METHOXYCHLOR
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
BENZENE, 1,1'-(2,2,2-TRICHLOROETHYLIDENE) BIS(4- METHOXY)- 2,2-BIS(p-ANISYL)-1,1,1-TRICHLOROETHANE 1,1-BIS(p-METHOXYPHENYL)-2,2,2-TRICHLOROETHANE 2,2-BIS(p-METHOXYPHENYL)-1,1,1-TRICHLOROETHANE CASWELL NO 550 CHEMFORM DIANISYLTRICHLORETHANE 2,2-DI-p-ANISYL-1,1,1-TRICHLOROETHANE DIMETHOXY-DDT DIMETHOXY-DT p,p'-DIMETHOXYDIPHENYLTRICHLOROETHANE DIMETHOXY-DT 2,2-DI-(p-METHOXYPHENYL)-1,1,1-TRICHLOROETHANE DI(p-METHOXYPHENYL)-TRICHLOROMETHYL METHANE DMDT p,p'-DMDT DOUBLE-M EC p,p'-DWUMETOKSYDWUFENYLOTROJCHLOROETAN (POLISH) ETHANE, 2,2-BIS(p-ANISYL)-1,1,1-TRICHLORO- ETHANE, 1,1,1-TRICHLORO-2,2-BIS(p- METHOXYPHENYL)- FLO PRO McSEED PROTECTANT HIGALMETOX MARALATE MARLATE METHOXCIDE METHOXO METHOXYCHLOR METHOXYCHLORE p,p'-METHOXYCHLOR METHOXYCHLOR 2 EC METHOXY-DDT METOKSYCHLOR (POLISH) METOX MEZOX K MOXIE OMS 466 1,1,1-TRICHLOR-2,2-BIS(4-METHOXY-PHENYL)- AETHAN (GERMAN) 1,1,1-TRICHLORO-2,2-BIS(p-ANISYL)ETHANE 1,1'-(2,2,2-TRICHLOROETHYLIDENE)BIS (4-METHOXYBENZENE) 1,1,1-TRICHLORO-2,2-BIS(p-METHOXYPHENOL)ETHANOL 1,1,1-TRICHLORO-2,2-BIS(p-METHOXYPHENYL)ETHANE 1,1,1-TRICHLORO-2,2-BIS(4-METHOXYPHENYL)ETHANE 2,2,2-TRICHLORO-1,1-BIS(4-METHOXYPHENYL)ETHANE 1,1,1-TRICHLORO-2,2-DI(4-METHOXYPHENYL)ETHANE 4,4-(2,2,2-TRICHLOROETHYLIDENE)DIANISOLE
IDENTIFIERS
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures.
SYNONYM REFERENCE
- (HSDB , 1993; RTECS , 1993)
USES/FORMS/SOURCES
It is used as an insecticide, effective against mosquito larvae and house flies. In veterinary medicine, it is used as an ectoparasiticide (Budavari, 1989; Sax & Lewis, 1987).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
Methoxychlor is a convulsant of low toxicity (Hathaway et al, 1991). It is slightly irritating to, but not absorbed appreciably through, skin. Continued ingestion over long periods may cause kidney damage (Budavari, 1989). Human systemic effects by skin contact: somnolence (Lewis, 1992) Methoxychlor is a weakly estrogenic compound that has been shown to alter fertility in male and female rats and to have developmental effects (Hathaway et al, 1991). Methoxychlor is a suspected carcinogen with experimental carcinogenic, tumorigenic, and teratogenic data. It also causes experimental reproductive effects. Mutation data have been reported for methoxychlor (Lewis, 1992).
- POTENTIAL HEALTH HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Highly toxic, may be fatal if inhaled, swallowed or absorbed through skin. Avoid any skin contact. Effects of contact or inhalation may be delayed. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause pollution.
-MEDICAL TREATMENT
LIFE SUPPORT
- Support respiratory and cardiovascular function.
SUMMARY
- FIRST AID - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Move victim to fresh air. Call 911 or emergency medical service. Give artificial respiration if victim is not breathing. Do not use mouth-to-mouth method if victim ingested or inhaled the substance;give artificial respiration with the aid of a pocket mask equipped with a one-way valve or other proper respiratory medical device. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. For minor skin contact, avoid spreading material on unaffected skin. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved and take precautions to protect themselves.
-RANGE OF TOXICITY
MINIMUM LETHAL EXPOSURE
Most dogs fed a daily diet containing 4 g/kg methoxychlor by weight died within 3 weeks after the onset of effects. Effects were typical signs of chlorinated hydrocarbon intoxication, including fasciculations, tremor, hyperesthesia, tonic seizures, and tetanic convulsions. These effects were noted after 5 to 8 weeks (Hathaway et al, 1991). Most dogs fed 2 g/kg per day died within nine weeks (ACGIH, 1986). Rabbits given oral daily doses of 200 mg/kg died after 4 to 14 doses (Hathaway et al, 1991).
MAXIMUM TOLERATED EXPOSURE
The lowest published toxic dose in humans via the dermal route is 2414 mg/kg. Toxic effect was somnolence (general depressed activity) (RTECS , 1993). The oral dose level estimated to produce toxic effects in humans is 6430 mg/kg (ACGIH, 1986). One investigator found that a dietary level of 100 ppm (equivalent to 350 mg/man/day) for two years was the highest safe dose producing no symptoms, although tissue change was absent at 200 ppm and appeared only at levels of 500 ppm or higher (ACGIH, 1986). No adverse effects on health or clinical laboratory data were found in groups of volunteers given 2 mg/kg/day for 8 weeks (Hathaway et al, 1991).
- Carcinogenicity Ratings for CAS72-43-5 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A4 ; Listed as: Methoxychlor EPA (U.S. Environmental Protection Agency, 2011): D ; Listed as: Methoxychlor IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): 3 ; Listed as: Methoxychlor 3 : The agent (mixture or exposure circumstance) is not classifiable as to its carcinogenicity to humans. This category is used most commonly for agents, mixtures and exposure circumstances for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents (mixtures) for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents, mixtures and exposure circumstances that do not fall into any other group are also placed in this category.
NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Methoxychlor MAK (DFG, 2002): Not Listed NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS72-43-5 (U.S. Environmental Protection Agency, 2011):
Oral: Slope Factor: RfD: 5x10(-3) mg/kg-day
Inhalation: Drinking Water:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS72-43-5 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
- AIHA WEEL Values for CAS72-43-5 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS72-43-5 (National Institute for Occupational Safety and Health, 2007):
Listed as: Methoxychlor REL: IDLH: IDLH: 5000 mg/m3 Note(s): Ca
- OSHA PEL Values for CAS72-43-5 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS72-43-5 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS72-43-5 (U.S. Environmental Protection Agency, 2010):
Listed as: Methoxychlor (D014) Final Reportable Quantity, in pounds (kilograms): Additional Information: Unlisted Hazardous Wastes Characteristic of Toxicity Listed as: Benzene,1,1'-(2,2,2-trichloroethylidene) bis[4-methoxy- Final Reportable Quantity, in pounds (kilograms): Additional Information: Listed as: Methoxychlor Final Reportable Quantity, in pounds (kilograms): Additional Information:
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS72-43-5 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS72-43-5 (U.S. Environmental Protection Agency, 2010b):
Listed as: Benzene, 1,1[prime]-(2,2,2-trichloroethylidene)bis[4- methoxy- P or U series number: U247 Footnote: Listed as: Methoxychlor P or U series number: U247 Footnote: Editor's Note: The D, F, and K series waste numbers and Appendix VIII to Part 261 -- Hazardous Constituents were not included. Please refer to 40 CFR Part 261.
- EPA SARA Title III, Extremely Hazardous Substance List for CAS72-43-5 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS72-43-5 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
Listed as: Methoxychlor Effective Date for Reporting Under 40 CFR 372.30: Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28: 100 Listed as: Methoxychlor [Benzene, 1,1'-(2,2,2-trichloroethylidene)bis[4-methoxy-] Effective Date for Reporting Under 40 CFR 372.30: 1/1/87 Lower Thresholds for Chemicals of Special Concern under 40 CFR 372.28:
- DOT List of Marine Pollutants for CAS72-43-5 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS72-43-5 (EPA, 2005):
SHIPPING REGULATIONS
- DOT -- Table of Hazardous Materials and Special Provisions (49 CFR 172.101, 2005):
- ICAO International Shipping Name (ICAO, 2002):
LABELS
- NFPA Hazard Ratings for CAS72-43-5 (NFPA, 2002):
-HANDLING AND STORAGE
STORAGE
- ROOM/CABINET RECOMMENDATIONS
Keep this compound in a well-ventilated area (OHM/TADS , 1993). Storage Temperature: Ambient (HSDB , 1993)
-PERSONAL PROTECTION
SUMMARY
- RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
RESPIRATORY PROTECTION
- Refer to "Recommendations for respirator selection" in the NIOSH Pocket Guide to Chemical Hazards on TOMES Plus(R) for respirator information.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 72-43-5.
-PHYSICAL HAZARDS
FIRE HAZARD
Editor's Note: This material is not listed in the Emergency Response Guidebook. Based on the material's physical and chemical properties, toxicity, or chemical group, a guide has been assigned. For additional technical information, contact one of the emergency response telephone numbers listed under Public Safety Measures. POTENTIAL FIRE OR EXPLOSION HAZARDS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Non-combustible, substance itself does not burn but may decompose upon heating to produce corrosive and/or toxic fumes. Containers may explode when heated. Runoff may pollute waterways.
Contact with strong oxidizers may cause fires and explosions (HSDB , 1993).
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS72-43-5 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- SMALL FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
- LARGE FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Water spray, fog or regular foam. Move containers from fire area if you can do it without risk. Dike fire control water for later disposal; do not scatter the material. Use water spray or fog; do not use straight streams.
- TANK OR CAR/TRAILER LOAD FIRE PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks engulfed in fire. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
- NFPA Extinguishing Methods for CAS72-43-5 (NFPA, 2002):
EXPLOSION HAZARD
- Contact with strong oxidizers may cause fires and explosions (HSDB , 1993).
DUST/VAPOR HAZARD
- When heated to decomposition, methoxychlor emits highly toxic fumes of chlorides (Lewis, 1992).
REACTIVITY HAZARD
- Methoxychlor decomposes in alkaline materials (ACGIH, 1986).
- Contact with strong oxidizers may cause fires and explosions (HSDB , 1993).
- When heated to decomposition, methoxychlor emits highly toxic fumes of chlorides (Lewis, 1992).
EVACUATION PROCEDURES
- Editor's Note: This material is not listed in the Table of Initial Isolation and Protective Action Distances.
- SPILL - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
Increase, in the downwind direction, as necessary, the isolation distance of at least 25 to 50 meters (80 to 160 feet) in all directions.
- FIRE - PUBLIC SAFETY EVACUATION DISTANCES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
If tank, rail car or tank truck is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
- PUBLIC SAFETY MEASURES - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004)
CALL Emergency Response Telephone Number on Shipping Paper first. If Shipping Paper not available or no answer, refer to appropriate telephone number: MEXICO: SETIQ: 01-800-00-214-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5559-1588; For calls originating elsewhere, call: 011-52-555-559-1588.
CENACOM: 01-800-00-413-00 in the Mexican Republic; For calls originating in Mexico City and the Metropolitan Area: 5550-1496, 5550-1552, 5550-1485, or 5550-4885; For calls originating elsewhere, call: 011-52-555-550-1496, or 011-52-555-550-1552; 011-52-555-550-1485, or 011-52-555-550-4885.
ARGENTINA: CIQUIME: 0-800-222-2933 in the Republic of Argentina; For calls originating elsewhere, call: +54-11-4613-1100.
BRAZIL: PRÓ-QUÍMICA: 0-800-118270 (Toll-free in Brazil); For calls originating elsewhere, call: +55-11-232-1144 (Collect calls are accepted).
COLUMBIA: CISPROQUIM: 01-800-091-6012 in Colombia; For calls originating in Bogotá, Colombia, call: 288-6012; For calls originating elsewhere, call: 011-57-1-288-6012.
CANADA: UNITED STATES:
For additional details see the section entitled "WHO TO CALL FOR ASSISTANCE" under the ERG Instructions. As an immediate precautionary measure, isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids. Keep unauthorized personnel away. Stay upwind. Keep out of low areas.
- AIHA ERPG Values for CAS72-43-5 (AIHA, 2006):
- DOE TEEL Values for CAS72-43-5 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Methoxychlor TEEL-0 (units = mg/m3): 15 TEEL-1 (units = mg/m3): 30 TEEL-2 (units = mg/m3): 250 TEEL-3 (units = mg/m3): 500 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS72-43-5 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS72-43-5 (National Institute for Occupational Safety and Health, 2007):
IDLH: 5000 mg/m3 Note(s): Ca
CONTAINMENT/WASTE TREATMENT OPTIONS
SPILL OR LEAK PRECAUTIONS - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Cover with plastic sheet to prevent spreading. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS.
RECOMMENDED PROTECTIVE CLOTHING - EMERGENCY RESPONSE GUIDEBOOK, GUIDE 151 (ERG, 2004) Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer. It may provide little or no thermal protection. Structural firefighters' protective clothing provides limited protection in fire situations ONLY; it is not effective in spill situations where direct contact with the substance is possible.
"At the time of this review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices." (HSDB , 1993) ENVIRONMENTAL CONSIDERATIONS - LAND SPILL (Agricultural insecticides nec, liquid) (AAR, 1987) Dig a pit, pond, lagoon, or holding area to contain liquid or solid material. Dike surface flow using soil, sand bags, foamed polyurethane, or foamed concrete. Absorb bulk liquid with fly ash or cement powder.
ENVIRONMENTAL CONSIDERATIONS - WATER SPILL (Agricultural insecticides nec, liquid) (AAR, 1987) Use natural barriers or oil spill control booms to limit spill travel. If dissolved in region of 10 ppm or greater concentration, apply activated carbon at ten times the spilled amount. Remove trapped material with suction hoses. Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates.
ENVIRONMENTAL CONSIDERATIONS - LAND SPILL (Agricultural insecticides nec, other than liquid (and) Insecticides, other than agricultural, nec) (AAR, 1987) Dig a pit, pond, lagoon, or holding area to contain liquid or solid material. Cover solids with a plastic sheet to prevent dissolving in rain or fire fighting water.
ENVIRONMENTAL CONSIDERATIONS - WATER SPILL (Agricultural insecticides nec, other than liquid (and) Insecticides, other than agricultural, nec) (AAR, 1987) Use natural deep water pockets, excavated lagoons, or sand bag barriers to trap material at bottom. If dissolved in region of 10 ppm or greater concentration, apply activated carbon at ten times the spilled amount. Remove trapped material with suction hoses. Use mechanical dredges or lifts to remove immobilized masses of pollutants and precipitates.
-ENVIRONMENTAL HAZARD MANAGEMENT
POLLUTION HAZARD
- Release of methoxychlor to the environment is expected to occur primarily due to its use as an insecticide. Other sources of release may include loss during manufacturing, formulation, packaging, and disposal of methoxychlor (HSDB , 1993).
- Air: If released to the atmosphere, methoxychlor may exist in either vapor or particulate form. It may undergo reaction with photochemically generated hydroxyl radicals (estimated vapor phase half-life 3.7 hours) or be physically removed by settling out or washing out in precipitation (HSDB , 1993).
- Air: Wind erosion of methoxychlor-contaminated earth is a route by which the pesticide can enter the atmosphere (HSDB , 1993).
- Water: If released to water, methoxychlor may be removed or transported by several different mechanisms. Methoxychlor may adsorb to suspended solids and sediments, or it may be taken up and bioaccumulate in some aquatic organisms, although fish are reported to metabolize methoxychlor fairly rapidly (HSDB , 1993).
- Water: Methoxychlor may undergo direct photolysis in water (half-life 4.5 months) or indirect "sensitized" photolysis (half-life 5 hours) depending upon the presence of photosensitizers. 1,1-Bis(p-methoxyphenyl)-2,2- dichloroethylene (DMDE) is a major photolysis product of methoxychlor (HSDB , 1993).
- Water/Sediment: Methoxychlor may volatilize significantly (calculated half-life 4.5 days from a shallow river) and it may biodegrade under anaerobic conditions (half-life less than 28 days) or aerobic conditions (half-life greater than 100 days) in sediments (HSDB , 1993).
- Water: Oxidation and chemical hydrolysis are not expected to be significant fate processes in an aquatic environment (HSDB , 1993).
- Water and Soil: Under anaerobic conditions, major degradation products are dechlorinated methoxychlor (DMDD), and mono- and di-hydroxy derivatives of methoxychlor and DMDD (HSDB , 1993).
- Soil: If released to soil, methoxychlor is expected to remain immobilized primarily in the upper layer of soil, although a small percentage may migrate to lower depths, possibly into groundwater as suggested by the detection of methoxychlor in some groundwater samples (HSDB , 1993).
- Soil: Under anaerobic conditions, biodegradation appears to be the dominant removal mechanism in soil; however, under aerobic conditions, biodegradation is expected to be less rapid and possibly negligible (HSDB , 1993).
- Soil: Methoxychlor may undergo indirect "sensitized" photolysis on the soil surfaces and it may undergo chemical hydrolysis in moist soils (half-life of approximately 1 year) (HSDB , 1993).
- Soil: Methoxychlor underwent rapid primary degradation in four types of flooded soil under anaerobic conditions (half-life 1 week to 2 months), but degraded less rapidly under aerobic conditions in four types of upland soil (half-life greater than 3 months) (HSDB , 1993).
- Soil: After 100 days incubation in soil, negligible degradation of methoxychlor was observed under aerobic conditions and 73% degradation was observed under anaerobic conditions (HSDB , 1993).
ENVIRONMENTAL FATE AND KINETICS
OTHER Air: The estimated vapor phase half-life for methoxychlor in air via reaction with photochemically generated hydroxyl radicals is 3.7 hours (HSDB , 1993). Water: Methoxychlor may undergo direct photolysis (half-life 4.5 months) or indirect "sensitized" photolysis (half-life 5 hours) depending upon the presence of photosensitizers (HSDB , 1993). Water: Methoxychlor may volatilize significantly (calculated half-life 4.5 days from a shallow river) and it may biodegrade under anaerobic conditions (half-life greater than 28 days) or aerobic conditions (half-life greater than 100 days) in sediments (HSDB , 1993). Soil: Methoxychlor may undergo chemical hydrolysis in moist soils, with a half-life of approximately 1 year (HSDB , 1993). Soil: Methoxychlor underwent rapid primary degradation in four types of flooded soil under anaerobic conditions (half-life 1 week to 2 months), but degraded less rapidly under aerobic conditions in four types of upland soil (half-life greater than 3 months) (HSDB , 1993). Soil: After 100 days incubation in soil, negligible degradation of methoxychlor was observed under aerobic conditions and 73% degradation was observed under anaerobic conditions (HSDB , 1993).
ENVIRONMENTAL TOXICITY
- ECOTOXICITY VALUES (HSDB , 1993):
LD50, Anas platyrhynchos (mallard), oral, greater than 2000 mg/kg, 3 to 4 month old females, technical grade LC50, Colinus virginianus (Bobwhite quail), oral, greater than 5000 ppm in 5-day diet (no mortality to 5000 ppm), age 23 days, technical grade LC50, Coturnix japonica (Japanese quail), oral, greater than 5000 ppm in 5-day diet (no mortality to 5000 ppm), age 14 days, technical grade, 89% LC50, Phasianus colchicus (Ring-necked pheasant), oral, greater than 5000 ppm in 5-day diet (no mortality to 5000 ppm), age 16 days, technical grade LC50, Anas platyrhynchos (mallard), oral, greater than 5000 ppm in 5-day diet (no mortality to 5000 ppm), age 16 days, technical grade LC50, Asellus brevicaudus (sowbug), 34 mcg/L/96 hours at 18 degrees C, mature, static bioassay, technical material, 89.5% LC50, Gammarus fasciatus (scud), 1.9 mcg/L/96 hours at 15 degrees C, mature, static bioassay, technical material, 89.5% LC50, Gammarus lacustris (scud), 0.80 mcg/L/96 hours at 21 degrees C, mature, static bioassay, technical material, 89.5% LC50, Orconectes nais (crayfish), 0.50 mcg/L/96 hours at 21 degrees C, early instar, static bioassay, technical material, 89.5% LC50, Palaemonetes kadiakensis (glass shrimp), 1.05 mcg/L/96 hours at 21 degrees C, mature, static bioassay, technical material, 89.5% LC50, Pteronarcella badia (stonefly), 5 mcg/L/96 hours at 10 degrees C, naiad, static bioassay, technical material, 89.5% LC50, Pteronarcys californica (stonefly), 1.4 mcg/L/96 hours at 15 degrees C, second year class, static bioassay, technical material, 89.5% LC50, Salmo clarki (cutthroat trout), 15 mcg/L/96 hours at 12 degrees C, weight 0.5 g, static bioassay, technical material, 89.5% LC50, Salmo gairdneri (rainbow trout), 62 mcg/L/96 hours at 12 degrees C, weight 1.2 g, static bioassay, technical material, 89.5% LC50, Salmo salar (Atlantic salmon), 16.4 mcg/L/96 hours at 12 degrees C, weight 0.6 g, static bioassay, technical material, 89.5% LC50, Salvelinus fontinalis (brook trout), 19 mcg/L/96 hours at 12 degrees C, weight 1.2 g, static bioassay, technical material, 89.5% LC50, Salvelinus namaycush (lake trout), 17 mcg/L/96 hours at 12 degrees C, weight 3 g, static bioassay, technical material, 89.5% LC50, Esox lucius (Northern pike), 12 mcg/L/96 hours at 18 degrees C, weight 0.7 g, static bioassay, technical material, 89.5% LC50, Carassius auratus (goldfish), 42 mcg/L/96 hours at 18 degrees C, weight 1 g, static bioassay, technical material, 89.5% LC50, Pimephales promelas (fathead minnow), 39 mcg/L/96 hours at 18 degrees C, weight 1 g, static bioassay, technical material, 89.5% LC50, Ictalarus punctatus (channel catfish), 52 mcg/L/96 hours at 18 degrees C, weight 1.2 g, static bioassay, technical material, 89.5% LC50, Lepomis macrochirus (bluegill), 32 mcg/L/96 hours at 17 degrees C, weight 1.2 g, static bioassay, technical material, 89.5% LC50, Micropterus salmoides (largemouth bass), 16 mcg/L/96 hours at 18 degrees C, weight 0.8 g, static bioassay, technical material, 89.5% LC50, Perca flavescens (yellow perch), 30 mcg/L/96 hours at 12 degrees C, weight 1 g, static bioassay, technical material, 89.5% LC50, Salmo salar (Atlantic salmon), 1.7 mcg/L/96 hours at 12 degrees C, weight 0.6 g, static bioassay, technical material, 89.5% LC50, Salvelinus fontinalis (brook trout), 11.7 mcg/L/96 hours at 12 degrees C, weight 0.7 g, static bioassay, technical material, 89.5% LC50, Perca flavescens (yellow perch), 17.5 mcg/L/96 hours at 12 degrees C, weight 1 g, static bioassay, technical material, 89.5% LD50, Anas platyrhynchos (mallard duck), male, 3 months old, oral, greater than 2000 mg/kg, technical grade, 88 and 12% related compound LD50, Tympanuchus phasianellus (Sharp-tailed grouse), male, adult (in reproductive condition), oral, greater than 2000 mg/kg, technical grade, 88 and 12% related compound LD50, Callipepla californica (California quail), female, 9 to 10 months old (in reproductive condition), oral, greater than 2000 mg/kg, technical grade, 88 and 12% related compound LC50, Thalassoma bifusicatum (blue head), 14 mcg/L/24 hours, conditions of bioassay not given LC50, Pteronarcys californica, 1.4 mcg/L/96 hours, conditions of bioassay not specified LC50, Taeniopteryx nivalis, 0.98 mcg/L/96 hours, conditions of bioassay not specified LC50, Stenonema spp, 0.63 mcg/L/96 hours, conditions of bioassay not specified LC50, Gammarus lacustris, 0.8 mcg/L/96 hours, conditions of bioassay not specified LC50, Gammarus fasciatus, 1.9 mcg/L/96 hours, conditions of bioassay not specified LC50, Palaemonetes kadiakenesis, 1 mcg/L/96 hours, conditions of bioassay not specified LC50, Orconectes nais, 0.5 mcg/L/96 hours, conditions of bioassay not specified LC50, Asellus brevicaudus, 3.2 mcg/L/96 hours, conditions of bioassay not specified LC50, Simocephalus serrulatus, 5 mcg/L/48 hours, conditions of bioassay not specified LC50, Daphnia pulex, 0.78 mcg/L/48 hours, conditions of bioassay not specified TL50, 89.5%, Palaemon macrodactylus (Korean shrimp), 0.44 ppb/96 hours (0.21 to 0.93 ppm), static bioassay, technical material TL50, 89.5%, Palaemon macrodactylus (Korean shrimp), 6.7 ppb/96 hours (4.37 to 10.7 ppm), intermittent flow-through bioassay, technical material LC50, 100%, Crangon septemspinosa (sand shrimp), 4 ppb/96 hours, static lab bioassay, technical material LC50, 100%, Palaemonetes vulgaris (grass shrimp), 12 ppb/96 hours, static lab bioassay, technical material LC50, 100%, Pagurus longicarpus (hermit crab), 7 ppb/96 hours, conditions of bioassay not stated, technical material LC50, Cancer magister (Dungeness crab), zoeae, 0.42 mcg/L/96 hours, static bioassay LC50, Cancer magister (Dungeness crab), adults, 1.3 mcg/L/96 hours, static bioassay LC50, Cyprinodon variegatus (sheepshead minnow), juvenile, 49 mcg/L/96 hours, flow-through bioassay LC50, Pimephales promelas (fathead minnow), juvenile, 7.5 mcg/L/96 hours, conditions of bioassay not specified LC50, Lepomis macrochirus (bluegill sunfish), juvenile, 62 mcg/L/96 hours, conditions of bioassay not specified LC50, Salmo gairdneri (rainbow trout), juvenile, 62.6 mcg/L/96 hours, conditions of bioassay not specified LC50, Oncorhynchus kisutch (coho salmon), juvenile, 66.2 mcg/L/96 hours, conditions of bioassay not specified LC50, Oncorhynchus tschawtscha (chinook), juvenile, 27.9 mcg/L/96 hours, conditions of bioassay not specified LC50, Salmo salar (Atlantic salmon), 75 to 92 mcg/L/24 hours, status bioassay LC50, 100%, Fundulus heteroclitus (mummichog), 35 ppb/96 hours, static bioassay, technical material LC50, 100%, Fundulus majalis (striped killifish), 30 ppb/96 hours, static bioassay, technical material LC50, 100%, Menidia menidia (Atlantic silverside), 33 ppb/96 hours, static bioassay, technical material LC50, 100%, Mugil cephalus (striped mullet), 63 ppb/96 hours, static bioassay, technical material LC50, 100%, Anguilla rostrata (American eel), 12 ppb/96 hours, static bioassay, technical material LC50, 100%, Thalassoma bifasiatum (bluehead), 13 ppb/96 hours, static bioassay, technical material LC50, 100%, Sphaeroides maculatus (northern puffer), 150 ppb/96 hours, static bioassay, technical material LC50, 89.5%, Gasterosteus aculeatus (threespine stickleback), 69.1 ppb/96 hours, static bioassay, technical material LC50, Salmo gairdneri (rainbow trout), 0.020 ppm/96 hours, conditions of bioassay not specified LC50, Rainbow trout, 30 mcg/L at 1.6 degrees C and 62 mcg/L at 12.7 degrees C, conditions of bioassay not specified LC50, Bluegill, 42 mcg/L at 1.6 degrees C and 75 mcg/L at 12.7 degrees C, conditions of bioassay not specified
-PHYSICAL/CHEMICAL PROPERTIES
MOLECULAR WEIGHT
DESCRIPTION/PHYSICAL STATE
- Methoxychlor exists as a white to yellow crystalline solid (dimorphic crystals) with a slightly fruity odor (ACGIH, 1986; Budavari, 1989; HSDB , 1993). Color turns to pink or tan on exposure to light (HSDB , 1993). Pure methoxychlor forms colorless crystals (HSDB , 1993). Technical methoxychlor is a pale buff to gray flaky powder (HSDB , 1993).
SPECIFIC GRAVITY
- TEMPERATURE AND/OR PRESSURE NOT LISTED
DENSITY
- NORMAL TEMPERATURE AND PRESSURE
FREEZING/MELTING POINT
78-78.2 degrees C (Budavari, 1989) 86-88 degrees C (Budavari, 1989)
BOILING POINT
SOLUBILITY
Methoxychlor is practically insoluble in water (Budavari, 1989). 0.10 mg/L in water (at 25 degrees C) (HSDB , 1993)
It is soluble in alcohol (Budavari, 1989). Solubility in g/kg (at 22 degrees C) (HSDB , 1993) : Chloroform: 440 Methanol: 50 Xylene: 440
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