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SITE INFORMATION AND CORRESPONDENCE_FILE 2
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SITE INFORMATION AND CORRESPONDENCE_FILE 2
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Last modified
12/6/2019 5:05:08 PM
Creation date
12/6/2019 2:55:44 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 2
RECORD_ID
PR0545028
PE
3528
FACILITY_ID
FA0003919
FACILITY_NAME
VAN DE POL ENTERPRISES
STREET_NUMBER
5491
STREET_NAME
F
STREET_TYPE
ST
City
BANTA
Zip
95304
CURRENT_STATUS
02
SITE_LOCATION
5491 F ST
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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EXTOXNET PIP -2,4-D Page 3 of 4 <br /> compound in eggs [7]. <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 [5- <br /> 7]. <br /> . Effects on aquatic organisms: Some formulations of 2,4-D are highly toxic to fish while others <br /> are less so. For example,the LC50 ranges between 1.0 and 100 mg/L in cutthroat trout, depending <br /> on the formulation used. Channel catfish had less than 10%mortality when exposed to 10 mg/L <br /> for 48 hours [1,9]. Green sunfish,when exposed to 110 mg/L for 41 hours, showed no effect on <br /> swimming response. Limited studies indicate a half-life of less than 2 days in fish and oysters <br /> [24]. Concentrations of 10 mg/L for 85 days did not adversely affect the survival of adult <br /> dungeness crabs. For immature crabs, the 96-hour LC50 is greater than 10 mg/L, indicating that <br /> 2,4-D is only slightly toxic. Brown shrimp showed a small increase in mortality at exposures of 2 <br /> mg/L for 48 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 /> . Breakdown in soil and groundwater: 2,4-D has low soil persistence. The half-life in soil is less <br /> than 7 days [21]. Soil microbes are primarily responsible for its disappearance [20]. Despite its <br /> short half-life in soil and in aquatic environments, the compound has been detected in <br /> groundwater supplies in at least five States and in Canada[20]. Very low concentrations have also <br /> been detected 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 /> . 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 <br /> and chemical pathways [10]. 2,4-D is toxic to most broad leaf crops, especially cotton, tomatoes, <br /> beets, and fruit trees [7]. <br /> Physical Properties: <br /> . Appearance: 2,4-D is a white powder[6]. <br /> . Chemical Name: (2,4-dichlorophenoxy)acetic acid [6] <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 /> . Partition Coefficient: 2.81 [20] <br /> . Adsorption Coefficient: 20 (acid) [21] <br /> Exposure Guidelines: , <br /> http://extoxnet.orst.edu/pips/24-D.htm 5/8/2008 <br />
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