Title: UNDERGROUND STORAGE TANK
111th Annual California Unified Program Training
Conference
UST Removal Sampling and ReportingCourse M-F1
Time 800-1000amJanuary 26, 2009
Moderator Ben Wright State Water Resources
Control Board, UST Cleanup Program (916)
323-9690 bwright_at_waterboards.ca.gov
2California USTs
- Active USTs 37,300
- Confirmed Releases 42,900
- Confirmed Releases For 2008 260
- LUST/DOD Case Closures For 2008 870
-
- April 1, 2008 through September 30, 2008
www.epa.gov/oust/cat/camarchv.htm
3Goals
- Get Familiar With the Tank Removal Process at UST
Sites - Review the Requirements of One of the Regulatory
Agencies (Santa Fe Springs) - Suggest Some of the Important Information that
Can be Gained During UST Removal - Present Case Studies and Discuss Considerations
for Clean and Dirty Sites -
4Presenters
Brenda ten Bruggencate, Environmental Protection
Specialist Santa Fe Springs Department of
Fire-Rescue (562) 906-3812 brendanelson_at_santafesp
rings.org Kelly Brown, Principal
Geologist Stantec (562) 354-2638 kelly.brown_at_stant
ec.com
5UST REMOVAL SAMPLING AND REPORTING
- Presented by
- Brenda ten Bruggencate
- Santa Fe Springs Fire-Rescue
6PRESENTATIONOUTLINE
- Overview of permanent closure requirements
report requirements - 23 CCR Art. 7
- Brenda ten Bruggencate, Santa Fe Springs FD
- Sampling collection and analysis
- Kelly Brown, SECOR
- 23 CCR 2672 (d)
- Case Studies
- Clean dirty sites
7CLOSURE VS. REMOVAL
- careful with the term closure
- when
- removal
- is meant
8PERMANENT UST CLOSURE REQUIREMENTS
- 23 CCR Art. 7
- 23 CCR 2670 - General to all UST closures
- 23 CCR 2671 - Temporary closures
- 23 CCR 2672 - Permanent closure
- 23 CCR 2672 (d) - Sampling requirements
- 23 CCR Art. 4
- 23 CCR 2649 - Boring Requirements
- HSC 25298 - general
9PERMANENT UST CLOSURE REQUIREMENTS
- LG 48-5, Contractor Licensing
- A
- B
- C-36
- C-61/D-40
- Hazardous Substance Certification issued by CSLB
BP 7058.7
10PERMANENT UST CLOSURE REQUIREMENTS
- Two types
- Removal 23 CCR 2672(b)
- Closure-in-place 23 CCR 2672(c)
11PERMANENT UST CLOSURE REQUIREMENTS
- 23 CCR Art. 7
- Time between cessation of hazardous substance
storage and application for closure shall not
exceed 90 days - Closure shall be completed within a reasonable
amount of time as determined by LIA - SFS 6 months, with possible 6 month extension
12PERMANENT UST CLOSURE REQUIREMENTS
- 23 CCR 2670 requires
- UST owner or operator must submit to the LIA for
approval, a proposal for compliance with closure
requirements - At least 30 days prior to closure or shorter is
allowed by LIA
13PERMANENT UST CLOSURE REQUIREMENTS
- Variety of Processes for UST Closure Permits
(handouts) - Workplans, no written guidance
- One inspector issues removal permit, another
witnesses removal - Prescriptive forms
SFSFR
14PERMANENT UST CLOSURE REQUIREMENTS
- Owner/Operator requirements applicable to all
permanent UST closures - Handle residual contents removed as hazardous
wastes or recyclable materials - Inert possible flammables vapor at STP to levels
that preclude explosion - lower if required by agency
- SFSFR requires a clean certification
15PERMANENT UST CLOSURE REQUIREMENTS
- Document to LIA disposition of UST
- If disposed
- Documentation to LIA within their required time
frame - If destined for reuse
- Check with LIA for local requirements
- Document to LIA within their required time frame
- Name of new owner and new operator of UST
- Location of intended use
- Nature of intended use
16verify info on site
17UST CLOSURE-IN-PLACE
- What justifies leaving UST in place?
- Check with Building Dept. LIA policy
- SFSFD requires UST be within a 45 angle of
footing of permanent structure
18UST CLOSURE-IN-PLACE
BUILDING
UST 2
UST 1
45
- Closure-in-place allowed for UST 2
19UST CLOSURE-IN-PLACE
- UST shall be filled with an inert solid
- Except if owner intends to reuse tank for
storage of a non-haz substance - Non-haz substance must be compatible with
previous UST use and construction - Check with LIA and Fire Departments on their
requirements
20UST PIPING CLOSURE-IN-PLACE
- Remove all piping unless it will damage
structures or other pipes - Piping to remaining in place must be emptied of
contents and capped - Piping does not have to be filled with an inert
solid, only the UST does
21SOIL SAMPLING REQUIREMENTS
- Must demonstrate no unauthorized release has
occurred - Must be performed during or immediately after
UST closure activities - Based on soil and (if present in excavation)
water analysis - Analyze for previously stored substance(s) and
breakdown products or transformation products.
22SOIL SAMPLING REQUIREMENTS
- Must analyzed in a State-certified lab 23 CCR
2649(f)(6) - Lower detection limits must be verified by the
lab - Be aware of dilution
- Raises detection limits
- May miss low conc. contaminants
23SOIL SAMPLING REQUIREMENTS
- Geological logs shall be prepared by a
Professional Geologist or Civil Engineer - technician working under the direct supervision
of one can do this provide the professional
reviews the logs and assumes responsibility for
them. 23 CCR 2649 (b)(1)(D)
24SOIL SAMPLING LOCATIONS
- Removal
- Minimum 2 below the UST bottom in native soil at
each end of tank - SFSFD suggests 2 4, sometimes also 10 bgs
- Every 20 linear feet of piping
- May include vent and vapor for VPH systems based
on change in piping definition - This include sampling under the dispenser
- Stockpile sampling (not specified in 23 CCR 2672)
252
26SOIL SAMPLING REQUIREMENTS
- Closure-in-place
- One slant boring as close as possible to the
midpoint of the UST OR - Vertical borings drilled along each long
dimensional side of UST OR - Other method as approved by LIA
27MTBE testing required
25296.15
Confirm sample location analysis with PG on site
Typical sampling for 1-12K gas 1-12K diesel
28SOIL SAMPLING REQUIREMENTS
- Prescribed on SFSFD UST Closure Permit
- Subject to change based on field observations
- SFSFR witnesses all UST removals
- Contaminated dispenser excavation confirmation
sampling - Encourage businesses to do limited excavation
- If contamination fails to visually clear up in
several scoops, discontinue and initiate site
characterization
29REPORTING REQUIREMENTS
30REPORTING REQUIREMENTS
- 23 CCR Art. 5 Release Reporting
- Closure (Removal) Report
- URF
- Geotracker Entry
- Fee Title Holder Notification
- Public Participation
31LEAK DISCOVERYRELEASE REPORTING
- Recordable release
- Does not
- Escape secondary containment
- Increase fire or explosion hazard
- Deteriorate the secondary containment
- Cleaned up in lt 8 hours
- Reportable release
- Does
- Escape secondary containment
- Increase fire or explosion hazard
- Deteriorate the secondary containment
- Cleaned up time irrelevant
- Other
- HSC reqmts.
- Check w/ LIA
32REPORTING TIME FRAMES
- Recordable release
- Document on company records (23 CCR 2651)
- Reportable release
- Notify LIA within 24 hours
- Full report within 5 days to LIA (23 CCR
2652)
- Refer to Response Plan in LG 133-2
- URF contains most info for reportable releases
- LIAs may have their own Response Plans
33RESPONSE PLANShttp//www.waterboards.ca.gov/water
_issues/programs/ust/leak_prevention/lgs/docs/133_
2.pdf
34UNAUTHORIZED RELEASE FORMhttp//www.waterboards.c
a.gov/water_issues/programs/ust/forms/docs/unauth_
release.pdf
352670(f)
SFSFD requirement
2670(f)
piping dispensers
2672(b)(3) (4)
2649(f)(5) (g)
2672(c)(1)
Bus. Prof. Code 7835
Professional
2649(f)(5) (g)
2649(f)(6) HSC 25298.5
2649(f)(5) (g) HSC 25298.5
Needed to de-termine if further action is needed
2672(b)(2) (c)(2)
Bus. Prof. Code 7835
Professional
36GEOTRACKER REPORTING REQUIREMENTS
- The Electronic Reporting Regulations (Chapter 30,
Division 3 of Title 23 Division 3 of Title 27,
CCR) require electronic submission of any report
or data required by a regulatory agency from a
cleanup site. - http//www.waterboards.ca.gov/ust/cleanup/electron
ic_reporting/report_rqmts.html
37FEE TITLE HOLDER NOTIFICATION
- AB681, HSC 25296.20 25297.15
- Agency/Board cannot is NFA at a UST site that had
an unauthorized release unless all current record
owners of fee title to the site have been
notified of the proposed action by Agency/Board. - Agency/Board must accommodate responsible
landowner participation in the cleanup or site
closure process and shall consider all input and
recommendations from any responsible landowner
wishing to participate.
38PUBLIC PARTICIPATION
- Comply with public notification regulations
- 23 CCR 2728
- Publication in a regulatory agency meeting agenda
- Public notice posted in a regulatory agency
office - Public notice in a newspaper
- Block advertisements
- A public service announcements
- Letters to individual households
- Personal contacts with affected parties by
regulatory agency staff
39LEAKING USTREPORTING REQUIREMENTS
40SAMPLING ANALYSIS COLLECTION
41UST Removal and Sampling
Kelly C. Brown January 26, 2009
Photo Optional
42UST Removal Process
- Dispensers are removed
- Product is removed from the USTs
- Gasoline, waste oil, etc.
- Product/vent lines are cleaned and drained back
to USTs
43UST Removal Process
- Concrete caps and islands are removed
- UST and piping locations are excavated
- Piping removed (and sampled in some cases)
44UST Removal Process
- Removal of turbines from USTs
- UST freed and tilted for rinsing and cleaning
- Dry ice applied to USTs to inert them and to
displace vapors - USTs certified as clean by Marine Chemist
45UST Removal Process
46UST Removal Process
- USTs removed and transported for disposal
47Sample Collection
- Sampling is performed under the supervision and
direction of the lead agency - Permits usually dictate sampling requirements and
analyses - Collect soil samples at each dispenser location
(2 to 4 feet bgs) - Collect soil samples approximately every 20
linear feet of piping - Some agencies require samples at elbows and
Ts
48Sample Collection
- Collect soil samples beneath each end of USTs (15
to 18 feet bgs) - Collect soil sample beneath waste oil UST (8 to
10 feet bgs), and excavation sidewalls (if
requested) - Collect soil stockpile samples for disposal
purposes - If groundwater is encountered in UST excavations,
collect groundwater samples - Is product or a product sheen observed?
49Sample Collection Equipment
- Soil samples are collected at dispenser and
piping locationsusing hand auger, drive sampler
or backhoe bucket
Hand Auger
Drive Sampler
50Sample Collection
Soil samples in UST excavations are collected
using excavatorbucket due to excavation/confined
space issues
51Sample Collection
When groundwater is encountered in the UST
excavation, at least one groundwater sample
should be collected If product or a product
sheen is identified on groundwater, then try to
collect a product sample Groundwater samples are
usually collected using a new disposable Teflon
bailer lowered into the excavation water The
groundwater sample is then decanted into the
appropriate sample containers
52Soil Sample Containers
- Sample collection is based on agency directives
- Soil samples are collected in accordance agency
directives, or EPA 5035A (LARWQCB jurisdiction) - Sample containers for soil are either
- Encore type sampling devices
- Stainless steel rings
- 4 oz glass jars
- TerraCore sampler and 40 ml VOAs (1) with
sodium bi-sulfate and methanol preservatives
(2-3)
53Soil Sample Containers
54Groundwater Sample Containers
- Sample containers for groundwater are either
- 40 ml VOA with HCL preservative
- 500 ml plastic bottle with HNO3 preservative
- 1 L amber glass bottle, with no preservative
- 40 ml VOA with no preservative for product
samples
55Groundwater Sample Containers
56Sample Containers and Analytical Methods
- Soil Samples
- GRO/VOCs (EPA 8260B/8270C) Encore or
TerraCore type sample containers - GRO, DRO, ORO (EPA 8015M), TRPH/OG (EPA
418.1) Stainless steel rings or glass
jars - CAM 17 Metals (EPA 6010B/7470) - Stainless
steel rings or glass jars - Groundwater Samples
- GRO/VOCs 40 ml VOA, HCL preservative
- DRO/ORO/TRPH/OG 1 liter amber,
non-preserved - CAM 17 Metals 500 ml plastic, HNO3
preservative
57Sample Identification
58Common Sampling Errors
- Improper decontamination of equipment
- Sampling equipment
- PPE Nitrile/latex gloves
- Improper sample containers
- Not enough sample quantity for analysis
- Not enough sample containers for required
analysis - Mis-interpretation of agency sampling, COC,
and/or analytical requirements - Inexperienced regulator and/or field staff
- Missed analytical hold times
59CASE STUDIES
CLEAN DIRTY SITES
60CASE STUDY DIRTY SITE
- Former Sunco Equipment Company
- History of non compliance
- Failed tank integrity testing
- Did not upgrade in 1998
- No response to enforcement
- Steps to prosecute civilly initiated
61- Former Sunco Equipment Company
62- Former Sunco Equipment Company
63- Former Sunco Equipment Company
64CASE STUDY DIRTY SITE
- Former Sunco Equipment Company
- SFSFR applied to the EAR account and was granted
40,000 - Company went bankrupt
- Property was foreclosed
- Bank quickly sold to new RP
- Obtained closure permit and removed tank
65(No Transcript)
66- Clayey soil
- Pasty texture
- Limited excavation discontinued
67TPHg 400 mg/kg TPHd 3900 mg/kg High
Ethylbenzene, naphthalene, TMB ND Benzene
MTBE
68CASE STUDY DIRTY SITE
- SFSFR issues directive
- Corrective Actions Plans submitted, reviewed, and
approved - assessment and excavation
- lateral vertical extent of contamination
defined - RP excavated but incompletely
69(No Transcript)
70N
Extent of excavation
UST
B-1 (contaminated)
LEGEND
Samples collected in Round 2
Samples collected in Round 3
71TPHg 900-4000 mg/kg B 15 mg/kg TEX high
72CASE STUDY DIRTY SITE
- Remaining contamination in B-1 exceeds screening
levels - SFSFR requires additional remediation a
determination if groundwater is threatened - RP refuses additional excavation SFSFR
determines GW is threatened without additional
remedial action - Case is referred to RWQCB
- Current remediation plan with RWQCB is to HSA
excavate
73NFA LETTERS
- Uniform UST Closure Letter
- LIA/Board is responsible to issue a Closure in
accordance with HSC 25296.10 for site that have
undergone corrective action - Standardized verbiage
74CLEAN SITE
- Clean
- site where risks are low enough to close without
corrective action - Approach to screening varies among agencies
- Check with LIA up staff and your Regional Board
- SFSFR uses Superfund PRGs LARWQCB Closure
Criteria
75EXAMPLE
- UST removal
- All samples ND except one which has hits of 3
contaminants - Individual concentrations are below Superfund
PRGs - What about the cumulative risk?
76EXAMPLE
- Superfund PRGs contain guidance for screening at
sites with multiple contaminants - http//www.epa.gov/reg3hwmd/risk/human/rb-concentr
ation_table/usersguide.htm - Link to calculator
77EXAMPLE
- Separate the carcinogenic from non-carcinogenic
contaminants - Determine the screening level for each
contaminant - Screening levels are not clean up numbers
- But you can screen out to the point of closure
78SCREENING SITES WITH MULITPLE CONTAMINANTS
If cancer risk is lt1,000,000 you may screen out
that contaminant
If Hazard Index is lt1 you may screen out that
contaminant
79UST CLOSURE LETTER
- SFSFR issues a modified version of a closure to
site where no corrective action was required - Similar to HSC 25296.10 except were remove
references to citations regarding corrective and
replace them with - 23 CCR 2672
- HSC 25298
80SAFETY PLANNING
81TIPS FOR INSPECTORS
- Before arriving on site
- Review the approved permit
- Know sampling locations and analyses
82JOB SITE TIPS FOR INSPECTORS
- Upon arriving on site
- Scan for immediate hazards
- Discuss overall removal plan logistics with the
contractor - Who is the site safety officer?
- Confirm tank disposition and destination
- Review sampling requirements with geologist
- Document differences on permit vs. actual
83JOB SITE TIPS FOR ALL
- Stop and look
- Assess the staging of the area
- What are the hazards?
- Traffic Heavy equipment
- Electrical
- Crane size
- Lift strap/cable
- Tank pit
- Tank path
- Where is the transport truck located?
84CONTACT INFO
- Brenda ten Bruggencate
- Santa Fe Springs Fire Rescue
- (562) 906-3812
- brendanelson_at_santafesprings.org