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SU0003944 SSCRPT
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SU0003944 SSCRPT
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Last modified
5/7/2020 11:30:22 AM
Creation date
9/4/2019 10:18:08 AM
Metadata
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EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0003944
PE
2611
FACILITY_NAME
PA-0400228
STREET_NUMBER
7770
Direction
W
STREET_NAME
BATES
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
24809009
ENTERED_DATE
5/11/2004 12:00:00 AM
SITE_LOCATION
7770 W BATES RD
RECEIVED_DATE
5/10/2004 12:00:00 AM
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\B\BATES\7770\PA-0400228\SU0003944\SSC RPT.PDF
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EHD - Public
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EXTOXNET PIP - DDT Page 2 of 5 <br /> 200 mg/kg. Single administrations of low doses to developing 10-day old mice are reported to have caused <br /> subtle effects on their neurological development(73). DDT is slightly to practically non-toxic to test animals <br /> via the dermal route, with reported dermal LD50s of 2,500-3,000 mg/kg in female rats (79, 73), 1000 in <br /> guinea pigs (73) and 300 in rabbits (73). It is not readily absorbed through the skin unless it is in solution(73). <br /> It is thought that inhalation exposure to DDT will not result in significant absorption through the lung alveoli <br /> (tiny gas-exchange sacs) but rather that it is probably trapped in mucous secretions and swallowed by exposed <br /> individuals following the tracheo-bronchial clearance of secretions by the cilia (73). Acute effects likely in <br /> humans due to low to moderate exposure may include nausea, diarrhea, increased liver enzyme activity, <br /> irritation (of the eyes, nose or throat), disturbed gait, malaise and excitability; at higher doses, tremors and <br /> convulsions are possible (73, 76). While adults appear to tolerate moderate to high ingested doses of up to 280 <br /> mg/kg, a case of fatal poisoning was seen in a child who ingested one ounce of a 5% DDT:kerosene solution <br /> (73). <br /> . Chronic Toxicity: DDT has caused chronic effects on the nervous system, liver, kidneys,and immune <br /> systems in experimental animals (73, 74). Effects on the nervous system observed in test animals include: <br /> tremors in rats at doses of 16-32 mg/kg/day over.26 weeks; tremors in mice at doses of 6.5-13mg/kg/day over <br /> 80-140 weeks; changes in cellular chemistry in the central nervous system of monkeys at doses of 10 <br /> f mg/kg/day over 100 days, and loss of equilibrium in monkeys at doses of 50 mg/kg/day for up to 6 months <br /> I (73). The main effect on the liver seen in animal studies was localized liver damage. This effect was seen in <br /> rats given 3.75 mg/kg/day over 36 weeks, rats exposed to 5 mg/kg/day over 2 years and dogs at doses of 80 <br /> mg/kg/day over the course of 39 months (73). In many cases lower doses produced subtle changes in liver cell <br /> physiology, and in some cases higher doses produced more severe effects (73). In mice doses of 8.33 <br /> mg/kg/day over 28 days caused increased liver weight and increased liver enzyme activity (73). Liver <br /> enzymes are commonly involved in detoxification of foreign compounds, so it is unclear whether increased <br /> liver enzyme activity in itself would constitute an adverse effect. In some species (monkeys and hamsters), <br /> doses as high as 8-20 mg/kg/day caused no observed adverse effects over exposure periods as long as 3.5-7 <br /> y years (73). Kidney effects observed in animal studies include adrenal gland hemorrhage in dogs at doses of <br /> 138.5 mg/kg/day over 10 days and adrenal gland damage at 50 mg/kg day over 150 days in dogs (73). Kidney <br /> damage was also seen in rats at doses of 10 mg/kg/day over 27 months (73). Immunological effects observed <br /> in test animals include: reduced antibody formation in mice following administration of 13 mg/kg/day for 3- <br /> 12 weeks and reduced levels of immune cells in rats at doses of 1 mg/kg/day (73). No immune system effects <br /> were observed in mice at doses of 6.5 mg/kg/day for 3-12 weeks (73). Dose levels at which effects were <br /> observed in test animals are very much higher than those which may be typically encountered by humans (74). <br /> The most significant source of exposure to individuals in the United States is occupational, occurring only to <br /> those who work or worked in the production or formulation of DDT products for export (75). Analysis of U. <br /> S' market basket surveys showed approximately a 30-fold decrease in detected levels of DDT and metabolites <br /> in foodstuffs from 1969-1974, and another threefold drop from 1975-1981, with a final estimated daily dose <br /> ' of approximately 0.002 mg/person/day (73). Based on a standard 70-kg person, this results in a daily intake of <br /> approximately 0.00003 mg/kg/day. Due to the persistence of DDT and its metabolites in the environment, <br /> very low levels may continue to be detected in foodstuffs grown in some areas of prior use (73). It has been <br /> suggested that, depending on patterns of international DDT use and trade, it is possible that dietary exposure <br /> levels may actually increase over time (73). Persons eating fish contaminated with DDT or metabolites may <br /> also be exposed via bioaccumulation of the compound in fish(73). Even though current dietary levels are <br /> quite low, past and current exposures may result in measurable body burdens due to its persistence in the body <br /> (73). More information on the metabolism and storage of DDT and its metabolites in mammalian systems is <br /> provided below (Fate in Humans and Animals). Adverse effects on the liver, kidney and immune system due <br /> to DDT exposure have not been demonstrated in humans in any of the studies which have been conducted to <br /> date (73). <br /> . Reproductive Effects; There is evidence that DDT causes reproductive effects in test animals. No <br /> reproductive effects were observed in rats at doses of 38 mg/kg/day administered at days 15-19 of gestation <br /> (73). In another study in rats, oral doses of 7.5 mg/kg/day for 36 weeks resulted in sterility (73). In rabbits, <br /> doses of 1 mg/kg/day administered on gestation days 4-7 resulted in decreased fetal weights and 10 mg/kg/day <br /> on days 7-9 of gestation resulted in increased resorptions (73). In mice, doses of 1.67 mg/kg/day resulted in <br /> decreased embryo implantation and irregularities in the estrus cycle over 28 weeks (73). It is thought that <br /> { many of these observed effects may be the result of disruptions in the endocrine (hormonal) system (73). <br /> Available epidemiological evidence from two studies does not indicate that reproductive effects have occurred <br /> in humans as a result of DDT exposure (73). No associations between maternal blood levels of DDT and <br /> miscarriage nor premature rupture of fetal membranes were observed in two separate studies (73, 77, 78). One <br /> study did report a significant association between maternal DDT blood levels and miscarriage, but the <br /> presence of other organochlorine chemicals (e.g., PCBs) in maternal blood which may have accounted for the <br /> 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 />
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