No. 28517 (Amendment): R311-205-2. Site Assessment Protocol

DAR File No.: 28517
Filed: 02/15/2006, 10:48
Received by: NL

 

RULE ANALYSIS

Purpose of the rule or reason for the change:

All references to "recommended cleanup levels" were changed to "initial screening levels" as a minimum reporting limit for laboratories analyzing environmental samples taken under this rule. The reference to "recommended cleanup levels" was a policy that has never been in rule. The change to "initial screening levels" is to be more explanatory as a change in the standard which is reflected in Rule R311-211. (DAR NOTE: The proposed amendment to Rule R311-211 in under DAR No. 28519 in this issue.)

 

Summary of the rule or change:

This amendment changes references to "recommended cleanup levels" to "initial screening levels".

 

State statutory or constitutional authorization for this rule:

Sections 19-6-105, 19-6-403, and 19-6-413

 

Anticipated cost or savings to:

the state budget:

None--There is no financial impact anticipated for changing terminology used within the changes made to Rule R311-205. The notice of proposed rule amendment for Rule R311-211 details the anticipated financial impact of changing the standards.

 

local governments:

None--There is no financial impact anticipated for changing terminology used within the changes made to Rule R311-205. Laboratories are already expected to meet a minimum reporting standard and the standard has not changed significantly enough to impact laboratory costs.

 

other persons:

None--There is no financial impact anticipated for changing terminology used within the changes made to Rule R311-205. Laboratories are already expected to meet a minimum reporting standard and the standard has not changed significantly enough to impact laboratory costs.

 

Compliance costs for affected persons:

None--There is no financial impact anticipated for changing terminology used within the changes made to Rule R311-205. Laboratories are already expected to meet a minimum reporting standard and the standard has not changed significantly enough to impact laboratory costs.

 

Comments by the department head on the fiscal impact the rule may have on businesses:

There is no financial impact anticipated. The change in terminology reflects a change made elsewhere in the rule and does not significantly affect current procedures used by laboratories when they analyze samples from underground tank sites. Dianne R. Nielson, Executive Director

 

The full text of this rule may be inspected, during regular business hours, at the Division of Administrative Rules, or at:

Environmental Quality
Environmental Response and Remediation
168 N 1950 W
SALT LAKE CITY UT 84116-3085

 

Direct questions regarding this rule to:

Gary Astin at the above address, by phone at 801-536-4103, by FAX at 801-359-8853, or by Internet E-mail at [e-mail]

 

Interested persons may present their views on this rule by submitting written comments to the address above no later than 5:00 p.m. on:

03/31/2006

 

Interested persons may attend a public hearing regarding this rule:

3/28/2006 at 2:00 PM, Department of Environmental Quality, 168 N 1950 W, Room 201, Salt Lake City, UT

 

This rule may become effective on:

05/15/2006

 

Authorized by:

Dianne R. Nielson, Executive Director

 

 

RULE TEXT

R311. Environmental Quality, Environmental Response and Remediation.

R311-205. Underground Storage Tanks: Site Assessment Protocol.

R311-205-2. Site Assessment Protocol.

(a) General Requirements.

(1) When a site assessment or site check is required, pursuant to 40 CFR 280 or Subsection 19-6-428(3), owners or operators shall perform or commission to be performed a site assessment or a site check according to the protocol outlined in Rule R311-205 or equivalent, as approved by the Executive Secretary. Additional environmental samples must be collected when contamination is found, suspected, or as requested by the Executive Secretary.

(2) Groundwater samples shall be collected in accordance with the "EPA RCRA Ground-water Monitoring Technical Enforcement Guidance Document" (OSWER Directive 9950.1), 1986 or as determined by the Executive Secretary. Surface water samples shall be collected in accordance with protocol established in the "EPA Compendium of ERT Surface Water and Sediment Sampling Procedures" January 1991, or as determined by the Executive Secretary. Soil samples shall be collected in accordance with the "EPA Description and Sampling of Contaminated Soils, A Field Pocket Guide", November 1991 or as determined by the Executive Secretary.

(3) Owners and operators must document and report to the Executive Secretary sample types, sample locations and depths, field and sampling measurement methods, the nature of the stored substance, the type of backfill and native soil, the depth to groundwater, and other factors appropriate for identifying the source area and the degree and extent of subsurface soil and groundwater contamination.

(4) The owner or operator shall report the discovery of any release or suspected release to the Executive Secretary within twenty-four hours. Owners or operators shall begin release investigation and confirmation steps in accordance with 40 CFR 280, Subpart E upon suspecting a release. Owners or operators shall begin release response and corrective action in accordance with 40 CFR 280, Subpart F upon confirming a release.

(5) All environmental samples shall be collected by a certified groundwater and soil sampler who meets the requirements of Rule R311-201. The certified groundwater and soil sampler shall record the depth below grade and location of each sample collected to within one foot.

(6) All environmental samples shall be analyzed within the time frame allowed, in accordance with Table 4.1 of the "EPA RCRA Ground-water Monitoring Technical Enforcement Guidance Document" (OSWER Directive 9950.1), by a Utah Certified Environmental Laboratory approved by the Executive Secretary. Soil samples must be corrected for moisture, if necessary, with percent moisture reported to accurately represent the level of contamination.

(7) Environmental samples for UST permanent closure or change in service shall be collected according to the protocol outlined in Subsection R311-205-2(b), after the UST system is emptied and cleaned and after the closure plan has been approved.

(8) Environmental confirmation samples are required following overexcavation of soils. Confirmation samples shall be taken at locations and depths sufficient to detect the presence, extent and degree of a release from any portion of the UST in accordance with 40 CFR 280, Subparts E, F and G. Additional confirmation samples may be required as determined by the Executive Secretary.

(9) Upon confirming a release, a site assessment report, an updated site plat, analytical laboratory results, chain of custody forms, and all other applicable documentation required by 40 CFR 280, Subparts E and F, following any abatement, investigation or assessment, monitoring, remediation or corrective action activities, shall be submitted to the Executive Secretary within the specified time frames as outlined in compliance schedules.

(10) When conducting environmental sampling to satisfy the requirements of 40 CFR 280, subparts E and F, soil classification samples to determine native soil type shall be collected at locations and depths as outlined in compliance schedules, or as determined by the Executive Secretary. Techniques of the Unified Soil Classification such as a sieve analysis or laboratory classification, or a field description from a qualified individual as determined by the Executive Secretary, may be used to satisfy requirements of determining native soil type.

(11) Other types of environmental or quality assurance samples may be required as determined by the Executive Secretary.

(b) Site Assessment Protocol for UST Closure.

(1) The appropriate number of environmental samples, as described in Subsection R311-205-2(b)(4) shall be collected in native soils, below the backfill material, and as close as technically feasible to the tank, piping or dispenser island. Any other samples required by Subsection R311-205-2(a) must also be collected. Soil samples shall be collected from a depth of zero to two feet below the backfill and native soil interface. If groundwater is contacted in the process of collecting the soil samples, the soil samples required by Subsection R311-205-2(b)(4) shall be collected from the unsaturated zone immediately above the capillary fringe. Groundwater samples shall be collected using proper surface water collection techniques, from a properly installed groundwater monitoring well, or as determined by the Executive Secretary. All environmental samples shall be analyzed using the appropriate analytical methods outlined in Subsection R311-205-2(d).

(2) One soil classification sample to determine native soil type shall be collected at the same depth as indicated for environmental samples, at each tank and product piping area. For all dispenser islands, only one representative sample to determine native soil type is required. Techniques of the Unified Soil Classification such as a sieve analysis or laboratory classification shall be used to satisfy requirements of determining native soil type when taking samples for UST closure.

(3) For purposes of complying with Rule R311-205, for tanks or piping to be removed, closed in-place or that undergo a change in service, a tank or product piping area is considered to be an excavation zone or equivalent volume of material containing one, or more than one immediately adjacent, UST or piping run.

(4) Environmental Sampling Protocol for UST closures:

(A) For a tank area containing one UST, one soil sample shall be collected at each end of the tank. If groundwater is contacted during the process of collecting soil samples, a minimum of one groundwater and one soil sample shall be collected from each end of the tank.

(B) For a tank area containing more than one UST, one soil sample shall be collected from each corner of the tank area. If groundwater is contacted during the process of collecting soil samples, a minimum of one groundwater and one soil sample shall be collected from each end of the tank area.

(C) Product piping samples shall be collected from each product piping area, at locations where leaking is most likely to occur, such as joints, connections and fittings, at intervals which do not allow more than 50 linear feet of piping in a single piping area to go unsampled. If groundwater is contacted during the process of collecting soil samples, a minimum of one groundwater and one soil sample shall be collected from each piping area where groundwater was encountered.

(D) For dispenser islands, environmental samples shall be collected from the middle of each dispenser island. Additional environmental samples shall be collected at intervals which do not allow more than 25 linear feet of dispenser island piping to go unsampled. If groundwater is contacted during the process of collecting soil samples, a minimum of one groundwater and one soil sample shall be collected from each dispenser island where groundwater was encountered.

(c) Site Check Requirements for Re-applying to Participate in the Petroleum Storage Tank Trust Fund Program.

(1) Owners or operators wishing to re-apply for participation in the Petroleum Storage Tank Trust Fund Program following a period of lapse or non-participation shall perform a tank tightness test and site check pursuant to Subsection 19-6-428(3)(a). The tank tightness test and site check shall be consistent with requirements for testing and site assessment as defined under 40 CFR 280, Subparts D and E.

(2) The owner or operator shall develop or commission to have developed a site check plan outlining the intended sampling program. The Executive Secretary shall review and approve the site check plan prior to its implementation. The site check shall meet the sampling requirements for USTs, dispensers and piping as defined in Subsection R311-205-2(b), or as determined by the Executive Secretary on a site-specific basis. Additional sampling may be required by the Executive Secretary based on review of the proposed site check plan and site specific conditions.

(d) Laboratory Analyses of Environmental Samples.

(1) Environmental samples which have been collected to determine levels of contamination from underground storage tanks shall be analyzed using appropriate laboratory analytical methods as referenced in the "Analytical Methods for Environmental Sampling at Underground Storage Tank Sites in Utah (July 2004)", or as determined by the Executive Secretary.

(2) Environmental samples which have been collected to determine levels of contamination by gasoline shall be analyzed for total petroleum hydrocarbons (purgeable TPH as gasoline range organics C₆ - C₁₀),benzene, toluene, ethylbenzene, xylenes and naphthalene (BTEXN), and for methyl tertiary butyl ether (MTBE).

(3) Environmental samples which have been collected to determine levels of contamination by diesel fuel shall be analyzed for total petroleum hydrocarbons (extractable TPH as diesel range organics C₁₀ - C₂₈), benzene, toluene, ethylbenzene, xylenes and naphthalene (BTEXN).

(4) Environmental samples which have been collected to determine levels of contamination by used oil shall be analyzed for oil and grease (O and G) or total recoverable petroleum hydrocarbons (TRPH); and for benzene, toluene, ethylbenzene, xylenes, naphthalene (BTEXN); methyl tertiary butyl ether (MTBE); and halogenated volatile organic compounds (VOX).

(5) Environmental samples which have been collected to determine levels of contamination by new oil shall be analyzed for oil and grease (O and G) or total recoverable petroleum hydrocarbons (TRPH).

(6) Environmental samples which have been collected to determine levels of contamination from underground storage tanks which contain substances other than or in addition to petroleum shall be analyzed for appropriate constituents as determined by the Executive Secretary.

(7) Environmental samples which have been collected to determine levels of contamination for an unknown petroleum product type shall be analyzed for total petroleum hydrocarbons (purgeable TPH as gasoline range organics C₆ - C₁₀); total petroleum hydrocarbons (extractable TPH as diesel range organics C₁₀ - C₂₈); oil and grease (O and G) or total recoverable petroleum hydrocarbons (TRPH); benzene, toluene, ethylbenzene, xylenes and naphthalene (BTEXN) and methyl tertiary butyl ether (MTBE); and for halogenated volatile organic compounds (VOX).

(8) All original laboratory sample results must be returned to the certified groundwater and soil sampler or certified UST consultant to verify all chain of custody protocols, including holding times and analytical procedures, were properly followed. Environmental samples shall be collected and transported under chain of custody according to EPA methods as approved by the Executive Secretary.

(9) Reporting limits used by laboratories analyzing environmental samples taken under this rule shall be below [recommended cleanup levels]initial screening levels for the contaminated media under study. Environmental samples shall be analyzed with the least possible dilution to ensure reporting limits are below [recommended cleanup levels]initial screening levels to the extent possible. If more than one determinative analysis is performed on any given environmental sample, the final dilution factor used and the reporting limit must be reported by the laboratory. As an alternative to diluting environmental samples, the laboratory shall consider using appropriate analytical cleanup methods and describe which analytical cleanup methods were used to eliminate or minimize matrix interference. Any analytical cleanup method used must not eliminate the contaminant of concern or target analyte.

 

KEY: [hazardous substances, ]petroleum, underground storage tanks

Date of Enactment or Last Substantive Amendment: [September 9, 2004]2006

Notice of Continuation: March 6, 2002

Authorizing, and Implemented or Interpreted Law: 19-6-[2]105; 19-6-403; 19-6-413