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Villa Mobile Home Park Battery Dump Site

All POL/SITREP's for this site Villa Mobile Home Park Battery Dump Site
Kannapolis, NC - EPA Region IV
POLREP #6
Removal Continues - Soil Treatment
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U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
Villa Mobile Home Park Battery Dump Site - Removal Polrep

EPA Emergency Response

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region IV

Subject: POLREP #6
Removal Continues - Soil Treatment
Villa Mobile Home Park Battery Dump Site
B4C3
Kannapolis, NC
Latitude: 35.4857860 Longitude: -80.6078920


To:
From: Alyssa Hughes, OSC
Date: 11/16/2012
Reporting Period: 11/12 - 11/21

1. Introduction
  1.1 Background
   
Site Number: B4C3    Contract Number: EP-S4-07-04
D.O. Number: 155    Action Memo Date: 9/12/2012
Response Authority: CERCLA    Response Type: Time-Critical
Response Lead: EPA    Incident Category: Removal Action
NPL Status: Non NPL    Operable Unit:
Mobilization Date: 10/29/2012    Start Date: 10/22/2012
Demob Date:      Completion Date:  
CERCLIS ID: NCN000410983    RCRIS ID:
ERNS No.:    State Notification:
FPN#:    Reimbursable Account #:

1.1.1 Incident Category

TIme- Critical Removal Action

1.1.2 Site Description

A Removal Site Evaluation (RSE) was conducted in response to a request from the North Carolina Department of Environment and Natural Resources (DENR).  The Villa Mobile Home Park Battery Dump Site (the Site) is isolated to a small portion of the Villa Mobile Home Park located in Kannapolis, Cabarrus County, North Carolina.  The mobile home park is comprised of several parcels over 10 acres of land containing approximately 54 mobile homes.  It is bound to the north and west by Verona Street, to the south by Irene Street and to the east by McLain Road.  The primary area of concern is located to the southeast of the intersection of Verona and Venice Streets.  The extent of the buried battery casings and associated contamination is unknown at this time, although estimated to be contained within three parcels of the property.

According to residents at the Villa Mobile Home Park, during periods of heavy precipitation, the current piped stream cannot contain the water flow and the stream overflows from the headwall located on the north side of Venice Street and flows overland to the open area approximately 100 feet downstream.  This overland flow is estimated to be partially responsible for the erosion of the stream, causing the battery casings to be exposed.


1.1.2.1 Location

The Villa Mobile Home Park (the Site) is located near the intersection of Venice Street and Verona Street in Kannapolis, Cabarrus County, North Carolina.  The geographic coordinates are 35.485786 ° N, -80.607892 ° W.  The surrounding land use to the north, south and west is residential.  The area to the east is wooded.  Groundwater is expected to flow to the stream channel that transects the Site, which then flows east approximately 500 feet through piping where it discharges to Coldwater Creek, which ultimately flows into Lake Concord approximately ½ mile from the boundary of the mobile home park. 

  
1.1.2.2 Description of Threat

Lead is a hazardous substance as listed in 40CFR302.4, and referred to in Section 101(14) of CERCLA, as amended.  Human exposure to lead contaminated soil at the Site poses a significant threat to public health.  Direct contact, ingestion and inhalation are the primary pathways of exposure.  Continued exposure to the soil contaminated with concentrations of lead exceeding the Removal Management Level (RML) of 400 ppm of lead may pose chronic health effects to persons living nearby.  During a demographic survey conducted in July 2012, NCDENR IHSB discovered approximately 70 adults and 70 children reside in the mobile home park.

Analytical results reveal that elevated lead levels are present in surface soils and in the open channel creating a potential for downstream migration.  Visual inspection indicates battery casings throughout the banks of the drainage ditch.  The presence of battery chips in the vicinity of the McLain Road outfall supports the possibility of contaminant migration through the culvert due to high flow rate following periods of heavy precipitation.  Lead concentrations in samples collected from the drainage ditch exceed the residential RML by an order of magnitude.

The neighboring City of Concord utilizes Lake Concord as a source for its municipal water supply.  Potential contamination of this water body exists due to the possibility that lead could migrate via the piped channel into Coldwater Creek which ultimately discharges into Lake Concord. Coldwater Creek is designated WS-IV; CA (Water Supply-IV/Highly developed; Critical Area).

1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results

In July 2012, EPA ERRB, START contractor OTIE and DENR IHSB met on-site to perform X-Ray Fluorescent (XRF) screening and lab analysis of samples at several locations in the vicinity of the test pits excavated during the S&ME investigation.  Ten locations were screened at the surface, near surface (0-6”), and subsurface (ranging from 1-3’ below ground surface).  Of the ten locations, five samples were collected for lab analysis.  Elevated lead concentrations for near surface screening ranged from 478 mg/kg to 5,940 mg/kg. Five out of seven locations where subsurface screening was performed indicate lead concentrations that exceed the residential RML for lead. Values range from 597 to 3,451 mg/kg of lead. 
 


2. Current Activities
  2.1 Operations Section
    2.1.1 Narrative

The Villa Mobile Home Park Battery Dump consists of an area containing exposed and buried battery casings.  The area of the footprint is estimated to be approximately 20,000 square feet, with casings extending to various depths.  The buried battery casings are exposed due to significant gully erosion.  Several factors contribute to the severe erosion that has occurred in this open channel area between the two piped portions of the culvert.  According to residents, during periods of heavy precipitation water flows in sheets across the property, which slopes down to the outfall at McLain Road.  The culvert to the west of Venice Street is improperly sized which causes an increase in sheet flow and an increase in velocity of the water through the pipe which leads to substantial scouring in this open area.  The continuing erosion increases the surface area of the exposed battery casings.  For these reasons, the entire source of buried battery casings will be removed.

2.1.2 Response Actions to Date


On Tuesday, November 13th the first load of triple super phosphate (TSP) arrived on-site.  During this reporting period a total of four loads arrived on-site.  Each load consists of approximately 23 tons, which equates to 92 tons of material.  This quantity of TSP is expected to treat the volume of excavated material to date, approximately 4000 tons. 

An initial five-point composite sample was collected for toxic characteristic leaching procedure analysis.  The results are expected by Tuesday, November 20th.  Based on these results, the material will be ready for disposal as non-hazardous, or alternatively, additional treatment with TSP will continue.

From November 14th through 17th the blending of the stockpile with TSP continued.  During the process, the stockpile was relocated from the northwest corner of the site to the northeast corner to allow for accessibility to areas still requiring excavation, not including the culvert.  Once the stockpile was relocated, excavation continued.  This area included four foot bands of concentrated battery casings, which appears to be the densest concentration on-site.  By November 19th, the excavated material from this area approximately doubled the volume of material stockpiled for an estimated total of 8,000 cubic yards.  Based on this figure, stabilization of the metals leachability will require additional loads of TSP.  Delivery of this material will occur following the Thanksgiving holiday.  Results from the initial five-point composite sample are expected before this time.  On November 20th the remaining TSP was mixed into the stockpile.  In addition efforts were focused on preparing the Site for temporary Thanksgiving holiday demobilization.  Activities include flattening and covering the stockpile and securing it with sandbags, backfilling excavated areas with overburden to the extent possible to prevent safety hazards, relocating silt fencing and manicuring security fencing.  Crews will remobilize on Monday, November 26th.

2.1.3 Enforcement Activities, Identity of Potentially Responsible Parties (PRPs)

The Villa Mobile Home Park was owned by the Wyrick Estate.  Mr. Wyrick filed for bankruptcy in 2010 and shortly thereafter passed away.  The property is now held by the bankruptcy court.

2.1.4 Progress Metrics

Waste Stream Medium Quantity Manifest # Treatment Disposal
           
           
           


  2.2 Planning Section
    2.2.1 Anticipated Activities

2.2.1.1 Planned Response Activities

The following removal activities are expected to take place:
- Excavate soil in which battery casings are observed
- Evaluate the need to remove soil from the drainage pathway exceeding the residential removal management level for lead of 400 ppm
- Provide temporary on-site storage of contaminated soils generated during removal activities
- Conduct in-situ and ex-situ screening and/or collect samples at the floor of the excavation
- Arrange for off-site transportation and disposal/treatment of hazardous substances according to applicable regulations

2.2.1.2 Next Steps

- Continue blending stockpile with triple super phosphate (TSP)
- Receive additional loads of TSP
- Arrange for and begin transportation and disposal of material as nonhazardous waste
- Identify a suitable source for general backfill

2.2.2 Issues

The increased volume of excavated material will require additional stabilization loads of the stabilization chemical.  Cost estimates are currently being evaluated.

  2.3 Logistics Section
    Site operations will be suspended in observance of the Thanksgiving holiday.  Crews will remobilize to the Site on Monday, November 26th.

  2.4 Finance Section
    No information available at this time.

  2.5 Other Command Staff
    2.5.1 Safety Officer

N/A

2.5.2 Liaison Officer

N/A

2.5.3 Information Officer

The community involvement coordinator for this site is Angela Miller.

3. Participating Entities
  DENR IHSB

4. Personnel On Site
  EPA - 1
START - 1
ERRS - 5

5. Definition of Terms
  No information available at this time.

6. Additional sources of information
  No information available at this time.

7. Situational Reference Materials
  No information available at this time.


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