trans-2,3-Dichlorbut-2-en

Wear positive pressure breathing apparatus and full protective clothing. Move containers from fire area if you can do so without risk. Spray containers with cooling water until well after fire is out. Isolate for one-half mile in all directions if tank car or truck is involved in a fire. For small fires, use dry chemical, carbon dioxide, spray or foam. For large fires, use water spray, fog, or foam. (EPA, 1998)

If material on fire or involved in fire: Use water in flooding quantities as fog. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Solid streams of water may be ineffective. Use foam, dry chemical, or carbon dioxide. Use water spray to knock-down vapors. /Dichlorobutene/

Keep unnecessary people away; isolate hazard area. Stay upwind; keep out of low areas. Shut off ignition sources. Do not touch spilled material. Use water spray to reduce vapors, but do not get water inside containers. For small spills, absorb with sand or other non-combustible absorbent material. For large spills, dike far ahead of spill for later disposal. (EPA, 1998)

At the time of 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.

/1,4-Dichloro-2-butene/ may be disposed of by the use of the following incineration methods: Rotary kiln with a temperature of 820-1600 °C and a residence time of seconds for liquids and gases, and hours for solids. Liquid injection with a temperature of 650-1600 °C with a residence time of 0.1-2 seconds. Fluidized bed with a temperature of 450-980 °C with a residence time of seconds for liquids and gases, longer for solids. /1,4-Dichloro-2-butene/

If material not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary. Use water spray to knock-down vapors. /Dichlorobutene/

Personnel protection: Avoid breathing vapors. Keep upwind. Avoid bodily contact with the material. ... Do not handle broken packages unless wearing appropriate personal protective equipment. Wash away any material which may have contacted the body with copious amounts of water or soap and water. Wear positive pressure self-contained breathing apparatus when fighting fires involving this material. If contact with the material anticipated, wear appropriate chemical protective clothing. /Dichlorobutene/

SRP: The scientific literature for the use of contact lenses in industry is conflicting. The benefit or detrimental effects of wearing contact lenses depend not only upon the substance, but also on factors including the form of the substance, characteristics and duration of the exposure, the uses of other eye protection equipment, and the hygiene of the lenses. However, there may be individual substances whose irritating or corrosive properties are such that the wearing of contact lenses would be harmful to the eye. In those specific cases, contact lenses should not be worn. In any event, the usual eye protection equipment should be worn even when contact lenses are in place.

SRP: Contaminated protective clothing should be segregated in such a manner so that there is no direct personal contact by personnel who handle, dispose, or clean the clothing. Quality assurance to ascertain the completeness of the cleaning procedures should be implemented before the decontaminated protective clothing is returned for reuse by the workers. Contaminated clothing should not be taken home at end of shift, but should remain at employee's place of work for cleaning.

8 hr Time Weighted Avg (TWA) 0.005 ppm, skin. /1,4-Dichloro-2-butene/

Excursion Limit Recommendation: Excursions in worker exposure levels may exceed 3 times the TLV-TWA for no more than a total of 30 minutes during a work day, and under no circumstances should they exceed 5 times the TLV-TWA, provided that the TLV-TWA is not exceeded. /1,4-Dichloro-2-butene/

A2: Suspected human carcinogen. /1,4-Dichloro-2-butene/

0.015 [ppm]

0.86 [ppm]

3.8 [ppm]

For emergency situations, wear a positive pressure, pressure-demand, full facepiece self-contained breathing apparatus (SCBA) or pressure- demand supplied air respirator with escape SCBA and a fully-encapsulating, chemical resistant suit. (EPA, 1998)

Rubber gloves; chemical splash goggles; Rubber boots & apron; Barrier cream; Organic canister mask. /Dichlorobutene/

Chemical protective clothing composed of polyvinyl alcohol (PVA), Viton (a proprietary fluoroelastomer), or Saranex (a multilayer laminate greater than 0.15 cm in thickness of polyethylene and Saran) is highly recommended, having break through times greater than one hour. Butyl rubber or polyethylene may be used but data suggest break through times of approximately an hour or more. Protective clothing composed of natural rubber, nitrile, chlorinated polyethylene, or polyvinyl chloride (material less than 0.015 cm thick) is not recommended since break through times were found to be significantly less than one hour. /1,4-Dichloro-2-butene/

Personnel protection: ... Wear appropriate chemical protective gloves, boots and goggles. /Dichlorobutene/

TERRESTRIAL FATE: Based on a classification scheme(1), a Koc value of 215(2) indicates that 1,4-dichloro-trans-2-butene is expected to have moderate mobility in soil(SRC). Volatilization of 1,4-dichloro-trans-2-butene from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 6.6X10-4 atm-cu m/mole(SRC), based upon its vapor pressure, 3.43 mm Hg(3), and water solubility, 850 mg/l(4). The potential for volatilization of 1,4-dichloro-trans-2-butene from dry soil surfaces may exist(SRC) based upon its vapor pressure(3). In a soil degradation study, approximately 5-15% of initially added 1,4-dichloro-2-butene (cis isomer) was recovered in gas-traps after a 7-day period, indicating soil volatilization had occurred(2). Soil degradation studies conducted over a week incubation period in a sandy loam and silt loam soils found degradation half-lives of 1.8 to 2.5 days in both sterile and non-sterile soils(2); degradation rates in non-sterile soils were not significantly faster than in sterile soils indicating that abiotic or evaporative processes were more important than biological processes for 1,4-dichloro-2-butene (cis-isomer)(2,5); similar results for the trans-isomer are expected because of the similar structure(SRC). The hydrolysis half-life of 1,4-dichloro-trans-2-butene was measured as 3.2 days under neutral conditions(6), suggesting hydrolysis may be an important fate process in moist soils.

AQUATIC FATE: Based on a classification scheme(1), a Koc value of 215(SRC), indicates that 1,4-dichloro-trans-2-butene is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(3) based upon an estimated Henry's Law constant of 6.6X10-4 atm-cu m/mole(SRC), derived from its vapor pressure, 3.43 mm Hg(4), and water solubility, 850 mg/l(5). Using this Henry's Law constant and an estimation method(3), volatilization half-lives for a model river and model lake are 2 hours and 5 days, respectively(SRC). According to a classification scheme(6), an estimated BCF of 14(SRC), from its water solubility(5) and a regression-derived equation(3), suggests the potential for bioconcentration in aquatic organisms is low. The hydrolysis half-life of 1,4-dichloro-trans-2-butene was measured as 3.2 days under neutral conditions(7). Limited data suggest that biodegradation will not be an important fate process in water since volatilization and hydrolysis are expected to occur rapidly(2,8).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), 1,4-dichloro-trans-2-butene, which has a vapor pressure of 3.43 mm Hg at 25 °C(1) is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase 1,4-dichloro-trans-2-butene is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals and ozone molecules(SRC). The half-life for the reaction in air with hydroxyl radicals is estimated to be 10 hours(SRC), calculated from its rate constants of 3.7X10-11 cu cm/molecule-sec at 25 °C(SRC) using a structure estimation method(3). The half-life for the reaction in air with ozone is estimated to be 8 days(SRC), calculated from its rate constants of 1.4X10-18 cu cm/molecule-sec at 25 °C(SRC) that was derived using a structure estimation method(3).

Using sandy loam and silt loam soils, the Koc of 1,4-dichloro-2-butene (cis-isomer) was experimental determined to be 215(1). According to a suggested classification scheme(2), this Koc value suggests that 1,4-dichloro-trans-2-butene will have moderate mobility in soil because of the similar structure(SRC).

AVAILABLE DATA DO NOT ALLOW AN EVALUATION OF CARCINOGENICITY ...

Inhalation of vapor irritates nose and throat. Contact with eyes causes intense irritation and tears. Contact of liquid with skin causes severe blistering and dermatitis. Ingestion causes severe irritation of the mouth and stomach. /Dichlorobutene/

... BOTH LIQUID AND VAPOR ARE HIGHLY DANGEROUS TO THE SKIN, EYES, LUNG, & INTERNAL ORGANS. /DICHLOROBUTENES/

Symptomatology: 1A) Inhalation, high vapor concn: gasping, refusal to breathe, coughing, substernal pain, & extreme respiratory distress at vapor concn over 1500 ppm. Irritation of eyes & upper respiratory mucosa appears promptly after exposure to concentrated vapors. Lacrimation & headache are prominent. Coma may occur rapidly. B) Inhalation, low vapor concn: central nervous depression & moderate irritation of respiratory system. Headache is frequent. 2) Dermal: severe skin irritation with marked inflammatory response of epidermis & underlying tissues. 3) Oral: acute gastrointestinal distress with pulmonary congestion & edema. Central nervous depression, perhaps even in the absence of impaired oxygen uptake. 4) By any route, possible late injuries to liver, kidneys & heart. 5) After inhalation exposures, malaise, headache, chest & abdominal discomfort & irritability have been reported to persist for several weeks & perhaps for several years.

1,4-Dichloro-trans-2-butene's production and use as a starting material in the manufacture of adiponitrile, butane-1,4-diol and tetrahydrofuran(1) may result in its release to the environment through various waste streams (SRC). It also occurs as an intermediate in the production of chloroprene(1).

Soil degradation studies conducted with 1,4-dichloro-2-butene (cis-isomer) over a one week incubation period in a sandy loam and silt loam soils found degradation half-lives of 1.8 to 2.5 days in both sterile and non-sterile soils(1); degradation rates in non-sterile soils were not significantly faster than in sterile soils indicating that abiotic or evaporative processes were more important than biological processes for 1,4-dichloro-2-butene(1,2); similar results for the trans-isomer are expected because of the similar structure(SRC).

trans-1,4-Dichlorobutene

Group 3: Not classifiable as to its carcinogenicity to humans

Volume 15: (1977) Some Fumigants, the Herbicides 2,4-D and 2,4,5-T, Chlorinated Dibenzodioxins and Miscellaneous Industrial Chemicals

1999

1998

An estimated BCF of 14 was calculated for 1,4-dichloro-trans-2-butene(SRC), using a water solubility of 850 mg/l(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is low(SRC).

The Henry's Law constant for 1,4-dichloro-trans-2-butene is estimated as 6.6X10-4 atm-cu m/mole(SRC) based upon its vapor pressure, 3.43 mm Hg(1), and water solubility, 850 mg/l(2). This Henry's Law constant indicates that 1,4-dichloro-trans-2-butene is expected to volatilize from water surfaces(3). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(3) is estimated as 2 hours(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(3) is estimated as 5 days(SRC). 1,4-Dichloro-trans-2-butene's estimated Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of 1,4-dichloro-trans-2-butene from dry soil surfaces may exist(SRC) based upon the vapor pressure of this compound(1). In a soil degradation study, approximately 5-15% of initially added 1,4-dichloro-2-butene (cis isomer) was recovered in gas-traps after a 7-day period suggesting volatilization will be important for the trans-isomer(3).

... 62 PPM (0.34 MG/L) GIVEN TO RATS BY INHALATION FOR 4 HR CAUSED MORTALITY IN 2/6 ANIMALS IN 14 DAYS.

... 30 FEMALE ICR/HA SWISS MICE WERE GIVEN SKIN APPLICATIONS OF 1 MG TRANS-1,4-DICHLOROBUTENE DISSOLVED IN 0.1 ML ACETONE THRICE WEEKLY FOR 77 WK. NO SKIN TUMORS WERE OBSERVED.

... /1,4-Dichloro-trans-2-butene/ was tested in a two-stage carcinogenesis experiment with phorbol myristyl acetate as a promoting agent in female ICR/Ha Swiss mice. Of 30 mice treated with 1 mg trans-1,4-dichlorobutene in 0.1 ml acetone plus 2.5 ug phorbol myristyl acetate in 0.1 ml acetone, 1 developed a skin papilloma, compared with 28 positive controls ... /which had/ 209 papillomas & 17 squamous-cell carcinomas of the skin after treatment with 7,12-dimethylbenz(a)anthracene & phorbol myristyl acetate. Of 30 mice treated with phorbol myristyl acetate alone, 3 had skin papillomas & 1 a skin carcinoma.

A group of 30 female ICR/Ha Swiss mice were given skin applications of 1 mg trans-1,4-dichlorobutene dissolved in 0.1 ml acetone thrice weekly for 77 weeks. No skin tumors were observed.

For more Non-Human Toxicity Excerpts (Complete) data for 1,4-DICHLORO-TRANS-2-BUTENE (7 total), please visit the HSDB record page.

A2: Suspected human carcinogen. /1,4-Dichloro-2-butene/

No epidemiological data relevant to the carcinogenicity of trans-1,4-dichlorobutene were available. There is inadequate evidence in experimental animals for the carcinogenicity of trans-1,4-dichlorobutene. Overall evaluation: trans-1,4-Dichlorobutene is not classifiable as to its carcinogenicity to humans (Group 3).

Releases of CERCLA hazardous substances are subject to the release reporting requirement of CERCLA section 103, codified at 40 CFR part 302, in addition to the requirements of 40 CFR part 355. 1,4-Dichloro-trans-2-butene is an extremely hazardous substance (EHS) subject to reporting requirements when stored in amounts in excess of its threshold planning quantity (TPQ) of 500 lbs.