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REMOVAL_2014 REMOVAL
EnvironmentalHealth
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26 (STATE ROUTE 26)
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2300 - Underground Storage Tank Program
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PR0539625
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REMOVAL_2014 REMOVAL
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Last modified
11/20/2024 8:48:39 AM
Creation date
11/8/2018 9:54:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
REMOVAL
FileName_PostFix
2014 REMOVAL
RECORD_ID
PR0539625
PE
2361
FACILITY_ID
FA0022676
FACILITY_NAME
CALTRANS
STREET_NUMBER
19107
Direction
E
STREET_NAME
STATE ROUTE 26
City
LINDEN
Zip
95236
CURRENT_STATUS
02
SITE_LOCATION
19107 E HWY 26
QC Status
Approved
Supplemental fields
FilePath
\MIGRATIONS3\T\HWY 26\19107\PR0539625\2014 REMOVAL.PDF
QuestysFileName
2014 REMOVAL
QuestysRecordDate
7/14/2017 3:08:20 PM
QuestysRecordID
3506712
QuestysRecordType
12
QuestysStateID
1
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EHD - Public
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S9800-01-34-ATTACHMENT C T8 CCR§1532 Cadmium-Appendix A <br /> evaluated as alternative causes(Friberg,Ex.29).Also,there are other factors that can cause 62-M <br /> to degrade so that low levels would result in workers with tubular dysfunction.For example, <br /> regarding the degradation of Lie-M,workers with acidic urine(pH<6)might have Lie-M levels <br /> that are within the "normal"range when in fact kidney dysfunction has occurred(Ex. L-140-1) <br /> and the low molecular weight proteins are degraded in acid urine.Thus, it is very important that <br /> the pH of urine be measured,that urine samples be buffered as necessary(See Appendix F.),and <br /> that urine samples be handled correctly,i.e.,measure the pH of freshly voided urine samples,then <br /> if necessary,buffer to pH>6(or above for shipping purposes),measure pH again and then, <br /> perhaps,freeze the sample for storage and shipping.(See also Appendix F.) Second,there is <br /> debate over the pathological significance of proteinuria,however,most world experts believe that <br /> 132-M levels greater than 300 µg/g Cr are abnormal(Elinder,Ex. 55,Friberg,Ex. 29). Such levels <br /> signify kidney dysfunction that constitutes material impairment of health.Finally,detection of 132- <br /> M at low levels has often been considered difficult,however,many laboratories have the <br /> capability of detecting excess 82-M using simple kits,such as the Phadebas Delphia test,that are <br /> accurate to levels of 100µg l3rM/g Cr U(Ex. L-140-1). <br /> Specific recommendations for ways to measure Lie-M and proper handling of urine samples to <br /> prevent degradation of 02-M have been addressed by OSHA in Appendix F,in the section on <br /> laboratory standardization.All biological samples must be analyzed in a laboratory that is <br /> proficient in the analysis of that particular analyte,under paragraph(1)(1)(iv). [See Appendix F]. <br /> Specifically,under paragraph(1)(1)(iv),the employer is to assure that the collecting and handling <br /> of biological samples of cadmium in urine(CdU),cadmium in blood(CdB),and beta-2 <br /> microglobulin in urine 032-M)taken from employees is collected in a manner that assures <br /> reliability. The employer must also assure that analysis of biological samples of cadmium in urine <br /> (CdU),cadmium in blood(CdB),and beta-2 microglobulin in urine(132-M)taken from employees <br /> L is performed in laboratories with demonstrated proficiency for that particular analyte. (See <br /> Appendix F.) <br /> 3. Lung and Prostrate Cancer <br /> L, The primary sites for cadmium-associated cancer appear to be the lung and the prostate(L-140- <br /> 50).Evidence for an association between cancer and cadmium exposure derives from both <br /> epidemiological studies and animal experiments.Mortality from prostrate cancer associated with <br /> cadmium is slightly elevated in several industrial cohorts,but the number of cases is small and <br /> ` there is not clear dose-response relationship.More substantive evidence exists for lung cancer. <br /> The major epidemiological study of lung cancer was conducted by Thum et al.,(Ex. 4-68). <br /> ` Adequate data on cadmium exposures were available to allow evaluation of dose-response <br /> relationships between cadmium exposure and lung cancer.A statistically significant excess of <br /> lung cancer attributed to cadmium exposure was observed in this study even when confounding <br /> variables such as co-exposure to arsenic and smoking habits were taken into consideration(Ex. L- <br /> 140-50). <br /> The primary evidence for quantifying a link between lung cancer and cadmium exposure from <br /> animal studies derives from two rat bioassay studies;one by Takenaka et al.,(1983),which is a <br /> ` study of cadmium chloride and a second study by Oldiges and Glaser(1990)of four cadmium <br /> compounds. <br /> ` Based on the above cited studies,the U.S. Environmental Protection Agency(EPA)classified <br /> cadmium as"B1",a probable human carcinogen, in 1985 (Ex.4-4). The International Agency for <br /> Research on Cancer(IARC)in 1987 also recommended that cadmium be listed as "2A", a <br /> Lprobable human carcinogen(Ex.4- 15). The American Conference of Governmental Industrial <br /> Hygienists(ACGIH)has recently recommended that cadmium be labeled as a carcinogen. Since <br /> 1984,NIOSH has concluded that cadmium is possibly a human carcinogen and has recommended <br /> that exposures be controlled to the lowest level feasible. <br /> L Linden UST Si and Remova4 Task Order No.34 Caltrans Contract 06A1895,EFIS 30-1300-0181-0 <br /> Geocon Project No.S9800-01-34 Page C-5 of 6 September 2014 <br /> L <br />
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