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SU0000077_SSC RPT
Environmental Health - Public
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SU0000077_SSC RPT
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Last modified
4/8/2022 5:23:23 PM
Creation date
3/29/2022 1:34:31 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSC RPT
RECORD_ID
SU0000077
PE
2622
FACILITY_NAME
MS-00-14
STREET_NUMBER
23755
Direction
N
STREET_NAME
DE VRIES
STREET_TYPE
RD
City
LODI
Zip
95240
ENTERED_DATE
8/8/2001 12:00:00 AM
SITE_LOCATION
23755 N DEVRIES RD
RECEIVED_DATE
6/13/2000 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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!XFO\NGT PIP-FENAMII1110S <br /> 'n:Hace.orst.edu/cgi-bin/mf's/01/pips/fcnamiph.htm <br /> Ecological Effects: <br /> • Effects on birds: Fenamiphos is very highly toxic to birds, with a reported acute oral LD50 for the <br /> most sensitive species tested, the ring-necked pheasant, of 0.5 mg/kg [6]. LD50 values for other <br /> species range from 1.0 to 2.4 mg/kg, all of which indicate that this is a very highly toxic compound <br /> [6]. In a controlled experiment, fenamiphos was determined to be the most toxic of thirteen <br /> different cholinesterase inhibitors [66]. In tests with wild songbirds (red-winged blackbirds and <br /> house sparrows) an unspecified dose of Nemacur was highly toxic to these species, with death of <br /> the birds occurring within an hour of eating the granules [66]. <br /> • Effects on aquatic organisms: The toxicity of fenamiphos to aquatic species varies from moderate <br /> to high. Bluegill sunfish are extremely sensitive to the presence of the compound. The LC50 for <br /> fenamiphos is 9.6 mg/L in this species. Other species tested include the rainbow trout (LC50 is 0.11 <br /> mg/L) and the goldfish (LC50 is 3.2 mg/L) [8]. The compound is not expected to bioaccumulate <br /> appreciably in aquatic organisms [6]. <br /> • Effects on other organisms: Fenamiphos is practically nontoxic to honeybees [8]. <br /> Environmental Fate: <br /> • Breakdown in soil and groundwater: Fenamiphos is of moderate persistence in the soil <br /> environment, with a reported soil half-life of about 50 days [19]. The compound appears to have no <br /> effect on the activity of soil bacteria [8]. Aerobic processes are most important for breakdown of <br /> the compound. Fenamiphos is not strongly adsorbed to soils [19], but neither it nor its breakdown <br /> products have been found in over 1200 wells tested in six states. <br /> • Breakdown in water: Fenamiphos disappears quickly from water in acidic and alkaline water, but <br /> it is stable in neutral water when held in the dark. The compound, when in the presence of artificial <br /> light, disappears very rapidly. In a neutral solution, half of the initial amount of the compound <br /> degraded within 4 hours. <br /> • Breakdown in vegetation: In plants, the compound is absorbed through the roots and translocated <br /> to the leaves. It is broken down within the plant. The products of its breakdown are relatively <br /> persistent and can also inhibit cholinesterase [6]. <br /> Physical Properties: <br /> • Appearance: Fenamiphos is a colorless crystal in its pure form, or a tan waxy solid in the technical <br /> form [13]. <br /> • Chemical Name: ethyl 4-methylthio-m-tolyl isopropylphosphoramidate [13] <br /> • CAS Number: 22224-92-6 <br /> • Molecular Weight: 303.40 <br /> • Water Solubility: 700 mg/L @ 20 C [13] <br /> • Solubility in Other Solvents: s. in dichloromethane, isopropanol, and toluene [13] <br /> • Melting Point: 46 C (technical) [13] <br /> • Vapor Pressure: 0.12 mPa @ 20 C [13] <br /> • Partition Coefficient: Not Available <br /> • Adsorption Coefficient: 100 [19] <br /> Exposure Guidelines: <br /> • ADI: 0.005 mg/kg/day [38] <br /> of 4 <br /> 5/12/00 2:05 PM <br />
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