HomeMy WebLinkAboutRS_ER_Dept_of_Ecology_Initial_Inv_Field_Report_190916_v1INITIAL INVESTIGATION FIELD REPORT
ERTS Number: 658832
Parcel #(s): 1352300005
County: King
FSID #: 54463839
CSID #: 12913
SITE INFORMATION
Site Name (Name over door):
Bryant Motors
Site Address (including City, State and Zip):
1300 Bronson Way N (SR 900)
Renton, WA 98057
Phone/email:
Site Contact, Title, Business:
Paul Craig, Senior Project Manager,
GeoEngineers, Inc.
Site Contact Address (including City, State and Zip):
pcraig@geoengineers.com
Phone/email:
425.861.6078
206.793.4589
Site Owner, Title, Business:
William R Bryant (Taxpayer)
Site Owner Address (including City, State and Zip):
1300 Bronson Way N
Renton, WA 98057
Phone/email:
Site Owner Contact, Title, Business:
Darrell Bryant,
Bryant Motors, Inc.
Site Owner Contact Address (including City, State and Zip):
1300 Bronson Way N
Renton, WA 98057
Phone/email:
Previous Site Owner(s):
Additional Info:
Alternate Site Name(s):
Bryant Motors Property
Additional Info:
Latitude (Decimal Degrees): 47.48467
Longitude (Decimal Degrees): -122.20012
INSPECTION INFORMATION
Inspection Conducted?
Yes No
Date/Time:
Entry Notice: Announced Unannounced
Photographs taken? Yes No
Samples collected? Yes No
RECOMMENDATION
No Further Action (Check appropriate box below): LIST on Confirmed and Suspected
Contaminated Sites List:
Release or threatened release does not pose a threat
No release or threatened release
Refer to program/agency (Name: __________________________)
Independent Cleanup Action Completed (contamination removed)
COMPLAINT (Brief Summary of ERTS Complaint):
GeoEngineers submitted a cleanup action report to document the remedial excavation of hydraulic oil contamination in soil
at Bryant Motors located at 1300 Bronson Way North in Renton, Washington. This report served as notification by the
owner of a petroleum release to soil within the 90-day reporting period required in MTCA.
CURRENT SITE STATUS (Brief Summary of why Site is recommended for Listing or NFA):
Soil removal and confirmation sampling was conducted at Bryant Motors inside the building during remodeling activities between
May and June 2015. Analytical results confirm all impacted soil was removed and remaining soils are in compliance with MTCA
Method A cleanup levels. Excavations were conducted to 19 feet bgs with no groundwater encountered.
Recommendation: NFA due to independent remediation.
Investigator: Donna Musa, NWRO TCP Date Submitted: 10/30/15
OBSERVATIONS
Description (If site visit made, please be sure to include the following: site observations, site features and cover,
chronology of events, sources/past practices likely responsible for contamination, presence of water supply wells and other
potential exposure pathways, etc.):
Documents reviewed:
Cleanup Action Report, Bryant Motors Property, 1300 Bronson Way North, Renton, Washington. GeoEngineers,
Inc., Redmond, Washington. August 12, 2015.
During building renovations, three hydraulic hoists (installed in 1968) were removed from within the building.
Soil characterization conducted on 5/15/15 revealed lube-oil range hydrocarbons in two of three soil samples at 5,900 ppm and
27,000 ppm. The third sample had detectible concentrations but below the MTCA Method A cleanup level. Diesel-range
hydrocarbons were above MTCA Method A in one of three samples, at 3,500 ppm. Soil samples were also analyzed for PCBs,
cPAHs, naphthalenes and RCRA metals. Results for PCBs, cPAHs, naphthalenes and RCRA metals were either non-detect or
less than the applicable MTCA cleanup levels.
Excavation and off-site disposal were the selected cleanup alternative. Approximately 236.71 tons of impacted soils were
removed from the site for permitted disposal. Confirmation samples obtained at the final limits of the excavation were below
MTCA Method A cleanup levels.
(fill in contaminant matrix below with appropriate status choice from the key below the table)
CONTAMINANT GROUP CONTAMINANT SOIL GROUNDWATER SURFACE WATERAIR BEDROCK DESCRIPTION
Non-Halogenated
Organics
Phenolic Compounds Compounds containing phenols (Examples: phenol; 4-
methylphenol; 2-methylphenol)
Non-Halogenated Solvents B
Organic solvents, typically volatile or semi-volatile, not
containing any halogens. To determine if a product has
halogens, search HSDB (http://toxnet.nlm.nih.gov/cgi-
bin/sis/htmlgen?HSDB ) and look at the Chemical/Physical
Properties, and Molecular Formula. If there is not a Cl, I, Br,
F in the formula, it’s not halogenated. (Examples: acetone,
benzene, toluene, xylenes, methyl ethyl ketone, ethyl
acetate, methanol, ethanol, isopropranol, formic acid, acetic
acid, stoddard solvent, Naptha). Use this when TEX
contaminants are present independently of gasoline.
Polynuclear Aromatic
Hydrocarbons (PAH) B Hydrocarbons composed of two or more benzene rings.
Tributyltin
The main active ingredients in biocides used to control a
broad spectrum of organisms. Found in antifouling marine
paint, antifungal action in textiles and industrial water
systems. (Examples: Tributyltin; monobutyltin; dibutyltin)
Methyl tertiary-butyl ether
MTBE is a volatile oxygen-containing organic compound that
was formerly used as a gasoline additive to promote
complete combustion and help reduce air pollution.
Benzene Benzene
Other Non-Halogenated
Organics TEX
Petroleum Diesel RB Petroleum Diesel
Petroleum Gasoline Petroleum Gasoline
Petroleum Other RB Oil range organics
Halogenated Organics
(see notes at bottom)
PBDE Polybrominated di-phenyl ether
Other Halogenated Organics
Other organic compounds with halogens (chlorine, fluorine,
bromine, iodine). search HSDB
(http://toxnet.nlm.nih.gov/cgi-bin/sis/htmlgen?HSDB ) and
look at the Chemical/Physical Properties, and Molecular
Formula. If there is a Cl, I, Br, F in the formula, it is
halogenated. (Examples: Hexachlorobutadiene;
hexachlorobenzene; pentachlorophenol)
Halogenated solvents PCE, chloroform, EDB, EDC, MTBE
Polychlorinated Biphenyls
(PCB) B
Any of a family of industrial compounds produced by
chlorination of biphenyl, noted primarily as an environmental
pollutant that accumulates in animal tissue with resultant
pathogenic and teratogenic effects
Dioxin/dibenzofuran compounds
(see notes at bottom)
A family of more than 70 compounds of chlorinated dioxins
or furans. (Examples: Dioxin; Furan; Dioxin TEQ; PCDD;
PCDF; TCDD; TCDF; OCDD; OCDF). Do not use for
'dibenzofuran', which is a non-chlorinated compound that is
detected using the semivolatile organics analysis 8270
Metals
Metals - Other B Cr, Ba
Lead B Lead
Mercury Mercury
Arsenic Arsenic
Pesticides
Non-halogenated pesticides
Pesticides without halogens (Examples: parathion,
malathion, diazinon, phosmet, carbaryl (sevin), fenoxycarb,
aldicarb)
Halogenated pesticides
Pesticides with halogens (Examples: DDT; DDE; Chlordane;
Heptachlor; alpha-beta and delta BHC; Aldrin; Endosulfan,
dieldrin, endrin)
CONTAMINANT GROUP CONTAMINANT SOIL GROUNDWATER SURFACE WATERAIR BEDROCK DESCRIPTION
Other Contaminants
Radioactive Wastes Wastes that emit more than background levels of radiation.
Conventional Contaminants,
Organic Unspecified organic matter that imposes an oxygen demand
during its decomposition (Example: Total Organic Carbon)
Conventional Contaminants,
Inorganic
Non-metallic inorganic substances or indicator parameters
that may indicate the existence of contamination if present at
unusual levels (Examples: Sulfides, ammonia)
Asbestos
All forms of Asbestos. Asbestos fibers have been used in
products such as building materials, friction products and
heat-resistant materials.
Other Deleterious Substances
Other contaminants or substances that cause subtle or
unexpected harm to sediments (Examples: Wood debris;
garbage (e.g., dumped in sediments))
Benthic Failures Failures of the benthic analysis standards from the Sediment
Management Standards.
Bioassay Failures
For sediments, a failure to meet bioassay criteria from the
Sediment Management Standards. For soils, a failure to
meet TEE bioassay criteria for plant, animal or soil biota
toxicity.
Reactive Wastes
Unexploded Ordinance Weapons that failed to detonate or discarded shells
containing volatile material.
Other Reactive Wastes Other Reactive Wastes (Examples: phosphorous, lithium
metal, sodium metal)
Corrosive Wastes
Corrosive wastes are acidic or alkaline (basic) wastes that
can readily corrode or dissolve materials they come into
contact with. Wastes that are highly corrosive as defined by
the Dangerous Waste Regulation (WAC 173-303-090(6)).
(Examples: Hydrochloric acid; sulfuric acid; caustic soda)
Status choices for
contaminants
Contaminant Status Definition
B - Below Cleanup
Levels (Confirmed)
The contaminant was tested and found to be below cleanup levels. (Generally, we would not enter each and every contaminant
that was tested; for example if an SVOC analysis was done we would not enter each SVOC with a status of "below". We would
use this for contaminants that were believed likely to be present but were found to be below standards when tested
S - Suspected The contaminant is suspected to be present; based on some knowledge about the history of the site, knowledge of regional
contaminants, or based on other contaminants known to be present
C - Confirmed Above
Cleanup Levels
The contaminant is confirmed to be present above any cleanup level. For example - above MTCA method A, B, or C; above
Sediment Quality Standards; or above a presumed site-specific cleanup level (such as human health criteria for a sediment
contaminant).
RA - Remediated -
Above The contaminant was remediated, but remains on site above the cleanup standards (for example - capped area).
RB - Remediated -
Below
The contaminant was remediated, and no area of the site contains this contaminant above cleanup standards (for example -
complete removal of contaminated soils).
Halogenated chemicals and solvents: Any chemical compound with chloro, bromo, iodo or fluoro is halogenated; those with eight
or fewer carbons are generally solvents (e.g. halogenated methane, ethane, propane, butane, pentane, hexane, heptane or octane )
and may also be used for or registered as pesticides or fumigants. Most are dangerous wastes, either listed or categorical. Organic
compounds with more carbons are almost always halogenated pesticides or a contaminant or derivitive. Referral to the HSDB is
recommended you are unfamiliar with a chemical name or compound, as it contains useful information about synonyms, uses, trade
names, waste codes, and other regulatory information about most toxic or potentially toxic chemicals.
Dibenzodioxins and dibenzofurans are normalized to a combined equivalent toxicity based on 2,3,7,8-tetrachloro-p-
dibenzodioxin as set out in Ch. 173-340-708(8)(d) and in the Evaluating the Toxicity and Assessing the Carcinogenic Risk of
Environmental Mixtures using Toxicity Equivalency Factors Focus Sheet (https://fortress.wa.gov/ecy/clarc/FocusSheets/tef.pdf ).
Results may be reported as individual compounds and isomers (usually lab results), or as a toxic equivalency value (reports).
FOR ECOLOGY II REVIEWER USE ONLY (For Listing Sites):
How did the Site come to be known: Site Discovery (received a report): 8/13/15 (Date Report Received)
ERTS Complaint
Other (please explain):
Does an Early Notice Letter need to be sent: Yes No
If No, please explain why:
NAICS Code (if known):
Otherwise, briefly explain how property is/was used (i.e., gas station, dry cleaner, paint shop, vacant land, etc.):
Site Unit(s) to be created (Unit Type): Upland (includes VCP & LUST) Sediment
If multiple Units needed, please explain why:
Cleanup Process Type (for the Unit): No Process Independent Action
Voluntary Cleanup Program Ecology-supervised or conducted
Federal-supervised or conducted
Site Status: Awaiting Cleanup Construction Complete – Performance Monitoring
Cleanup Started Cleanup Complete – Active O&M/Monitoring
No Further Action Required
Site Manager (Default: Donna Musa): Donna Musa
Specific confirmed contaminants include: Facility/Site ID No. (if known):
54463839
in Soil Cleanup Site ID No. (if known):
12913
in Groundwater
in Other (specify matrix: )
COUNTY ASSESSOR INFO: Please attach to this report a copy of the tax parcel/ownership information for each parcel
associated with the site, as well as a parcel map illustrating the parcel boundary and location.