U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
Former Carter White Lead Facility/Area - Removal Polrep
Initial Removal Polrep

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region VII
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Subject:
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POLREP #1
Initial
Former Carter White Lead Facility/Area
NEN000704909
Omaha, NE
Latitude: 41.2841000 Longitude: -95.9032000
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To:
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From:
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Michael Davis, OSC
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Date:
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9/10/2012
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Reporting Period:
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8/20/2012 - 08/31/2012
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1. Introduction
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1.1 Background
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Site Number: |
NEN000704909 |
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Contract Number: |
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D.O. Number: |
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Action Memo Date: |
6/5/2012 |
Response Authority: |
CERCLA |
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Response Type: |
Time-Critical |
Response Lead: |
PRP |
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Incident Category: |
Removal Action |
NPL Status: |
Non NPL |
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Operable Unit: |
00 |
Mobilization Date: |
8/21/2012 |
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Start Date: |
8/21/2012 |
Demob Date: |
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Completion Date: |
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CERCLIS ID: |
NEN000704909 |
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RCRIS ID: |
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ERNS No.: |
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State Notification: |
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FPN#: |
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Reimbursable Account #: |
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1.1.1 Incident Category
This is a potentially responsible party-lead (PRP), time-critical removal action at the Former Carter White Lead Site (Site). The Site is a former lead-based white pigment manufacturing facility which occupies a city block in east Omaha, Douglas County, Nebraska. Investigations conducted by the U.S. Environmental Protection Agency (EPA) determined that lead-contaminated soil is present at the Site, which is the subject of this removal action. As detailed below, the objective of this removal action is to protect public health and the environment by responding to the release of hazardous substances into the environment as presented by soils contaminated with lead.
1.1.2 Site Description
The former Carter White Lead facility manufactured lead-based white paint pigments from 1881 to 1926, when the company ceased operations. In the early 20th century, the daily output of the facility was about 32,000 pounds of white lead. No portion of the site is currently or has ever been owned by any federal agency. No state or local government body has been an owner or operator of any facility or operation which contributed to contamination at the Site. There have been no previous removal actions taken at the Site.
Businesses currently on the Site include the Carter Lake Outreach Center building and a FleetPride truck service center. The Carter Lake Outreach Center building is located on the north central portion of the Site along East Locust Avenue between 21st and 22nd Streets, and is owned by Open Door Mission. The Carter Lake Outreach Center building is a thrift store used for distributing clothing and household items. FleetPride is located on the southeast portion of the Site. FleetPride leases the property for use as a heavy-duty truck repair and maintenance facility. The southwest portion of the Site is an unmaintained gravel parking lot. The two parcels comprising the south portion of the site are owned by Morgan Wheel and Engine Company (Moweco), Inc. A development plan proposed by Open Door Mission includes the purchase and redevelopment of the south portion of this Site into a vocational and educational training center, along with a grassy yard and a paved parking area.
1.1.2.1 Location
The Site is located in the city of Omaha, Nebraska, between North 21st Street East and North 22nd Street East, and East Locust Street and Avenue J, in the southwest one-quarter of Section 12, Township 15 North, Range 13 East (U.S. Geological Survey 1994). The approximate geographic coordinates of the subject property are 41.2841 degrees north latitude and 95.9032 degrees west longitude.
North of the Site is the Omaha Airport Authority. To the east, southwest, and west of the Site is Open Door Mission property. Open Door Mission provides support programs for those recovering from life-altering addictions and abuse. Southwest of the Site, located at the corner of North 21st Street East and Avenue J, is the Open Door Mission building which is a residential outreach and shelter facility for men. On the southwest corner of North 21st Street East and East Locust Street, Open Door Mission is developing a new residential building for disadvantaged women and families. To the east, at the corner of North 22nd Street East and East Locust Street, is an Open Door Mission apartment house and children’s playground which is currently not in use. South of the Site is the Omaha Box Company, which began production as a wooden box manufacturer in 1890. Presently, Omaha Box Company is an independent corrugated paper manufacturer and distributor.
The area immediately surrounding the Site is primarily commercial with some light industrial and residential properties. The 2000 Census data indicated that the population within 4 miles of the Site is approximately 81,373 persons. Of these, 88 residents live within one-quarter of a mile. Daycare and residential facilities are located adjacent to the Site. Employees of FleetPride and the Open Door Mission organizations are present at the Site as well as patrons of these entities.
The Site is located in a primarily commercial and industrial area. The Missouri River is approximately one-half mile south of the Site, and Carter Lake is approximately one-half mile north of the Site. With the exception of man-made storm water conveyances, there are no streams or creeks directly influenced by runoff from the site. The Region 7 Omaha/Council Bluffs Sub-area Contingency Plan includes a detailed analysis of environmentally sensitive areas and endangered and threatened species. There are no known environmentally sensitive habitats in the immediate vicinity of the Site. The nearest sensitive area is the Boyer Chute National Wildlife Refuge, approximately ten miles north of the Site.
1.1.2.2 Description of Threat
Based on the results of sampling, a soil release associated with known activities at the Former Carter White Lead facility has been established. The primary contaminant of concern at the Site is lead. Soil contamination is widespread across the footprint of the former facility boundaries and extends to a depth of approximately 4 to 5 feet below ground.
Lead is listed as a hazardous substance pursuant to 40 CFR § 302.4. As such, it is a “hazardous substance” as defined in section 101(14) of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), 42 U.S.C. § 9601(14).
Lead was detected in surface soils at concentrations up to 17,800 mg/kg. Detected levels of lead in surface soil exceed applicable risk-based screening levels for recreational and residential receptors as determined by an EPA Region 7 toxicologist. More importantly, the average concentration of lead at the Site, which likely represents typical exposure conditions, exceeds all screening levels except for the one day/week recreational visitor. For these reasons, levels of lead in surface soils at the Site pose unacceptable human health risks to recreational and residential receptors under current and future use conditions. Lead-contaminated soils may migrate via airborne dusts, surface runoff to nearby storm water and surface water bodies, construction and utility worker activity, children and adults transporting soils/dusts into nearby residential facilities and homes, and foot traffic into residences.
The actual or threatened release of a hazardous substance from this Site presents an imminent and substantial endangerment to the public health, or welfare, or the environment.
1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results
An investigation and remedial action are ongoing to address widespread lead contamination in the Omaha, Nebraska, area (referred to as the Omaha Lead Site [OLS]). In November 2004, as part of the OLS project, the EPA screened surface soils at 2706 North 21st Street East and 2802 North 21st Street East, two properties adjacent to the Site. The lead concentrations in those soils were below the 400 milligrams per kilogram (mg/kg) lead screening level.
There have been several past investigations at the Site. Open Door Mission, the current property owner for the north portion of the Site, retained Jacobson Helgoth Consultants, Inc. (JHC), to provide professional environmental consulting services regarding one parcel of the Site. From September through December 2004, JHC conducted several soil investigations to determine the extent of lead impact. JHC collected a total of 38 soil samples from 0 to 2 feet below ground surface (bgs) under the asphalt parking lot on the referenced parcel using direct push technology and a truck-mounted drill rig. The soil samples were analyzed for total lead by EPA Method 6010. Lead was detected in all of the soil samples, with concentrations ranging from 65.7 to 9,796 mg/kg. Sixteen of the samples underwent Toxicity Characteristic Leachate Procedure (TCLP) analysis and contained concentrations of lead in leachate ranging from 0.12 to 91.7 milligrams per liter (mg/L).
In October 2005, the EPA conducted a Preliminary Assessment (PA) at the Site. Field activities included: (1) in situ analysis of surficial soils for metals using a portable X-ray fluorescence (XRF) analyzer, and (2) collection of soil samples for laboratory confirmation analysis. The PA focused on the unpaved areas of the Site. A total of 111 samples collected across the Site identified ubiquitous lead contamination in surficial soil. The maximum detected concentration was 17,800 mg/kg and the average concentration of all samples was 1,700 mg/kg.
In July 2009, the EPA conducted a Removal Site Evaluation (RSE) at the Site. The main objective of the RSE was to delineate the extent of lead-contaminated soil. RSE sampling was conducted on July 13 and 14, 2009. Field activities included in situ XRF readings on-site and off-site, collection of surface and subsurface soil samples for field screening and laboratory analysis for metals, and collection of soil samples for lead speciation. First, in situ samples were analyzed using XRF to demonstrate conformance with data from the October 2005 PA. After data conformance was demonstrated, in situ samples were analyzed using XRF from systematically selected locations on adjacent properties to delineate the lateral extent of lead contamination in surficial soil. In total, 45 in situ XRF readings were taken. The EPA also collected six surface soil samples (including one background sample) for lab analysis to demonstrate statistical correlation with in situ XRF analysis. Surface soil concentrations of lead ranged from 18 mg/kg in an off-site delineation sample to 5,063 mg/kg in a central location within the Site.
Six subsurface soil borings were also sampled from depths ranging from 0 to 8 feet bgs to approximate the vertical extent of lead contamination in soil across the Site. The highest levels of lead contamination at the Site were detected between 2 to 4 feet bgs, with maximum concentrations around 22,000 mg/kg. Lead concentrations decreased significantly at depths below 4 feet bgs. Correspondingly, soil borings indicated a transition from fill material and debris to predominately native silty clays at 4 to 5 feet bgs across the Site.
Sampling from adjacent properties and at background locations indicates that the area of soil contamination does not extend appreciably beyond the footprint of the Former Carter White Lead facility. Three samples from a drainage swale in the right-of-way on the north and east sides of the Omaha Box Company, south of the Site across Avenue J, identified surficial lead concentrations ranging from 485 mg/kg to 731 mg/kg, which is statistically elevated relative to background, but does not exceed the Regional Screening Level for industrial properties of 800 mg/kg. One surficial sample from the roadside right-of-way along North 21st Street immediately west of the Site identified lead at 1,740 mg/kg.
Lead speciation analysis was conducted on three samples to identify and quantify the forms of lead present at the Site. Lead speciation was conducted by the University of Colorado’s Laboratory of Environmental and Geological Studies. The most common form of lead in soil (74 to 84 percent by mass) was cerussite, also known as white lead ore, which is a mineral consisting of lead carbonate that was formerly used as an ingredient for the manufacturing of white lead paint.
Findings from the PA and RSE are summarized as follows:
• Soil contamination: Surface and subsurface soil sampling identified widespread lead contamination on the parcels comprising the Site. Soil concentrations ranged from around 100 mg/kg to around 22,000 mg/kg total lead. Detected levels of lead in surface soil exceed the risk-based screening levels for recreational and residential receptors. More importantly, the average concentration of lead at the Site, which likely represents typical exposure conditions, exceeds all screening levels except for the one day/week recreational visitor. Contamination extends to a depth of 4 to 5 feet bgs, where soil borings indicate a transition from fill and construction debris to native geologic materials.
• Potential groundwater contamination: No groundwater sampling was conducted at this Site. During a Phase 1 Environmental Site Assessment conducted by a contractor for Open Door Mission in 2001, an attempt was made to collect groundwater samples from two shallow (below 15 feet bgs) monitoring wells located on an adjacent property east of 22nd Street, but these wells were found to be dry. The vertical extent of soil contamination was readily delineated and did not extend to the water table. Due to the predominantly insoluble nature of the primary contaminant, and considering that soil sampling indicates that the extent of contamination does not extend to the water table, a significant release to groundwater is not expected to have occurred.
• Unrestricted access: Currently there is no fencing around the Site to inhibit access. The Site is regularly accessed by patrons of immediately surrounding properties operated by Open Door Mission. Pedestrian traffic is frequent and recurrent. A portion of the Site is used for parking by the surrounding Open Door Mission organizations. Routine vehicle traffic across the Site generates considerable airborne dust as witnessed during the July 2009 sampling event, further contributing to human exposures.
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2. Current Activities
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2.1 Operations Section
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2.1.1 Narrative
Lead is the only contaminant of concern detected above applicable action levels at the Site. Lead-contaminated soil will be excavated and transported off-site for disposal. The southwest portion of the Site is currently vacant except for use as a parking lot by nearby facilities and for storage of construction materials and other items for use by FleetPride and Open Door Mission. Contaminated soils underlying the Carter Lake Outreach Center building, the FleetPride truck service center building, and existing structurally sound caps including asphalt and concrete parking areas will not be excavated. The objective of the excavation will be to mitigate lead contamination to levels determined to be protective for current and prospective future uses of the Site. The cleanup will be consistent with the Superfund Lead-Contaminated Residential Sites Handbook, OSWER 9285.7-50, August 2003, and will focus on mitigating impacts to human health and the environment given the site-specific property uses and exposure pathways, including reasonably anticipated future uses. The depth of excavation will be a minimum of 12 inches in all accessible areas of the site, and 24 inches in a pre-designated area which may be utilized as a garden area pending future redevelopment plans for the site.
Based on previous sampling, excavated remediation waste may exhibit a characteristic of hazardous waste for lead toxicity as defined in 40 CFR subpart C. However, the remediation waste will not be a listed hazardous waste as defined in 40 CFR subpart D. If contaminated soils need to be stabilized on-site prior to disposal to treat the toxicity characteristics, an Area of Contamination (AOC) will be delineated and soils will be treated in situ within the delineated AOC. If treatment or management of remediation waste occurs within an AOC, remediation waste will be managed in place for no longer than 90 days. Additionally, best management practices will be implemented to prevent cross-media contamination through particulate dispersion and runoff which are substantially equivalent to the performance standards for staging piles outlined in 40 CFR § 264.554(d)(1)(i)-(ii) and CFR § 264.554(d)(2), including fugitive dust suppression, stockpile liner(s) and cover(s), filter berms, and silt fencing. Transportation and disposal of the soil will be completed in accordance with all applicable local, state and federal requirements.
After removing the soils from the affected area, confirmation sampling will be conducted using field-based instrumentation and laboratory analysis to ensure that all removal objectives have been achieved, and the area will be backfilled, regraded and restored to original conditions or in a manner consistent with future uses as requested by the property owner(s). The backfill source will be evaluated to ensure the material could not reasonably be expected to have been impacted by hazardous substances, pollutants, or contaminants.
Post Removal Site Controls (restrictive environmental covenants) will be required because lead-contaminated soil will remain on-site at levels that do not allow unlimited use and unrestricted exposure to soils, namely, contaminated soils underlying the Carter Lake Outreach Center building, the FleetPride truck service center building, and existing asphalt and concrete parking areas that will not be excavated. Therefore, the EPA and the Nebraska Department of Environmental Quality (NDEQ) will jointly coordinate with the current property owners to identify and select institutional controls that are necessary to protect human health and the environment after the removal action is complete. The EPA expects that institutional controls will be implemented and maintained by the property owners.
Restrictive environmental covenants have been placed on the properties in which residual contamination will remain in place that will, in perpetuity, notify any potential purchaser of the known extent of contamination. Such covenants specify the location and extent of all residual contamination, require prior approval from the EPA and NDEQ for any construction activities which disturb contaminated soil, and require notification for anyone engaged in subsurface activities, such as utility or construction workers, of the presence of residual contamination. Such notice would be consistent with EPA guidance on institutional controls and the Nebraska Uniform Environmental Covenants Acts, LB 298. Additionally, portions of the Site may require listing on the “Nebraska Public Record,” an inventory of contaminated properties in the state that are not suitable for unrestricted land use and have institutional controls. Institutional controls would remain in place until contamination at the Site reaches levels considered safe for an any-use scenario based upon an evaluation of risk in accordance with appropriate and applicable EPA guidance and directives.
The EPA entered into an Administrative Settlement Agreement and Order on Consent ("AOC"), CERCLA-07-2012-0053, with NL Industries, Inc. and approved a Time Critical Removal Action Work Plan ("Work Plan"), dated June 20, 2012, incorporated into the AOC by reference. The Work Plan outlines the actions to meet the removal objectives outlined in this POLREP and the June 5, 2012 Action Memorandum issued by the EPA. The Work Plan, the Action Memorandum, and related documentation pertinent to the administrative record for this Site may be viewed on the project website at http://www.epaosc.org/formercarterwhite.
2.1.2 Response Actions to Date
NL Industries, Inc. (NL), selected ENTACT Environmental Services, LLC (ENTACT), as the principal contractor to conduct the removal action. The EPA completed a pre-mobilization walkthrough with the property owners and their legal representatives, NL and ENTACT personnel, on August 21, 2012. During the walkthrough, the scope and logistics of the removal action were discussed in detail. Parties playing a major role during the implementation of the time‐critical removal action were introduced. The following were present:
• Greg Dambold, ENTACT Project Coordinator
• Josh Carroll, ENTACT Field Project Manager
• Jenny Self, ENTACT Regulatory/Technical Specialist
• Kevin Lombardozzi, NL Industries Project Coordinator
• Richard DenHerder, Open Door Mission (ODM)
• Brad Stenslokken, ODM Maintenance Supervisor
• Morgan Holmes, Moweco, Inc.
On August 23, 2012, ENTACT mobilized equipment to the Site. Pre-construction video and photographs were taken to document pre-existing Site conditions. The haul route was established to the designated off-site disposal facility, which will be the Butler County Landfill. The landfill received Off-Site Rule approval from the EPA Region 7 Off-Site Rule coordinator, Deborah Bredehoff, on July 13, 2012. A schedule and call-in number was established for weekly project update meetings. Security fencing was constructed around the Site perimeter. Air monitoring locations were selected and approved by the EPA for time-integrated and real-time air monitoring stations. The office trailer was delivered, as were two excavators and an extended-fork forklift. Enviroblend was delivered and staged on pallets outside the work zone.
On August 24, 2012, the EPA conducted field screening along the western edge of 2107 East Locust Street in an area that had been redeveloped and grassed since the RSE sampling event. Screening was conducted using an XRF. Based on the screening results, which are summarized in the OSC log book, the southwestern corner of the parcel still showed elevated levels of lead, while two hotspots previously identified in the RSE did not. EPA also met with ODM and NL representative Richard DenHerder to discuss proposed changes requested by ODM to the Work Plan. The Work Plan was approved by the EPA pursuant to the AOC effective August 7, 2012. The EPA and NL considered and agreed to certain modifications to the Work Plan as noted below:
- “Section 3.0 Removal Action” of the Work Plan is modified by replacing the first paragraph with the following: “Even though the Site is zoned General Industrial District rather than Residential, this Work Plan proposes a removal action consistent with the protections for residential properties by conforming to the EPA’s Superfund Lead-Contaminated Residential Sites Handbook (OSWER 9285.7-50, August 2003). The Work Plan will remove exposed soils to a depth of one foot bgs in all areas that are not capped by intact asphalt or concrete or covered by a current or historic building foundation or pad, and will remove exposed soil to a depth of two feet bgs in an area not to exceed 14,000 square feet. The general location of this two-foot excavation area is shown on Figure 3 — revised (8/30/2012) and the exact location will be depicted after completion of all Work Plan activities in a surveyed as-built figure.
- "The area identified as Phase 3 work will be divided into two components as identified on Figure 3 — revised (8/30/20 12). The eastern portion of that Phase 3 area will be excavated to a depth of one foot, backfilled, and capped with a six-inch asphalt cover (four inches of base and two inches of compacted asphalt). The western portion of that Phase 3 area will not be excavated, but the existing asphalt surface will be restored in-place with a tack layer, a leveling course of asphalt and a new surface course of two inches of compacted asphalt as a final cover, except that a former utility corridor (approximately four feet wide) through the existing asphalted area will be excavated to a depth of one foot and backfilled prior to placement of the new cover, and a small portion at the southwest corner of the Phase 3 area that is not covered with asphalt will be excavated to a depth of one foot and restored with topsoil and revegetated. The location of these areas are shown on Figure 3 - revised (8/30/2012).
- "Within the area identified as Phase 1, NL will excavate that portion of the Phase 1 area at the southern side of the site to the curbline as shown on Figure 3 - revised (8/30/12), which is presumed to be consistent with the curbline of the properties to the east and west of the site, but not any part of the active roadway. NL will excavate those open areas of the Phase 1 and Phase 2 areas between the Fleetpride building and the fenceline behind that building to a depth of one foot to the extent that those areas are machine accessible, but will not disturb the building foundation, covered surfaces, equipment, or utilities in this area, or the soil at the fenceline. Work in the Phase 1 area will not disturb or otherwise jeopardize the integrity of the underground oil/water separator west of the FleetPride wash rack area.”
- Although the Work Plan and Figure 3 — revised (8/30/2012) retain the terms Phase 1, Phase 2 and Phase 3, the work at the Site, with the above-mentioned modifications to accommodate ODM, will be carried out by the project contractor to most effectively use the available resources. Therefore, the work may not move from one Phase area to the next as originally contemplated. This became necessary due to scheduling constraints with the asphalt subcontractors and in order to complete the project within the original schedule. The revised Figure 3 may be viewed on the project website at ttp://www.epaosc.org/formercarterwhite.
On August 27, excavation work started. As described in the Work Plan, soil is excavated and consolidated into 250 cubic yard stockpiles within the secured Area of Contamination, as delineated by NL and approved by NDEQ. A water truck is maintained on-site, and visible dust emissions from stockpiles are low, despite substance particulate contributions caused by off-site truck traffic on roadways surrounding the Site.
On August 29, stockpile waste characterization sampling began. Sampling was conducted by ENTACT personnel in accordance with the procedures specified in the Work Plan (i.e., four-part composite).
On August 31, excavation, on-site soil consolidation, and stockpile waste characterization sampling was completed. Initial rounds of waste characterization data were received, indicating high leachability with TCLP lead concentrations ranging from 30 mg/L - 100 mg/L. Waste stabilization treatment will begin in the next reporting period.
2.1.3 Enforcement Activities, Identity of Potentially Responsible Parties (PRPs)
An Administrative Settlement Agreement and Order on Consent CERCLA-07-2012-0053 was established between NL, the EPA and Moweco, Inc., effective August 7, 2012. ODM is a property owner and has provided access to complete the removal action as well an Environmental Covenant for implementation of Post-Removal Site Controls. Moweco filed a similar environmental covenant for the parcels under their ownership.
2.1.4 Progress Metrics
As of the close of this reporting period, no waste has been shipped off-site. Approximately 400 cubic yards of contaminated soil has been excavated and stockpiled awaiting treatment.
Waste Stream |
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Manifest # |
Treatment |
Disposal |
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2.2 Planning Section
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2.2.1 Anticipated Activities
2.2.1.1 Planned Response Activities
During the next reporting period, excavated soil will be treated and analyzed to determine if the waste soil was adequately stabilized to permit land disposal in the designated off-site disposal facility.
2.2.1.2 Next Steps
Enviroblend stabilization amendment will be mixed into the stockpiled soil in batches, at a ratio of approximately 4 percent by weight. One four-point aliquot sample will be collected from each of the 11 stockpiles on-site in accordance with the sampling procedures set forth in the approved Work Plan. Samples will be analyzed for lead and potential underlying hazardous constituents via EPA's SW-846 Method 1311, Toxicity Characteristic Leachate Procedure (TCLP).
2.2.2 Issues
Potential sources of contamination associated with the FleetPride facility were identified during the implementation of this removal action. Namely, stained soil and petroleum odors were observed near the underground oil-water separator, and a viscous tar-like substance was observed pooling inside the sand blasting room, apparently rising up from subslab through cracks in the shop floor and also through cracks in the foundation to soil outside the south wall of the FleetPride building. This information was shared with EPA Region 7 On-Scene Coordinator (OSC) Todd Davis and with TetraTech EMI, who will include sampling in a forthcoming Phase 2 Environmental Site Assessment (ESA) of the FleetPride property. Potential removal implications will be considered following receipt of the Phase 2 ESA data.
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2.3 Logistics Section
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The scope of this response does not warrant a structured incident management team (IMT), and there is no Logistics Section Chief or separate logistics section. No logistical issues are anticipated 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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2.5.1 Safety Officer
The safety officer on-site is Josh Carroll with ENTACT. No safety issues have been observed by the OSC, and no significant safety incidents have occurred at this time.
2.5.2 Liaison Officer
The scope of this response does not warrant a structured IMT, and there is no Liaison Officer assigned.
2.5.3 Information Officer
Belinda Young is the EPA Public Information Officer (PIO) assigned to this project. A public information fact sheet was developed by the PIO and distributed as follows:
(1) E-mailed to federal and state elected officials on July 26, 2012
(a) Senators Nelson and Johanns
(b) Congressman Terry
(c) State Senators Ashford, Cook, Council, Haar, Howard, Krist, Lathrop, Lautenbaugh, McCoy, Mello, Nelson, Nordquist, and Pirsch.
(2) E-mailed to local elected officials on July 26, 2012
Omaha Mayor and City Council
(3) Mailed to nearby businesses and residents on July 27, 2012
(4) Posted on the EPA R7 website on July 27, 2012
The Administrative Record will be made available for public review after it has been compiled and finalized by the EPA R7 Records Center staff at the following locations:
Omaha Public Libraries
Charles B. Washington Branch
2868 Ames Avenue
Omaha, Nebraska 68111
Phone: 402-444-4849
EPA Region 7 Records Center
901 North 5th Street
Kansas City, Kansas 66101
Toll Free: 1-800-223-0425
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3. Participating Entities
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3.1 Unified Command
The limited scope of this removal action did not warrant a Unified Command.
3.2 Cooperating Agencies
NDEQ and the City of Omaha have assisted in the planning and implementation of this removal action.
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4. Personnel On Site
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Beyond the EPA OSC, the composition and staffing of on-site personnel to implement this removal action is determined by the PRP and the designated contractor representative, namely Josh Carroll, the ENTACT Field Project Manager, and Kevin Lombardozzi, the NL Industries Project Coordinator. In general, field personnel consist of the Field Project Manager, one equipment operator, one analytical technician, and three laborers.
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5. Definition of Terms
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N/A
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6. Additional sources of information
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6.1 Internet location of additional information/report
http://www.epaosc.org/formercarterwhite
6.2 Reporting Schedule
The next operational period will be September 4 - September 14, 2012. A progress POLREP will be completed covering the next operational period.
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7. Situational Reference Materials
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N/A
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