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ARCHIVED REPORTS XR0008945
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0503634
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ARCHIVED REPORTS XR0008945
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Last modified
5/7/2019 4:56:18 PM
Creation date
5/7/2019 4:28:51 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008945
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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White et al (2003) reported EPA data showing a half-life of about 22 minutes at pH=1 <br /> and 80°C, and about 154 minutes at pH=2 and 80°C Within the limits of the data, this <br /> roughly represents an order of magnitude difference in rate with a difference of one pH <br /> unit <br /> These data indicate that under conditions of pH near 2 and temperature near 80°C, <br /> hydrolysis of MTBE in samples is possible These conditions will not occur in the <br /> subsurface, nor during sample storage As noted (White et al , 2003), some analytical <br /> procedures may include a step of heating an acid-treated sample to about 80°C for <br /> between 3 to 30 minutes, depending upon the specific method If the sample is at pH=1, <br /> this could potentially be a cause for concern <br /> Given this review, it is apparent that hydrolysis can occur in storage and heating of <br /> aqueous MtBE samples under low pH conditions and high temperature Additional <br /> testing with field and controlled samples would be required to establish a range of <br /> measured hydrolysis data with a sufficient accuracy to predict MtBE hydrolysis under a <br /> broad range of arbitrary conditions Within the scope of this project, however, we have <br /> instead focused directly on examining and testing the range of conditions and analytical <br /> methods commonly used for analysis of groundwater samples <br /> 7.9. Potential Conversion of MtBE to TBA Under Storage <br /> Conditions: <br /> Studies done to date indicate that there is no significant contribution to formation of TBA <br /> from hydrolysis of MtBE under normal sample preservation and storage conditions (pH <br /> <2 and 4°C) A recent study performed by Shell indicates no conversion of MtBE to TBA <br /> during the time of the study (14 days) A modest conversion of MTBE to TBA (-0 4%) <br /> was observed when the sample was kept below pH I The study was done with an MtBE <br /> concentration of 20,000 mg/L <br /> It must be emphasized that samples are acidified in the field directly by having the acid <br /> already placed in the laboratory provided Volatile Organic Analysis (VOA) vials, or by <br /> adding the acid in the field Typically, 4 drops of 1 1 hydrochloric acid water are added <br /> for this purpose The pH achieved by this acid addition is in the range of 1 5 to 2 It is our <br /> experience that to reach a pH level less than 1, more than twice the number of drops <br /> would be required It is unlikely that the pH would be near 1 in groundwater samples <br /> preserved using this method <br /> 7.2. Potential Conversion of MtBE to TBA During Analysis <br /> Because alcohols such as TBA are not readily stripped (or volatilized) from water, it is <br /> common for laboratories to heat samples to improve detection sensitivity This raises the <br /> concern for potential hydrolysis of ethers such as MtBE while heating under acidic <br /> conditions It is expected that MtBE can hydrolyze and form TBA at low pH and high <br /> temperature Because of this conversion possibility and the observance of TBA in <br /> groundwater, there has been a great deal of speculation and interest in this issue <br /> 20 <br />
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