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SU0006490_SSCRPT
Environmental Health - Public
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120 (STATE ROUTE 120)
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2600 - Land Use Program
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PA-0700108
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SU0006490_SSCRPT
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Last modified
11/19/2024 3:59:59 PM
Creation date
9/8/2019 12:32:06 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0006490
PE
2622
FACILITY_NAME
PA-0700108
STREET_NUMBER
10800
Direction
E
STREET_NAME
STATE ROUTE 120
City
MANTECA
APN
22803024
ENTERED_DATE
3/27/2007 12:00:00 AM
SITE_LOCATION
10800 E HWY 120
RECEIVED_DATE
3/27/2007 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\O\HWY 120\10800\PA-0700108\SU0006490\SSC RPT.PDF
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EHD - Public
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EXTOXNET PIP -DDT Page 3 of 6 <br /> study in rats, oral doses of 7.5 mg/kg/day for 36 weeks resulted in sterility(73). In rabbits, doses of 1 mg/kg/day <br /> administered on gestation days 4-7 resulted in decreased fetal weights and 10 mg/kg/day on days 7-9 of gestation <br /> resulted in increased resorptions (73). In mice, doses of 1.67 mg/kg/day resulted in decreased embryo implantation <br /> and irregularities in the estrus cycle over 28 weeks (73). It is thought that many of these observed effects may be the <br /> result of disruptions in the endocrine (hormonal) system (73). Available epidemiological evidence from two studies <br /> does not indicate that reproductive effects have occurred in humans as a result of DDT exposure(73). No <br /> associations between maternal blood levels of DDT and miscarriage nor premature rupture of fetal membranes were <br /> observed in two separate studies (73, 77, 78). One study did report a significant association between maternal DDT <br /> blood levels and miscarriage,but the presence of other organochlorine chemicals (e.g., PCBs) in maternal blood <br /> which may have accounted for the effect make it impossible to attribute the effect to DDT and its metabolites (79). <br /> • Teratogenic Effects: There is evidence that DDT causes teratogenic effects in test animals as well. In mice, <br /> maternal doses of 26 mg/kg/day DDT from gestation through lactation resulted in impaired learning performance in <br /> maze tests (73). In a two-generational study of rats, 10 mg/kg/day resulted in abnormal tail development(73). <br /> Epidemiological evidence regarding the occurance of teratogenic effects as a result of DDT exposure are <br /> unavailable(73). It seems unlikely that teratogenic effects will occur in humans due to DDT at likely exposure <br /> levels. <br /> • Mutagenic Effects: The evidence for mutagenicity and genotoxicity is contradictory. In only 1 out of 11 <br /> mutagenicity assays in various cell cultures and organisms did DDT show positive results (73). Results of in vitro <br /> and in vivo genotoxocity assays for chromosomal aberrations indicated that DDT was genotoxic in 8 out of 12 <br /> cases, and weakly genotoxic in 1 case (73). In humans, blood cell cultures of men occupationally exposed to DDT <br /> showed an increase in chromosomal damage. In a separate study, significant increases in chromosomal damage <br /> were reported in workers who had direct and indirect occupational exposure to DDT(73). Thus it appears that DDT <br /> may have the potential to cause genotoxic effects in humans, but does not appear to be strongly mutagenic. It is <br /> unclear whether these effects may occur at exposure levels likely to be encountered by most people. <br /> • Carcinogenic Effects: The evidence regarding the carcinogenicity of DDT is equivocal. It has been shown to cause <br /> increased tumor production (mainly in the liver and lung) in test animals such as rats, mice and hamsters in some <br /> studies but not in others (73) In rats, liver tumors were induced in three separate studies at doses of 12.5 mg/kg/day <br /> over periods of 78 weeks to life, and thyroid tumors were induced at doses of 85 mg/kg/day over 78 weeks (73). In <br /> mice, lifetime doses of 0.4 mg/kg/day resulted in lung tumors in the second generation and leukemia in the third <br /> generation; liver tumors were induced at oral doses of 0.26 mg/kg/day in two separate studies over several <br /> generations. In hamsters, significant increases in adrenal gland tumors were seen at doses of 83 mg/kg/day in <br /> females (but not males) , and in males (but not females) at doses of 40 mg/kg/day(73). In other studies, however, <br /> no carcinogenic activity was observed in rats at doses less than 25 mg/kg/day; no carcinogenic activity was seen in <br /> mice with at doses of 3-23 mg/kg/day over an unspecified period, and in other hamster studies there have been no <br /> indications of carcinogenic effects (73). The available epidemiological evidence regarding DDTOs carcinogenicity <br /> in humans,when taken as a whole, does not suggest that DDT and its metabolites are carcinogenic in humans at <br /> likely dose levels (73). In several epimiological studies, no significant associations were seen between DDT <br /> exposure and disease, but in one other study, a weak association was observed (73, 80). In this latter study, which <br /> found a significant association between long-term, high DDT exposures and pancreatic cancers in chemical <br /> workers, there were questions raised as to the reliability of the medical records of a large proportion of the cancer <br /> cases (73,80). <br /> • Organ Toxicity: Acute human exposure data and animal studies reveal that DDT can affect the nervous system, <br /> liver, kidney(73). Increased tumor production in the liver and lung has been observed in test animals(73). An <br /> association with pancreatic cancer was suggested in humans in one study(73, 80). <br /> • Fate in Humans & Animals: DDT is very slowly transformed in animal systems (74). Initial degradates in <br /> mammalian systems are 1,1-dichloro-2,2-bis(p-dichlorodiphenyl)ethylene (DDE) and 1,1-dichloro-2,2-bis(p- <br /> chlorophenyl)ethane (DDD), which are very readily stored in fatty tissues (73). These compounds in turn are <br /> ultimately transformed into bis(dichlorodiphenyl) acetic acid (DDA) via other metabolites at a very slow rate (73). <br /> DDA, or conjugates of DDA, are readily excreted via the urine (73). Available data from analysis of human blood <br /> and fat tissue samples collected in the early 1970s showed detectable levels in all samples,but a downward trend in <br /> the levels over time (73). Later study of blood samples collected in the latter half of the 1970s showed that blood <br /> http://extoxnet.orst.edu/pips/ddt.htm 3/7/2007 <br />
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