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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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Template:
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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,XT PIP - DIFLUBENZURON Page 2 of 3 <br /> _n three-generation study on rats at low doses showed no effect on mating performance. It does not appear that <br /> diflubenzuron has a significant effect on reproduction [16,28]. <br /> . Teratogenic effects: Diflubenzuron does not appear to be teratogenic. Newborn rats and rabbits did not <br /> develop any birth defects after their mothers were exposed to low levels of diflubenzuron (1 to 4 mg/kg/day) <br /> on days 6 to 18 of gestation [16,28]. <br /> . Mutagenic effects: Extensive testing on mamalian cells and on bacterial cells shows that diflubenzuron is not <br /> mutagenic [16,28]. <br /> e Carcinogenic effects: Rats fed diets containing low to moderate amounts of diflubenzuron daily for 2 years <br /> had no increase in the number of new or abnormal tissue growths or lesions. Mice fed low doses for 80 weeks <br /> showed no significant tumor development. Other studies on both species at higher levels were also negative <br /> for malignant tumors [16]. Diflubenzuron does not appear to be carcinogenic. <br /> . Organ toxicity: Animal studies have shown the liver and spleen to be target organs. <br /> . Fate in humans and animals: Intestinal absorption in mammals decreases with increasing dose levels [28]. <br /> For example, in rats , the total excretion in urine and bile decreased from about 50% of the dose at 4 mg/kg to <br /> only 4%at 900 mg/kg. Mice showed similar results. A cow given 10 mg/kg orally, eliminated almost all of <br /> the product over a 4-day period. There were only minute amounts of the pesticide in the milk. The chemical is <br /> not degraded in the digestive tract, but that which is absorbed by the gut is completely broken down before <br /> excretion [16]. Rabbits' skin absorbed only very small amounts, all of which was recovered in the urine. <br /> Chickens excreted almost all of an oral dose in 13 days. Their eggs had low levels of pesticide residues (0.3 to <br /> 0.6 mg/kg) from day 9 to the end of the 9-week study. Body tissues (non-fatty) do not retain diflubenzuron <br /> [16]. <br /> Ecological Effects: <br /> . Effects on birds: Diflubenzuron is practically nontoxic to wild birds. Bobwhite quail and mallard ducks both <br /> have an 8-day dietary LC50 of greater than 4640 ppm [4,7,8]. <br /> . Effects on aquatic organisms: Diflubenzuron is practically nontoxic to fish and aquatic invertebrates. The <br /> LC50 values (96-hour) for diflubenzuron in various fish are: bluegill sunfish, 660 mg/L; rainbow trout, 2.40 <br /> mg/L'; saltwater minnow, 255 mg/L; and channel catfish, 180 mg/L. In oyster larvae and juveniles EC50 <br /> values were 130 and 250 mg/L, respectively [4,7,8]. Arthropods are most susceptible in the premolting stage. <br /> For instance, fiddler crabs, exposed for as little as I week at levels up to 0.05'mg/L exhibited limb <br /> regeneration effects [29]. Fish tissue can show some traces of the metabolites when water is contaminated <br /> with diflubenzuron; however, tissue concentrations decline steadily with time in clean water. <br /> . Effects on other organisms: The compound is nontoxic to bees [4]. <br /> Environimental Fate:: <br /> . Breakdown in soil and groundwateri Diflubenzuron has a low persistence in soil. The rate of degradation in <br /> soil is strongly dependent on the particle size of the diflubenzuron [12]. It is rapidly degraded by microbial <br /> processes. The half-life in soil is 3 to 4 days [19]. Under field conditions, diflubenzuron has very low mobility <br /> [8,19]. <br /> . Breakdown in water:.dn sterilized water(no microbes), there appears to be little degradation under neutral or <br /> acidic conditions. However, under field conditions, it is degraded rapidly. Residues could not be detected in <br /> field water 72 hours after an application of 110 g/hectare. Other studies suggest a half-life of 1 to 3 weeks <br /> [4,7,8]• <br /> . Breakdown in vegetation: Very little diflubenzuron is absorbed, metabolized, or translocated in plants. <br /> Residues on crops such as apples have a half-life of 5 to 10 weeks. The half-life in oak leaf litter is 6 to 9 <br /> months [4,7.,8]. <br /> Physical Properties: <br /> . Appearance: Diflubenzuron is a white crystalline solid [7]. <br /> . Chemical Name: 1-(4-chlorophenyl)-3-(2,6-difluorobenzoyl)urea [7] <br /> . CAS Number: 35367-38-5 <br /> . Molecular Weight: 310.70 <br /> . Water Solubility: 0.14 mg/L @ 20 C, insoluble [7] <br /> . Solubility in Other Solvents: DMSO s.; acetone s.s.; methanol s. <br />
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