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Former Wisconsin Die Cast Facility

All POL/SITREP's for this site Former Wisconsin Die Cast Facility
Milwaukee, WI - EPA Region V
POLREP #1
Initial
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U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
Former Wisconsin Die Cast Facility - Removal Polrep
Initial Removal Polrep

EPA Emergency Response

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region V

Subject: POLREP #1
Initial
Former Wisconsin Die Cast Facility
C5ZB
Milwaukee, WI
Latitude: 42.9852820 Longitude: -87.9118670


To:
From: Kathy Halbur & Paul Ruesch, OSC
Date: 9/30/2014
Reporting Period: 9/22/2014 - 9/30/2014

1. Introduction
  1.1 Background
   
Site Number: C5ZB    Contract Number: EP-S5-08-02
D.O. Number: 0144    Action Memo Date: 8/12/2014
Response Authority: CERCLA    Response Type: Time-Critical
Response Lead: EPA    Incident Category: Removal Action
NPL Status: Non NPL    Operable Unit:
Mobilization Date: 9/22/2014    Start Date: 9/22/2014
Demob Date:      Completion Date:  
CERCLIS ID:    RCRIS ID: None
ERNS No.:    State Notification: WDNR
FPN#:    Reimbursable Account #:

1.1.1 Incident Category
Time Critical Removal Action

1.1.2 Site Description

The Site is a 2.8 acre lot with a 61,000 ft2 abandoned industrial building, formerly occupied by Wisconsin Die Casting, LLC, in a mixed residential, commercial, and industrial area. The Site building is currently vacant and has fallen into disrepair, with continuous and persistent trespassing by scavengers and vandals.

1.1.2.1 Location
The Site is located at 201 West Oklahoma Avenue in Milwaukee, Milwaukee County, Wisconsin.

1.1.2.2 Description of Threat
The Site contains abandoned foundry ovens as well as numerous piles of dusts, wastes, pipe wrap, broken floor tile, and containers of waste oil. Some of the waste containers are open, bulging, and/or leaking. Fallen lead and PCB-contaminated paint chips and friable asbestos are uncontrolled in the building. There is evidence that contamination is being tracked out of the building.

On December 12, 2013, RACM sent a letter requesting assistance from EPA. According to RACM, broken doors/windows and continued dilapidation of the Site building create entrance points, exposing friable asbestos and PCB contaminated building materials to the elements, rendering the building an imminent threat to the neighborhood.

 

MHD sent a letter to EPA on July 17, 2014 requesting immediate action by EPA to remove all contaminated building materials on the floor of the Site building.  On July 18, 2014, WDHS sent a letter to EPA concluding that the conditions at the Site pose a human health hazard and requesting EPA Removal Assistance with the contamination at the Site

1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results
On March 20, 2014, EPA conducted a site reconnaissance to document Site conditions. Numerous drums and containers were observed that were open or in poor condition, knocked over, bulging, or with visible evidence of spills. In addition, several overhead and personnel doors were open with evidence of recent trespassing for scavenging and vandalism.

 

On April 23, 2014, EPA collected samples of liquids in containers; solid wastes in containers and on the floor; wipe samples; paint chip samples; surface soil samples outside the building; and building material samples. The removal site assessment documented metals and PCBs in solid wastes strewn about the floors throughout the building at concentrations above EPA RMLs for industrial soils.
 

PCBs were found in several solid waste samples taken from the floors inside the building. One sample of floor solids had a concentration of PCBs at 6,900 mg/kg, exceeding the EPA RML for industrial soil of 100 mg/kg.  Another floor solid sample had a PCB concentration at 1,600 mg/kg, exceeding the EPA RML for industrial soil of 44 mg/kg.

 

Paint chip samples taken from floor debris had detections of lead at concentrations exceeding EPA RMLs. One paint chip sample in a high traffic area for trespassers leading out a side door had a total lead level of 19,000 mg/kg, which exceeds the EPA RML for industrial soils of 800 mg/kg.

 

Surface soil samples were taken along a pathway leading from the adjacent railroad property through breaches in the fence to broken doors and windows of the Site building. Results from samples taken along this pathway detected PCBs (as high as 23 mg/kg), which documents the migration of PCBs outside of the building.

 

Friable ACMs were identified in dislodged, broken and/or crushed floor tiles at numerous locations on floors throughout the building. Detections ranging from 2.5% to 24.5% chrysotile (by volume) were detected in samples of materials found on the floors in high traffic areas for trespassers. In addition, pipe insulation is strewn about the building floors, presumably by scavengers removing metal piping.  There is clear visual evidence that trespassers are handling and walking over the pipe wrap, which has become friable, on the building floors.

 

At least thirteen drums of liquids and solids are present inside the building. Several of the drums have missing bungs or are laying on their sides. The liquid contents of these drums appear to be waste oil, mineral oil, and or oil/water mixtures.

On August 8, 2014, EPA observed that several of these drums had been tipped over with their contents spilled onto the floor, presumably by scavengers seeking scrap value in the metal drums.

2. Current Activities
  2.1 Operations Section
    2.1.1 Narrative
EPA, ERRS and START personnel mobilized to the Site, set-up support and staging areas, and began removal activities during the reporting period.

2.1.2 Response Actions to Date
Site activities during the reporting period included the following:

- Mobilization of crew, equipment, supplies, office trailer and heavy equipment;
- Mobilization and set-up of air monitoring equipment;
- Vegetation clearing, lighting, and securing of perimeter fence breaches;
- Mobilize armed security services during off hours;
- Clearing of debris from rear part of building;
- Removal of asbestos-containing floor tiles in rear of building;
- Collection and staging of drums containing liquid wastes and oils; and
- Removal of metal scrap for recycling.

2.1.3 Enforcement Activities, Identity of Potentially Responsible Parties (PRPs)
The Enforcement Team has sent information request letters to several potentially responsible parties that have been historically involved in the Site. Responses to these letters are being evaluated for subsequent action.

2.1.4 Progress Metrics

Waste Stream Medium Quantity Manifest # Treatment Disposal
 Solid Waste  solid  7.66 tons  NA  disposal  landfill
 Scrap Metal  solid  2.63 tons  NA  recovery  recycling


  2.2 Planning Section
    2.2.1 Anticipated Activities
During the next reporting period, the following activities are planned:

- Debris removal from the mid-section of the building;
- Removal of asbestos and PCB wastes from mid-section of building;
- Crushing and removal of foundry ovens in the mid-section of the building;
- Excavation, staging and removal of PCB contaminated soils on the east side of the building; and
- Hazcatting and preparation of liquid wastes in drums for transport and disposal.

2.2.1.1 Planned Response Activities
See Section 2.2.1

2.2.1.2 Next Steps
See Section 2.2.1

2.2.2 Issues
None

  2.3 Logistics Section
    Site logistics and support are being coordinated and provided by EPA ERRS contractor Environmental Quality Management, Inc. The following equipment was used on site during the reporting period:

- Heavy equipment
- Office & storage trailers
- Waste containers

  2.4 Finance Section
    No information available at this time.

  2.5 Other Command Staff
    2.5.1 Safety Officer
OSCs Kathy Halbur and Paul Ruesch are serving as safety officers for the project and Site for EPA. RM Mark Douglas is serving as safety officer for ERRS contractor.

A HASP has been established for the project and is signed by all personnel. Daily safety briefings are held each day before the start of work and are attended by all Site personnel.

2.5.2 Liaison Officer
OSCs Kathy Halbur and Paul Ruesch

2.5.3 Information Officer
OSCs Kathy Halbur and Paul Ruesch

3. Participating Entities
  3.1 Unified Command
N/A

3.2 Cooperating Agencies
City of Milwaukee
    Redevelopment Authority (RACM)
    Health Department
    Police Department
    Fire Department
    Department of Neighborhood Services
State of Wisconsin
    Department of Health Services
    Department of Natural Resources
WE Energies

4. Personnel On Site
  U.S. EPA - 1
ERRS (EQM, Inc.) - 5
START (Tetra Tech EM, Inc.) - 1
DRP Security Services, LLC - 1

TOTAL - 8

5. Definition of Terms
  ACM - Asbestos Containing Material
EPA - Environmental Protection Agency
ERRS - Emergency & Rapid Response Services
HASP - Health and Safety Plan
MDNS - Milwaukee Department of Neighborhood Services
MDPW - Milwaukee Department of Public Works
MFD - Milwaukee Fire Department
mg/kg - milligrams per kilogram
MHD - Milwaukee Health Department
MFD - Milwaukee Fire Department
MPD - Milwaukee Police Department
NR - Natural Resources
OSC - On scene coordinator
PCBs -Poly-Chlorinated Biphenyls
ppb - parts per billion
ppm - parts per million
RACM - Redevelopment Authority of the City of Milwaukee
RCL - Residual Contaminant Level
RML - Removal Management Level
RM - Response Manager
START - Superfund Technical Assessment & Response Team
TDD - Technical Direction Document]
TO - Task Order
WDHS - Wisconsin Department of Health Services
WDNR - Wisconsin Department of Natural Resources

6. Additional sources of information
  6.1 Internet location of additional information/report
http://epaosc.org/WisconsinDieCast

6.2 Reporting Schedule
The next POLREP will be issued in mid-October.

7. Situational Reference Materials
  None


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