U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
Delhi Mercury Spill - Removal Polrep
Initial Removal Polrep

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region V
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Subject:
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POLREP #1
Initial
Delhi Mercury Spill
Ann Arbor, MI
Latitude: 42.2940870 Longitude: -83.8190560
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To:
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From:
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Elizabeth Nightingale, OSC
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Date:
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9/23/2014
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Reporting Period:
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9/22/14-9/23/14
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1. Introduction
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1.1 Background
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Site Number: |
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Contract Number: |
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D.O. Number: |
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Action Memo Date: |
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Response Authority: |
CERCLA |
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Response Type: |
Emergency |
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Response Lead: |
EPA |
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Incident Category: |
Removal Action |
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NPL Status: |
Non NPL |
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Operable Unit: |
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Mobilization Date: |
9/22/2014 |
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Start Date: |
9/22/2014 |
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Demob Date: |
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Completion Date: |
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CERCLIS ID: |
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RCRIS ID: |
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ERNS No.: |
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State Notification: |
MDCH |
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FPN#: |
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Reimbursable Account #: |
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1.1.1 Incident Category
Emergency Response
1.1.2 Site Description
Single family residence in a suburban neighborhood.
1.1.2.1 Location
Ann Arbor, Michigan.
1.1.2.2 Description of Threat
On 9/22/14, MDCH filed an NRC Report (# 1096105), indicating
that a furnace repair technician had identified a mercury spill from a switch
on the furnace while completing a service call. The County Health Department screened
the site with a Lumex, and reported ambient mercury levels of up to 50,000 (nanograms per cubic meter) ng/m3 near the furnace and 34,000 ng/m3 in the basement. After opening windows
and ventilating the house, levels were generally reduced to less than 1,000
ng/m3. MDCH and the County Health Department requested EPA assistance to address the situation.
Mercury is a characteristically hazardous waste under the Resource Conservation and Recovery Act (RCRA), 42 U.S.C. 6901 et seq., as amended, and 40 CFR 261.24. Mercury exhibits the characteristic of toxicity (D009), and is therefore a hazardous substance under Section 101 (14) of CERCLA, 42 U.S.C. 9601(14).
The health effects of mercury are detailed by the ATSDR as follows:
The nervous system is very sensitive to all forms of mercury. Exposure to high levels of metallic, inorganic, or organic mercury can permanently damage the brain, kidneys, and developing fetus. Effects on brain functioning may result in irritability, shyness, tremors, changes in vision or hearing, and memory problems. Short-term exposure to high levels of metallic mercury vapors may cause effects including lung damage, nausea, vomiting, diarrhea, increases in blood pressure or heart rate, skin rashes, and eye irritation.
1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results
EPA mobilized to the site at approximately 5:00 PM on
9/22/14 and met with the County Health Department representative, and later with the homeowner. The homeowner requested that we return the next
morning to conduct monitoring and cleanup work. The homeowner planned to stay
in the home overnight, with the windows open to maintain ventilation. EPA and
START arrived on site at 8:00 AM on 9/23/14. The team closed windows and
screened all rooms in the house with the Lumex. Mercury vapor concentrations were below the acceptable concentrations
for most sensitive people (less than 1,000
ng/m3) in the breathing zone in all areas of the house except right near the furnace. Mercury vapors
were roughly 2,000 ng/m3 there. Visible beads of
mercury were present in the furnace. As these conditions presented an imminent and substantial endangerment to public health, welfare, or the environment, ERRS was mobilized and a removal action was initiated at the site.
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2. Current Activities
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2.1 Operations Section
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2.1.1 Narrative
Planned response activities on-site include:
a) Assessing the site;
b) Securing, staging characterizing spilled mercury and mercury contaminated waste;
c) Consolidating and packaging all materials containing hazardous substances, pollutants and contaminants for transportation and off-site disposal; and
d) Transporting and disposing of all characterized or identified hazardous substances, pollutants, wastes, or contaminants that pose a substantial threat of release at a Resource Conservation and Recovery Act/CERCLA-approved disposal facility in accordance with EPA’s Off-site Rule (40 C.F.R. § 300.440).
2.1.2 Response Actions to Date
ERRS mobilized to the site on 9/23. The laundry room area (that contains the furnace) was isolated from the rest of the house with poly sheeting and tape. Porous materials within the room were bagged for screening. A mercury vacuum was used to remove most visible mercury beads from the furnace. Some beads could not be accessed readily - work will continue on this effort tomorrow. The floor of the laundry room was inspected, and visible beads were removed from flooring, from behind molding and from under the hot water heater. Surfaces were cleaned with DI water. A ventilation system was set up in the laundry to vent the room overnight. EPA monitoring has not identified elevated mercury in other areas of the house to date - however investigation in ongoing.
Mercury Monitoring Results
During response activities conducted on 9/23, levels of mercury vapors inside the furnace within the laundry room exceeded 20,000 ng/m3, but did not exceed 1,000 ng/m3 in any other areas of the house after the laundry room was sealed.
Mercury Action Levels
According to the Agency for Toxic Substances and Disease Registry (ATSDR) and the Michigan Department of Community Health, a residential structure is safe for occupancy by sensitive persons when mercury levels are below 1,000 nanograms/cubic meter (ng/m3), in the breathing zone. or this response, the site will be considered cleaned up at this site when the visible mercury has been removed, and mercury levels in the breathing zone are less than 1,000 ng/m^3.
For screening objects, and debris, the Michigan Department of Community Health recommends that objects with mercury levels above 10,000 ng/m3 be disposed of outright. Objects with mercury levels between 10,000 and 1,000 ng/m^3 may aired out to reduce levels, and objects with mercury levels below 1,000 ng/m^3 may be kept. At this site, debris that was suspected to be contaminated with mercury was bagged and mercury levels within the bags will be measured. If the mercury level of the bagged debris exceed 10,000 ng/m^3, and levels do not reduce after airing out, the debris will be disposed of outright as mercury contaminated debris.
2.1.3 Enforcement Activities, Identity of Potentially Responsible Parties (PRPs)
Investigation into potentially responsible parties is ongoing.
2.1.4 Progress Metrics
| Waste Stream |
Medium |
Quantity |
Manifest # |
Treatment |
Disposal |
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2.2 Planning Section
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2.2.1 Anticipated Activities
Continue response action.
2.2.1.1 Planned Response Activities
The team will reconvene on site on 9/24 (tomorrow) to continue work to remove inaccessible beads of mercury from the furnace. Assuming these beads can be removed, at least one cycle of heating and venting of the laundry room to reevaluate ambient mercury levels and determine whether additional clean up work is needed in that area. Sealed bags containing materials removed from the laundry room will be placed in the sun then mercury levels within them will be measured. The home's ventilation system will also be evaluated for contamination as well.
2.2.1.2 Next Steps
Prior to completing the cleanup, the entire house will be rescreened to ensure that ambient air levels are below applicable action levels. Verification samples will be collected once the cleanup has been determined to be complete to verify that screened results are accurate.
2.2.2 Issues
The homeowner is planning to stay in the home, with the windows open to maintain ventilation.
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2.3 Logistics Section
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No information available at this time.
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2.4 Finance Section
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No information available at this time.
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2.5 Other Command Staff
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No information available at this time.
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3. Participating Entities
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3.1 Unified Command
3.2 Cooperating Agencies
Washtenaw County
Michigan Department of Community Health
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4. Personnel On Site
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Personnel on site on 9/22/14:
EPA: 1
Washtenaw County: 1
START: 0
ERRS: 0
Personnel on site on 9/23/14:
EPA: 1
Washtenaw County: 1
START: 1
ERRS: 3
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5. Definition of Terms
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| ATSDR |
Agency for Toxic Substances and Disease Registry |
| BZ |
Breathing Zone |
| CERCLA |
Comprehensive Environmental Response, Compensation, and Liability Act |
| CERCLIS |
Comprehensive Environmental Response, Compensation, and Liability Information System |
| DNR |
Department of Natural Resources |
| EPA |
Environmental Protection Agency |
| ERNS |
Emergency Response Notification System |
| ERRS |
Emergency and Rapid Response Service |
| MDCH |
Michigan Department of Community Health |
| MDEQ |
Michigan Department of Environmental Quality |
| NG/M^3 |
nanograms per cubic meter |
| NCP |
National Oil and Hazardous Substance Pollution Contingency Plan |
| NOAA |
National Oceanic and Atmospheric Administration |
| NPL |
National Priorities List |
| NRC |
National Response Center |
| OSC |
On Scene Coordinator |
| PPE |
Personal Protective Equipment |
| PPM |
Parts per million |
| RCRIS |
Resource Conservation and Recovery Act Information System |
| RP |
Responsible Party |
| RRT |
Regional Response Team |
| START |
Superfund Technical Assessment and Response Team |
| US FWS |
United States Fish and Wildlife Service |
| USCG |
United States Coast Guard |
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6. Additional sources of information
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6.1 Internet location of additional information/report
epaosc.net/delhi
6.2 Reporting Schedule
A final report will be issued when the removal action has been completed.
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7. Situational Reference Materials
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No information available at this time.
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