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Baycote Metal Finishing Site

All POL/SITREP's for this site Baycote Metal Finishing Site
Mishawaka, IN - EPA Region V
POLREP #16
Special
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U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
Baycote Metal Finishing Site - Removal Polrep

EPA Emergency Response

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region V

Subject: POLREP #16
Special
Baycote Metal Finishing Site
C5B2
Mishawaka, IN
Latitude: 41.6497046 Longitude: -86.1648540


To:
From: Paul Atkociunas, OSC
Date: 9/15/2012
Reporting Period: September 14 -15, 2012

1. Introduction
  1.1 Background
   
Site Number: C5B2    Contract Number: EP-S5-09-05
D.O. Number:      Action Memo Date: 2/23/2012
Response Authority: CERCLA    Response Type: Time-Critical
Response Lead: EPA    Incident Category: Removal Action
NPL Status: Non NPL    Operable Unit:
Mobilization Date: 5/29/2012    Start Date: 5/29/2012
Demob Date:      Completion Date:  
CERCLIS ID:    RCRIS ID:
ERNS No.:    State Notification:
FPN#:    Reimbursable Account #:

1.1.1 Incident Category

Time-Critical Removal Action:  Manufacturing/Processing/Maintenance – Electroplating, Metal Finishing


1.1.2 Site Description

See Initial Polrep.

1.1.2.1 Location

The Baycote Metal Finishing Site is located at 1302 Industrial Drive in Mishawaka, St. Joseph County, Indiana 46544.  The geographical coordinates for the Site are 41°39’0.03” North latitude and 86°09’57.11” West longitude.  The Site is bordered by industrial properties to the north, east, and south and Industrial Drive and industrial properties to the west.  Residential properties are located approximately 700 feet to the west.  Seven churches and two schools are located within 1 mile of the Site. The St. Joseph River, a major surface water body that terminates in Lake Michigan, is located 0.85 mile northwest of the Site. 

1.1.2.2 Description of Threat

See Initial Polrep.

1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results  
See Initial Polrep.

2. Current Activities
  2.1 Operations Section
    2.1.1 Narrative

In a letter dated November 11, 2011, the St. Joseph County Health Department (SJCHD) requested assistance from the U.S. EPA to secure hazardous wastes left on-site.  SJCHD was concerned that the Site posed a significant threat to the health and safety of companies within the industrial park as well as the residential area located less than a 1,000 feet from the facility.  On February 23, 2012, the Director of U.S. EPA's Superfund Division approved an Action Memorandum for a time-critical removal action at the Baycote Metal Finishing Site.

 

On April 6, 2012, U.S. EPA issued a Unilateral Administrative Order to the potentially responsible parties to conduct a removal action at the Site.  The potentially responsible parties presented and inability to pay argument and indicated that they did not intend to conduct a removal action at the Site.  EPA began time-critical removal actions at the Baycote Site on May 29, 2012. 

 

This is a large Site, with 11 plating lines in 6 areas and several waste water treatment systems.  The OSC and its contractors have adopted a work plan to prioritize the high hazard areas / plating lines.

2.1.2 Response Actions

 

September 14

Ten containers of waste were placed into the cubic yard container for consolidation / disposal (approximately 1,000 pounds total).  Laboratory data from the composite sample contained 49,000 milligrams per kilogram of total cyanide.  Hazard Categorization data from the waste placed into the composite container did not document reactive substances.  However, there were four 35-gallon containers that contained bagged labeled as Sodium hydrosulfite (reactive material). 

 

At approximately 1900 a fire/chemical reaction occurred in the shipping container located in the storage area of the facility.  The local Fire Department reported the incident to the U.S. EPA.  The local Fire Dept. extinguished the fire, but a vapor cloud was observed around the container.  Initial readings by the Fire Dept. were 6.5 ppm of HCN inside the building but, HCN was not detected outside the building.  The incident was confined to the container and the building structure was not involved.  Fire Dept. waited for EPA before further site entries.  Roads were closed between Byrkit Avenue west to Merrifield, and 12th Street north to Lincoln Way East.  Approximately 200-300 residents were advised to shelter-in-place, and 34 residents in a nearby senior center were evacuated to a shelter and assisted by the Red Cross.  No injuries have been reported at this time.

 

2200hrs

OSC Mendoza arrived on scene and is coordinated response activities with the Fire Chief.  AreaRAEs will were deployed in the evacuation zone.  Mark Johnson (ATSDR) arrived to assist the OSC with health related questions and concerns, and advise on evacuation decisions.  ERRS crew arrived and will initiated cleanup actions to address the released waste material and repackage the contents. 

 

September 15, 2012

0100 -   OSC, ERRS and Fire chief worked out a plan to send in ERRS in level B to break up the burning pile into several pieces and secure the pieces in steel drums to let the reaction take its course in a controlled environment with monitoring.

 

0451-  ATSDR and OSC sent Incident Command (Fire Chief) an email recommending the lifting of the evacuation order based on non-detects for the contaminants of concern.

 

0500 -  Air monitoring onsite and in the community is ongoing non-detects continue for hydrogen sulfide, hydrogen cyanide, and sulfur dioxide.

 

0730 OSC Atkociunas arrived onsite.  OSCs Atkociunas, Mendoza and ATSDR Representative Mark Johnson conducted news interviews with WSBT (CBS Affiliate),WNDU (NBC Affiliate) and Fox 28 News regarding the incident.  The reaction has stabilized.  EPA, START and ERRS will continue to monitor the drums.   No temperature changes in the drums have been detected.  Air monitoring results of the ambient air near the drums is at background.  The evacuation order was lifted by Incident Command.


  2.2 Planning Section
    2.2.1 Anticipated Activities

2.2.1.1 Planned Response Activities

2.2.1.2 Next Steps

The next steps for the incident that ocurred on September 14 include:

1.           Monitoring the containers for any additional reactions.

2            Conduct air monitoring / sampling in the community.
3.           Determine final management of the waste in the eight containers
4.           Investigate the cause of incident and implement corrective measures

2.2.2 Issues

The exact cause of the fire is under investigation.  Ten containers of waste were placed into the cubic yard container for consolidation / disposal.  Laboratory data from the composite sample contained 49,000 milligrams per kilogram of total cyanide.   Hazard Categorization data from the waste placed into the composite container did not document reactive substances.  However, there were four 35-gallon containers that contained bagged containers labeled as Sodium hydrosulfite. Sodium hydrosulfite is spontaneously combustible material.  The material within the container was not consumed, however the liner and cubic yard box caught on fire.  The consolidation of the wastes caused incompatible materials to react exothermically with decomposition products likely generated (including hydrogen cyanide, hydrogen sulfide, and sulfur dioxide).


  2.3 Logistics Section
    NA

  2.4 Finance Section
    No information available at this time.

  2.5 Other Command Staff
    2.5.1 Safety Officer

The Health and Safety Plan was approved and signed by all site personnel. 
Health and Safety meetings are held daily. 

2.5.2 Liaison Officer

NA

2.5.3 Information Officer:
Community Involvement Coordinator: Ginny Narsete

3. Participating Entities
  3.1 Unified Command
City of Mishawaka Fire Department was the Incident Commander for the Emergency Response. 
U.S. EPA will resume removal activities on Monday, September 17.

3.2 Cooperating Agencies

IDEM

City of Mishawaka

St. Joseph County Health Department

Mishawaka Fire Department
ATSDR

4. Personnel On Site
 

The following numbers of personnel were on-Site during the reporting period:

  
Organization Position # Personnel
EPA OSC 1
ERRS Response Manager 1
  Chemist
  Foreman 1
  Laborer 4
  Field Cost Accountant
  Equipment Operator 2
Weston START 2


5. Definition of Terms
 

Baycote            Baycote Metal Finishing Site

CERCLA           Comprehensive Environmental Response, Compensation, and Liability Act
CRZ                  Contamination Reduction Zone

EPA                 Environmental Protection Agency

ERRS               Emergency and Rapid Response Services
D.O.T.              Department of Transportation

FCA                 Field Cost Accountant

HASP               Health and Safety Plan

HAZCAT            Hazardous Categorization 
IDEM                Indiana Department of Environmental Management

NA                    Not Applicable

OSC                 On-Scene Coordinator

PolRep              Pollution Report

RCRA                Resource Conservation and Recovery Act

PRP                  Potentially Responsible Party

RM                    Response Manager

START               Superfund Technical Assessment and Response Team
ATSDR              Agency for Toxic Substances and Disease Registry   

6. Additional sources of information
  6.1 Internet location of additional information/report

www.epaosc.org/BaycoteMetalFinishing

6.2 Reporting Schedule

Progress POLREPS will resume during the week of September 17.

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


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