FORD NEWPORT BEACH OPEN HOUSE · Site History 1957-1993 • Ford operated an aeronutronics facility...
Transcript of FORD NEWPORT BEACH OPEN HOUSE · Site History 1957-1993 • Ford operated an aeronutronics facility...
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FORD NEWPORT BEACH OPEN HOUSE
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WELCOME / CHECK IN
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BACKGROUND AND SITE HISTORY
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SITE HISTORY & CLEANUP
Site History 1957-1993 • Ford operated an aeronutronics facility from 1957 to 1993
• Operations included the research, engineering and manufacture of aerospace systems – Missile guidance components, rocket motors and computer hardware
• Volatile organic compounds (VOCs) were used to clean metal parts – Trichloroethylene (TCE) and tetrachloroethylene (PCE)
Facility was closed and demolished in 1993
Ford Aeronutronic provided major support for the development of Project Space Track (1957-1961)
Pho
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nian
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ion.
Site Cleanup 1993-1996 • Oversight provided by Santa Ana Regional
Water Quality Control Board (Water Board)
• Cleanup in accordance with regulatory standards established in the 1990s
• Soil and groundwater remediation included:
– Bioremediation – Excavation and disposal of soils – Groundwater and soil vapor
treatment systems
• In 1996/97, the Water Board and Orange County Health Care Agency determined no further remediation was required for the main area for the anticipated land reuse
• Site was rezoned and redeveloped
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WHAT ARE VOCs?
VOCs: Volatile Organic Compounds (VOCs) get their name from their ability to pass easily from a liquid into a gaseous state. VOCs, which include TCE and PCE, are commonly used in industry as well as in the home. Recent research has shown that VOCs in soil and groundwater can evaporate as vapors, and can collect under buildings potentially afecting the quality of indoor air. This process is called vapor intrusion.
TCE: Trichloroethylene (TCE) is used as a solvent for degreasing metal parts during the manufacture of a variety of products. It can also be found in consumer products, including some wood fnishes, adhesives, paint removers, and stain removers. Due to its widespread use, very low levels of TCE are common in the air of homes and businesses and in outdoor air in urban areas.
PCE: Tetrachloroethylene (PCE) is a chemical compound that is commonly used in clothes dry cleaning and metal degreasing. It is also used to make other chemicals and can be found in some consumer products.
Air fresheners (including electric varieties and room sprays)
Scented candles
Perfume/cologne
Beauty products (e.g., hairspray, hair dye, aerosolized products)
Pepper spray
Paints, varnishes and lacquers
Nail polish and nail polish removers
Paint thinner
Paint, varnish, rust and lacquer removers
Shoe polish
Adhesives/glues (e.g., wood glue, craft glue, model glue, carpet glue)
Markers
Cleaning agents (e.g., bleach, ammonia)
Rubber cement and epoxy adhesives
Toilet disinfectant
Moth balls
Gasoline
Automobile exhaust
Cigarette smoke
Cleaning solvent (e.g., carburetor/car part cleaner)
Petroleum products
Carpet/rug/upholstery cleaners
Plastic foam insulation
Refrigerant
Printing inks
Insecticides, fungicides and pesticides
Flame retardant fabrics
Plastic products
Polyresin molded decorations (particularly from China)
Soil or space fumigant
Building materials (e.g., particle board)
White correction fuid (for typewriters and print)
Furniture polish and foor polish
Residential wood combustion
Fiberglass
Dry cleaning chemicals
Metal degreasers and metal cleaners
Drain cleaners
Source: California Water Board
Common Household Sources of Volatile Organic Compounds (VOCs)
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ONGOING MONITORING
Ongoing Monitoring 1996-2018 • As a condition of regulatory approval, Water
Board required Ford to continue to monitor groundwater for VOCs – Groundwater has been regularly
monitored since 1996
• Soil gas investigation work conducted in 2006, 2008 and 2012 found TCE and PCE below acceptable health risk levels at the time – Soil gas samples (collected from tiny air pockets between soil grains)
collected periodically
• In 2014, the USEPA published a memo for TCE, specifc to sensitive receptors
• In 2016, the Water Board’s environmental screening levels were updated and made more stringent
• In June of 2018, TCE and PCE were detected in soil gas above the current environmental screening levels at some areas of the site
• Based on the results of soil gas sampling in June of 2018, Ford initiated a soil vapor and vapor intrusion investigation
Mobile Laboratory
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TIMELINE
1957 1993 1996 2016 2017 2018
Advances in science and changes in regulatory screening levels:
• More sensitive instrumentation
• Lower laboratory detection limits
• Identifcation of the potential for vapor intrusion
• Improved investigation techniques
Ford Aeronutronic 0perations
Site demolished, environmental investigation, and remediation
Water Board requires ongoing groundwater monitoring
Soil and groundwater remediation complete for the main area, site rezoned and redeveloped
Water Board updates
Environmental Screening
Levels (ESLs)
Most recent Water Board update to Environmental Screening Levels
Ford initiates soil gas and vapor intrusion investigation
Water Board requests additional investigation activities TCE and PCE
detected above updated Environmental Screening Levels
2014
Water Board requests compilation and re-evaluation of all existing data (Conceptual Site Model)
USEPA publishes a memo for TCE, specifc to sensitive receptors
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CURRENT INVESTIGATIONS
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SITE MAP
North Area
Big Canyon Arroyo
(BCA Area)
Former ATC Area
Former FordAeronutronic Facility
Main Area
Unive
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San Diego Creek
Bison Avenue
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Big Canyon Country Club
Ford Road
Camelback
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Explanation
North Area and Big Canyon Arroyo Areainvestigation boundaries
Location of former facility buildings
Former facility boundary
Base map from NAIP, Orange County, CA, dated 2009.
861739717.02.3B
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SITE VICINITY MAPFormer Ford Aeronutronic Property
Newport Beach, California
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NORTH AREA SOIL GAS INVESTIGATION (subsurface)
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Bellis St
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Aralia St
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Crooked Stick Dr
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Edgewood Dr
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SG-40SG-40SG-39SG-39
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SG-36SG-36SG-35SG-35
SG-34SG-34
SG-33SG-33SG-32SG-32
SG-31SG-31
SG-30SG-30
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SG-14SG-14
SG-13SG-13
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SG-113SG-113
SG-112SG-112
SG-111SG-111SG-110SG-110
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screening level micrograms per cubic meter
Abbreviations:
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Parcel Identifiers1 - Newport North Apartment Homes2 - Newport North Townhomes Association3 - Calty Design Research, Inc. & Toyota Motors4 - U.S. Post Office & Way Basics5 - Mini U Storage - Newport 2 & Pensky Truck Rental6 - Liberty Baptist Church & Newport Christian School7 - Powerstation8 - Mini U Storage - Newport 19 - Newport North Shopping Centre10 - Bayridge Park Homeowners Association11 - Belcourt Terrace Homeowners Association12 - Belcourt Master Community Association13 - One Ford Road Community Association14 - Belcourt Park Homeowners Association21 - Irvine Company Property22 - Belcourt Hill Homeowners Association
Chemical of Concern
Current Residential Soil Gas SL (μg/m3)
Current Commercial Soil Gas SL (μg/m3)
TCE 240 3,000PCE 230 2,000cis-1,2-DCE 4,200 35000trans-1,2-DCE 42,000 350,0001,2-DCA 55 4701,1-DCE 37,000 310,0001,1-DCA 900 7,7001,1,1-TCA 500,000 4,400,000Vinyl Chloride 4.8 160
Explanation
Soil Gas Probes
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Isoconcentration Line, Dashed WhereInferred
Residential TCE isoconcentrationline
Commercial TCEisoconcentration line
Residential PCEisoconcentration line
Proposed Indoor Sampling Areas
Commercial area proposedindoor air sampling
Residential area proposed indoorair sampling
Boundary Lines
North Area investigationboundary
Former facility boundary
Former ATC
Parcel boundary and numberdesignation
Approximate axis of historicalgroundwater plume
Base map from NAIP, Orange County, CA, dated 2009.
By:
Date:
Project No.
09/06/2018
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NORTH AREASOIL GAS PROBE INSTALLATIONS
RESIDENTIAL & COMMERCIAL INDOOR AIR SAMPLINGFormer Ford Aeronutronic Property
Newport Beach, California8618397107.02.3B
What does the blue shading represent? Commercial areas for proposed indoor air sampling
What do the diferent colored dashed lines represent? The green contour lines indicate the approximate area of concentrations above 240 micrograms per cubic meter for TCE Environmental Screening Level
The purple contour lines indicate the approximate area of concentrations 230 micrograms per cubic meter for PCE Environmental Screening Level
What is a soil gas probe? A soil gas probe is a small, cylindrical hole that extends to about 15 feet deep that soil vapor samples are extracted from
What does the green shading represent? Residential areas for proposed indoor air sampling
Information represented on the map is current as of 9/18 and is subject to change as investigations progress
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Residential areas for proposed indoor air sampling
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17 Former historical Big Canyon Creek location based on 1931 USGS Topographic map. Base map from NAIP,
Explanation Orange County, CA, DATED 2009. Soil Gas Probes Boundary Lines
BIG CANYON ARROYO AREA Big Canyon Arroyo Area Soil gas probe location (installed and sampled) Parcel Identifiers investigation boundary SOIL GAS PROBE INSTALLATIONS 15 - Big Canyon Community Association-Master Association Soil gas probe location (installed/sampling pending) (Big Canyon Country Club Golf Course) & RESIDENTIAL INDOOR AIR SAMPLING Former ATC 16 - Sea Island Community Association Former Ford Aeronutronic Property 17 - Canyon Mesa Community Association
Parcel boundary and number Newport Beach, California 18 - Canyon Lakes Community Association 22 designation 19 - Canyon Crest Community Association Residential proposed indoor air sampling 20 - Canyon Point Community Association By: KLU 22 - Belcourt Hill Homeowners Association
Date: 09/06/2018 Big Canyon Creek 21 21
Information represented on the map is current as of 9/18 and is subject to change as investigations progress
http:8615397107.02.3B
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WHAT IS VAPOR INTRUSION AND HOW IS IT INVESTIGATED?
Soil Gas Monitoring Probes (5-15 feet)
Permanent Groundwater Monitoring Well (Average 50 feet)
Residual VOCs in groundwater can move up into soil
Typically from historic uses Chemicals in groundwater can spread by its natural flow
Groundwater Contaminants: measured in micrograms per liter (µg/L)/parts per billion (ppb)
Soil Gases: measured in micrograms per cubic meter (µg/m3)
Indoor Air: measured in micrograms per cubic meter (µg/m3)
Soil gas can pass through cracks in the foundation and gaps where pipes enter the building
SOURCE OF CONTAMINATION MOVED BY GROUNDWATER
WHAT ARE WE STUDYING?
Sand or gravel fill around foundation can be easier for vapor to pass through
BACKFILL PATHWAYS
GETTING THROUGH THE FOUNDATION
Chemicals in soils can move along undergound pipes
PIPE PATHWAYS
Groundwater, Soil Gas and Indoor Air Investigation Areas Groundwater • Groundwater monitoring has been
ongoing since 1996
Soil Gas • As a result of advances in science
and technology, as well as resulting changes in regulatory screening levels, Ford is conducting additional soil gas investigations to determine location and extent of subsurface soil gases
• Subsurface soil gases occur when VOCs pass from groundwater into the soil gas above by volatilization
Vapor Intrusion • There is a potential for soil gas to
move towards the ground surface and potentially impact indoor air
• Ford is conducting indoor air sampling to determine if there are any impacts from subsurface soil gas
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INDOOR AIR AND SUB-SLAB SAMPLING PROCESS
Purpose Determine if VOCs (TCE and PCE) in indoor air are above Water Board Environmental Screening Levels
Sampling Process • Indoor Air Samples
– Building survey: pre-sampling questionnaire
– Identifcation of household items that contain VOCs
– Placement of canisters in targeted areas
– Leave canisters for 24-hours to collect air (8-hours for business)
– Return to retrieve canisters
- Process typically takes 2 hours in total
• Sub-slab (directly beneath foundation, typically in garage) or perimeter soil gas samples collected (outside) for correlation with indoor air samples
DRY-CLEANED CLOTHING
TYPE AND AGE OF HEATING/ COOLING
HOUSEHOLD
FURNITURE
SYSTEM CHEMICALS AND CLEANERS
NEW CARPETING
BUILDING MATERIALS
CONDITION OF FOUNDATION AND FLOOR
Indoor Air Testing and VOCs in Household Use Measuring chemicals in indoor air can be tricky because many common household items and materials can afect levels
Carpets, cleaning products and building materials can off-gas chemicals
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VAPOR INTRUSION INVESTIGATION PROCESS
1. Volatile chemicals are identifed in the soil, 2. Sample for vapors underground to groundwater, or vapors coming from the soil. determine area of concern. Former Facility
Sites where VOCs were historically Crews drill into the ground to collect soil, used are being re-evaluated Former Facility groundwater, and soil gas samples.
Sampling sites
3. Test for vapor intrusion inside homes and buildings within the area of concern. Area of concern
Former Facility This is the area where testing shows that vapor intrusion may occur in buildings.
Testing beneath the home for vapors is called sub-slab soil gas sampling. It involves drilling small holes in your garage foor to collect soil gas samples from under the building. Indoor air samples are collected as well.
Sampling Area
The sampling areas may grow or shrink based on test results.
4. Take steps to mitigate for vapor intrusion. If testing fnds vapor intrusion is a problem, there are actions that can be taken to quickly address the situation such as sealing cracks in the foundation, installing mobile air purifers, adjusting the heating/ventilation system and in some cases installing a mitigation system to vent vapors from beneath the home.
SOIL GAS
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WHAT YOU MAY SEE Subsurface Soil Gas Sampling in Public Areas
Utility Clearance Street Markings Removal of Street Markings Soil Gas Probe Drill Rig Top of Soil Vapor Probe Identifying Utilities after Restoration
Subsurface Soil Gas Sampling - Residential/Commercial
Hand Auger Installing Perimeter Probe Sampling Top of Soil Vapor Probe
Indoor Air and Sub-Slab Sampling
Pre-Sampling Building Survey
Indoor Sampling Canister
Sub-Slab Install (eg. garage)
Sub-Slab Sampling Sub-Slab Patch (eg. garage)
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SAMPLING RESULTS
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INDOOR AIR SAMPLING RESULTS
• Sample results are provided in about 2 weeks • At a minimum two rounds of sampling are needed
per current Water Board sampling protocol guidance
Status of Access Agreements to date* Residential Indoor Air Sampling Summary to date - TCE • 300 Access Agreements sent • 28 Buildings sampled • 62 Access Agreements signed
– 13 Non-detect – 8 Below Environmental Screening Levels – 7 Above Environmental Screening Levels
and are being evaluated
Potential Mitigation Measures • Seal cracks and openings in foundation
• Mobile air treatment units (temporary)
• Adjust heating and ventilation system parameters
• Install mitigation system beneath foundation to safely vent vapors into the atmosphere
• Continue testing indoor air to confrm efectiveness of mitigation measures
Temporary mobile air treatment unit
* This information is current as of September 21, 2018
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INTERPRETING RESULTS/RESIDENTIAL
8 102/20/70: etaD Project 8618397107
NORTH AND BCA AREAS VI EVALUATION STRATEGY RESIDENTIAL PROPERTIES
Former Ford Aeronutronic Property Newport Beach, California
Notes (1) Amec Foster Wheeler, 2017. Revised Addenum to Work Plan for Groundwater Investigation – North Area, Former Ford Aeronutronic Property, Newport Beach, California (2) Source of soil vapor screening levels: February 2016 San Francisco Bay RWQCB ESLs of 240 (final screening level) and 1000 μg/m3 (“Trigger” level and noncancer ESL) for TCE. (3) Indoor air concentrations will be evaluated with respect to the following:
˜ Outdoor air concentrations ˜ Sub-slab and/or crawl space concentrations, if applicable ˜ Presence of preferential pathways indicating possible migration via sewer line ˜ Indoor air screening levels: 0.48 μg/m3 (long-term; U.S. EPA 2018 RSL and 2016 SFRWQCB ESL) and
2 and 6 μg/m3 [short-term; Accelerated and Urgent Response Action Levels, respectively; DTSC 2014 HHRA Note 5: Health-based Indoor Air Screening Criteria for Trichloroethylene (TCE)].
Abbreviations IA = indoor air SV = soil vapor μg/m3 = micrograms per cubic meter VI = vapor intrusion BCA = Big Canyon Arroyo
Deliver factsheets regarding upcoming SV sampling to
residences in the North and BCA Areas
Install and sample SV probes at proposed locations in the North
and BCA Areas(1)
Extent and proximity of delineation around individual homes will be performed on a
building-specific basis
Perform step-out SV sampling where SV concentrations are
>240 μg/m3
Prioritize IA sampling at residences within 30 days
TCE concentration
in IA, evaluated on a per-home basis(3)
Between 2 and 6 μg/m3
Between 0.48 and 2 μg/m3
Perform seasonal SV sampling to confirm
results; if results are
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REAL ESTATE
We are fully investigating the environmental issues and prioritizing health and safety. We have no information at this time on property values. We recommend contacting a real estate professional to obtain any further information regarding this or related issues.
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NEXT STEPS
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NEXT STEPS
Continue with subsurface soil gas investigation in common areas outside and indoor air investigation
Refne study areas based on results of subsurface soil gas investigation
Interim response measures as needed to address indoor air impacts
Develop long-term strategy for subsurface soil gas and/or groundwater
Community Outreach
Open houses to share key information
Fact sheets and results letters issued by mail and email
Website and project information line
CONTACT US
www.FordNBFacts.com 833-949-3673 [email protected]
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SIGN-UP FOR INDOOR AIR SAMPLING
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SANTA ANA REGIONAL WATER BOARD
AND OFFICE OF ENVIRONMENTAL
HEALTH HAZARD ASSESSMENT
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SANTA ANA REGIONAL WATER BOARD ROLE
• Santa Ana Regional Water Quality Control Board (SARWQCB) is one of nine Regional Boards which along with State Water Resources Control Board (SWRCB) are under the umbrella of California Environmental Protection Agency (CalEPA).
• SARWQCB is in charge of issuing permits and enforcing the State policies to protect water quality.
• SARWQCB has jurisdiction over the more populated areas of Orange, Riverside, and San Bernardino Counties (approximately 2,800 square miles), covering a population of approximately 5 million people.
• SARWQCB works with the responsible parties that caused environmental contamination to conduct assessment and remediation of the impacted sites.
• SARWQCB also coordinates and collaborates with public and other stakeholders who may have been afected by contamination.
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OFFICE OF ENVIRONMENTAL HEALTH HAZARD ASSESSMENT
• The Ofce of Environmental Health Hazard Assessment (OEHHA) is the lead state agency for the assessment of health risks posed by environmental contaminants and is one of six departments within the California Environmental Protection Agency (CalEPA).
• OEHHA’s mission is to protect human health and the environment through scientifc evaluation of risks posed by hazardous substances.
• OEHHA develops health-protective exposure levels for contaminants in air, water, and soil as guidance for regulatory agencies and the public.
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Commercial Indoor Air Decision Flow Chart
Date: 4/17/2018 Figure A2 Project 9615397106
NORTH AND BCA AREAS VI EVALUATION STRATEGY COMMERCIAL PROPERTIES
Former Ford Aeronutronic Property Newport Beach, California
Deliver factsheets regarding upcoming SV sampling to
businesses in the North and BCA Areas
Install and sample SV probes at proposed locations in the North
and BCA Areas(1)
Extent and proximity of delineation
around individual commercial buildings will be performed on a
building-specific basis
Perform step-out SV sampling where SV concentrations are
>240 µg/m3(3)
Prioritize IA sampling at commercial properties within 30
days
TCE concentration
in IA, evaluated on a per-building basis(4)
Between 8 and 24 µg/m3
Notes (1) Amec Foster Wheeler, 2017. Revised Addenum to Work Plan for Groundwater Investigation – North Area,
Former Ford Aeronutronic Property, Newport Beach, California (2) Source of soil vapor screening levels: February 2016 San Francisco Bay RWQCB ESLs of 3,000 (final
screening level) and 8,000 µg/m3 (“Trigger Level”) for TCE. (3) The Santa Ana Regional Water Quality Control Board recommended delineating to the residential value of 240
µg/m3 (instead of 3,000 µg/m3) because of mixed land use. (4) Indoor air concentrations will be evaluated with respect to the following:
• Outdoor air concentrations • Sub-slab and/or crawl space concentrations, if applicable • Presence of preferential pathways indicating possible migration via sewer line • Indoor air screening levels: 3 μg/m3 (long-term; U.S. EPA 2017 RSL and 2016 SFRWQCB ESL) and 8
and 24 μg/m3 [short-term; Accelerated and Urgent Response Action Levels, respectively; DTSC 2014 HHRA Note 5: Health-based Indoor Air Screening Criteria for Trichloroethylene (TCE)].
Between 3 and 8 µg/m3
Abbreviations IA = indoor air SV = soil vapor µg/m3 = micrograms per cubic meter VI = vapor intrusion BCA = Big Canyon Arroyo
Perform seasonal SV sampling to
confirm results; if results are 24 µg/m3
Between 3,000 and 8,000 µg/m3
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Residential Indoor Air Decision Flow Chart
Date: 4/17/2018 Figure A1 Project 9615397106
NORTH AND BCA AREAS VI EVALUATION STRATEGY RESIDENTIAL PROPERTIES
Former Ford Aeronutronic Property Newport Beach, California
Deliver factsheets regarding upcoming SV sampling to
residences in the North and BCA Areas
Install and sample SV probes at proposed locations in the North
and BCA Areas(1)
Extent and proximity of delineation around individual homes will be performed on a
building-specific basis
Perform step-out SV sampling where SV concentrations are
>240 µg/m3
Prioritize IA sampling at residences within 30 days
TCE concentration
in IA, evaluated on a per-home basis(3)
Between 2 and 6 µg/m3
Notes (1) Amec Foster Wheeler, 2017. Revised Addenum to Work Plan for Groundwater Investigation – North Area, Former Ford Aeronutronic Property, Newport Beach, California (2) Source of soil vapor screening levels: February 2016 San Francisco Bay RWQCB ESLs of 240 (final screening level) and 1000 μg/m3 (“Trigger” level and noncancer ESL) for TCE. (3) Indoor air concentrations will be evaluated with respect to the following:
• Outdoor air concentrations • Sub-slab and/or crawl space concentrations, if applicable • Presence of preferential pathways indicating possible migration via sewer line • Indoor air screening levels: 0.48 μg/m3 (long-term; U.S. EPA 2017 RSL and 2016 SFRWQCB ESL) and
2 and 6 μg/m3 [short-term; Accelerated and Urgent Response Action Levels, respectively; DTSC 2014 HHRA Note 5: Health-based Indoor Air Screening Criteria for Trichloroethylene (TCE)].
Between 0.48 and 2 µg/m3
Abbreviations IA = indoor air SV = soil vapor µg/m3 = micrograms per cubic meter VI = vapor intrusion BCA = Big Canyon Arroyo
Perform seasonal SV sampling to confirm
results; if results are
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TCE SCREENING LEVELS
Long-Term Exposure Screening Levels TCE Sub-slab/Soil
Gas Vapor Intrusion1 Indoor Air Direct Exposure1
Residential
Commercial
240 µg/m3
3,000 µg/m3
0.48 µg/m3
3 µg/m3
Short-Term Exposure Screening Levels TCE Sub-slab/Soil
Gas Vapor Intrusion1 Indoor Air Direct Exposure—Accelerated2
Indoor Air Direct Exposure—Urgent2
Residential
Commercial (8-hour workday)
Commercial (10-hour workday)
1,000 µg/m3
8,000 µg/m3
8,000 µg/m3
2 µg/m3
8 µg/m3
7 µg/m3
6 µg/m3
24 µg/m3
21 µg/m3
Sources:
1. San Francisco Bay Regional Water Quality Control Board, Environmental Screening Levels, Updated February 2016
2. United States Environmental Protection Agency, July 9, 2014, Memorandum, EPA Region 9 Response Action Levels and Recommendations to Address Near-Term Inhalation Exposures to TCE in Air from Subsurface Vapor Intrusion
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Structure BookmarksFord Aeronutronic provided major support for the development of Project Space Track (1957-1961) Mobile Laboratory Pre-Sampling Building Survey Indoor Sampling Canister Sub-Slab Install (eg. garage)