U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
Bremerton Auto Wrecking - Gorst Creek Site - Removal Polrep

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region X
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Subject:
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POLREP #6
Progress
Bremerton Auto Wrecking - Gorst Creek Site
10GL
Port Orchard, WA
Latitude: 47.5099832 Longitude: -122.7405453
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To:
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From:
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Jeffry Rodin, OSC
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Date:
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6/20/2016
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Reporting Period:
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6/20/2016 - 7/1/2016
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1. Introduction
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1.1 Background
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Site Number: |
10GL |
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Contract Number: |
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D.O. Number: |
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Action Memo Date: |
1/20/2016 |
Response Authority: |
CERCLA |
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Response Type: |
Non-Time-Critical |
Response Lead: |
EPA |
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Incident Category: |
Removal Action |
NPL Status: |
Non NPL |
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Operable Unit: |
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Mobilization Date: |
4/11/2016 |
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Start Date: |
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Demob Date: |
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Completion Date: |
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CERCLIS ID: |
WAN001002414 |
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RCRIS ID: |
WAH000048636 |
ERNS No.: |
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State Notification: |
Yes |
FPN#: |
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Reimbursable Account #: |
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Site Description and Background
Gorst Creek Landfill (GCL) is an unpermitted landfill
on the Kitsap Peninsula near Port Orchard (western WA) created in the late
1960s when the property owner at the time began disposing of waste in a deep
ravine holding Gorst Creek. The creek was channeled through a culvert along the
bottom of the ravine and waste was piled on top of the culvert to fill the
ravine. During operation of GCL (1968-1989), local residents and businesses
used GCL as a dump. For one year (1969-1970), the U.S. Navy contracted to
dispose of all waste from the Puget Sound Naval Station at GCL (est. 93,000
cy).
CGL is currently estimated to
contain 150,000 cy of waste. The culvert channeling the creek beneath the
landfill has collapsed beneath the weight of the landfill in at least two
locations, resulting in the impoundment of the creek upstream of the landfill.
During periods of heavy precipitation, impounded water seeps through the
landfill releasing contaminants downstream, and occasionally over tops the
landfill causing the downstream slope to collapse into the creek, washing waste
downstream and presenting a threat to State Highway 3 which is 100 yards
downstream. There have been five major slope failures at GCL since 1997,
typically associated with periods of heavy precipitation. Contaminants include
PCBs, pesticides, SVOCs and metals.
EPA Site History
- 2005 to 2009: EPA conducts
site assessments - Site does not list on NPL
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2009: EPA notifies Navy of
liability.
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2012: EPA proceeds with EE/CA
for removal action that proposes three alternatives: (1) replace existing
culvert, $3 million; (2) reroute the creek around landfill, $7-8 million; (3)
remove landfill and restore ravine and habitat, $30 million.
RCRA Unilateral Admin. Order
(UAO) to U.S. Navy
CERCLA Admin.
Order on Consent (AOC)
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2. Current Activities
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2.1 Operations Section
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2.1.1 Narrative/On-Site Activities
Monday, June 20
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cells 4 and 5.
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ERRS loaded waste from Containment Cells 5 and 6
into trucks and trailers for off-site disposal as non-hazardous waste; one load
of steel was also shipped off site for recycling.
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START collected samples from Containment Cells 4
and 8 for waste profile analysis; the samples were delivered to the laboratory
via courier service.
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START shipped air samples for asbestos analysis;
the samples were collected 6/16/16 through 6/18/16.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos. Air monitoring
results were below action levels and within normal limits.
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START submitted weekly equipment report to the
OSC, which includes an inventory of assets from the following sources: EPA
Region 10 Warehouse, EPA Region 10 Manchester Laboratory, EPA ERT-Las Vegas,
EPA ERT-Cincinnati, EPA ERT-New Jersey, USCG Pacific Strike Team, and WA
Department of Fish and Wildlife, as well as assets purchased for use by site
funds.
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START engineer, was on site to meet with the
OSC.
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ERRS mobilized two additional personnel to the
site to begin removing the fence separating Airport Auto Wrecking property and
the landfill.
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ERRS performed a site walk for hydroseed
contracting.
Tuesday, June 21
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cells 5 and 6.
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ERRS loaded waste from Containment Cells 6 and 7
into trucks and trailers for off-site disposal as non-hazardous waste.
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START collected samples from Containment Cell 5
for waste profile analysis; the samples were delivered to the laboratory via
courier service.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos and lead. Air
monitoring results were below action levels and within normal limits.
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Site visitors included EPA R7 Contracting
Officer, other R10 OSCs and R10 WES, ERRS
EQM was also on site.
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ERRS continued removing the fence separating
Airport Auto Wrecking property and the landfill.
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Additional equipment was received at the site,
including six electronic personal dosimeters for field personnel.
Wednesday, June 22
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cells 6 and 7.
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ERRS loaded waste from Containment Cells 2 and 7
into trucks and trailers for off-site disposal as non-hazardous waste.
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START collected samples from Containment Cell 6
for waste profile analysis, the samples were delivered to the laboratory via
courier service.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos. Air monitoring
results were below action levels and within normal limits.
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START shipped air samples for asbestos analysis;
the samples were collected 6/20/16 and 6/21/16.
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START performed in-situ screening with the XRF
instrument in the northwest corner of landfill at 10 locations; the maximum
concentration of lead was 122 mg/kg.
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EPA OSC Rodin and OSC Parker performed a site
walk at the Airport Auto Wrecking property along with representatives from
START and ERRS. START collected GPS coordinates of features at the Airport Auto
Wrecking property during the site walk.
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ERRS continued removing the fence separating
Airport Auto Wrecking property and the landfill, and began installing a
temporary fence approximately 20 yards northeast of the original fenceline.
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START submitted a draft Equipment Repositioning
Memorandum to EPA which outlined the process for repositioning EPA R10 assets
in case of an emergency response.
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START performed a radiation survey at
Containment Cell 8 and detected elevated readings with the Ludlum 19
(background was 5 uR/hr with maximum reading was 300 uR/hr ) and the Ludlum
2241-2 with 44-9 probe (background was 35 counts per minute [cpm] with a
maximum of 581 cpm). START began to develop a plan and arrange for specialized
staff and equipment to be site early the following day. A survey of Containment
Cells 1 to 7 with the Ludlum 19 revealed no radiation above background
concentrations.
Thursday, June 23
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cells 2 and 7.
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ERRS loaded waste from Containment Cells 2 and 3
into trucks and trailers for off-site disposal as non-hazardous waste.
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START collected samples from Containment Cell 7
for waste profile analysis; the samples were delivered to the laboratory via
courier service.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos and lead. Air
monitoring results were below action levels and within normal limits.
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EPA coordinated with the EPA Radiological
Emergency Response Team (RERT) personnel regarding procedures for entry and
identification of the radiological sources.
Notifications were also made with the Kitsap Co. Health District.
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Additional START personnel arrived on site with
additional radiation instrumentation, including Ludlum 2241-2 with 44-2
“sausage” probe, the Sam-940, and Rad-Eye B20. START/ERRS/PSTS isolated the
source (a cable 3 feet in length, tan in color) along with the surrounding soil
and debris, and placed the items inside two drum liners, which were then placed
inside a 55 gallon metal drum. The SAM-940 identified the cable as the source
containing Radium 226 with 94% confidence; it also provided readings of 1,745
uR/hr and 14,492 cpm. The drum was then relocated to the cylinder staging
area which is at the far corner of the stockpile area and away from most site
activity. START performed a survey of the drum in its new location with the
Ludlum 2241-2 and 44-2 probe; at the drum the readings were 175 uR/hr, and 5
feet away from the drum the readings were 8 uR/hr which was twice background
readings.
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OSC Rodin met with OSC Parker to discuss
additional Viper purchases, the Airport Auto Wrecking SSSP, and the Soil
Confirmation SSSP.
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START collected GPS coordinates of features of
the landfill including depth of excavation.
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Kitsap Co.
Health district personnel visited the site and met with OSC Rodin.
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ERRS continued removing the fence separating
Airport Auto Wrecking property and the landfill.
Friday, June 24
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cells 2 and 3.
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ERRS loaded waste from Containment Cells 1 and 3
into trucks and trailers for off-site disposal as non-hazardous waste.
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START performed air monitoring with AreaRAEs, MultiRAEs,
and DataRAMs and collected air samples for asbestos. Air monitoring results
were below action levels and within normal limits.
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A 30-gallon container was uncovered in the
landfill and was partially filled with a watery substance; the material was sampled
and determined to be rusty water using the FirstStep process.
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OSC Parker proposed revisions to the Airport
Auto Wrecking Property SSSP because it appears that a majority of the road
adjacent to the fence line will be excavated, thus negating the need for soil
sampling from the road.
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New EQM personnel arrived on site to transition
in as replacement as the Transportation and Disposal Coordinator.
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START collected samples from Containment Cell 2
for waste profile analysis; the samples were delivered to the laboratory via
courier service.
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START shipped asbestos air samples collected
6/22 and 6/23 (COC 10GL-043) for laboratory analysis. START also shipped lead
air samples collected 6/21 and 6/23 for laboratory analysis.
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OSC and
START inventoried new equipment delivered to the site including three 5-minute
ELSA escape breathing devices and four stationary high volume sampling pumps.
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ERRS continued removing the fence separating
Airport Auto Wrecking property and the landfill.
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START conducted weekly SWPPP inspection. No stormwater discharge from site, and water quality was monitored for pH and turbidity at Gorst Creek, downstream of Hwy 3 culvert.
Saturday, June 25
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cell 2
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ERRS loaded waste from Containment Cells 1 into
trucks and trailers for off-site disposal as non-hazardous waste, although
capacity was limited due to trucks breaking down.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos. All six air
stations had high volume sampling pumps for the first time which was made possible
by the recent acquisition of additional pumps. Air monitoring results were
below action levels and within normal limits.
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Current ERRS T&D Coordinator had his final
day on site, and continued to brief his replacement.
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No samples were collected from Containment Cells
today.
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Representatives from Alpine Evergreen arrived on
site at approximately 1300 hours for an abbreviated tour of the site; they
did not proceed into the stockpile area because of ongoing site operations.
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START performed data management tasks including
updating the site equipment tracking spreadsheet, revising the checklist for
equipment deployed at the six air stations, and downloading and processing XRF
data collected to date.
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ERRS continued removing the fence separating
Airport Auto Wrecking property and the landfill.
Monday, June 27
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cell 1.
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ERRS loaded waste from Containment Cell 8 into
trucks and trailers for off-site disposal as non-hazardous waste. A few rounds in the morning included
intermodal containers in addition to the trucks and pups.
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START collected samples from Containment Cells 1
and 3 for waste profile analysis; the samples were delivered to the laboratory via
courier service.
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START shipped air samples for asbestos analysis;
the samples were collected 6/24 and 6/25.
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START deployed time-lapse camera near Air
Station 2 to collect a single day of site activities.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos. Air monitoring
results were below action levels and within normal limits.
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START screened Containment Cells 1, 2, 3, and 8
for radiation with the Ludlum 19; nothing was detected above background.
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ERRS finished removing the fence separating
Airport Auto Wrecking property and the landfill with the exception of the metal
posts which will be removed by the heavy equipment during targeted excavation
of demolition debris.
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Additional ERRS personnel arrived on site to transition
in as the new on site ERRS Response Manager.
Tuesday, June 28
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cell 8.
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ERRS loaded waste from Containment Cell 4 and 8
into trucks and trailers for off-site disposal as non-hazardous waste.
Additionally, two bins of steel were transported off site.
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No soil samples were collected today.
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START deployed time-lapse camera near Air
Station 2 to collect a single day of site activities. The time-lapse video
collected from 6/27 was uploaded and can be accessed through a link on the main
site profile page.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos. Air monitoring
results were below action levels and within normal limits.
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Staff from Waste Management arrived on site to meet with
ERRS Transportation and disposal staff..
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USCG PST Executive Officer arrived on site along with a Dustrak
particulate monitoring instrument to deploy alongside a DataRam.
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Preliminary data for one of the samples
collected from Containment Cell 6 on 6/22 had elevated concentrations of lead
(44 mg/L) which exceeded the TCLP limit of 5 mg/L. EPA was notified of the
results, and ERRS began making preparations for transportation and disposal of
the waste to RCRA Subtitle C facility in Arlington, OR.
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OSC Rodin and START engineer performed a site
walk and noted that the sidewalls should be maintained at a height no greater
than 5 feet high, per the excavation plan.
Wednesday, June 29
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ERRS continued to excavate in the landfill and
transferred waste to Containment Cells 4 and 8.
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ERRS loaded waste from Containment Cells 4 and 5
into trucks and trailers for off-site disposal as non-hazardous waste.
Additionally, tires were transported off site.
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START collected samples from Containment Cell 8
for waste profile analysis; the samples were delivered to the laboratory via
courier service.
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START shipped air samples for asbestos analysis;
the samples were collected 6/27 and 6/28.
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START shipped air samples for lead analysis; the
samples were collected 6/28.
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START deployed time-lapse camera near Air
Station 2 to collect a single day of site activities.
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START performed air monitoring with AreaRAEs,
MultiRAEs, and DataRAMs and collected air samples for asbestos. Air monitoring
results were below action levels and within normal limits.
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All GES and most EQM personnel plan to demobilize
from the site after today for the extended holiday weekend. Only 5 EQM personnel
will be on site tomorrow.
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Two air samples collected for lead analysis on
6/21 indicated elevated concentrations, including one sample (58.4 ug/m3) from
the stockpile spotter that exceeded the site action level (50 ug/m3). Site activities on the day in question
including filling Containment Cell 6 which had an elevated sample that exceeded
the TCLP action level for lead. OSC Rodin and OSC Parker met with START and
ERRS to discuss the results and determine a plan of action which included
upgrading to respiratory protection in modified Level C.
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START conducted weekly SWPPP inspection. No stormwater discharge from site, and water quality was monitored for pH and turbidity at Gorst Creek, downstream of Hwy 3 culvert.
Thursday, June 30
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ERRS loaded waste from Containment Cells 5 and 7 into trucks and trailers for off-site disposal as non-hazardous waste. Additionally, 23 tons of steel was transported off site.
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Only 5 EQM personnel on site. No excavation was conducted within landfill area.
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START collected samples from Containment Cell 4 for waste profile analysis; the samples were delivered to the laboratory via courier service.
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No excavation activity within landfill area today, only within stockpile area
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START performed air monitoring with AreaRAEs, MultiRAEs, and DataRAMs at reduced number of stations, located only in active area of site within stockpile area, and collected air samples for metals and asbestos. Air monitoring results were below action levels and within normal limits.
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Air samples to be shipped to lab on 7/1/2016.
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Kitsap County Solid Waste personnel on-site today for site tour.
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EPA, EQM/ERRS, START, and PST to demob from site today for extended holiday weekend. Activities resume and personnel on-site starting 7/6/2016.
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2.2 Planning Section
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Disposal
Waste will continue to be segregated, staged in stockpiles, and characterized for proper disposal.
Progress
MATERIAL HAULED FROM LANDFILL TO STOCKPILE (Loads)
Day/Date
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Debris/Soil
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Concrete
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Steel
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Tires
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Debris/Soil Distribution
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Mon, June 20
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97 |
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Cell 4 - 34 loads, Cell 5 - 63 loads |
Tue, June 21
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57 |
13 |
5 |
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Cell 5 - 11 loads, Cell 6 - 46 loads |
Wed, June 22
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85 |
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Cell 6 - 47 loads, Cell 7 - 38 loads |
Thu, June 23
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89 |
1 |
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Cell 7 - 61 loads, Cell 2 - 28 loads |
Fri, June 24
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102 |
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Cell 2 - 63 loads, Cell 3 - 39 loads |
Sat, June 25
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59 |
8 |
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Cell 3 - 52 loads, Cell 1 - 7 loads |
Mon, June 27
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78 |
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Cell 1 - 78 loads |
Tue, June 28
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84 |
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3 |
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Cell 8 - 84 loads |
Wed, June 29
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75 |
6 |
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Cell 8 -7, Cell 4 - 68 |
Thu, June 30
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No activity |
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Fri, July 1
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No activity |
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Sat, July 2
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No activity |
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Subtotal for Reporting Period
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582 |
20 |
10 |
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MATERIAL HAULTED OFF-SITE FROM STOCKPILE TO LANDFILL OR RECYCLING FACILITY (Tons)
Day/Date
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Debris/Soil
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Loads of Debris/Soil
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Concrete
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Steel
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Tires
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Notes |
Mon, June 20
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1,473.48
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44 |
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17.64 |
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Tue, June 21
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1,636.41 |
48 |
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Wed,June 22
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1,719.59 |
50 |
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17.30 |
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Thu, June 23
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1,732.94 |
51 |
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Fri, June 24
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1,715.62 |
51 |
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Sat, June 25
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1,364.35 |
41 |
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Mon,June 27
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1,757.91
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54 |
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Tue, June 28
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1,658.65
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52 |
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20.65 |
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Wed, June 29
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1660.90
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52 |
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33.56
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Thu, June 30
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2,141.61
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66 |
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23.10 |
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Fri, July 1
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no activity
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Sat, July 2
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no activity
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Subtotal for Reporting Period
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16,861.46
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506 |
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78.69 |
33.56 |
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Subtotal for All Previous Reporting Periods |
19,961.81 |
614 |
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109.81 |
79.13 |
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Total Material Hauled Off Site |
36,823.27 |
1120 |
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188.50 |
112.69 |
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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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2.5 Safety Officer
An Integrated Health and Safety Plan (HASP) has been developed that combines the ERRS and START safety plans for consistency of response levels, emergency procedures, and other safety issues. Site workers have been briefed on the Integrated HASP, and it is available to everyone on site.
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3. Participating Entities
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3.2 Cooperating Agencies
EPA Emergency Management Program has been cooperatively working with multiple agencies to develop the removal and restoration plan. The following agencies continue be involved in the review process as the plan is developed to the 90% stage.
Suquamish Tribe
Kitsap Co. Health District
Kitsap Co. Emergency Management
WA State Department of Transportation
WA State Department of Fish & Wildlife
City Of Bremerton
In addition EPA has completed ESA consultation with National Marine fishers Service and USFW, and NHPA consultations with the WA State Historic Preservation office, and Suquamish Tribe.
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4. Personnel On Site
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For the week of June 6 - 11:
EPA 1-2
USCG 3-4
START 4-6
ERRS 18
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5. Definition of Terms
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SWPP – Stormwater Protection Plan
Thalweg – Lowest point in a stream (may or may not coincide
with centerline)
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6. Additional sources of information
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6.1 Internet location of additional information/report
The administrative record for the GCL Removal can be accessed through the following link:
https://semspub.epa.gov/src/collection/10/AR64302
Link for time lapse videos from the Gorst Removal Site:
https://vimeo.com/user54097859
6.2 Reporting Schedule
Currently Every 2 weeks
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7. Situational Reference Materials
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No information available at this time.
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