master 2018 vapor forum presentation -...
TRANSCRIPT
When Vapor Intrusion Strikes –Staying Ahead of the Plume
Minnesota Brownfields Educational Forum
March 7, 2018
Welcome to the Vapor Intrusion Forum
Martha Faust – Minnesota BrownfieldsWalt Donnay – Home Safety Solutions
Membership – Renew or Join Today
March is membership renewal month
Discounts on event registrations
Access to members-only events, networking, and tours
Read more about member benefits at mnbrownfields.org
Contact Angela Tangen at atangen@mnbrownfields or 612-710-0160
New in 2018: Brownfields Bootcamp
6-part series covering brownfield redevelopment from start to finish
Knowledge and networking for new professionals and allied fields
Monthly sessions beginning in September 2018:
Brownfield Redevelopment Primer
Site Investigations
Response Action Plans & Materials Management
Risk & Exposure
Financing
Getting the Deal Done
REGION 5 PERSPECTIVE ON VI:WHAT ARE OTHER STATES DOING?
Alyssa Sellwood, P.E.Vapor Intrusion Team Leader
Wisconsin Department of Natural ResourcesRemediation and Redevelopment
101 S. Webster Street, Madison, WI 53707Alyssa.Sel [email protected] | 608.266.3084
Minnesota Brownfields Vapor Intrusion Forum March 7, 2018
Region 5 States We talk to each other Common goal and challenges Many similarities
Vapor Intrusion in Wisconsin’s One cleanup program New VI Guidance Pathway to Closure
MESSAGE
Formed Jan 2016 Quarterly calls Environmental
Regulators Dept. of Health
Purpose Understand framework Discuss challenges Share solutions & policy
REGION 5 VI WORKGROUP
Access IssuesVI Assessments Sampling Approaches TCE Risk Risk Communication
REGION 5VI WORKGROUP TOPICS
Preemptive Mitigation Parking GaragesO&M and StewardshipAudits More….
People Access Risk Communication
Mitigation Performance verification Passive Parking Garages
Tracking properties Long-term care
REGION 5COMMON CHALLENGES
State Yes? Additional Information
Illinois Owner must agree to restrictive covenant
Michigan Uncertainty with effectiveness
Minnesota Performance verification required
Ohio Uncertainty with effectiveness
Wisconsin If a new building, test after construction
REGION 5SIMILARITIES AND DIFFERENCES
Is preemptive mitigation allowed?
State Criteria
Indiana 1 to 3 rounds(Depends on results and if worst case conditions)
Michigan 4 Quarterly Samples(More required for TCE)
Minnesota 2 seasonsOhio 2 seasonsWisconsin 2 to 3 rounds
REGION 5SIMILARITIES AND DIFFERENCES
How much sampling needed?
StateSub-slab
Data ResultSub-slab + Indoor Air
Soil Gas + J&E Model
Illinois
Indiana*
Minnesota
Ohio
Wisconsin
REGION 5SIMILARITIES AND DIFFERENCES
What data determines mitigation?
* Has a matrix for range of conditions. Remedy or indefinite monitoring required if high sub-slab with clean indoor air.
REGION 5SIMILARITIES AND DIFFERENCES
Are parking garages allowed as mitigation?
Yes, but questions remain Does ventilation pull in subslab vapor? What is optimal exchange rate for VI? Is intermittent operation ok? How to verify performance?
State Yes?Typical Requirements for
Sub-slab Depressurization Systems
Illinois Pressure field extension (PFE)
Indiana PFE and indoor air
Michigan PFE (indoor air sometimes)
Minnesota PFE and indoor air
Ohio PFE and indoor air
Wisconsin PFE (indoor air sometimes)
REGION 5SIMILARITIES AND DIFFERENCES
Is performance verification important for mitigation?
REGION 5SIMILARITIES AND DIFFERENCES
Who is responsible for O&M of mitigation?
Most states = responsible partyMichigan DEQ does all orphan sites (a lot!)Wisconsin Responsible party until closure Property owner after closure
WI PERSPECTIVEREMEDIATION & REDEVELOPMENT
One cleanup program: Hazardous cleanup USTs Spill response State-funded cleanups Brownfields
dnr.wi.gov/topic/Brownfields/
Revised January 2018 Good Table of Contents Covers all parts of VI
assessments
WI PERSPECTIVEVAPOR INTRUSION GUIDANCE
dnr.wi.gov/topic/Brownfields/Vapor.html/
Addressing Vapor Intrusion at Remediation & Redevelopment Sites in Wisconsin (RR-800)
Can VI be screened out with existing data?
WI PERSPECTIVESCREENING
Chlorinated VOC Screening Criteria
Can vapor investigation be completed now?
Sub-slab is best Building present? Access?
Soil gas has value High confirms risk Low, may not rule out VI
Indoor air informative How urgent of response Is pathway complete today
WI PERSPECTIVESAMPLING
Is site-specific attenuation factor an option?
Allowed in non-residential Radon tracer test Reduces over-engineering Maintain building conditions Maintain land use No additional controls
WI PERSPECTIVESAMPLING
Continuous Radon Monitor
Is remediation of vapor source an option?
Is mitigation needed to address VI potential?
WI PERSPECTIVEVI MITIGATION & REMEDIATION
If new buildings, sample subslab after construction
Take advantage of opportunity during redevelopment
Is performance verification complete?
Is a Maintenance Plan in place?
WI PERSPECTIVELONG-TERM O&M
Have all property owners been notified?
Continuing Obligations
O&M of mitigation or Land use restriction Any affected property Owners are responsible
Tracked in databaseAudited randomly
RR Sites Map
WI PERSPECTIVECLOSURE OF SITES
dnr.wi.gov/topic/Brownfields/wrrd.html
Common Goal = Protection of human healthVI science applied similarly Some differences b/c of regulatory frameworkWI allows closure of sites with VI, but… No preemptive mitigation Rigorous performance verification Planning ahead with property owners Maintenance Plan Formal notification
TAKE HOME MESSAGES
MPCA Vapor Intrusion Updates & Clarifications
1. Sub-slab Sampling Methodology Video
2. Partial building investigation/mitigation
3. BMP clarifications
32
Sub-slab Sampling Methodology Video
Appendix B – Sampling Methodology https://www.pca.state.mn.us/waste/cleanup-guidance#vapor-intrusion-best-management-practices
State Contract labs providing tubing and valve set-ups for sub-slab testing.
33
Sub-slab Sampling Methodology Video
Important components of sub-slab sampling include:
1. Leak testing the sample point (e.g. water dam method)
2. “Shut-In” test – confirming that the sample train connections don’t leak
3. Purging the sample train and sample point without disconnecting the sample train connections
34
Partial Building Investigation/Mitigation
October 2017 - Investigation/Mitigation Decision BMP updated with Partial Building Investigation (PBI) and Partial Building Mitigation (PBM) pp 10-11
• Updates based on stakeholder feedback regarding overall approach to evaluating & mitigating larger buildings
• Includes larger residential buildings (multi-unit residential, schools) and commercial / industrial buildings
35
Partial Building Investigation/Mitigation
Partial Building Investigation (PBI) Approach:
• Larger buildings - start with 30,000 ft2 for VI investigation = 8 sub-slabs
• PBI should focus on area of building near VI Area of Concern (AOC) or recognized environmental conditions (RECs)
• May need to expand VI investigation if VI AOC > 30,000 ft2
• Despite building size, ALL VOC vapor sources and RECs must be investigated for VI
• Evaluate and investigate any preferential pathways from VI AOC areas36
Partial Building Investigation/Mitigation
Partial Building Mitigation (PBM) Approach:
• Determine area of building needing mitigation based on sub-slab data from PBI
• All areas where sub-slab exceeds 33XISVs (VI AOC) require mitigation
• Mitigation area may be smaller than 30,000 ft2
• Mitigation may commence after initial round of sub-slab testing; however, 2nd seasonal round to define mitigation (VI AOC) boundary is still necessary
37
BMP Clarifications
Most common VI hotline questions are about:
1. Seasonal sampling
2. Vapor investigation/mitigation approach
3. Brownfield assurances/requirements
38
BMP Clarification – Seasonal Sampling
Seasonal Sampling – Are You Sure?
Temporal variability in vapor sampling with a seasonal component due to:• Groundwater table fluctuations• Soil moisture content – precipitation (or lack of)• Frost capping• Barometric pressure/wind speed
Not following seasonal sampling would result in:• Destabilization of VI decisions across all programs including Brownfields
• Liability assurances would be compromised as they would not be based on sufficient data
• MN being out of sync with EPA and other States (i.e. Region 5)39
BMP Clarification – Seasonal Sampling
Are the Seasonal Dates Firm?YES!!!
Non-heating season = April 1 – October 31Heating season = November 1 – March 31
WHY???“Seasonal” is not just outside temperature or snow/frost conditions.
It is not practical to monitor all of the sub-surface variables that may affect temporal variability and come up with a “worst-case scenario” for sampling.
40
BMP Clarification – Seasonal Sampling
Does seasonal sampling apply to sub-slab and soil-gas? YES
What if the first round is non-detect? YES - 2nd seasonal round to confirm
What if the first round is >33X ISVs? NO – VI AOC is identified or mitigation
What about post mitigation verification testing?
If heating season and passing – then NO, if non-heating – then YES41
BMP Clarification – VI Investigation
What question are we trying to answer?
1. Is a VI AOC present?
• defining the boundaries of a VI AOC
2. Does this building need mitigation?
• is the building even within a VI AOC?
42
BMP Clarification – VI Investigation
Why are these questions important?
Knowing the question will assist with:
• How many samples you need
• What type of samples to collect (soil-gas and/or sub-slab)
• Where to collect the samples
• What assurance(s) you may need
43
BMP Clarification – VI Investigation
When do I use Appendix C?
When trying to determine if mitigation is necessary for a building that is within a VI AOC as determined by:
• shallow impacted groundwater below the building• soil-gas >33XISV w/in 100ft. of building
If I’m collecting a sub-slab within a building, do I automatically use Appx C?• No – not if evaluating a REC within the building (i.e. flame waste trap)• No – not if trying to define a VI AOC with sub-slab data (i.e. new building or lack of
space on site for soil-gas)45
VI BMP Path Forward & Stakeholder Input
46
Residential Mitigation
BMP March 2015
Investigation Mitigation Long Term O&M
Investigation and Mitigation
Decision BMP October 2017
(updated)
Commercial/ Industrial
Mitigation BMP
IN PROGRESS
Long term O&M and Future Property
Owner Notification (2019)
We Are
Here
Commercial / Industrial Mitigation BMP
Stakeholder Advisory Group • MN Brownfields
• Environmental Consultants
• Banking/Lenders
• Grant Funders
• Legal
• Real Estate – Any volunteers?47
Commercial / Industrial Mitigation BMP
First BMP Stakeholder Meeting is scheduled: Mid April, 2018
Public BMP development website posted yesterday featuring:
• Stakeholder group members
• Meeting agendas and discussion items
• Regular meeting notes & updates
• Draft work productshttps://www.pca.state.mn.us/waste/development-commercialindustrial-vapor-intrusion-mitigation-bmps
48
Commercial / Industrial Mitigation BMP
Stakeholder input improves BMP development by providing:
• Technical expertise
• Multiple perspectives
• Your needs and concerns as a program user
49
Commercial / Industrial Mitigation BMP
Issues and questions for stakeholder advisory group• Passive Mitigation
• Vapor Barriers
• HVAC for Mitigation
• Indoor Air Filtration
• Underground Parking
• Mitigation Systems vs. Remediation Systems
• Required Verification Testing
51
Commercial / Industrial Mitigation BMP
52
How can you contribute to the BMP process?
1. Contact the MPCA Vapor Specialist Team (VST)
• Email: [email protected]
• Phone: (651) 757-2040
2. Contact any Stakeholder Advisory Group Member https://www.pca.state.mn.us/waste/development-commercialindustrial-vapor-intrusion-mitigation-bmps
No Association Determination Letter
Minn. Stat. 115B.178 – Commissioner May issue determination to Requests that proposed actions will not associate Requestor with Identified Releases of Hazardous Substances
Soil gas only investigations are generally not sufficient. Soil and/or Groundwater sampling also needed, or justify not necessary.
i.e. within known PLP listed vapor plume site.
One sampling event is enough data to document an Identified Release and get a NAD
Minn. Stat. 115B.177 – Off-Site Source Determination is not limited to Groundwater Releases
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Conditions of NAD Letter
Minn. Stat. 115B.178 – Commissioner’s Determination may be subject to Reasonable terms and conditions
Conduct and report 2nd seasonal sampling event
Resolve potential vapor risks for building(s) on the property
Define the vapor impacts on property
Record appropriate institutional control
55
Two “New” Vapor Assurance Letters
Completion of vapor mitigation response actions for on-site
buildings
Issued for a specific building(s)
Non-Responsible Parties only
Must have met terms/conditions of NAD
56
Two “New” Vapor Assurance Letters
Completion of vapor assessment
Determination that building(s) mitigation is not necessary
Non-Responsible Parties only
Must have met terms/conditions of NAD
57
Two “New” Vapor Assurance Letters
No changes in requirements for No Action/No Further Action letters
Apply under Technical Assistance on Voluntary Remediation application
portal
Outline request in cover/proposed actions letter
Phase One needed?
Brownfields Program Services Document
58
Intrusion Screening Values - ISVs
Bonnie Brooks | Research Scientist
Minnesota Brownfields - March 7, 2018
Protecting and improving the environment and enhancing human health.
ISV TSD and spreadsheet
62
• Intrusion Screening Value Technical Support Document (ISV TSD)
• Derivation of ISVs
• Concepts to consider when using ISVs
• Audience – risk assessors, toxicologist
• Does NOT replace program specific guidance
• ISV Spreadsheet• ISVs applicable to Minnesota
• Replaces 2009 ISV spreadsheet
• Replaces 2017 Interim ISV Short Guidance
• NO changes to interim ISVs, only 2009 ISVs
• NO changes to interim ISV methodology or exposure parameters
• Toxicity values may change
ISV TSD – What ISVs evaluate
63
• Chronic (long-term) risks from vapor intrusion
• Exposure route
• Inhalation
• 2 sets associated with a type of building
• Residential ISVs
• Commercial/Industrial ISVs
ISV TSD – How ISVs are derived
64
EPA Superfund Methodology
Cancer ISV = 10 μg/m3
Chronic noncancer ISV = 32 μg/m3
Final ISV = 10 μg/m3 based on cancer impacts
Exposure Parameters• Residential• Commercial/
Industrial
Toxicity Values• Cancer• Noncancer
ISV TSD - Expedited ISVs (EISVs)
65
• Expedited ISVs (EISVs)• Higher value than ISVs
• Represent increased exposure
• Example – Residential ISVs
ISV Type Cancer Risk Noncancer Risk
ISV1E-05
1 in 100,000 excess cancer cases1
EISV 1E-04
1 in 10,000 excess cancer cases3
ISV and EISV cancer and noncancer risk
ISV – Intrusion Screening ValueEISV – Expedited Intrusion Screening Value
ChemicalISV
µg/m3
EISVµg/m3
Benzene 4.6 46
Xylene 100 310
ISV TSD – 33X ISV & 33X EISV
66
• EPA’s default vapor intrusion attenuation factor
• 33X is familiar terminology - NOT how it is calculated
•33X ISV =
•33X EISV =
ISV TSD - Why TCE is treated differently(Trichloroethylene)
67
• ISVs evaluate chronic (long-term) exposure
• TCE + pregnant woman or woman that could become pregnant
• Shorter than chronic risks
• Acute (24 hr.) & short-term (30 days)
• Cardiac malformations to fetus
• Occurring in a shorter timeframe than long-term chronic risks
• Need to be evaluated in a shorter timeframe
ISV spreadsheet summary
68
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
ISV spreadsheet summary
69
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
ISV spreadsheet summary
70
• Worksheets
• Overview
• Toxicity data
• BUC equations -Residential
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
ISV spreadsheet summary
71
• Worksheets
• Overview
• Toxicity data
• BUC equations –Commercial/Industrial
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
ISV spreadsheet summary
72
• Worksheets
• Overview
• Toxicity data
• BUC equations -Residential
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
ISV spreadsheet summary
73
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations -Residential
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
ISV spreadsheet summary
74
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
25 samples
ISV spreadsheet summary
75
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
• Cell remains blue with concentration in black font • Concentration = or < 33X ISV
• Cell turns orange with concentration in brown, bolded font• Concentration > 33X ISV
• Cell turns red with concentration in red, bolded font• Concentration > 33X EISV and 33X ISV
ISV spreadsheet summary
76
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
25 samples
ISV spreadsheet summary
77
• Worksheets
• Overview
• Toxicity data
• BUC equations
• BUC calculations
• BUC sub-slab & soil gas worksheet
• BUC indoor air worksheet
BUC – Building use category
• Cell remains blue with concentration in black font • Concentration = or < ISV
• Cell turns orange with concentration in brown, bolded font• Concentration > ISV
• Cell turns red with concentration in red, bolded font• Concentration > EISV and ISV