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Site Mitigation 101
CUPA Conference February 4, 2015
Wednesday 8-9:45 AM
New (and not so new) corrective action agency employees
IndustryConsultants (Potential) Responsible Parties
Students
Target Audience
Charles Ice, PG, San Mateo County Environmental Health LOP, voluntary cleanup program,
Corrective Action UPA, and well permitting, also biotoxin sampling and groundwater sustainability
Jerry Wickham, PG, Alameda County Environmental Health LOP, voluntary cleanup program
Speakers
Regulatory authority Cleanup Process
Opening a case Typical field activities and documentation Financing Enforcement options Closing a case
Whether to Open or Close a Case Examples
Meeting Outline
Corrective Action Programs
Local Agencies/Districts
Voluntary Programsall other
contaminantsHealth and Safety Code
Section 101480
9 Regional Water Quality Control Boards
Petroleum releases from USTs onlyCode of Regulations, Title 23, Chapter
16, Article 11, Section 2720 defines Responsible Party (RP) as: Tank owner and operator (or last known operator) Business owner and operator Property owner at time of contaminant discovery
Can be named secondary RP if another RP will remain as primary and potential secondary RP had no direct involvement in discharge
Leaking Underground Storage Tanks (LUST)
Health & Safety Code 25296 – word for word language for Remedial Action Completion Certificate (i.e. closure letter), appeals process for closure request denial
Health & Safety Code 25299 – the UST Cleanup Fund, currently authorized until 2026 and a fee of 2 cents per gallon
Health and Safety Code Sections
Local Oversight Program started as pilot program by Resolution 88-23 Counties contracted directly with SWRCB Appeals process, RWQCB concurrence
Health & Safety Code 25297 – authorizes the SWRCB to implement the LOP, Responsible Party to identify and notify affected property owners, and requires reimbursement for reasonable cost
Local Oversight Program
CUPAs had to be certified in 1996 Local Implementing Agencies (LIAs)
AB1701 (2012) required certification to be an LOP, no more LIAs (or quasi-LIAs)
Certification requirements Professional Geologist (PG) or Engineer
(PE), requirements for minimum education and training for all staff
Agency Certification
2009-42 Immediately review all cases for closure and
post impediments for closure by 6/30/10 2009-81
Use decisional framework outlined in resolution 92-49 and previous closure orders
2012-16 Low Threat UST Petroleum Closure Policy (LTCP)
Improvement Resolutions
2012-62 Plan for Implementation of LTCP and Additional Program Improvements Review all sites against LTCP by 8/16/13,
create Path to Closure Plan by 1/1/14 SWRCB review of all closure denials 60-day TAT work plans and closure requests Emphasis on high threat cases Pushing for well destruction and waste
removal of pending closure cases
Improvement Resolutions
RWQCBs have 3,050 open, 13,308 closed Another 209 listed as Open - Inactive
17 local agencies with 1,767 open, 19,044 closed cases Another 4 listed as Open - Inactive
LUST Case numbers
RWQCBs Water Code Sections 13267, 13304, and 13365
Local agencies Health & Safety Code Section 101480, SB1248 (1996)
Responsible Party [can be anyone] that requests the local officer [county or city health officer or county environmental health director] to supervise remedial action at a site
Must enter into a Remedial Action Agreement specifying assessment, remediation, and cleanup goals
Voluntary Cleanup Program
Letter certifies completion of activities Charge RP a fee to recover reasonable
costs; no enforcement option Local agency sites
Must first notify DTSC and RWQCB of site Either party at any time may ask DTSC or
RWQCB to take over through agency referral or RP applies for Site Designation or Brownfield MOA processes
Voluntary Cleanup Program
RWQCBs have 3,050 open cases, 5,911 closed, 1,565 Listed as Open - Inactive
32 local agencies with 586 VCP open sites, 3,494 closed cases, 61 sites listed as Open - Inactive 14 agencies >4 sites each, total of 567
sites
Voluntary Cleanup Program
Mandated by statue in 1997 Regulations for designation (i.e. application) developed in 2006 Allows Health & Safety Code Chapter 6.5 Section 25187, 25200.3, 25200.10, 25407.14 orders at facilities subject to oversight by CUPA
Generators, Conditional Authorization, Conditional Exemption, and Permit by Rule (except TTUs) Less versus more complex sites for Tier 1 and 2 designations
Corrective Action UPA
Phase 1 Assessment Checklist (DTSC Form 1151 required be filled out by 1/1/97 identified many corrective action sites ) or 1 year after CA or PBR notification
Generators that can not obtain clean closure during facility closure and property or business transfers identify a majority of corrective action UPA sites
Delegation to UPAs only applies to Health & Safety Code Chapters 6.5
Corrective Action UPA Regulations
Los Angeles County, Ventura County, San Mateo County, Sacramento County, San Diego County, and Merced County currently designated
Orange County has appliedOnly 3 sites officially so far
Implementation
Cleanup process
Opening a case Funding Conceptual site model Site investigation Remedy selection Groundwater monitoring GeoTracker Public participation Enforcement options Case closure
LOP/UST Cleanup Process
UST Cleanup Fund for eligible sites Responsible party funds Less Common
Emergency, Abandoned, and Recalcitrant (EAR) Account
Orphan Site Cleanup Fund School District Account
LOPs operate under contract to State Water Resources Control Board
Funding
Definitions and various forms Description of sources, distribution,
pathways, and receptors.ProcessWhen is site investigation
adequate?
Conceptual Site Model
Example of CSM Pictorial
Example of CSM Flow Diagram
Worker
Resident
Recreational
Definitions and various forms Description of sources, distribution,
pathways, and receptors.ProcessWhen is site investigation
adequate?
Conceptual Site Model
Various approaches Fixed scope of work Flexible or expedited
Methods and technologiesWork plans and reporting
Site Investigation
When are groundwater monitoring wells installed?
What information do we get?How long do we monitor?
Groundwater Monitoring
Interim remedial actionsPilot testsCorrective action plans
Public participation Green and Environmentally
Responsible Cleanups
Remedy Selection
Opening a case Funding Conceptual site model Site investigation Remedy selection Groundwater monitoring GeoTracker Public participation Enforcement options Case closure
LOP/UST Cleanup Process
Make sure site is claimed and keep it up to date
Site history and case status Document and EDF submittals Low Threat Closure Policy checklist Path to closure plan Regulatory actions (activities) Post closure site management requirements Getting information out of GeoTracker
GeoTracker
Level of effort based on site Threshold level for all sites Adjust level of effort as needed
Categories Rural/urban
Activities “Public Participation at Cleanup Sites, Final
Draft,” April 2005, State Water Resources Control Board and Regional Boards
Public Participation
Progressively increase enforcement Meetings Notice of Violation District Attorney Regional Water Quality Control Boards State Water Resources Control Board
Enforcement Options
Opening a case Funding Conceptual site model Site investigation Remedy selection Groundwater monitoring GeoTracker Public participation Enforcement options Case closure
Voluntary Cleanup Program Process
Full and meaningful public involvement (CEQA) Site screening (Preliminary Endangerment Assessment) Site investigation (using DTSC guidance documents) Selection of remedy and cleanup levels Adequate resources & oversight Written documentation of corrective action
activities Enforcement of corrective action completeness Financial assurance Land use controls
Corrective Action Process
Most common ways of site discovery Tank removal and upgrade sampling or
release detected by UST monitoring equipment
Voluntary Phase 2 work requested by banks for property transactions, data voluntarily submitted or as required by drilling permit
CUPA facility closure sampling Public complaints, usually nuisance based
Opening a Case
Request any additional info anyone has to help determine if site should be opened and who might be responsible parties (RPs)
Identify RPs (assessor’s records and CUPA files for LUST) or potential RPs (current and perspective property owner and current or most recent facility in CUPA files for VCP), send them initial letter
Open site in Geotracker and have meeting with RPs or potential RPs to discuss why, what, and how, and request initial work plan
Steps for Opening A Case
Concentrations versus screening levels (ESLs by SFRWQCB or LARWQCB, RLs by USEPA Region 9)
Location of contamination in relation to sensitive receptors (current and imminent land use involved)
Fate and transport pathways initially assessed
Deciding Whether to Open a Case
Case opening Example
Voluntary Phase II work for redevelopment of a former electronics lab from the 1960s reportedly with electroplating
Grab groundwater 20 feet below ground surface in 5 borings but monitoring wells on other sites in the vicinity have 10 feet depth of groundwater
Analyzed soil and groundwater for TPH, SVOCs, and VOCs
Circuitron
Soil Data (ppb)
Groundwater Data (ppb)
Site Map
Max TCE in soil 0.055 mg/kg @ 20 ft bgs @ SB-8
Soil (SFRWQCB) ESL 0.46 mg/kg Max TCE in groundwater 870 ug/L
@ 25 ft bgs @ SB-6Groundwater (SFRWQCB) ESL 1,300
ug/L for vapor intrusion, 5 ug/L drinking water
Summary and Screening Information for Voting
SFRWQCB TCE Vapor Intrusion acute trigger level in fine soil (or deep groundwater) 460 ug/L
Development plans incorporate 2 levels of parking garages (~20 feet deep)
Any possible additional info they could get to stop agency from opening site?
Does This Change Your Vote?
Low Threat UST Closure Policy Resolution 92-49 Relevant State Water Board Orders Closure requests are tracked on GeoTracker Denials of closure reviewed by State Water
Resources Control Board
LOP/UST Case Closure
Eight General Criteria Three Media Specific Criteria
Groundwater – Four prescriptive classes of sites or regulatory agency determination
Vapor – Four scenarios, sit-specific risk assessment or regulatory agency determination
Direct Contact and Outdoor Air Exposure –Table 1, site-specific risk assessment, or regulatory agency determination
Low Threat UST Closure Policy
Provides a framework for the cleanup process. Establishes the basis for determining cleanup levels of waters
of the State and soils that impact waters of the State. Resolution No. 92-49 requires cleanup to occur in a manner
that promotes attainment of either background water quality or that level that is reasonable if background levels of water quality cannot be restored.
Resolution No. 92-49 does not require that the requisite level of water quality be met at the time of case closure; it specifies compliance with cleanup goals and objectives within a reasonable time frame.
Resolution 92-49
Case closure EXAMPLE
Urban site Active retail truck stop Gasoline and diesel Multiple releases from tank pit and piping
Time to Play “Would You Close That Site”
APARTMENTS
RESTAURANT AND PARKING LOTRESTAURANT AND PARKING LOT
RAILROADRAILROAD
Dispensers
BUILDING
TANK PIT
Truck Stop Site Plan
Depth to groundwater 2 to 6 feet bgs Groundwater not used in area of site for water
supply Free product removal until 2006; no free
product currently Overexcavation in tank pit area and scale (2,644
cy) In-situ Remediation but likely not effective
Example LOP/UST Site
APARTMENTS
RESTAURANT AND PARKING LOTRESTAURANT AND PARKING LOT
RAILROADRAILROAD
Dispensers
BUILDING
TANK PIT
TPHg In Groundwater
EW
East-West Cross Section TPHg In Soil
APARTMENTS
RESTAURANT AND PARKING LOTRESTAURANT AND PARKING LOT
RAILROADRAILROAD
Dispensers
BUILDING
TANK PIT
Benzene In Groundwater
500 µg/L
APARTMENTS
RESTAURANT AND PARKING LOTRESTAURANT AND PARKING LOT
RAILROADRAILROAD
Dispensers
BUILDING
TANK PIT
MTBE in Groundwater
500 µg/L
APARTMENTS
RESTAURANT AND PARKING LOTRESTAURANT AND PARKING LOT
RAILROADRAILROAD
Dispensers
BUILDING
TANK PIT
TBA in Groundwater
Within service area of a public water system
Consists only of petroleum Currently no free product Primary release has been stopped Conceptual site model was developed Secondary source removal Soil and groundwater tested for MTBE No nuisance conditions
General LTCP Criteria
Site DataLTCP
Class 1 Criteria (µg/L)
LTCP Class 2 Criteria (µg/L)
LTCPClass 3 Criteria (µg/L)
LTCP Class 4 Criteria (µg/L)
Plume LengthApproximately 200 feet from source to edge of
plume<100 feet <250 feet <250 feet <1,000 feet
Free Product Currently no free product
No free product
No free product
Removed to maximum
extent practicable
No free product
Plume Stable or Decreasing
Appears to be decreasing over long
term but sporadic increases observed.
Stable or decreasing
Stable or decreasing
Stable or decreasing
for minimum of 5 Years
Stable or decreasing
Distance to Nearest Water Supply Well >1,000 feet >250 feet >1,000
feet >1,000 feet >1,000 feet
Distance to Nearest Surface Water and Direction
2,000 feet downgradient >250 feet >1,000
feet >1,000 feet >1,000 feet
Property Owner Willing to Accept a Land Use Restriction?
Yes Not applicable
Not applicable Yes Not
applicable
Groundwater-Specific Criteria
Site DataLTCP Class
2 Criteria (µg/L)
LTCPClass 3
Criteria (µg/L)
LTCP Class 4 Criteria (µg/L)
Plume LengthApproximately 200 feet from source to edge of
plume<250 feet <250 feet <1,000 feet
Free Product Currently no free product No free product
Removed to maximum
extent practicable
No free product
Plume Stable or DecreasingAppears to be decreasing
over long term but sporadic increases
observed
Stable or decreasing
Stable or decreasing
for minimum of 5 Years
Stable or decreasing
Distance to Nearest Water Supply Well >1,000 feet >1,000 feet >1,000 feet >1,000 feet
Distance to Nearest Surface Water and Direction
2,000 feet downgradient >1,000 feet >1,000 feet >1,000 feet
Property Owner Willing to Accept a Land Use Restriction?
Yes Not applicable Yes Not
applicable
Groundwater-Specific Criteria
ConstituentHistoric Site Maximum
(µg/L)
Current SiteMaximum
(µg/L)
LTCP Class 2 Criteria (µg/L)
LTCP Class 3 Criteria (µg/L)
LTCP Class 4 Criteria (µg/L)
Benzene 77,000 740 3,000 No criteria 1,000
MTBE 920,000 530 1,000 No criteria 1,000
TBA 310,000 35,000 No criteria No criteria No criteria
Groundwater Concentrations
Not required for active service stations No threat to nearby sites
Vapor-Specific Criteria
Constituent
Residential Commercial/Industrial Utility Worker
0 to 5 feet bgs
(mg/kg)
Volatilization to outdoor air (5 to 10 feet bgs)
mg/kg
0 to 5 feet bgs
(mg/kg)
Volatilization to outdoor air (5 to
10 feet bgs) mg/kg
0 to 10 feet bgs(mg/kg)
Site Maximum Benzene 3.5 200 3.5 200 200
LTCP Criteria Benzene ≤1.9 ≤2.8 ≤8.2 ≤12 ≤14
Site Maximum Ethylbenzene 9.4 160 9.4 160 160
LTCP Criteria Ethylbenzene ≤21 ≤32 ≤89 ≤134 ≤314
Site Maximum Naphthalene ---- ---- ---- ---- ----
LTCP Criteria Naphthalene ≤9.7 ≤9.7 ≤45 ≤45 ≤219
Direct Contact and Volatilization to Outdoor Air
Maximum site concentrations less than Table 1 concentrations
Maximum concentrations less than levels from site-specific risk assessment
As a result of controlling exposure through use of mitigation measures or institutional or engineering controls, regulatory agency determines that petroleum constituents in soil will have no significant risk of adversely affecting human health
Three Ways to Meet Direct Contact and Volatilization to Outdoor Air
Criteria
Does it meet general criteria? Does it meet scenarios 2, 3, and 4 of
groundwater criteria? Exempt from vapor criteria Could site meet direct contact criteria
with land use controls?
Summary of LTCP Criteria for Voting
What about variations in groundwater concentrations?
What about TBA in groundwater at concentrations up to 35,000 µg/L?
TPH mass remaining (estimated 17,600 pounds) Shallow soil contamination with concentrations
that exceed LTCP Table 1 and no naphthalene data
Do Any of These Conditions Change Your
Vote?
QUESTIONS/DISCUSSION