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SU0000027 SSC RPT
Environmental Health - Public
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2600 - Land Use Program
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MS-01-08
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SU0000027 SSC RPT
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Last modified
11/22/2019 4:12:13 PM
Creation date
9/4/2019 6:30:39 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSC RPT
RECORD_ID
SU0000027
PE
2622
FACILITY_NAME
MS-01-08
STREET_NUMBER
27475
Direction
S
STREET_NAME
FAIROAKS
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
24811033
ENTERED_DATE
8/8/2001 12:00:00 AM
SITE_LOCATION
27475 S FAIROAKS RD
RECEIVED_DATE
2/26/2001 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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FilePath
\MIGRATIONS\F\FAIROAKS\27475\MS-01-08\SU0000027\SSC RPT.PDF
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EHD - Public
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'.X7'OXNET PIP-2,4-D http://ace.ace.orst.edu/info/extoxnetipips/24-1).htm <br /> Ecological Effects: <br /> • Effects on birds: 2,4-D is slightly toxic to wildfowl and slightly to moderately toxic to birds. The <br /> LD50 is 1000 mg/kg in mallards, 272 mg/kg in pheasants, and 668 mg/kg in quail and pigeons <br /> [5-7] <br /> • Effects on aquatic organisms: Some formulations of 2,4-D are highly toxic to fish while others are <br /> less so. For example, the LC50 ranges between 1.0 and 100 mg/L in cutthroat trout, depending on <br /> the formulation used. Channel catfish had less than 10% mortality when exposed to 10 mg/L for 48 <br /> hours [1,9]. Green sunfish, when exposed to 110 mg/L for 41 hours, showed no effect on swimming <br /> response. Limited studies indicate a half-life of less than 2 days in fish and oysters [24]. <br /> Concentrations of 10 mg/L for 85 days did not adversely affect the survival of adult dungeness <br /> crabs. For immature crabs, the 96-hour LC50 is greater than 10 mg/L, indicating that 2,4-D is only <br /> slightly toxic. Brown shrimp showed a small increase in mortality at exposures of 2 mg/L for 48 <br /> hours [7,20]. <br /> • Effects on other organisms: Moderate doses of 2,4-D.severely impaired honeybees brood <br /> production. At lower levels of exposure, exposed bees lived significantly longer than the controls. <br /> The honeybee LD50 is 0.0115 mg/bee [6,7]. <br /> Environmental Fate: <br /> i <br /> • <br /> Breakdowninsoil and groundwater: 2,4-D has low soil persistence.ITh--e:half'-1ife_in soil•is-less <br /> than 7 days [21]. Soil microbes are primarily responsible for its disappearance [20]. Despite its short ' <br /> half-life in soil and in aquatic environments, the compound has been detected in groundwater <br /> supplies in at least five States and in Canada [20]. Very low concentrations have also been detected <br /> in surface waters throughout the U.S. [23]. <br /> • Breakdown in water: In aquatic environments, microorganisms readily degrade 2,4-D. Rates of ' <br /> breakdown increase with increased nutrients, sediment load, and dissolved organic carbon. Under <br /> oxygenated conditions the half-life is 1 week to several weeks [20]. <br /> I Breakdown in vegetation: 2,4-D interferes with normal plant growth processes. Uptake of the <br /> compound is through leaves, stems, and roots. Breakdown in plants is by a variety of biological and <br /> E chemical pathways [10]. 2,4-D is toxic to most broad leaf crops, especially cotton, tomatoes, beets, <br /> and fruit trees [7]. <br /> Physical Properties: <br /> i <br /> • Appearance: 2,4-D is a white powder [6]. <br /> • Chemical Name: (2,4-dichlorophenoxy)acetic acid [6] j <br /> • CAS Number: 94-75-7 <br /> • Molecular Weight: 221.04 <br /> * Water Solubility: 900 mg/L @ 25 C (acid) [5] <br /> • Solubility in Other Solvents: ethanol v.s.; diethyl ether v.s.; toluene s.; xylene s. [6] <br /> • Melting Point: 140.5 C [6] <br /> • Vapor Pressure: 0.02 mPa @ 25 C (acid) [5] <br /> t Partition Coefficient: 2.81 [20] <br /> • Adsorption Coefficient: 20 (acid) [21] <br /> Exposure Guidelines: <br /> 'of 4 1/26/009:00 AM <br /> A � <br />
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