, •• ~.~ ,.,,,.,_.,.~ ...... ,:,.:.;,., ..... -...... ..-1:C:: .. t'"''/.
GEOLOGY AND CJWUND \VATEJ\ IN THE CJL\J\LOTTE AnEA 1 Nrnn11 ('.AJ<OLfN,\
GASTON COUNTY
(Area, ;:;ss square miles; population i~1 1950, 110,S3GJ
Geography and phy:,.;iog-raphy.-Gasto11 County lies in the south-central part of the Charlotte area.
Gastonia1 with a population of 2:3,003, is the largest municipality and the county scat. '1':~xtile manufac-
turing is the largest industry in the county although I.here is ConsitlCrable farming activity. The cOunty is
\vcll served by railroads and paved roads.
Gaston County is a rolling upland portion of the Piedmont province, the general altitude b~ing slight-
ly more _than 800 feet. Some of the strcan1s have incised their vulle·ys as mm.:h as 200· feet below the up-
land, and as a result the topography near the streams is quite hilly. Rising several hundred feet above the
general level of the country are several pronounced northeast trending ridges, all of which are composed
of resistant quartzite. Prominent among these are Kings fdountain Pinn~1cle, Crowders 1\tountain, and
Spencer 1\·Iountain.
The county is drained by Catawba River, which flows south along the east boundary. The main tribu-
taries of the Catawba flow southeastward across the general trend of the rocks and for the most part are
not noticeably influe11ced by any differential resistance of rocks to erosion. The tributaries arc closely
spaced, resulting in a fine-textured draina.ge pattern and the absence of extensive, flat interstream areas.
With the exception of South Fork Catawba River, the streams have fairly short steep courses, and conse-
quently are rather swift.
Gcolog-y.-l\'umerous types of rocks occur in Gaston County (fig. 13), and their relations one with au-
other are complex. The general northeaSt"sCi1istose structure prevails so that rocks of eastern -Cleveland
County exten,l northeastward into the western part of Gaston.
Mica schist forms the dominant host rock_ into which the granite was injected in Casto:, County. Nat-
urally enough, the granite did not intrude the schist evenly and in a few areas granite is either scant or ab-
sent in the schist. The belt of schist 2 miles east of Gastonia and parts of the schist near Kings Mountain
Pinnacle and Cro,vders Mountain contain very little granite. Muscovite or sericite, and quartz are generally
the chief components of the schist although manganese and chlorite are not uncommon.
Composite rocks in which mica schist and granite are interlayered, generally in northeasV trending
belts, arc widespread in the western two-thirds of the county. The largest belt in which the schist is pre-
dominant surrounds Kings Mountain Pinnacle and extends through the western side of Bessemer City to
High Shoals in the northern part of the county. The schist is subordinate in quantity to the granite in· the
area between Dallas and Stanley and along the Cleveland County line southeast of Cherryville.
Several masses or belts of homogeneous or nearly homogeneous granite occur in Gaston County. The
largest of these extends northward from the basin of South Crowders Creek at the South Carolina line,
through Gastonia lo Lincoln County east of High Shoals. One finger of this mass extends southwestward
to Bessemer City where it is the type locality for Keith's Bessemer granite." Another large mass of gran-
ite occurs southeast of Cherryville.
The granites are not uniform in appearance and mineral constituents. The granite.at Bessemer City
is locally more gneissic and contains more biotite than most of the granite in the county .. The granites for
the most part have a light color and medium texture, although small bodies within the complex pr9per are
coarse textured and niay be called pegmatite. ·
Gneisses and schists, containing hornblende as a prominent dark mineral, are common in Gaston Coun-
ty. In addition to the numerous lenses of hornblendic rocks interlayered with other country rocks, several
'·· large areas of hornblende gneiss occur. One of these, in the vicinity of Beaverdam Creek in the northwest-
ern part of the county, has been studied in some detail.'° Soils derived from the hornblende gneiss are gen-
erally dark brown or ~ed in color and are more fertile than those from other rocks.
' A composite rock in which diorite and granite appear as intermixed bodies occurs in a gener1:I north-
south belt along the eastern border of the county. This belt extends eastward into Mecklenburg· County
~-Keith, .,\rthur, op, cit .. p. ,L
~"Kesler, T. L., Correlation ol some metamorphic;_ ro<'Ks in the central Carolina Pie<lmont: Geo!. So<:. of Am>:!rica Bull.. vol. 55. P-773, 1944.
figure 13
t:f?@l
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L.Til
QITJ -E]
111l1lll!1lii
-~~
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-v,.,_o fx,
EXPLANATION
Mica s.chist
. and granite Mica s,:h,Sl dominanl sthist pr,
mica schis1 Granite arid edomin~n, gran,t• pr
Gr;,.nite
d dio1ite Gran~\~~'~' prrdomin,nt
.
i'ss and granite Hornb!end_e gne
in!erb,n
Hornbloende gneiss
Gabbro-diorile . ,ocL5 and ,n,rd bHoe
Quartzite
Limestone
/ ..
I :-,
FIGURE
' I • ,,_ -l > •-, <
' " • < J " \ ·. . : ,v::.
" (,-I> < ,..
~--?I,,,....,>
,; ,:> t-..., ,; ,'\ Y ' 's
"1 i-" ..j " .J ~ __ ,,__.,__,,_ so
GEOLOGIC MAP
OF
GASTON COUNTY
SCALE
0
GEOLOGIC MAP OF 13.-GASTON COUNTY.
C) > "' 0 t: z >
GEOLOGY AND GJWUND \VATl~R IN THE CH,\RLOTTE t\rU~A. NORTH C,\IWLINA
where it is of gre~~ter prominence. The roe.ks of the complex arc not well exposed, and as a _eon:-;cquence their relation with aclj:teent rocks to lht.: west is nut l'.Crtain. In this eonncelion1 a zone ot' diorite and diorite gneiss extending northeastward through Lowell is adjacent to the complex and may ue genetically ,related to it. South of Mt. Holly the amount of granite appears to be subordinate to diorite but northward the dio-rite is subordinate in amount. Pronounced granular disintegration is charncteristic of both components of the complex in the Charlotte area.
Several northeast-trending belts of quartzite occur in the .central part of Gaston Counly. The ridges that they form by their resistance to erosion serve to show the liroad structural trends of the rocks. ln the area south of Crowclers Mountain, Keith" has noted three divisions of the quartzite, nanwly kyanite quartz. ite, white, nearly pure quartzite, chloritic quartzite, and seritic quartzite. The bed:; of quartzite arc con-sidered to be of the same general age, but the relation of one with another is not clear.
Ground Wutur.-Most of the domestic water supplies, many of the industrial supplies, and two of the municipal supplies in Gaston County are· obtained from wells (fig. 14). Most of the water in rural sec-tions comes from dug wells that derive water fro1n the weathered and disintegrated zone between the soil .and the underlying unweathered rock. Where the unweathered rock lies near the surface difficulty· may arise in digging a well deep enough to obtain a dependable well. The failure of dug wells is not confined to any one rock type although attempts to dig wells on upland areas underlain by quartzite are likely to be unsuccessful.
Records of more than 200 drilled wells are included in the table of well data. The records of 151 wells were complete enough for use in compiling table_ll below.
T.\ll!.~: 11.-SU:.DL\nY o~· DAT.\ o:-. WELLS IN GASTON COUNTY
(Drilled wells 3 inches or more in diameter)
Schiiit .••..••.. ···-----______ .• ___ _
Cr:,nit,1 ........•.•........•........
All wi-lL, .......•...........••.•..
'J'Ol'OOfU,f'[llC LOCATION
HiU •••.••••••••••••••.•.••••••••••
Flat ••.......••....•.••.....•......
Slope ....•••.......•.••.........•..
Dr•"······························
ACCORDING TO ROCK TYPE .
:-l"nmh!,r of
weli:i
73
151
Average
Jepth
(rcct)
!!i5
172
Yield (gallons a miuute)
llanp;c
0-150
0-100
0-150
,\ vcra~e
23
13
Pn foot
of well
.13
ACCORDING TO TOPOGRAPHIC LOCATION
Numb,>r of
well.,
H
Avrrn!(o
depth
(feet)
1'3
HJ
191
Ji9
H3
Yie\J (!(allon~ ::i minul~)
A v~rage
0-" ·11
5-40 IR
1-150 "
2-10:? 26
0-25 1,
·Per root
· of well
.07
.13
. 13
. 14
.JO
Percent of wdb
yio:l,Ji11~ I ,-;,11!011
a minutu or
l'rrCTot of well.,
yieldio1s I gaUon
a rniuutc or
. le1111.
0
0
"
\
' \ ,
\
MAP OF
GASTON COUNTY
SHOWING LOCATION OF WELLS
I
I
!_
0
,iJ•
SC/I.LE
IJ ILES
2 ' ' =
-....f.QU!fTr
FIGURE 14.-l\IAP OF GASTON COUNTY SHOWING LOC..\TJON OF' WELLS
en
0
z
GEOLOGY AND GROUND WATER IN THE CHARLOTTE AREA, NORTH CAROLINA :iJ
Although the wells in table 11 were drilleci in schist and grnnilc, some of the wells probably. penetr,il-ed other types of rocks also. As the spacing between the different rocks can be 111Casured in terms of reei ancl inches it is inevitable that many wells pass through rocks other than that indicated at the I.op of thr well. The schist is composed of 111uscovite and quartz in most places, but iL 1nay contain beds of 1iorll-bicncle gneiss and schist, pegmatites, and other rocks.
Table 11 indicates that the average depth of wells in schist is 180 feet and that the average yield i, 2:~ gallons a minute; this compares with an average depth of 165 feet in granite and an average yield ot 1S gallons a minute. If average yield per foot of well is considered, the water-yielding characteristics of the schist is only slightly greater than that of granite. The average yield of wells in both schist and granite is 21 gallons a minute, which is 4 gallons a minute higher than the average for all wells in the Charlotte area. It is not certain that the higher yield of wells. in Gaston County is significant because the same general geology and topography occur also in Lincoln and Cleveland Counties.
The part of table 11 showing the relation of average yield and average yield per foot of well to the topography is signitieant. Wells located on hills have by far the smallest average yield and average yield per foot of well. In addition 7 percent of the wells on hills in the county yield l gallon a minute or less. As is the case in the Charlotte area as a whole, the wells on hills yield only about half as much water per foot of well as wells·in draws.
Analyses of samples of water from nine wells and one spring in Gaston County are given in a table following the well records. All but well 97 penetrated schist or granite or both.schist anci granite. Well U7 penetrated both granite and diorile. The water ranged in hardness from 26 to 158 parts per million. The iron content ranged from 0.08 to 8.6 parts per million. Water from different wells in the towns of Cherryville and Stanley showed a considerable local variation in content of iron.
Analysis of water from one spring is shown in the table. This water contained only 59 parts per mil-lion of dissolved solicls, despite the fact that it flows from hornblende gneiss, one of the most readily soluble rocks of the Charlotte area. The low mineral content of this spring 'Yater is thought to· be typical inasmuch as water from springs normally flows through the rocks more rapidly than water from wells.
Temperatures of waters ranged from 60" to 66° F. and averaged 62°.F. Tiie water havine; a tempera-ture of 66° F. is pumped from a well 1,053 feet deep.
There are two municipally owned ground-water supplies in Gaston County; in addition the town of McAdenville is supplied with water from a well owned and operated by a mill.
Cherryville, population 3,486, obtains its water from eight wells in various parts of the town. Ali the wells penetrate granite. The wells range from 132 to 238 feet in depth and from 10 to 75 gallons a mi:i~ ute in yield. · Six of the wells yield approximately 20 gallons a minute each. The chemical quality of the . water is good. The total dissolved ·solids of the water froin any of the wells_ does not exceed 115 parts per million. The water receives no regular treatment. . ..
Stanley, population 1,645, obtains its supply from four wells. Three of the wells are at least :J50 feet deep. They vary in yield from 15 to 45 gallons a minute .. The water from the ·four wells co,itains more than the average amount of mineral matter for all wells in the county and is slightly hard; the water from well 10 contained 4.9 parts per million of iron on November 20, 1947. The water is not treated.
tilt.·· _ McAdenville, population 1,059, is supplied with water from ~ well ow'.1ed by Stowe Mills, Inc. The Lt;:.. . well, 132, is 523 feet deep and yields in excess of 100 gallons a mmute. A field test showed the water had i:>-• a total hardness of 230 parts per million. The water is not treated.
\.rr~vL'.AJJ Af'OJ I.JtHJUJ\'ll \-'\' ATt.:t{ IN THE GHARLOTTE AREA, NORTH CAROLINA
Well
"°·
LocAflU,.. 0,,1nr ., DitlLU:K TyJJ•· of
-..~Jl
Omile!I l',K o[ Mou1Jt }folly .... Duke l'ower Co ....... H. L. l.1uer ......••• Cr-f>r
.... do ............................ do .................... do ........•..... 'Cr-Dr
.. • . do ••••.........•.............. dr> ..•....•.•......•.•. do.............. Cr-DrT
Lucia, 6 miln K. of Mount
Holly .•.•.•......... .Mr". W. T. Bratty ..•• Juli1U1 lh.~n ........ Cr-·Dr
.••• do ..•••.......•••• · J. A. Mdnto11h •....•••..................•. Dug
..•. Jo .•.....••............... W. C. McI11lO#h.: .•......••..•.....•....... Dlli
E:tanley ......•..........•.... G. K. DHr ..••...••.....•........ · ........ Cr-Dr
.... do .........••..••...•..... H. C. Mm1go ...............•••.••..••...• Cr-Dr
.... do ...............••.••.•.. Town ......••......•. \'a. Mach. Co ....•.. Dr
10 •••• do .••••...............•.....•. do .................... <lo ..•••.•••••... Dr
11 .... do ..•.•..••••..........•...... do .••••.••••...•...... do .......••.• ~·· Dr
Ila .••• do ........•.••..•••........•.. do .••••.••••.............. '. ........... Dr
12 ..•. do .•••••.......•• ~ .••••••• Lola Mil.Li, Joe ........•.•.•......•....•... Dr
13 •••• do ............................ do ...................................• Dr
H Alexia, 3 miles NW of.. •....••. JI. D.11radBhaw •...••.••••••...••......... Dr
15 2mileBSE.ofHighShoa!l! ..•••. llardioMfg.Co, .••••••.••••••••...••..•. Dr
16 llighShoa!l! ..•...•.••..•.•... Caroliriiau Mill ......•....... : ...•...••••.. Dr
17 .... do ••.••......•••••••.•.••..... do ..•............. R. E. Faw.......... Dr
1!1 •.•. do ...••••........•.....••..... do ...••........•••......•...................•.
IP 2 mill"!! W. o[ High Shl'.>lllii ...... 1' •• \. Ki~l"r ...•.•.•.•• Ya, Macb. Co ....... Dug-Ur
20 2~; milea W. of High Shoals .... Mra. M.A. Carpenter .••..• do ..........•... fJr
21 4 mi!ea W. of High Shoal.a...... A. M. Ki~r... ••••••• Robhina............ Dr
22 .... do ••......•••..•••••...... D. C. Ki11er ...•....•...... do ...•••..•••••. Dr
23
" " " 27
4},J miles W. of High Shoala ••..
6 milea W. of High Shoals ...•••
4 mil.-a SW. of High SLoalll ...•.
6 milr.1 E. of Chcrrn·iUr ••.•••.
4½ n.ii!ea E. of Cherryville
i-'orrel!t Dallioger •.....•... do ....•....••••. Dr
W. E. Ki11tr •.••••..••...• do.............. Dr
A. L. Barbee.......... Robbirui............ Dr
F. F. Allen •..•••......... do.............. Dr
G. A. Belt •...•••.....................•••. Dug
" 30
28 ..•. do ........................ G. W. He..m •.••...... RoU,ioa ..••....•... Cr-I~r
3½ mile.a E. of Cherryville ..... H. R.11ea.m ..••••..... Hiclory Pump Co .•. Dr
4 mile11 E. or Chcrrr,ille ••...•• .S. C. Carpenter. ••..•. Co!Jed ...•••..••••• Cr-Dr
3 mi1'2l. E. of ChnryviUe ••...•. Mu. Yrrna Payaour ...........•••••....... Cr-Dr
33 .••. do .•........••.•..•....... C. r;. lleam ..•.•...... Hickory !'ump Co .•. Dr
3~ •••. tlo •••.......•••..•••.......... do ........•.•.••..•... ti<> •••••••••••••• Dr
35 l½mileBNE.ofChnrpille .••..... do ..............•••... Jo .•........••.• Dr
36 Cbrrryville ....•.••....•...... C11rll,m ~lill11 .•.•..... Robl,iua ...••....... Dr
37 .••• do .•••••••..••...••••.....•.•• do .........••••.•.•... do .•.....••..... Dr
38 .••. do........................ C11roliua }'rci11:ht I_
C1mie!"l............ Hickory Pump Co... Dr
Jg •.•• do ...•••...........•.•..•. lth;·ue--llau11er Co ....•.... do ....•••..•.... Dr
40 ••.. do •.••••.......•.•••......•••• do .....•..•••.....•.........•.•.•••••. Dr
41 .•.. do ............................ do •......•.••••...•• _ ................. Dr
DrJ>th
of -,.,.JI
(ft-1,l)
4Ji},J
210
305
36
2:1
34
" 130
350
300
350
400
70
8.1
80
220
310
351
JOO
160
'°' 18
83
105½
J>O
128
1'3
"
80
121
"
127
100±
225
JOO
458
" I 18
300
170
IJ>OI
200±
ToLi.l h,,.r,!-DU.meter l~pth of W•ler kvd ,,_ (fitkl of wtll cs.ini:: ((C't't llf'lo-.. YJ"kl \f-11!1) (ind>~ll) (f ..... l) aurf~) (1.;.uu.) (p.p.rn.)
75+ ......... .
30+ ······•···
...,
3-J 20
········ .......... ········ ············
24
lb
60 30
25 "
26
20
120± "
IHO
JO
28
15
21
11-0
"
30
20-lS
5-6
6 60 10-15
5 6/8 .•••••......••.•.. ·••·•···
S 5/!i 73 •••·····•• 30--40
55/8 .•..•.....••••.... S
"'
30
35
"
"
50
35
110
75
50
40
'°
5 5/8 ..••••.•. ·•...••.•• ~-S 30
5 5/8 •....... ······•·•· 10 50
5 5/8 ......................... ··········-·
"
JOO
"
40
45
30
5 5/8 •.................
6 •••••••• ••••••••••
6 ········ ··••······
S 6/S ..••••......•.....
S S/8 .....••.....•••••.
IO
Mi,-
QUli~
IO
35
25·30
25-30
15
26
20
"
,0
60
60
'° 45
"
"
35
" " ············
Gn,nitr.
fut .
Hr.>IAHU
Gr1.ni~. Wdl 1.I rornn1illllllry.
Slope.
Not Ull(,.J •
Supp!ieii w111tr 'to IK'l1ool, f,.,-111
•t>d home. Cirnuih•. DrQW.
Slop/ Granite.
Gn.nile. Good yielJ reported.
Hill
Granite, Hill
Grnnite, At oue time wupplio:•d
IJ f1uuilie11 and &everal storea
Dr1...-,
62° F. Granite, A111.lyaia,
Well iii at tank. HiU.
62~~° F. Grauite. An.!y1ia.
Wei! i~ one-fourth mile nortl,
of tank. Hill.'
62½° F. Granite, An11lyni1.
Well i,•sw. of town, Hill.
Granite. l'umJJ acttio'1: at 150
feet; drawdoW"o rapid but
held at 20 g.p.m. 1.t 150 foot
aeltin1t, Slope.
Granite. Well at reiM"rvoir,
Hill.
Dye houae well. HiU.
Sel,iat, Formerly Ull(,<l l,y NIIW•
mill: large yie\J report-ed.
Slope.
Granite. u .. ' h.p. pump.
\'alley.
Granite. u .. ' b.p. pump. ""'·· Schist. Uae 10 'h.p. pump.
Slope.
Grauit.e. \'alley. '
Dug 61 ft~ drilled gg_
Hi!!.
Sehiat. Good yield reporteJ.
Slope.
60° F. Schiat. Coukl r.iot
lower 11"1.ter level wilb
bailer. J."lat.
Schist. Hill
HiU.
Slope.
Hill
Slope.
Hill.
Waler reported aoft, with no
iroo. Hill. '
"'ak-r reJ)()rte<l 80ft. Slope.
Slope,
Hill.
Hill.
Wrllaupplie:"Lai,ho=. SloJ>e.
Wei! Ly ..-a.ah Lou~c. Draw-.
6!½° F. Well at -..c.t rnd of
w1111le holUIC. Draw.
Draw,
61¼0 J,', Draw.
63,(' F. Draw.
62¾° F. DtQW.
GEOLOGY AND GROUND WATER IN THE CHARLOTTE AREA, NOltTH CAROl,INA
w,,11 Depth
Type of of well
If ell (fc~t)
4'!. Ch,.rry¥'1lle .••....•.......•.. Dorn Yarn ~lilb ...... H.li.lph Ro!,bin! ..•••. Dr 4Za .... t.10 ••••••••••••••••••••••••••• do ................•....••.....•....••. Dr -IJ .... Jo......... . ....... Tc,wn ................ Lre .•.•...•........ Dr H .... do......... . ... do..... Dr 45 •••• do........ ······:· .... ,Jo ........•...•...•.....•....••....... Dr
46 •.•. do ...........•.............•• do ..••........•... Lre .............••....•....
48 •••• do .•••••.•••••••
49 •... do ...•..••....••.
50 .... do .•.....••
51 .... do .••......•
!>2 •••• .J,i .•......•
SJ ...• do .•...
.•..... do ..•••....••......•••..•..
.... do .............••. Rohbir11.
.. fo................ Dr ..do.......... Dr .......• .... do .......••...•••....•.......••....... Dr
....... Jo................ . ......••.......•.•• Dr ...... ~o ...••.....•....•.••....••........••• Dr
SI .... do ..•. .......•........ Jo .................•..•...•.........•• Dr 5$ .... do.... . .....•..... Nu..-11.ySpinningCo .••. RalphRobbina ....•• Dr 50 •••. Jo ...• · .......•.....•.....••.. Jo ........•.....•..... do ..••.........• Dr 57 •••• do ...••...... . ....... Hhrne-llauser ~lfg.
Co ...••....••....••.... do .•••...•..•... Dr ..... Jo........... . ... ,Jo .••......•..•. Dr
59 ..•• do ...•.......•.....•••... !lo•cU MfR. Co ....•.....• do .............. Dr 60 •••• do ......••...•••....••....•.. do ..•.•...•••...•• Robhina .....••..... Dr 61 .... do ........••....••.....•.•..•. do ..•.•...•••.......•. Jo .••••.......•• Dr 62 4½ 111ib SE. ol Chun·vi!le.... Tryon School. ...........• do.............. Dr 03 .... ,lei. .....••...••..... F'rcJ lliggerstalf •....••. _ .. Jo.............. Dr 64 •... do Awler.'IOn Jf;;gcr ..•...•.•.. do ........••.... Dr
" D. L. K~r ..•......•.•... do ........•..... Dr
66 C. C. llarnl&on ••....••... Jo .......••....• Dr
o; 2!"!1 mib:,; W. ·of ll1-:,.vmcr City. H. V. Ouiton... •..... Hickory Pump Co... Dr
" 3 mill'! W. of Dall:lll ......••... Joe Holland ••............••.....•..•....• Du,i;
69 I¾ mile, W. of D111l"-'!..... •... It. E. Summey........ Rohhina .... . o,
o,, 70 2 'milr~ SI\'. of Jhl!u •......... E. D. Pa!\Our .........••.. do ....... . ;1
i'J.
;3
I¼ niiles W. of Dallaa ....•....
! mile SW. of Dalla!! ..•........
Dalla.ii •....•.......••....••
.Mountain .........•.....•..
County Home .••..•.• ·······-····· Dr, C. S. \'inceuL ........ Robbillll..... ....... Cr-Dr
~lorowrb Cotton Mill!!
Co .•....••....••......••....••....•.... Dr
Saro Love ............ R,Jph Rohbina ...... Dr
75 Speucrr ~!ouut.ain •••..•..•..•• Spen~r !llount.in
Mill ..•••••.••• ·.-••. R. E. Faw .....•••.. Dr ~~ .~~tl1:'.~e.~~\:·.~~:\~~'.''.1.t.~~o.l~~:: .Glo~ ~tilla, Jne .. ,1 ••• ··········:········· ~:
78 ! mile>:\\'. of !llmrnt Holly .••. K~ntlrick Brick,&.
Tile Co ...•. ~ •..•.•.•.•...•••.......•••. Dr 711 .••. Jo •..•.....••••..•••...••..••. do.• ••.•.••...•••......••••..•.•..•.•. Cr-Dr· 80 lmile::...ufMountHoUy ...••• ArnericanY,rn,Inc
Nilll.l,P!..nL .•.•... J.B. Hin110n ..•...•. Dr
81 3 milf'I N". of !lliJUnt Holly..... Duke Power Co.
Mou~tain Ialand
D,m ....••••..•••..•.•...•.•...•.....•• Cr-Dr
82 2½ rui!~ N". o( .\fount HoUy... Duke Power Co.
SupplyYard •.•••••. H.L.Luer ......••. Cr-Dr
2,0 ,oo
ISO
200
200±
182
177
150-200
150--ZOO
l'J2
H:J
\,0
no
11B~"z
J.',()!-;i
190!:;'.
H5
13'
90
00
lZS
119
15i
120
330
"'
H2
HO
" 82
"
130
" 65±
H3
60
185
''"
,oo+
"
223
Dia.meter Dt"pth of Wa.l~r level
of w~U ca:,i11~ (f'1't !,.,lo..-YidJ
(inches) (lt'ct) .,u,faee) fK-P.UJ,)
5 5/8
0
S 5/8 ••...... ···•··· .••
5 5/8 ........ JOO
S 5/8 ......•.
55/8 .......• 90
5 5/8 ·•···· ........... .
S 5/8 . ····••·
5 5/8 ······•· " 90
s s;s ........ ~o
5 5/S 11S ~I
5 S/8 .•••...••.•••....•
80
IIS
5 5/8 ··•••··• •.......•.
5 S/8 ...••......••....•
5 5/8 ·•··· .•.......•...
;5
!lO
"
ID
'° 50
30
"
30
20
,0
20.2s
'20•25
20-25
" IS
10-12
80
ID
26
IS
' " ,0
Total Jia.nl-
nn1s (fidd
lf'flb)
(p,p,111,)
f>O
'"
'°
65
"
"
,o
5 5/8 ·•······ .......... ········ ··•···•·· ..•
5 5/8 ·•·••···
30
5 5/8
S S/8
5 5/8
2
"
120
102
,0
IOI½
,0
H.18
"
62½
IS
12
" 10
ti
1'
10
0
2-3
46
" 45
" 35
60
"
53
~ot 1L-.cd; io!ulfieient yid,I.
Dr.J.w.
6t° F. Draw.
On E:~t ~lain Sttl'f'.t. r1at.
,\t old Churyville Mf~-Co.
Slop,•.
Analysis. Wdl 200 yda. S. of
Chrrryville Cuttou .\!ill. A-
n1J,yai1 in table. Dn.w.
A1,alysia. Ui1Jer water \ank.
Hill
At tool houu. Capped. 1.Jfil!.
At the pump at..tion. Hill.
At tank; i11 yard. llil!.
Analyait. llehinJ Canntry.
. Slope.
At cannery. Slope. I
Analysis. South of tank, oo
cannery lot. Draw.
~ear N°u•W•y mill!!.
Dr,w.
Draw.
Pt..ni 2. Draw.
l'fant 2, not w,eJ; inaufficiut
water. Hill.
Corupany"well I. Hill.
Company well 2. Hill.
Ifill.
&hiat. mu.
&hist. Draw.
Water reporte-d to eont,io iron.
&hist.
Schist. Large yield • .aoft w,1-er
anti no iron "port«!. Hill.
Soft water reported. Schiirt.
Slope.
\\'ell drilled on g-nnite le-dge.
Grauite. Hill. •-Granite. Good yield reported.
Slope.
Granite. Slope.
Granite. Slupe.
Oranite. Hill.
Juat helow top of sharp hill.
Schiat
Quartzite. D,-w.
Uaed by mill aud vill&ge. Slope.·
U8ed by mill and village. Hill.
Diorite. llill.
61° F. Diorite. Slope.
Well oot ueed; oo wa~r ob--
ta.ioed. Diorite. ~•..ney.
Granite. SuppliNI II futilin.
Slope.
G~i~. Hill.
SuppliNI J holl9et,
62° F. Schutt Supplie-,ill-
*<t!. Slope.
' ' ' ' '
54 GEOLOGY AND GROUND WATER TN THE CHARLOTTE AREA, NORTH CAROLINA
w~11
J)111u.,.11 l)ll.
~.5 2 mi!f'II R. of Mouut Jlc,Jly. _____ 8up1•riur Y,m, MilLi,
TurklLl't',11:..,. Plant.__ C.utN __ ..... ___ .•. 1i6 2½ milt·~ SW.of Mouut Holl)' .. J. \\'. Hyrd .....•••... J. W. J!oLLinr. 8i North Jlf'lmout. ......•.....•.. Acme Spinniuii: Co .••.. ___ _ 88 .... do ___________ ---·-------· .•.. do ___________________ _
ll()
01
.. do ..•• do .... ----·-..•... ---
Linford Mi]!,., Iu~------___ _ •. do ....• ·----·-------------l'f'rfeetiou S1,_inuiui;::
Co. _______ . _________ --------------------92 •... do ...•......••..••.....•.. F. E. llrlld!hn• ....•.. JiJ.ri.11M11 ...•....... 93 ..•. do........................ Stowt Spi1J11ii,11; Cu..... liiel.ory Drilling c~, .............. .
I I Typ,, of
-~11
Cr-Dr
Cr-Dr
I),
I),
Dt
D,
D,
Cr-Dr
!),
94 .... do ........................... do ..••..•......••. Jlobliina ..•...•...•. Dr 115 •... do .•..••..•...•...•.....•..•. do ..••..•••.....•. Wiue .............• Dr
96 ..•. do ..•.•.•...•.....••..••.....• do .•......... Wiue (T) ••••••••••• Dr
• 97 1% u1iJ,.s N. nf ~)moot........ Belmont AJ.,!..-_1·.. \'.11. !ll.11ch. Co Dr 98 lmileN\\'.ofJltlmout. ....... &>uthFork.Mh;.Co ... SydnorWrllC'o ....• !Jr
99 Belmont. ......••......• CliruaxSpi111JinJ;:"Co .... ······-·········-:-··· Cr--Dr 100 •••. do .•......•...•..••.. Stnlint Srii11nin11: Co ... Sydnor Well Co..... Dr
JOJ •••• do ... Cr1>ll{'c11l Spinni1111: Co .............•...•.... Cr-Dr 102 •••. do .•. ...•...• do ..•.•...••...••. H.F.. Fn· .......... J)r
103 •... do .•....••..•.....••...... X"tioru,1 Yam Mills
• •. . do ................•......•...• do ....•............ 10.5 .••. do ••......•...•......•....•... do .•...••..•• · ...•....
106 ••.. do ..•....•... · ..•...•...... Imperial Yarn Mills,
l11t .....•.. _ •.... .. Kirkley ..••........ 107 ..•• do •.....•••...••.....•...••... do ....•...•..•........ do ....••..•..... 108 .••. do •......••...•......•....•... do .•..•................•...•...••.... 109 ..•• do ••..•...••..••..........•.... do .....••...•................••..••... 110 •..• do ....•...••...••.•...•... Moutt..tU lee« Fuel
Co .•...•.....••...•••...•••..•...•....• 111 •.•• do ....•...•...•......••..••... do ....•••...•......•....••..••....•... 112 I milr S. oflJl']mo11t •....•..•.. lleury I.inel►t•riter
}'. \\". Muaa (Tl'lllllll) HoLLins ..••..•....• 113 l¼ milf'I S. of Belmont •...•... Mr. M11therw11 .........••. dn ••..••... 114 I mile SW. of Belmont ••..••... MiRS Floreuee A!11.-e
H. I,. Brooks
(Te11aut) ••••••••••••••• do ... 115 4mibSE.oflltlrnn11!. .......• W.G.Dreu11.11H ..•.....••. do .•• 116 •••• do ........................ J, M. Howen
S. H. lleufield ........... do .•....•...•... lli I¼ milt~ SW. of llelmo11t. ..•.. Eli.itle Yarn Milh ...... \\'ine (1) ••••••••••• 118 l½milrsSW.ofCnunerton •... H.R.J..ane ........... Jlurri8 ••••••••••••••
l Ill 2 miles Ir. of Cr"merton ....... II". S. Quinu .• • .. .•... lloLl,i1tJ ....••...... 120 ...• do •..•......•...•......•.. Artbor Sugga ..•...•....•. do •...........•• 121 •4mileliSKofG...,tonis ....••.. 1'lli.nlllliou!'ilc_ JlaruillmL ...•...•.. 122 I½ milcir XI\". of Cramerton .•.. l .. W. Fll.rif'I! .••....•.. ll.ll.lpl, Hobbina •...•. · 123 .... do ....•..•...•...••.. _.... Church or Gotl ........•.......••..•....... 124 •.•. do ......•...•...•..•..•••. \\'. K !->fitthl'IL ...... 11.li.lph Robbins ....••
125 ••.• do •.....•...•......••..••....• do .••.....•...•....••• do •......••..... 126 •••. do........................ W. J. si,~rer ...••..•.....• do •.......•..••• 127 •••. do .••.••....•.•.••.......• H. Q. McAt~r. .......... ~do ••..••..•...•.
.
Cr-Dr
.. c"r-D;
Cr·Ilr
Cr--Dr
Cr-Dr n,
Cr-Dr
D,
Cr-Dr
D,
IJ,
n,
D,
n,
D,
Du~·Dr
o,
IJ,
IJ,
Dr.
Cr-Dr
D,
D,
D,
D,
128 .••• do ..•.••••..•••..••.•••.•. Uf"t'Ce1lr11udo11, ...•••...•••.•••...•.....•• Cr-Dr
Dt>Joth
of -.,.U
{f ..... t)
37
IH
!1)3
31~
.52i
JO()
:_,~q ·~
1,053
85
300
"'
. 1/0
375
100+
132
128
118
]J'.!
148
160
103
"
80
JOO
112H
86
" 71½
142½
365
"
105
72~~
"10
M½
" 101
83
" 121
"
D,-1,tL or).W,tn levrl Di11m,.t..r
of •di l2lling (fed l~low
(incb'1!)
' 6
,_,
10-S·6
JO
'
JO
JO
(feet)
········
,0
·······-
........
........
~.\ (of
10 inch}
,~
00
80
80
1urf11ce)
··········
··········
..........
·········-
23
'°
. ••..•.• 3.5 10 40
"
5 6/8 ···••"•• s 5/S ;o
5 5/8 49
.5 .5/8 ..•.....
.5M!I
IH
JO
" '°
" "
.5 5/8 ···••"• .••..•.•••.
5 5/8 50
s ........ ··········
Yidd
(,i:.p.u,.)
10+
JO.
30
"
"
00·
2~~
BS
' 12-15
1'
I 16
60
I½
'
12
'
Tut>1I h11.rtl-
1 ...... (tjt'I<./
lat,)
(p.p.m.)
1'5
60
110
60
60
"
'° 60
80
60
60
............
"'
" 60
30
3½ •... ~ .••..••
3½ .......••..•
6
'
" 15° ·•••···•··•·
25
15
" '
16
27
2-3
15
JOO
"
" '°
35
125
140
" " 30
Schist Y•Hry.
nat.
62° F. &hi~t. Bill.
6J0 'F, &hi.,1. Company well 2: uorth tide of r,1.nt. lb,..-. &hi~t. Com, ... ny _we!! I; r..iit
end of mill. Hill.
62.!,;° F. Sd,iat. Hlupt>.
63¼° F. Schi~t. Slupe,
Schiiil. Hill
6!io J,', Schiiit. We!J ia cro()I.:.
l'U and turbine cau 't be •rt lower thau 85 ft. !JO PUnl),;;
only 35 i-1,.m. Slope.
&hl!Jt. Behiud church. Hill.
&hiiit. YielMd 60 gallons J>er minute when driUct.!. Draw Schist. Slof'('.
Draw. Ana.lyais.
M¼° F. Scbiiit. Pump art
to yield ◄Ii g.p.m. Draw.
Schllt. Ridge.
Schiiit. Yielded 18 g.p.m.
'll'hen drilled. Draw,
62° J.'. Schist. Hill.
Schi1l. Wdl 1.l111ridoned; uot
enough w1.ter. HiU.
Schist, 62° F. At upper end
or'mill. Slope .
Across road froru mill. Slope .
Schist. At. loll'er end of mill.
Slope.
Schist, Hill.
Schlllt. Slope.
Do.
Schllt. Dru.II'.
Do.
Do.
Schiiit.
Granite. Slope.
Supplies sii: ho= Dr11w,
&hilt.. mu.
Schiat. Slope.
03° J,'. Scbllt. Draw •. ' Schi3t. Dug 31 feet, Rodi~
fine grained: green to vray
1chi1t. mu.
Granite.
0
Slope.
6J0 r?. Granite. HiU.
Schist. Slnpe, .5 ,5/~ •..•.....• ···••··· .••..•.. Hill.
.5 ,5/8 ..•.....
5 .5/8
.5 5/8 ..
/j 5/!I
6-0
" 22
½------------
SuppliM II hollll('tl. Bill.
Schiiit, Not UMd; not e11ou11:b
w1.1.fr. Slope, 20 .••.•..•..•• Slope.
•..••....••. Slope,
3¼ Z.5 A well & fe-et de,ep, liO fe-et
from well 127-Yiel<h '11
r1.Ilon per mlllute. Slope. I½ .••.••..•..• ·Sofl wal4:r. Slope.
' i l ' t )
q GEOLOGY AND GROUND WATER IN THE CHARLOTTE AREA, NORTH CAROLINA 55
Rt:co1w:; OF Wtr.1.s IX G.\STOX CoVXTY-l'ontinuect
,q
!.•x.:1nos
12!1 2 mil,•~ X\\'. ofCramfrlon ....•• T. 1101)(' .•.•.......••. Halph Hol,l,i11~
130 .... do ...................•.... L. C. Hoard..... ..Jo ........ .
1.11 ____ Jo .... _____________ ........ __ .do .•... :. _____ ••.....• do .. .
!33 •.•• do ... __ .•.•. ______ _ .... Jo .. -!lol,hins ............ Dr
134 .... Jo ________________ _
135 ~: nii!e E. of Lowell .•......•.. Dr. ,J. W. Bri,J
11. T. !bwl.: (len:11,t). Ralph lto\.hin~---
!36 Lowell ...................... J. JL l!uJ11<>u.
l:!S ____ Jo ....................•....... do ...............•.. ·--·-············ Dr
1:19 · •••. do ...••• _··--·····--··-·-· _ ... do .....••. ·-······-··················· Dr
!~O I mile SW. of Lo.,ell .•.• _ ..•. _. \\" .. \. Fron"l>(:rii:er ..••. Ralph Rohl,in•······ Dr
Ill .... do __ ····-··-··········-··· Sc1icr'sCatnp ... · .•...•. _.do D,
II:! '.!!'1mik:iE,ofC:11.3toni.l .• _ .•.• (:a.1tonCou11tryClul, ...... do
11:J .••• do .•..•.• ·---·····-·····-· .... </(, ......... · ........... <lo .•
IH
115
'.! milr3 E. of G....itouia .•. ,\ krra .\1 otor l.i11c:i Co ...... do.......... Di·
3!'4 111i!1•s ;,,·~:. o[ Ga,,trn,ia ...••. ,\. ,\1. S111nr ,\If~ Ralph !tolil,i11~... .•. Dr
._ .. Jo ........ -··-···· .... do .......•.. ···-· .... do·-·-·-········ Dr
1-17 4mibSE.ufGa.:itonia ... -....
HS .• _.Jo .. ·-···-········
H.11n!o ;'\!fa, Co ..
Tcxtilr~. Inc.
. ... ,Jo ••.. _ ........• Or
/'ri-'filla !'l..ul....... ::iyduur l\'eU Co..... Dr
149 -···,1"··-········-·--···-····· .... do .• ·--··-··-···--!t-'llph ltohhio~ ...
150 __ .. do ••......••• -.. -·····-··· .'._.do .......•.• ... _.<lo ..• __ ········· Dr
1~! -··.du.·--·····-··-··· ... .do ... ···-··-·-··
15Z •••• do .•.. ·-······-••--· . do .. ·-··· ...... .
15,l •.. do .• _ .... ····-·-····-· -·. Rn Spinuin1 Co ...... .
151 •••• do···----····· _.do.·-········
... . do _____ ..... __ .... tlo._ .•....•.•
Z½ mik~ :-; E. uf (;aB1011i"··· .• . {;,o,•,·., Thrl"a1<l Co ..
\"a .. \laeh. C"···. ..• Dr
!bl1,h !tohl,iu~.--.
.... ,Jo.·-······.
0) ...........•..
D,
IJ,
llalr,h ltnbbi1,~...... Dr
15;" .. ;.do··-·······----··--······ .... do ••...... ·-··-··· ...• Jo .......•.•... _ Dr
1.5~ .... do.·-·-······-···-··-····· .... do ... ·-·····-····· .. _.do .•. _ .......... Dr
15tl° .••. Jo·····-······---·-······· .... Jo···-·-··-·--·-·· -·-·do .•• ·-········· Dr
100 -.'._<lu •.. -.. ·····-······•·-•·· __ .• do ..............••.... do.·-··-·······-Dr
161 --•• do •• _····--··--··········· .... do·-········-··--· .•.. do .........•.... Dr
163 ... ~do·-··---····---··-······· I-lint ;'\!fii:. Co ........• -·-·d_o ••. -..••..•..• Dr
· _ . 162 ... _do··--····-··--··········· _ ..• do_"·······-···~··· ._._do.-·-······--·· Dr
164 ---.do.·-·-····--·-········-·· ·-•• do ...... -····-·-·· __ .. do .••. ·-······-· Dr
lM .•.. do·-··--····-··-···--·--·· ._ .. do ......•••••• _ .. _ ••. _Jo.·-······-···· Or l -166 1!,,4mile,N,ofGMtonii; ... ---· C.A.B11-rkley •..•. -·· .... do .••• _ ...••.... Or
ti 167 ·n~ionia __ ···--··~---··-···-·· (:rrlllon Mills •••.•
'.!08 ·1··-·.-Jo._._._ ... ____ ..... -.. -.. Suori-"' O11-irr .••...... Ralph lloLLin1 .... _-· Dr .... ·'
1 .-/i'itlfl ,
1
r.a1tooL-1. __ ·------··-·---···· Su11ri:ie Dairy .• ·--·--· Hah1h Rohl,i11~ •. -... Dr :11 .. •'1.:;(f _l.milf S. of (;:i.3lmii11 •..•.. -··--T~itill"II, lnr.
S.-111inole !'!ant .•...• ··-········-······· Dr
I; I ! .~f mil~, 1$. of n:i..,tonii.. .. . . . . . lfol,y Cotton ;<.!ill. ....... ___ .......•... _.. Dr
r:::",' ..... J•>--··-·--···-············ _ .. Jo .... .
1;3 .... J,i .......... ·-· ...•....... , ... Jo ... .
(T) •••• ·-··········· Dr
D,
Drpth
of well
(feet)
,;
66
Ill
52:J
""
120
;1
1-IO
IIXl
r,o
22.S
5&1
;o
!ill
:mo
130
191
·145
" 90 ,.
132
60
69½
" 167
133
:?65{1)
136
120
!35
'" 185
Diainekr
ofwdl
(iuches)
Depth )Waler level
,·a.11iu,: (f~t lwlow
(feet) ~urface)
5 .5/8 " 5S/11 50
-~ 5/8 so
10-8 t;O
5 5/.S ........
···---··
32
.S 5/8 55
5 .s:.~ ....... .
.5 ,\IH
5 5/11
.S 5/S
~ 5/S 60
,.,
.s .5/8 ·-···· ..
5 5/8 ·····-·.
.~ .S/8 Si
5 ,\/8 --··---·
5 -~/8 ··•·•··.
6.
"
······-···
19. I
3S
"
6 ····-··· ••••••• ··-
5 5/8 ·-··-·-· .W
.S 5/8 ··-·-·--.
6 5/8 ··---··· H
5 5/8 9i ZS
15 z.s
30
:io
I Tota! hard-
. ,. I nt1111 (field
) i,•ld lr~l~)
(g.p,m.) {11.11.m.)
100+ no
II
w
10 " I.I
"" I .: ...... .
II
60
20
20
I
" ll
12
20
20
IO
!02
IO
10
"
15
""
35
15
::o
16
12
12
II
8
30
20
30
15
21
!
"'
.15
30
p
····-···--··
so
,0
l 15
31)
"
30
Slope.
SchisL Ifill.
&hi~t. Sot W1cJ. Xn water.
Hill.
6,1!{° F. Suppli(•a mills and
town. Slope.
&hi!t. Use,.! only in emer•
gency. Slope.
&hi,t. UseJ only in emer•
gcMy.
Schiat. Drnw,
Supp]iu .15 ho11~1·s :,nJ 5rnra1
bwim·='~-Draw,
:-.ot in u.,,e. Water reporlt'd
to be harJ. Orn ....
Do. Slope.
&billt. Slol)t.
&hi1t, Water rcport<.'t.l lo be
corrosive. Dra.,,
&:hist. Draw.
Not U1C1l; not enouii:11 .,1dcr.
Schi,t. Slope.
Schist. Slope .
2 other ,imilar .,db at n;ill
anJ yi!la;;e. Flat.
Yidded Z7 gallonn a n1inute
.,hen JrilleJ. Hill.
Draw.
Not used. Te3ted at 651.p.m .
.,hen Jti!led. Yield de-
creased to 20 g,p,m. whco
abamlon<.'t.1. Hill.
Schist. Not u~cd; cu.pr,<·d.
Hill.
Schist. !'iot U$Cd; ca11pcJ.
Dra.,.
62!7° F. Schi:it and quart1ite.
Dra".
SchUlt. Yielded 2.5 to 30 1,p.m .
.,h,:n Jrillt'J. Dra.,,
Schist. Hill.
8chist. Al1$udo111:d ))(.'(:.illlle
.,ater l~c:ame mutlJy. Ora.,
Bill .
(;r11.nitc. Water oUt.i.iued a.t 80
fttt. Dr"""·
61½° F. Grauitc. Dra ....
Gnuiite. Dra.,,
Granite'. Well al rc11ervoir.
Draw.
Granite·. Draw.
Granite. Ora ....
Granite. llitl.
Gr:.nite. Dr:..,,
Do,
Do.
Supplie. 9 boUJ1CS.
Slope.
&hint. Dra ....
Schiat.
Schilll. Water obtaineJ at ;"O
fe(!t. ~lope;
Granite. Dra ....
Granite. Slopr,.
62° F. Grauite. Ora ....
Granite. Ora ....
C'iranite.-!Iii!.
f;.
II
II
• I
q
q
q
IJ
I
I
I
I
I
. ~··
11:/
•.'
56 GEOLOGY AN!l GROUND WATER IN THE CHARLOTTE AREA, .NORTH CAROLINA
Well Loc~TION o ....... ,:'n l)JUI.LLII Tnieof
well
174 l),(ruile11S.ofG11,11Wui11 •••••••• Tntile1, Inc.
~la J'lant •••.•••...•.•.•••.••..•••. ~ Dr
Ji5 I½ mill'.& 8. of GMtonia........ Di loo Milli1........... H1tlph Hc>!,hins...... Dr 176 •... do ...•.......••....••..••..•.. do ...••..••••..••....• do •••...•.....•. Dr ]ii 2mil~S.ofGutouia ...•....•• Tntilt'!I, foe.
\'ictory Pliml. ...••. ·--···--·--······:·· Dr
Jill 2½ miles S. o(_Gut.ouia •....••. Tntilea, Inc.
Myen Plaut •....••. JLv,lpli Kol,l,irJJ1 ..•..• Dr 1711 .... do ..•....••...•....•••..••...• do .••••....••..•••••.. do ..•••..••.••.• Dr·
180 .... do .•..•....••....•••....•..•.. do •....••....••......• do .•...••...•..• Dr 181 2X mil~ S. of Gutonia ..•...•• Ile1-Hanovcr Mi]!.,, Jue.
{Hanovtr Plant) ..•.••.. Jo ...•••..••.... Dr
J82 ..•. do ....•.....•............•.••. do .•.....••...••.. Ware •••...••..••.. Dr }83 ...• do .....•.....................• do .••..........••• lto1il,i118 •...••...••. Dr 181 3!,,l rniles S. of Gaiitouia ........ Tcxtile6, Inc.
Jtidge f'lant. •••....••.. do ....••...•••.• Dr 185 .... do .....••......•.........•...• do .•....•....•••...••. do •••. · .••...•... Vr
]86 2½mi!esSl-:.ofGa.donia.· ..•.. J.A.llr&(bh11.w .....••••.. do •.•..•... : •..• Dr 187 3½ milea SE. of G1LStoni11 ...... Roloert M. Jll"!rndon .•.•••. do ....•••..••... Dr J88 .•.• do .•.••....••......••...•• H. It. Kendrick. ••...•••.. do • .c •••••••••••• Dr !89 Guto11ia ..•.....•.......•...• rireatonc Milla, Irie .•....•• do •••..•••..••.• Dr
190 .... do .•.....•.....••....••......• do ...•...•....•••. Holiliina (!) ••...•••. Dr·
191 ••.. do ...•.•...•••....••...••..•.. do •.•.•...•••...•••... do ...••...••..•• Dr
Jf/2 ..•. do .....•.....•..•...••...•..•. cl"················ GllY Hobhi11s ..•••.. Dr 193 .... do ...............•...••....... do ..••..•••...••....••...•••..•...•••• Dr
194 •... Jo ......•...........••..••.... do................ • ..• . . .• . . .• • . . . • ..• Dr 195 .•.. do .•........•....•....•......• do ...•....••....•. lfol,t.in, •....•..•••. Dr 196 1!1 milt's W. of Castoniw. •••.••. 1':irkdalt· .\Iii!, Jut: ...•••..• do ..•••.....•••. Or 19i ...• do ...•••••...••....•....•..•.. do .....••..••....••... do •...••..••..•• Dr 198 •... do .......•......•....•...• Bloom .\lillll, Iuc .•..•..•••...••.. , .••..••... Dr 199 ...• do ..•.•....•.•..•••..•••.. Textil,~. Inc.
,oo
. 201
,02
· 203
204
205
,06
207
• Arliugtou l'l.aut ••.•..•••....••••••..•••• Dr 2 1nile8 \\'. o{ Ga.:itonia .•...••.. Threads, Inc ...•..•... ltol,L,in, ..•..••..••. Dr . • . . do ......•....••....•....•...•. do ••...••....•• · .• J. S. llin11<m.... ... • Dr .... do ............................ do •••..••...••...• RoU.'i1111 ..••..•••..• Dr •... dn ...........••...••...•..... do ......•...•..... J.S. !liJJ~ou ..••..•. Dr .•.. do ..... . .. do .••...••..•••..•.... do •..••••..•...• Dr 2¼ r11ile, I\'. of G11.~t.onia ...•... T~xtili·a, Inc.
Myrtle !'!ant •.••••..••...•••..••...••.. JJr !~1 mile~.'\\\". of GlL1tonia ..... Clyde Bradford .•...•• Jt.Mlph Rohl,iru ...••. Dr .... do ..............•... · ••..• D. W. Dr.wJJ .•••..•.•.•... do ....•••.••...• Dr
208 •... do .........•..........•... O. L. Hhyne ...•.......••. tlu ••..••...••.•• Dr 209 2½ iniln Kl\". of(;uto1Li11 .•.•. (). H. Jrnliru ..•••.•• '. ..•• dn .••...••.•••.. Dr 210 ...• tin ......••......•...•....• .\I. B. Jrnlius ••...•.•.••.. do ..•..•...•...• Dr :!!I ..•. ti" .........••.......••••. IJ. L. Wyont •....••..••... do ...••......... Dr 212 •... do ....................•.. J. Frourlocr11:rr •••...•..••. do .•••.•.•..•... Ur. 213 3!{ mil~};\\". of G~tcmia ..... l). n. Jlurr,~ .•....•... \';,.. Mad,. Co ......• Dr 2H 2 milr6E.of B=mn City .•... Jt.1:1111 S11in11i11R Co .•..••...••..••....••..• Dr
215 •... do .•...•....•••....•.•.....•.. do .••..•....•...•• ft.Mlph Jtnbl>i1111 ..•... Dr
216 •.•• do ........•....•..•..••.•...•• tlo •••.•.•••..••..•.. ~.do .... a ...•...•. Dr
2li I¼ niibE. of lll'$.~n1tr City ..• Jtle11I .\lr.rhiue Shop ... !Ullr,J, !lol,t,ir111 .•..•. Dr
J)epth
or .. ,.iJ
(Ifft}
"'
JS.,
63
110
!OJ½
120
180
26i
140
18'
120
.,
55
3.1
80±
214
125
1-15
w;
" (I)
I&>
''° "
]60.
105
''° i6½
4!i0
(l{M)•!OC)()
160
53
64½
11~
100
110½
ii
1:ii
110
271½
130
Dlllmet,·r J~pth r>f w .. 1rr frvel
of wdl 01.11i11i (fe"'('l bdow
(incht>a) (feet) aurface)
• \MB .•.•..•.
5 6/8 ....••..
16
10
5 li/8 .::.: •.. ·········~
Ii 6(8 •••••••• ••••••••••
· 5 5/8 ·····-·· ...•.....•
'°
112 ··-·······
6 5/8 ·•···•·· ·•··••··••
5 5/8 35 10
5 5/8 ··•··••· .....•..•.
5 6/8
5 5/8
Ii 5/8
6
6
5· 6/8
5 5/8
5 5/8
5 5/8
" 40
"
100
100
44
'°
" ,15
13
"
. J3
10.2
J0.6
5.0i
"
JO
Ji
20
.S S/H ....•...
5 5/8
5 S/~ r,
6
6
5 5/8
I,\
40 as
l.'i± ......•...
80
106 50
110 27
Yield
(~.p.m.)
35
16
12
5
16
6
20
JO
' 20+
'
40
44
80
20
18
:1:1
" IZ
IO
35
8
J8
JO
12
15
JO
' IO
'5
15
50
"
12
Tou.1 hard-,e~ (!ield
ln!JJ)
(p.p.m.)
35
,0
············
35
"
············
············
35
············
" 20
55
············
............
············
............
············
······•····· ............
35
············
35
30
,.1
30
35
w
" 25
35
'°
"
50
Grr.nitt:.
Hill .
Grr.nit.t .
Do.
Granite.
Grw.nite.
61½° F.
Draw.
Ori11:in~Hy yiddrd n
Flw.t.
WeU 111 mill. F!~t.
Gran it!'. OriRinally yielded 29 g.p.1u. Dra.,.._
Gr11nite. \\'ell in villai-e. Iii~
62½° F. Grauit!', \\'db1s1
182 and 183 supply •atcr
for plaot r.JJd TIii.age. Analr••
ai~ of water from well 152 in table. Ttmf"'rature 10rcil
182, 64° F.
Gl"lrnite. J)ra11".
Granite. Dr11,r.
Granite crof)<S out SO fl-cl fro!ll well. Hill.
Grr.JJitc. Draw.
Schist. Fiat.
Sehi~t. Flat.
Granite. Water reported ao[t.
Draw.
GraJJitc. Well l; not in ou . Draw. ' Grr.uite. Well 2; 'not i11 Ust.
Draw.
GraJJitc. Wl'll :1 • Drai><.
Wet!~; not iu u~c. Uranit,.
Draw.
Graoitc. Well 5. ,Dra"··
Granite. Kell 6.
GraJJite. Draw,
Granite. Slope.
GH.f' F. Grr.nite. 1 Hill.
62½° F .. Grnnite., lli!L
Granite. Not iu u~. Drall'.
Granite. AhandoJJt:d. Drall' .
Granite. NotiJJ use . ,'$1(Jpr.
6:l~C F . Grauite.
Grauite. Draw.
Grauite. Slope.
Granite. Slupe.
Granite. Supr,lirs ' liou~es .
Slope.
Grnr,itc. Hill.
Grauitr. Hill.
Gr1111itr. !!ill.
Slope.
Sopplir.s larl(C form. S/opr.
Schist. Did well iu firld, oot
U8Cd. Slope.
62!-:' }'. Schi~t. ('ompaoY
wrll I. Draw.
Cor111111ur wPIJ (at ~hool
housr). Hill.
Schist. Draw.
GEOLOGY ANIJ GROUND WATER IN THE CH,\I<LOTTE AREA, NORTH CAROLl1'A
Hf;COJli)S OF \Vt:r.J,S IS G,\l'IT():', Col.iS'fY-Conlinued
Ow.~,:11 DRJl.f.r.R Type nf no.
wdl
ZIS B~cmu Cilr. -,\lgodon .\lfg. Co ......•... do ......•...•..• Dr
:!:!0 !,!1mile!SE.ofBc:iimnerCity __ L.A. Wolfe ......•.... Ralph Rol:.!,ius ..••.. Dr 221 2 mile~ SW. of Bri111cmer City ___ ILL. Lc'lfi~ Dairy ..•....•. Ju......... Dr :!22 2½mi!e11S\\'.of/!e!•mnnCity. J'ineCroveGri!I ......•... Jo ..•..........• Dr 223 I mile NW. c,f Kiu,:s :\lountain.. Earle K Carr,...nt<:-r _ .•..•.. do.............. Dr 221 .\lountaiu \'icw •.............. Frieda .\lfg. Co ....•....•....•......... : ••. DnJP; 225 .... du ••••••••••••••••••.••••••••• do ...•....•..••....••..•...•.......... Duii; :?26 .. Jo .....•....•............. H. IL !look. ..•.....•. Ralph Roht,ins ...••. Dr 22i .... do ....••....•....•...•.•.. Harvey Flume •....•....•. do ......•....••• Dr 22S !-7 mile :,a;, of .\!ountain
\'icw ...........• ,. ......•.. Mra. E11re Rob.·rls .••.•.•..•.•..•.•....•.. Duw: 229 2H miles SE. of .\louotain
Yirw ..••..........•.......• A. L. Dial. .......••.. Ralph ftobbius ....•. Or 230 3 ruile3 S. o[ Mouut11in View .... J. A. Stroupe .•..••....••...•..........••. Br
231 ~)'2 niilt'>l S. of .\lount11in Vie".. WifflOn and Brotl'n..... .•....•..••..•....•. Dr 232 5111ilfsS.ofG11,11to11i11 .•...••..• T. I .. Hovis .•.....••.. R..lph Rohbiu, .....• Dr 233 51/JmilfsS.ofGaMonia ..•••. KnnBr:rndoo .•......•..• do .••...•......• Dr 23~ 6 mi)!'a S. ofG.uitoui;i. ...•....•. C. E. Hoi1eycutt .•••.•.••. do ....•..•....•. Dr 2:\.5 ••.. Jo ....•....•....•....••.•. W. L. Hutchison ..•..• Tom York ....•...•• Cr-Dr nt; 7rnilraS.of(;ut.ooia .•....•..• Tom Sparrow ..•....•...••...••...•....•.. Duii; 237 iH rnile11 S. of Gaatonia .•...•.....• do ...•....•.. : ...• Ralph Jtohbina ....•. Dr
23.S 4¼'1nilcsSE.nf(iMtoni11 ....•. Carroll Kerr •..•....•...•• do .••...•...•..• Dr 239 Hi mi lea SE. of Ga3toni11. ...•• W. S. Torrrn!'e
F>1irvie" D>1iry .......... do .......••...•. Dr 210 .•.. do .•...••...••........•..• Gutoni.1. Airport ...... U.S. Army ..•....•. Dr 2t: 5~{ n,il!'s SE. of Gaatooi.1 .....• S11.n,Jy Plain Church .•. Tom YorL ..••..••. Cr-Dr 212 liJ-:i milt>~ SE. of Ga&to11i>1. D. F. lia.rrison .•...•.. Gffirge Stepheru,on .• Cr-Dr
De 11th
Of WpjJ
(f~el)
l lJ
t,0
ti"
160
t65H
too
1t
t7
tot
07
"
J3i½
"
70
108
"' too
90
" 1'25
90
t,\O
I0'2
90
"
Di,on,elrr Depth of Water level ,,r ,..ell ca.,ini; (feet h1:low
{inche1) (fed) !Hrface)
.~/8 101 11
,0
5 5/8 " " 5 5/8 "' 65
5 l/8 ........ ..........
S 5/S 80 50
" 1t Ji .08
" t7 6 .50
5 5/8 ........ 6t
5 5/S 56 13
30 0 . 80.9S
5 5/8 ........ ..........
12 -16 .'!2
6 40
5 5/8 ........ 48.00
5 5/8 ........ ·········· 5 5/8 ........ ·········-
10 ·t8
" 6t 56.25
5 5/8 ··-····· ..........
5 5/8 ........ 2t
5 5/8 ........ '° · i8 t5
........ ·········· 18
Tot.al hard• ,~, (lidd Yir.ld te11t.11) (g,p.rn.) (1q1.m.)
" ............
t5 ············
10 ············ '" '° 20 1'
" ........ ............
t5 ............
2H " '°' ,0
........ ············
H 35
,0
50
' " t5 20
IS-20 ,0
1 ···•········
35
20 ............
,0
10 JO
,0 ............
1-5 ············ ' ············
ANALYSt:s OF Glt0UN11 \VAT~;Jt FJtO:Ol GAHTON COUNTY,• N. C. (Numbers at heads or columns correspond to numbers in table or well data) (parts per million)
9 10
Si!ic'ut. (SiO,) .•••...•...•.••..•. " 20 Iron (l-'e) •..•••••••••.••••.•••. .23 .. , Calcium (Ca) •••••.•....•..•.••. H Jt Magne11ium (Mg) .•••••..•.••••• 3 ' ,.o Sodium and pot.ugiu111 (NA+i{) .• ti '·' C11.rbonate (CO,) ••..••..•••..••• 0 0 Dicarbon11.te (HCO,) .•••..•.••.•. t60 t2' Sulfa.le (SO,) .••...••.•..•.•.... o.7 10 Chloride (Cl) ••.••••••••.••••••• 7.0 ,.,
l-1uoritle (~') .••.•.••.•.....••... .3 ·' Nitr•te (NO,) ••••.••• ~········· ., .0 DiMolveJ 11alid1 •••••••.••.•..••• t66 138
To Lal h.11.rdnemi 1o1 C.CO, •...••••• "' " ---Date of N)\Jeclioo ..••••••.•••..• I t/20/47 11/20/47
• Au&!yBis made by U. 3. Oeolnttieal Survry. •• Plow~ 011"°h1o!f g,p,lll. from hornhl~ude gnei!IIJ. •Fein !IOlution .OJ
ti '" '7
---
Jt '!7 35
.H ,., . 15
" ti to
,. t ,., LL
" ,., 8.3
0 0 0
107 " 10
113 Lt t.9
2.2 u t3 LO .0 .0
t.t ,0 10
WO to7 ttl
"' " 0
llf~'0/4i 2/111/48 2/111/t~
Spring•• 5t " 97 182 (Gaiiton
Xo. A) ------
30 :15 :Ji 31 23 .oa .59 .till t.O .:?la ti 9.2 t2 8.:! u 6.2 . 4.5 ·f.i t.l 2 .2 '·' ,., ff.1 10 5.3 0 0 0 ·o 0. 52 37 " 3t 3t 3,9 2.9 t ' t.3 u 7.1 ,., t.6 " LO .o .o .I· ,t .0 8,8 " 1.0 6.t ., tl1 10; tot " " " " " " 21
2/13/411 2/lll/4S 8/11/45 8/11/~5 5/'l0/49
57
J{r.lolAtl~i!
Sot t~d; wat.:r rt Ported to ~ too ha.rd. FLot.
Pumped at ~.:'i g.p.m. b11! "ill not ma.ini.i,in thi8 yield Flat.
Slo~.
SchUJt. SloJJC,
Schi~t. Slow·.
&hiH. mu.
Schist. Supplie11 vill,~,. Hill.
Grave!T. VaHey.
Schist. Slo~.
Schist. Dr•"·
Schist. Hill. .. , ,.
Do.
&hiat. Supply (a.lk<l <lurinii;
autumn or IIHO ood 1941. .Hill. ... Schiat. HiU. '(, Granite. Hill.
Schi•t. S!n11e.
SchUJt. /, Granitr.. t Schist. Hill.
62° F. Schifft. c_.d " to i5 reet. Hill.
Schi~t. Slope.
Schist. Dra'lf,
Do.
lli!J.
W11ter reported 110ft. Hill.
DATE:
TO:
FRCM:
December 23, 1993
File
Harry Zinn, Environmental Engineer
North Carolina DEHNR, Superfund Section
RE: Hydrogeology of Gastonia Area
Davis Park Road TCE Site
Gastonia, Gaston County, North Carolina
NO) 986 175 644
Reference 13
On December 22, 1993 I talked to Mr. Mark Durway (704-868-
3743), the former Hydrogeologist for Gaston County Health
Department, Environmental Health Section from 1991 to 1993, about
the hydrogeology in the vicinity of South Gastonia and specifically
the Davis Park Road site. Mr. Durway stated that. in the area of
concern, there is no confining layer between the saprolite
(weathered bedrock) and the bedrock. The majority of the potable
water is obtained from fractures in the bedrock. His conclusion is
supported in three ways. First, this is based on all of the current
literature available on the local geology. Second, it is supported
by field observations of the stratigraphy in the area in the
vicinities of bedrock outcrops and stream bed cuts. Finally, it ,is
supported by personal geologic experience in the area during his
three years in this area.
UNITED STATES
DEPARTMENT OF THE INTERIOR
GEOLOGICAL SU'RVEY
I
DEPARTMENT OF NATURAL AND ECONOMIC RESOURCES
STATE OF NORTH CAROLJNA
81 "22'30''
3G 0 22'JC,''
"14000~ N
"13
RlOOCC FEET
IS 8 I
, ..
ii ,, ,,. , '" , . ,_ '_,
"" J(!; ,
•
-/-"' •• , :,II ,.
12' 30" ,.
f,
510000 °£ET
(N CI
3.5' 07'30"
81°22'30'
BESSEMER ClT'(, N. C.
1 lrff.OUTON 15 J.U.\J~MUL.>:
N3515-'/'<8,J 5/7 !i ..
1973
AMS 4734 IV SE-SERIFS ,'511 • 1/// ,: ~'\ '
-rz ,M, ictt:;1~1-:~ ~:i;f,:.:~y ;'-:r ,<,, ·~---, r-
~~; c-· !~~f _:J11 ~~:~ -::,i,~-~s.~ -.)~:~~~<~,S~;
' ' ' c , '•"•• ,-,SC, 37 ', ,-✓ --~ ~-J
,,, ./) , I 'ti ]!f} · •~ " · J ·"''iffllil/': -d._,, -• (_, --1· fl&-. _,,.-Ji ,;J,",,,i,.,s:._c.t_,, J I\ -~ ~~•¾ G,ove ~--,. "" ·w,, ,, ... = 1,;, 1
/ (h / ,ffi~•I ,. ••i,;_<1j !ij/'j,'f. JJ i i:'~•;'~ or,· • ½,1i!fJf,, . . i e ' I ] ,~ . \-," . --::-. Xv: ')'--; ,.. ' . -'i/iJ '. I
,--(,)&fr;, : I <; ' "''!It.·•, ·ts,:;,;,_~)' !J;,, .,t ->, .,,~~ ,, .. /
• ,, •j /• "';, . ', / •' ---.f'l!j>:.
DL
/0-¼ mile
¼-½mile
I
GROUNDWATER POPULATION
DAVIS PARK ROAD TCE SITE
COMMUNJTY WELLS
Well ID and Name
B -Hednewood Corole C0-11
NA -Moore Communit W.11 C0-22 " Puntan ComlTl'-Jnit Weil co-4,
Subtotal
A Jenk1r,s Corr,mun1
3 -Cedar Oak Park SID
Well lCQ-3)
6 • Penn" Park Dr SID
9-Sk.land Dr. S/0
12-Vallevdale S/D ,
!Subtotal
½-1m1le 26 -Old Providence SID
28 -Silverstone SID
Subtotal
1 <2m1les
I 15-Kin Grant S/D
21 -Mountain Villa e MHP
23 -Brrmer Rental Pro ert
25 -Oalde Park #2
/2-3 ITll/es
3 -4 mrles
1 -Alan Acres
2 -Bever1~ Acres
11 -Sunset Park SID
13-Lamar Acres
14 Park Plaoe
16 -Ma"lecrest'S/D
17-Hickorv V,lla□e MHP
19 -Brenvwood MHP
24 -Northwoods MHP
27 Rabv's MHP
29 -South Lane S/0
30 -Suburban MHP
32 • Woodland Acres
34 -Windwood Acres SID
35 -Raintree SID
39 -Fallscrest IJ SID
40 • South Forest S/0
41 -Am" Acres
42 Cas~ewood SID
45 -Shad, Rest MHP
~al Acres MHP
~rowMHP
50 -D M Rentals
51 -Hrckoru Creek SID
52 -Rob1nwood Lake
Subtotal'
53 Cnanel Grove Elem School
/Subtotal
5 • Lakewood SID
7 -Pines MHP
8-Robmbrook Place
10-Suburban Hei his SID
18 -Jack-A-Shell MHP
22 -Fairfax SID
31 -Wesle Acres #2
36 -S□utham ton S/D
37 -South Hills Estate 111
38 • Woodle, h SID
43 -,Stone Oaks SID
44-Bethan MHP
46 -Snowshoe MHP
49 • Covin ton MHP
Subtotal
These population figures are based on house
counts from Figure 2 mult1plied by_the density
for Gaston County
Mapped, edited, and pub I 1shed by t he Gecbg1ca I Survey
C0 ntrol by USGS, USC&G S, and South Ca rolina Geooel1G Survey
Topogra ,hy by phutogrdrri metric methods "rom aerial phM02°aphs
ldk~n 1971 Field checked 1971
ProJect1on Nur!h Ca roll 10 coordinate system (L~mber L euaformal con1c:1
10 000 /cot ~nd licks based on North Carolina cc-ar:J,n~te system and
Sc ut1 Carol1ca coo rd,110 Le sys1em , north zone
1000-mater LJ n1versa I Trnr1s.crsa Mercator grid ticks,
,one 17, shown 1n b'He 1927 No rth Am erican datum
Red t1nl nd ,catcs ~ma 1n wh,ch only landma rk bu1ldmgs •re shown
* '·" 111 Gh
44 :::JI_Q_,, I 13 M 1.S
'\
l' ~ ~RID ;r 1971 MASS.IIC NORTH
OE8LLN<TICJN Al nN rm Of Sn ET
A FOLDER
RALIJlGH,
I 'Ii \ :s •·
' Po~.
' " ' ' rn
' "
29
' " I " ' 60
mo
I "'
"' "" 100
519
'35
40
300
"'
150
70
75
S4
4a
100
"' 88
'56
I ''° I 124
I 60
I 135
65
160
I '1
I '5
I ,s
100
757
4339
14,
210
"
18'
''° 76
, 353
3S
75,
5e
'2CO
2137
NORTH CAROLINA
. . .
•
•
I
I REQUEST
'
• ; d .!#{ u!s ' •
BESSEMER CITY QUApRANGLE
· UNITED STATES
iPARTMENT OF THE INTERIOR
NORTH CAROLINA
7.5 MINtlTE SERIES (TOPOGRAPHIC)
~E,4 LINCOLNTON 15' ().U!illRANGI F
-= !
R I ·/:__.;,,_: •• ;:,{---T:=P· '"'~--::-.,
L ~hl-d uly road, had or
111pro,ed surfs :e
Unir 111,rc-vej "~:Jc
GEOLOGlCAL
"11~,;t -'\' ' \fJ!.· "' ,_\ /'( ' \~~i,i ', ·, "'i';'"\,
' ',"··
"_-1.,11' ,,.\,
•L'../J.'/' 'II /". ~d:e'411,~·· IJ;{Jir,1,:;,-,) ,.,,, " " ,,, ~ ,'(i / P-1 ,-,,ill -r-• \-,h,-1 I I'-.'\'-. '& . ,, ,,
l ' ,;I
SURVEY
;ontrol by lViGS ,rn,i NUS/NUAA I
=ropography by piiotograrnn,etric methods from ae.,al J-'hotogrnphs
tak~n 197~ Fi eld checked l<J/3 I
==rro1~u1on: North Ca:ol1 nc coard1n~te1syslerri :Lambert conformal con ic)
'1 0,00'0-toot g:id ticks based on Nort1 Carclina coord1r1<ic~ system and
South Carolina ccwd1nate s\•stem, norh zone
1000-metre lhversal Transverse M~rcator grid t1cks,
KINGS mne 17, sho"n in blue. 1927 NMth /\mencan datum MOUNT AIN, N.C.-S.C.1 ,
~1ne red dashed 'mes 1nd1cate selected f~nc~ end f,eld l,ries where 'J /4 KINU~ M<JUNTAIN 15 Gl'WRANGLE
NJ,507" -W811~// 5
1971
generally v1>1bl~ on aeri~I ph otcgrsphs rn1s rnformatinn ,s unchecked
. ' tmt 1nd ,ca!es d(O S 1n which onlyildridmark bu1ld,ngs are shown
, , oz:
UTM GRID AN~ 197' MAGNrnc ~ORTH
ULCLINATION .r CENTER o.c 511!:ET
A FOLDER
= , ,
CCNTi":UR INTERVAL 10 FEET
NATIOIJAl_(;'c:)DETIC VCRTICAL DAI UM OF l'l2')
THIS MAP COMP! IES WITH NATIONAL MAP IICCURACY STANOAROS
FOR SALE BY U.S. GEOLOGICAL SURVEY
DENVER, COLO$,no 80225, OR RESTON, VIRGINIA 22092
DESCRIBING TOP0$APHIC MAPS AND SYMBOLS IS AVAILABLE ON
" "' i
REQUEST
:-LH l c::?i#h ..
GASTONfA NORTH auApRANGLE
-NORTH CAROLINA-GASTON CO.
7.5 MlNUTE SERIES (TOPOGRAPHIC)
SW,+CAc ~NIA 10' GUJ/,::;R,'.HGLF.
ROAD CLASSICICATION
Primary h1ghwa),
ha rd surfar;~
SPccndary highway
hard surface
1,, _; Interstate Rc.1\e
Light duty r<.>ad hard or
1rr,pro,c8 surface -
Unimproved r~ao . ' U S Rout~ , ___ , Stal~ Route
GASTONIA SOUTH, N. C.-S. C.
'IW/• CLOVER 15' QU~DRANGL~
N3507.5-WR107.G/7 5
1973
AMS 47~4 II NW-SERIES Y842
30''
r
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' ., 19SJJ su0cri. -~ _(qflJNDSfCTtON
NPL Characteristics
. Data Collection Form
(V ersiori 2.0, October 1992)
Site Name: o,,.v~ PMK. RoAll TX S1TE
Region: 1 V State: __ N:..cc::...._ ____ _
Office of Emergency and Remedial Response
U.S. Environmental Protection Agency
&EPA
! ; ,
i
NPL Characteristics Data Collection Form
General Instructions
The NPL Characteristics Data Collection Form is designed to standardize the site info~ation
collected for input into the NPL Characterization Data Base. This data base serves as a repository
for general information about NPL sites and is used to respond to queries about NPL sites from a
variety of sources including the general public, the press, other government agencies, and members
of Congress. The primary source materials for completing this form are Regional site file documents
(e.g., PA and SI reports), along with the site's HRS scoring package. Although inuch of the
information needed to complete the form is expected to be available in the HRS scoring package,
other sources in a site file may need to be consulted for some questions.· If definitive data are not
·available in the site file to answer a question, estimates based on best professional judgment and
other sources o.f information are acceptable.
As you complete tbe NPL Characteristics Da.ta Collection Form, keep the following points in
mind.
!> Please complete ihe form in ink, and print legibly.
> Use the most accurate level of information available (e.g., SI-level information has priority
over PA-level information).
· l> Try to use the listed response options when answering a question, and use "unknown" ~nd
"other" responses only when absolutely n=sary. If, however, the available'response
op.lions for a question·are not adequate to accurately describe the site, use the "other"
respon_se and provide a brief ex-planation in the space provided.
!> Use the margins to explain responses that do not match listed response options or to
provide clarifying information. If you need additional room to clarify responses, use the
space provided in Appendix C.
!> Some questions may go beyond tbe scope of the HRS scoring package (e.g., may relate
to pathways not scored). Answer these questions witb tbe best information available,
making reasonable "educated guesses' if necessary.
> "Current," as used in this form, should be interpreted as the general time period of HRS
scoring package preparation.
!> · "Principal contamination," as used in this form, should be interpreted·as tlie contamination
that is primarily responsible for a site's proposal to the NPL ·
Please respond to all questions with the answer that you believe best represents the site
conditions, given the information available at the time of HRS scoring package preparation. Do rwt
skip questions except where specifically directed to do so.
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Srte Name: Page 1
1. Basic Identifying Information
1.1 Site Name (as entered in CERCLIS):
1.2 CERCLIS ID Number:
1.3 Name of Person(s) Completing Form: ---"f+cc""'&,'-"o{"t'--'2=,,.o,_·_,,Nc.· _____________ _
Affiliation (agency/company): 1"ce,' ""-'"-"-'•wtli...:LA=M=· '-'=N,::1-1_..cD=i:''-i-\::.cl\i:c· l'.c,__-".1"'· -'..:.f..::0::.:.1'-:.:.F.:..u ,_,,,_o.,_~.5"',,;'-'cr::,_;_-__
Phone Number: ( 9•5 ) 1 :>'> )."to/ -:,13
1.4
J.5
1.6
Date Form Was Completed: _.Q_ _1_ /~ _'l_ /-3._. _(,_ (mm/dd/yy)
Site Location: City __ _,.C--="cs·'L:-r-c,•ccN,_,1ceA,___ _______ _ State N c.
County __ ..!,&-=Q.J='~L· ___________ _ Zip Code .1.-S-0 S-l...
Site Coordinates (in degrees, minutes, seconds, and tenths of seconds):
_Q_ _I_ _I -__ ! l _D 2.._._Q_·
N. Latitude W. Longitude
If tenths of secomis are unknown, use •rr ll.!' a default value. If necessary, refer to Appendix E of
EPA 's 1991 PA guidance document for directioru on how to determine coordinates.
1.7 . ATSDR HEALTH ADVISORY. Has an Agency for Toxic Substances and Disease Registry
(ATSDR) Health Advisory been issued?
0 Yes 0 No
If yes, what was the date of issue? ____ / ______ /__ __ · (mm/ddlyy)
1.8 HOW INITIALLY IDENTIFIED. How was the site initially identified to EPA? If this information
is not available _in the HRS scoring package, check the PA narrative or other parts of the site
file. (check one)
□ Citizen complaint (including PA petition)
□ State/local program
□ CERCLA notification
D RCRA notification
□ Other Federal program (specify)
□ Incidental (e.g., identified while discovering/investigating another NPL site)
□ Anonymous ~ Other (specify) G,,,/\-m1,; 1t,e-o Wei..... D;s, •. ·em.i!.D OvtctN ... C,..,,.-,µ« 1ifi,n1y<..
□ Unknown
1.9 UNKNOWN SOURCE. Does the site consist exclusively of contaminated ground water or
contaminated surface water sediments with M idenllf'uihle primary source(s)? (check one)
□ Yes, ground water plume(s)
D Yes, surface water sediments
l)<I No
NPL Characteristics Data Collecilon Form
I .,
Page 2
2. General Site Description
I
2.1
2.2
2.3
SETTING. What is the site setting? (check one)
D Large city: within boundaries of a city with a population.:: 100,000
D Small city/town: within boundaries of a city/town with a population_:: 10,000 and < 100,000
!Kl Suburban: within immediate suburbs of a city
D Rural: outside of city and suburban areas
LAND USE. What is the current land use(s) within I mile of the site? .(check all that apply)
D Industrial
~ Commercial
131 Residential
D Agricultural
D Forest/fields/wetlands/other undeveloped
D Parks/recreation
D School/university/day care
D Military
D Other (specify)
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lf readily available informaiwn indicates that projected future land use(s) within I mile of the site I
. may differ from the current use(s) checked above (e.g., building a mobile home park or other new
residential area adjacent to a forrner landfill), write them in ·the blank that follows. Use the
response options listed above if possible. I
AREA. Wh;:,t is the approximate area of contamination (i.e., total area that includes all sources I
of contamination and other areas where co~tamination has come to be located, plus the area
between the sources)? lf the site is large with only a smal! contaminated ponion, only the area I
of the contaminated portion should be estimated. lf the approximate area of .contamination
cannot be estimated, use the area within the property boundary. (check one)
· l!!J ss acres
.. □ > 5 and .:s. 20 acres
D > 20 and < 100 acres
D > 100 acres
D Unknown·
NPL Characteristics Data Collection Form
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Stte Nam€: Page 3
2.4 OWNER AND OPERATOR. What/who are the current owner(s) and operator(s) of the site,·and
who we,re the owner(s) and operator(s) aJ the time of principal contamination? If the owner and
operator are the same, then check the same box under "Owner(s)" and "Operator(s)." If the
current owner and/or operator and the owner and/or operator at time of principal contamination
are the same, then check th(; same box under "CURRENr and "AT TIME OF
CONTAMINATION." (check all that apply, including at least one in each column; "NA"
indicates that a response is not applicable)
CURRENT· AT TIME OF CONTAMINATION
Owner(s) Operator(s) Owner(s) Operator(s)
D D Private • industrial/commercial · D D
D ~ Private • smaU business D GI
f,il D Private. individual ~ D
D D County/city D D
D D State D D
D D Federal D D
D D Indian lands D D
D D Bankruptcy/receivership NA NA
NA D None/currently inactive or abandoned NA NA
NA D None/spill or other one-time event . NA D
D NA Other (specify) NA NA
NA D Other (specify) NA NA
NA NA Other (specify) D NA
NA NA Other (specify) NA D
NA NA Unknown □ NA
NA NA Unknown NA D
I
2.5 SPILLJOTHER ONE;TIME EVENT. ls this site the result of a one-time spill (e.g., truck, rail car,
or barge accid~nt) or other one-time even·t (e.g., one-time· illegal dumping), with no other
ongoing waste management or waste generat_ion activities on site? (check one)
D Yes, specify year of spill/other one-time event
1!i1 No
If answer is "Yes" to this question, proceed to Section 3. If answer is "No," continue to question·
#2.6. .
2.6 YEARS OF OPERATION. What are the beginning and ending years of operation at the site?
"Operation" includes any activity occurring at the site (other than site remediation and related
site investigation activity), and does ,wt necessarily have to involve waste generation and/or
management. · Aggregated sites that have a combination of active and inactive/abandoned
operations, and active sites that have had periods of inoperation during their existence, should·
be considered currently operating. For these sites, indicate the beginning year of their earliest'
operation. If sites such as this are no longer operating, indicate the beginning year of their
earliest operation and the ending year of their latest operation. (check one)
l'il Currently operating: from (beginning year) --~)_q~1,_o_' ~~-----------
□ Inactive or abandoned: from (beginning year) ____ to (ending year)
D Unknown (only if rw historical information is available)
NPL Characteristics Data Collection Form
Page 4
3.
2.7 YEARS OF WASTE MANAGEMENT ACTIVITIES. What are the beginning and ending years
of waste management _at the site? Applicable waste managem.ent activities include generation,
treatment, and/or recycling of waste containing hazardous substances and/or receipt of such
wastes from off-site sources. Aggregated sites that have a combination of active and
inactive/abandoned waste management activities, and sites that are actively managing waste that
have had periods without waste management activities during their existence, should be
considered currently managing waste. For these sites, indicate the beginning year of their earliest
waste management activity. If sites such as this are no longer managing waste, indicate the
beginning year of their earliest activity and the ending year of their latest activity. All responses
should be consistent with responses given for question #2.6. (check one)
D Currently managing waste: from (beginning year)
D No longer managing waste: from (beginning year) ___ to (ending year) ____ _
D Unknown (only if no· historical information is available)
Site Type
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3.1 SITE ACTIVITIES. Which of the following best describe current activities/operations/conditions
at the site '(i.e., on-site activities)? Also, identify all former activities that are at least partly I
responsible for the principal contamination at the site. Check all responses that apply, including
.at least one in each column; if a primary item is checked, at least one sub-item also must be
checked (e.g., if "Federal facility" is checked, a sub-item such as "DOD" a_lso must be checked). I
Current
D
□
D
D
D
D
D
D
D
D
D
D
D
D
□
D
D
D
D
D
D
D
D
D
D
D
Former··
D Federal facility (must also indicate Federal in question #2.4)
D DOD
D DOE
D DOI (e.g.; Bureau of Land Management)
D USDA (e.g., Forest Service)
D Other (specify) ---------~----'----~
D Manufacturing/processing ·. □ Chemicals and allied products
D Pesticides
D Other (specify)
D .Primary metals/mineral processing
. D Petroleum refining
D Metal fab.rication/finishing/coating and allied industries
□ Lumber and wood product.5/pulp and paper
D Wood preserving/treatment
D Other (specify)
D Plastic and rubber products
· D Electronic/electrical equipment
D Electrkpower generation and distribution .
D Other (specify)
D Mining
D Coal
D Oil and gas
D Metals
□
D
Non-metal minerals
Other (specify)
(response options for question #3.1 continue on next page)
NPL Characteristics Data Collection Form
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Site Name:
Current
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
□
NA
' Page 5
Fonner
□ Waste management as principal activity (i.e., no manufacturing or. other
principal activity)
□ Municipal solid waste landfill
□ RCRA Subtitle C TSDF (non-generamr)
□ Other industrial waste facility, including landfill (non-generator)
□ Radioactive waste treatment, smrage, disposal (non-generator)
□ Recycling
□ Baneries
□ Used/waste oil
□ . Aummobiles/scrap me_tal/tires
□ Drums
□ Chemicals/chemical ,wastes (e.g., solvent recovery)
□ Other (specify)
□ Publicly owned treatment works/septic tanks/other sewage treatment
□ Illegal/open dump
□ Other (specify)
□ lJ-ansportation (e.g., railroad yard, airport, barge docking site)
□ Product storage/distribution as principal activity
□ Retail/commercial
□
NA
NA
□
Agricultural
Residential
None/currently inactive or abandoned
Spill or other" one-time event, with no other ·activities (mu.st also indicate
spill in question #2.5) / . '
Other (specify)CJ,lu!CNT U/hl/J.1!f<>51"'' 5;-,.p iwmtcit ),::A,11= 5rfln•1-1
3.2 WA_STE TREATMENT, STORAGE, AND DISPOSAL ACTIVITIES. What treatment, storage,
and/or disposal activities occur/occurred at the site? (check all that apply)
□ Municipal landfill (must also indicate municipal solid waste landfill in question #3.1)
□ Industrial landfill
□ Surface impoundment (primarily liquid) , ,
□ Waste pile (primarily solid, covered or uncovered)
□ Drum/container storage (intentional storage in specified areas)
□ -Tonk -above ground (if tank type is unknown check here)
□ Tank -below ground
□ Discharge t0 sewer/surface v.-ater-(intentional perrnined or illegal .discharge; not secondary
runoff)
□ Recycling (must also indicate recycling in question #3.1)
□ Incineration/other combustion activity (including burn pits)
□ Underground injection well
□ Land application/treatment
□ Drain/leach field
Iii!' illegal dumping (unperrnined dumping by site owner/operator in undesignated disposal area)
□ Unauthorized dumping by a party other than the site owner/operator
D None/spill or other one-time event (must also indicate spill in question #2.5)
□ Other (specify)
NPL Characteristics Data Collection Form
Page 6
4. Waste Description I
4.1
4.2
ON-SITE/OFF-SITE GENERATION. Is an on-site or off-site generator responsible for the waste I
disposed or deposited on site that resulted in the principal ccntamination? For ccnsistency,
recycling facilities should be ccnsidered on-site generators. (check one) ·
I D On-site generator only
D Off-site generator(s) only
D Both on-site and off-site generators -_ . - I
ENTITY THAT GENERATED THE WASTE. _What is the source(s) of the waste disposed or
deposited on site that re,iulted in the principal ccntamination (not necessarily the entity that ·
generated the original product)? Note that this question is different from question #3.1 I
regarding site activities,although the response options are similar. This question targets the
generator(s) of the waste present on site, not the site activities.· However, if the waste is/was
generated entirely on site, then the respcinse(s) to this question should match the response(s) I
. to question #3.1. (check all that apply)
D Federal facility
D DOD
D DOE
D DOI
D USDA
D Other (specify)
D Manufacturing ..
D Chemicals and allied products
D Pesticides
D Other (specify) ------~~----~------
□ Primary metal.5/mineral processing
D Petroleum refining
D . Metal fabrication/finishing/ccating and allied industries
·o Lumber and wood products
D Wood preserving/treatment
D Other (specify)
D Plastic and rubber products
D Electronic/electrical equipment·
D Electric power generation and distribution
D Other (specify)
D Mining
D Coal
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D Oil and gas
D Metal.5
D Non-metal mineral.5 I
D Other (specify) ---~-------------,------
□ Recycling
D Batteries
D Used/waste oil
D Automoliile junkyard/scrap metal/tires
D Drums
D Chemical.5/chemical wastes (e.g., solvent recovery)
D Other (specify)
(response options for question #4.2 continue on next page)
NPL Characteristics Data Collectlon Form
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Site Name:
D Transponation (e.g., railroad yard, airport, barge docking site)
D Product storage/distribution facility
D Retail/commercial ·
D Agricultural
D Residential
□ Laboratory/hospital
D Construction/demolition
D Site remediation (e.g., wastes from site cleanups)
D Waste management (e.g., leachate or ash from waste treatment processes)
D Other (specify)
Page 7
4.3 PHYSICAL STATE OF WASTE. Whai is the physical state(s) of the hazardous substance-
_containfng waste(s) deposited or detected on site? (check all that apply)
D Solid
lit Liquid
. D Sludge
D .Gas
4.4 GENERAL WASTE TYPES. Whal are the waste types deposited or detected on site? lndica_te
4.5
all the waste types present on site under "Overall." If three or fewer waste types are known lO
· comprise the majority (i.e., over 50%) of the waste volume on site, indicate their types under
"Predominant." Otherwise, leave the "Predominant" column blank. · (check all that apply)
Overall Predominant
D D Organic chemicals
D D ·Metals
D D Non-metal inorganic chemicals
□ D Strong acids/bases
r,;i' fa'' Chlorinated solvents
□ D Pesticides
D □ _Paints/pigments
□ [>l' Oily wastes
□ □ Explosives
□ □ Fuels/propellants
□ □ Fly and bouom ash
□ D POTW sludge
□ D Still and tank bcinoms
□ D Contaminated soil/sediment
□ D Radioactive wastes
□ D Other (specify)
SPECIFIC WASTE CONSTITUENTS. Which of the following waste constituents have been
deposited or detected on site? (check all that apply, and make sure that response is consistent
with response to question #4.4)
□ Asbestos
□ Creosote
□ Cyanides
□ Dioxins (e.g., TCDD)
□ Lead
□ Pentachlorophenol (PCP)
□ Polychlorinated biphenyls (PCBs)
□ Polycyclic aromatic hydrocarbons (PAI-ls)
OZ None of the above
NPL Characteristics Data Collection Form
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5.
4.6 QUANTITY OF WASTE. What is the highest HRS hazardous waste quantity factor value among
the pathways scored, regardless of which tier(s) (A, B, C, and/or D) was used in scoring? (check I
on~ _
D 1
D 10
i,!"100
D 10,000
D 1,000,000
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4.7 WASTE: ACCESSIBIUTY. Ls the waste on site currently accessible to the public (e.g., is site
access unrestricted so people can potentially come into direct contact with contaminated I
materials)? Items to be considered when judging accessibility include, for example, presence or.
absence of a complete cover over the waste area and a secure fence around the site. A site with
natural access restrictions (e.g., steep terrain) also can be considered i.naccessible. Do not count 1 on-sit.e workers as part of the public when answering this question. (check one)
D Yes
f;;!' No
D Unknown
Demographics
For this section, do not directly use ihe populationJactor values calculated in the HRS and entered in HRS
scoresheets. Use actual (i_e., unweighted, unadjusted) population figures, which shoulil be available in'the
HRS ·supporting documentatio!L ·
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5.1 NUMBER OF WORKERS ON SITE. What· is the current number of workers present on site I
. (not including workers involved in response activities)? (check one)
5.2
D 0
llt _2'.. 1 and < 10
D _2'.. 11 and .:::_ 100
D > 101 and < 1,000
D >.1,000
D Unknown
DISTANCE TO POPULATION .. What is the shortest distance from any source or area of
contamination at the site to the nearest residential individual (include aU persons occupying
homes, apartments, businesses, or schools)? U contamination has migrated off site onto the
property of a nearby resident(s), then check the box next to ·o .miles." If the source or
contaminated area is not clearly identified, use distance from the site property boundary. (check
one)
D O miles (i.e., on site)
9' > 0 and .:::_ 1/4 mile
D > 1/4 and < 1/2 mile
D > 1/2 and < 1 mile
D > I and < 4 miles
D > 4 miles
NPL Characteristics Data Collection Form
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Stte Name: Page 9
6 ..
5.3 POPULATION. What is the tot.al residential population within 1 mile and 4 miles of the site
(include all persons occupying homes, apanments, businesses, or schools)? (check one in each
column)
Within Within
l mile 4 miles
□ □ 0
□ □ > 0 and< 10
□ □ > 10 and.'.:. 100
□ □ > 100 and < 1,000
0 □ . > 1,001 and < · 10,000
□ @( > 10,000 and < 100,000
□ □ > 100,000
□ □ Unknown
Water Use
. '
For purposes of this section, "/ocar refers to ground water wilhdrawa/s wilhin 4 miles and surface water
withdrawals wilhin 15 "in-water" miles (e.g., downstream miles for streams and rivers) of the sile (i.e., ·within
HRS target distance limils).
6.1 TOTAL DRINKING WATER POPULATION SERVED. What is the total population served by
local ground and surface water sources of drinking water? Use actual population numbers and
not adjusted values taken directly from HRS scoresheets. For blended systems, use total
population served instead of prorated values. Note that the total population served does not
have to reside within the HRS target distance limits, only the drinking-water supply withdrawal
point(s) needs to be within the limits. (check one in each column)
Ground
□
□
□
□ 0
□
□
Surface
□ < 10
□ > 10 and .'.:. 100
□ > 100 and < 1,000
□ > 1,000 and < 10,000
□ > 10,000 and < 100,000
□ > 100,000
g'· Not applicable (no drinking water withdrawals within HRS target distance
limits)
. 6.2 TYPE OF DRINKING WATER SUPPLY SYSTEM. What type(s) of local drinking water supply
system(s) is present? "Public" should be checked for any central water supply system, even if
operated by a private entity. (check all that appiy) ·
Ground
0
r.,J'
□
□
Surface
□ Public (serves over 25 people; e.g., municipal syste~)
□ Private (e.g., individual wells) '
□ Unknown
10' Not applicable (no drinking water withdrawals within HRS t:lrget distance
limits)
NPL Characteristics Data Collection Form
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6.3 OTHER GROUND WATER USES. What are the other uses of ground water withdrawn within
4 miles of the site? (check all that apply)
D lrriga tion
D Stock watering
D Commercial uses (e.g., food p'reparation, aquaculture)
D Industrial process/cooling
D Recreation (e.g., water supply for municipal swimming pool, infiltration into lakes used for
recreation) D Other (specify) _________________________ _
.l'ef None
D Unknown
6.4 DEPTH TO AQUIFER. What is the approximate depth from the ground surface to the
6.5
uppermost usable aquifer (i.e., an-aquifer having sufficient yield and water quality to be usable
· as drinking water or for other beneficial uses) beneath the site? (check one)
D < 10 feet
· D > 10 and :::,_ 25 feet
D > 25 and < 50 feet
· g' > 50 and < 100 feet
D > 100 feet·
D U nknov.-n
OTHER SURFACE WATER USES. What are the other uses of surface water withdrawn within
15 "in-water" miles of the site? (check all that apply)
D Not currently used, but designated by the state for potential drinking viater use
li1!' Recreational fishing
D Other recreation
D Irrigation
D Stock watering
D Industrial process/cooling
D Commercial fishery, including aquaculture
D Other commercial uses
D Other (specify) --~-~-------------------
□ None
D Unknov.'11
NPL Characteristics Data Collectlon Form
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7.
6.6 TYPE OF SURFACE WATER ADJACENT TO/DRAINING SITE. What are the type(s) of
surface water adjacent to/draining the site that could potentially be affected by overland runoff
from the site (i.e., are within 2 miles of any source)? Indicate whether the water body is known
or suspected of being contaminated by the site. •yes· would indicate that the surface. water body
meets the HRS criteria for observed release. •suspected" would indicate that there is' some
evidence of contamination that is anributable to the site, but the surface water body does not
meet the HRS criteria for observed release. (check all that apply)
Contaminated?
ii"unknown □ lnterrn.iuent stream CI Yes □ Suspected El No
□ Perennial stream rJ Yes □ Suspected .. □ No ·lla'Unknown
□ River(> 1,000 cfs annual avg. flow) ·□ Yes □ Suspected D No □ Unknown
□ Lake/reservoir □ Yes □ Suspected □ No □ Unkno~
□ Pond □ Yes □ Suspected D No □ Unknown
□ Bay □ Yes □ Suspected □ No □ Unknown
□ Ocean □ Yes □ Suspected D No .□ Unknown
□ Drainage ditch □ Yes □ Suspected D No □ Unknown
□ Canal □ Yes □ Suspected D No □ Unknown
□ Other (specify) □ Yes □ Suspected □No □ Unknown
□ No surface water within 2 miles
□ Unknown
Sensitive Environment and Reported Environmental Damage
Information
7.1 EXISTENCE OF SENSITIVE OR POTENTIALLY VULNERABLE ENVIRONMENT. ls the site
in or near (i.e.;within a 4-mile radial distance, or for surface water within 15 "in-water" -miies)
an HRS-designated sensitive environment(s) or ot_her potentially vulnerable environn\ent(s)?
(check au that apply)
if Yes, HRS-<lesignated sensitive environment(s)
0 Wetland
0' Habitat used by Federal or state_ designated endangered or threatened species
□ Other (specify)
□ Yes, other potentially vulnerable environment(s) (see Appendix B for definitions)
□ Karst terrain ·
□ Seismic impact area
□ 100:year floodplain
□ Unstable terrain
□ Vulnerable ground water (class I, as defined by EPA)
□ Wellhead protection area
□ Other (specify) ____________________ _
□ No
□ Unknown
7.2 HUMAN HEALTH/BIOLOGICAL IMPACTS. Have human health or biological impact.s
anributable ·10 the site been reported or observed? (check all that apply)
□ Yes
□ Human health
□ Flora (e.g., stressed vegetation)
□ Fauna (e.g., fish kills, wildlife impacts)
l\li No
□ Unknown
NPL Characteristics Data Collection Form
Page 12
8. Response Actions
8.1 TYPE OF RESPONSE ACTION. What type(s) of response actions bas already occurred at or
near the site? (check all that apply)
□ Action has been taken to reduce an immediate threat of fire or explosion
□ Waste has been physically removed from the site
□ Waste has been treated/stabilized/contained on site
D Site access has been restricted in response to the contamination
19' Drinking water well(s) bas been closed (on or off site)
Ii?' Alternate water supply(ies) bas b•,en provided (on or off site)
□ Residents have been relocated
□ Other (specify) --------------------'-----
□ None
8.2 AUTHORITY RESPONSIBLE FOR RESPONSE ACTION. Who performed (or contracted for)
the response action(s)? (check all ihat apply)
□ EPA under authority of CERCLA
D EPA under other authority
□ Other Federal agency (specify)
~ State/local authority
□ Private party
□ Other (specify)
□ Not applicable (check only if checked "None" in question #8.l) .
REVIEW OF COMPLETED FORM. When you have completed Sections 1 through 8 of the NPL
Characteristics Data Collection Form, please check to make sure that: ·
(1) All questions are answered,.except for ones that you ·were specifically directed to skip; and
(2) All questions have been answered such that the responses are internally consistent, especially
those in Sections 2 and 3. For example, if the site is the result of a spill or other one-time
. event, the responses· for questions #2.4, #2.5, #3.1, and #3.2 should be consistent, while if the
site is inactive or abandoned, the responses for questions #2.4, #2.6, #2.7, and #3.1 shciuld be
consistent. · ·
NPL Characteristics Data Collection Form
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