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PR0503634
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/7/2019 4:40:56 PM
Creation date
5/7/2019 4:15:53 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0503634
PE
2950
FACILITY_ID
FA0005914
FACILITY_NAME
VICTOR ROAD SHELL
STREET_NUMBER
880
STREET_NAME
VICTOR
STREET_TYPE
RD
City
LODI
Zip
95240
APN
04905032
CURRENT_STATUS
02
SITE_LOCATION
880 VICTOR RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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OctobeT2002 • LUSTLine Bidlefin42 <br /> spohn t"Hach # 907-00 or equivalent). anywhere in the United States, it is ical method for fuel oxygenates (and <br /> In the field,each vial is filled with the also important to respond promptly other contaminants of concern)when <br /> groundwater sample and sealed to any petroleum release.The sooner the analyses will be used to(1)char- <br /> without headspace (the same as is all of the contaminants in a plume are acterize the three-dimensional extent <br /> done if the sample is preserved with identified and their subsurface extent of a contaminant plume, (2) deter- <br /> acid). determined, the sooner a remedy can mine whether a site requires active <br /> The salt is added to excess. If a be selected and implemented. remediation, (3)select an active rem- <br /> portion of the salt is washed out of Because a contaminant plume is edy, (4) design an active remedy, (5) <br /> the vial as the vial is filled with sam- smaller and more easily managed determine whether a site has met <br /> ple, enough TSP will remain to pre- early on,the magnitude of the impact site-specific cleanup objectives, or(6) <br /> serve the sample. As the salt and the overall cost of the cleanup determine if it is no longer necessary <br /> dissolves, it buffers the sample to a should be less than if the plume is to continue monitoring a site. <br /> pH greater than 11. allowed to expand. After all of the oxygenates (and <br /> No special handling of the sam- other contaminants of concern)pre- <br /> ples is required prior to analysis, The protocol described in this artiC sent at a site have been identified and <br /> although they should be stored in a their concentration and extent deter- <br /> refrigerator at 4° C. Water samples enables us to determine the mined,future analyses might then be <br /> preserved with TSP are 1 percent presence and concentration of all o conducted using a less expensive <br /> salt by weight. If purge-and-trap the common oxygenates and BTEX 8 determinative method (e.g., 8015). <br /> (Method 5030)is used to prepare the Situations that might not require con- <br /> water samples, it is particularly levels of regulatory interest. Rout firmatory analysis would include <br /> important to prevent the transfer of use of this protocol will greatly routine long-term performance moni- <br /> aerosols from the purged water to the improve the quality of the data tha toring as part of a MNA remedy or <br /> trap and GC column.This should be are Sported, which in turn will exposure management strategy. <br /> no different than current good labo- To properly implement this pro- <br /> ratory practice. enable us to make better decision tocol, groundwater samples should <br /> It is prudent to check the pH of which will ultimately result in mar, be collected from locations where <br /> the sample with indicator paper to effective utilization ofawl' oxygenates are most likely to occur, <br /> ensure that the pH is greater than 11 based on their chemical and physical <br /> prior to introducing it into the purge esou behavior. Because oxygenates are <br /> vessel or the headspace sampler for more soluble than petroleum hydro- <br /> analysis.IE it is necessary to analyze Consequently, it is prudent to carbons and can be more recalcitrant, <br /> samples that have already been pre- analyze samples for the entire suite of oxygenate plumes may be longer <br /> served with acid, the acid can be than typical BTEX plumes. <br /> oxygenates as identified in this proto- <br /> destroyed with TSP prior to analysis. Oxygenate plumes may also <br /> An amount of TSP sufficient to raise TAEcol (i.e., MTBE,TAME, ETRE, mIPE, "dive" beneath conventional moni- <br /> the pH of the sample to greater than should be TAA, and TBA). Samples toring wells and migrate undetected <br /> 11 is added to the sample vial, which shoulprepared for analysis, until a drinking water source is <br /> preferably using EPA Method 5030 <br /> is quickly resealed without head- heated to 80impacted. (See Weaver and Wilson's <br /> ° C (although either <br /> space and shaken gently to dissolve article in LUSTLine #36.) To ensure <br /> used if the lab <br /> the salt. Generally,about 0.7 gram of Method 5021 aMethod 5032 maybe that such plumes aren't migrating <br /> TSP is sufficient for a 40 mL VOA laboratory can demon- undetected, samples should be col- <br /> vial,but sometimes(depending upon strate appropriate performance with lected from a series of discrete sam- <br /> these methods). <br /> the of the sample) more must be The determinative method (e.g., opoints that draw in <br /> addeded groundwater <br /> to elevate the pH to greater Method 8260, 8015, or other appro- groundwater only over short vertical <br /> than 11. priate method)should be calibrated intervals.There should a sufficient <br /> for the entire suite of oxygenates,and number of sampling points cover <br /> Recommended Protocol these analytes should be reported for the entire vertical distancece over <br /> The protocol described in this article every sample analyzed. With the which an oxygenate plume may <br /> enables us to determine the presence understanding that ethanol and migrate. Generally this means that <br /> and concentration of all of the com- methanol are potentially present at additional sampling points are <br /> mon oxygenates and BTEX at levels fuel release sites, it is also advisable required at progressively greater <br /> of regulatory interest.Routine use of to have samples analyzed for these depths below the water table as the <br /> o distance from the <br /> this protocol will greatlyurove the alcohol oxygenates usingappropriate source increases. <br /> Increasing the <br /> quality of the data that are reported, preparative and determinative meth- length of monitoring well screens is <br /> which in turn will enable us to make ods. not appropriate as this will only <br /> better decisions, which will ulti- EPA Method 8260 (or another dilute the concentration of contami- <br /> mately result in more effective uti- method that provides confirmatory nants in the sample and mask the <br /> lization of available resources. identification of all of the fuel oxy- true concentration in the plume. <br /> Because MTBE (and potentially genates and can be demonstrated to To prevent constituents in the <br /> any other oxygenate)may be present meet project data quality objectives) samples from being biodegraded <br /> at any petroleum UST site, whether is the preferred determinative analyt- <br /> the release is new or old, virtually ■continued on page 8 <br /> 7 <br />
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