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UNDERGROUND STORAGE TANK

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Title: UNDERGROUND STORAGE TANK


1
11th 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
2
California 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
3
Goals
  • 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

4
Presenters
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
5
UST REMOVAL SAMPLING AND REPORTING
  • Presented by
  • Brenda ten Bruggencate
  • Santa Fe Springs Fire-Rescue

6
PRESENTATIONOUTLINE
  • 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

7
CLOSURE VS. REMOVAL
  • careful with the term closure
  • when
  • removal
  • is meant

8
PERMANENT 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

9
PERMANENT 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

10
PERMANENT UST CLOSURE REQUIREMENTS
  • Two types
  • Removal 23 CCR 2672(b)
  • Closure-in-place 23 CCR 2672(c)

11
PERMANENT 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

12
PERMANENT 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

13
PERMANENT 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
14
PERMANENT 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

15
PERMANENT 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

16
verify info on site
17
UST 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

18
UST CLOSURE-IN-PLACE
BUILDING
UST 2
UST 1
45
  • Closure-in-place allowed for UST 2

19
UST 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

20
UST 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

21
SOIL 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.

22
SOIL 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

23
SOIL 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)

24
SOIL 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)

25
2
26
SOIL 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

27
MTBE testing required
25296.15
Confirm sample location analysis with PG on site
Typical sampling for 1-12K gas 1-12K diesel
28
SOIL 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

29
REPORTING REQUIREMENTS
30
REPORTING REQUIREMENTS
  • 23 CCR Art. 5 Release Reporting
  • Closure (Removal) Report
  • URF
  • Geotracker Entry
  • Fee Title Holder Notification
  • Public Participation

31
LEAK 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

32
REPORTING 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

33
RESPONSE PLANShttp//www.waterboards.ca.gov/water
_issues/programs/ust/leak_prevention/lgs/docs/133_
2.pdf
34
UNAUTHORIZED RELEASE FORMhttp//www.waterboards.c
a.gov/water_issues/programs/ust/forms/docs/unauth_
release.pdf
35
2670(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
36
GEOTRACKER 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

37
FEE 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.

38
PUBLIC 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

39
LEAKING USTREPORTING REQUIREMENTS
40
SAMPLING ANALYSIS COLLECTION
41
UST Removal and Sampling
Kelly C. Brown January 26, 2009
Photo Optional
42
UST 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

43
UST Removal Process
  • Concrete caps and islands are removed
  • UST and piping locations are excavated
  • Piping removed (and sampled in some cases)

44
UST 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

45
UST Removal Process
46
UST Removal Process
  • USTs removed and transported for disposal

47
Sample 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

48
Sample 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?

49
Sample Collection Equipment
  • Soil samples are collected at dispenser and
    piping locationsusing hand auger, drive sampler
    or backhoe bucket

Hand Auger
Drive Sampler
50
Sample Collection
Soil samples in UST excavations are collected
using excavatorbucket due to excavation/confined
space issues
51
Sample 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
52
Soil 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)

53
Soil Sample Containers
54
Groundwater 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

55
Groundwater Sample Containers
56
Sample 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

57
Sample Identification
58
Common 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

59
CASE STUDIES
CLEAN DIRTY SITES
60
CASE 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

64
CASE 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

67
TPHg 400 mg/kg TPHd 3900 mg/kg High
Ethylbenzene, naphthalene, TMB ND Benzene
MTBE
68
CASE 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)
70
N
Extent of excavation
UST
B-1 (contaminated)
LEGEND
Samples collected in Round 2
Samples collected in Round 3
71
TPHg 900-4000 mg/kg B 15 mg/kg TEX high
72
CASE 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

73
NFA 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

74
CLEAN 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

75
EXAMPLE
  • UST removal
  • All samples ND except one which has hits of 3
    contaminants
  • Individual concentrations are below Superfund
    PRGs
  • What about the cumulative risk?

76
EXAMPLE
  • 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

77
EXAMPLE
  • 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

78
SCREENING 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
79
UST 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

80
SAFETY PLANNING
81
TIPS FOR INSPECTORS
  • Before arriving on site
  • Review the approved permit
  • Know sampling locations and analyses

82
JOB 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

83
JOB 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?

84
CONTACT INFO
  • Brenda ten Bruggencate
  • Santa Fe Springs Fire Rescue
  • (562) 906-3812
  • brendanelson_at_santafesprings.org
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