에틸렌디아민

Wear full protective clothing including gloves and boots. If necessary to enter closed area, wear full-faced gas masks with self-contained breathing apparatus. Use water spray, dry chemical, alcohol foam, or carbon dioxide. Do not use water in case of drum or tank fires. If a leak or spill has not ignited, use water spray to reduce the vapors and dilute spills to nonflammable mixtures. Use water to keep fire-exposed containers cool. (EPA, 1998)

Use water spray, powder, alcohol-resistant foam, carbon dioxide. In case of fire: keep drums, etc., cool by spraying with water.

Fresh air, rest. Refer immediately for medical attention.

Remove contaminated clothes. Rinse skin with plenty of water or shower. Refer immediately for medical attention.

First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.

Rinse mouth. Do NOT induce vomiting. Give one or two glasses of water to drink. Refer immediately for medical attention.

· CALL 911. Then call emergency response telephone number on shipping paper. If shipping paper not available or no answer, refer to appropriate telephone number listed on the inside back cover.

· ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from immediate area.

Signs and Symptoms of Acute Ethylenediamine Exposure: Acute exposure to ethylenediamine may result in cough, difficulty in breathing, irritation of the lungs, and pneumonia. Nausea, vomiting, and diarrhea are often seen. Contact with ethylenediamine may result in redness, pain, irritation, and burns.

General First Aid:

(General first aid procedures)

Use water spray, dry chem, "alcohol resistant" foam, or carbon dioxide. Use water spray to keep fire-exposed containers cool. Solid streams may be ineffective and spread material.

Do not use water in case of drum or tank fires.

1. Remove all ignition sources. 2. Ventilate area of spill or leak. 3. If in the liq form, absorb on paper towels. Evaporate in a safe place (such as a fume hood). Allow sufficient time for evaporating vapors to completely clear the hood ductwork. Burn the paper in a suitable location away from combustible materials. Large quantities can be collected and atomized in a suitable combustion chamber equipped with an appropriate effluent gas cleaning device. ... 4. If in the solid form, collect, allow to melt, and dispose of the liq as above.

Overspread /spill with/ sufficient sodium bisulfate and sprinkle water.

SRP: 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.

Ethylenediamine may be disposed of by atomizing in a suitable combustion chamber equipped with an appropriate effluent gas cleaning device.

Catalytic /destruction/ of waste gases from ethylenediamine production is described.

Removal of ethylenediamine from wastewater using ion exchange is described.

Remove all ignition sources. Personal protection: complete protective clothing including self-contained breathing apparatus. Ventilation. Collect leaking and spilled liquid in covered containers as far as possible. Absorb remaining liquid in sand or inert absorbent. Then store and dispose of according to local regulations. Collect the spilled substance into containers. The container should be made of the same material as the original container.

Ethylenediamine (EDA) (31.6-1000 mg/kg, ip) inhibited the convulsive effects of pentylenetetrazol (100 mg/kg, ip) in mice. EDA (100-1000 mg/kg, ip) incr the convulsion threshold to the iv infusion of 3 convulsants in the order pentylenetetrazol > bicuculline > strychnine.

A 37-yr-old pt sensitized to ethylenediamine by topical use of a steroid cream for scaly rash, developed an itchy morbilliform rash affecting the whole body following piperazine citrate therapy for threadworms.

LC50 Pimephales promelas (fathead minnow) 115.7 mg/l/96 hr @ 22 °C (95% confidence limit 98.6-131.6 mg/l) /Static bioassay/

TLM: ORYZIAS LATIPES 1000 MG/L/24 HR /CONDITIONS OF BIOASSAY NOT SPECIFIED/

Toxicity Threshold (Cell Multiplication Inhibition Test) Uronema parduczi Chatton-Lwoff (protozoa) 52 mg/l /Conditions of bioassay not specified/

Toxicity Threshold (Cell Multiplication Inhibition Test) Scenedesmus quadricauda (green algae) 0.85 mg/l /Conditions of bioassay not specified/

For more Ecotoxicity Values (Complete) data for ETHYLENEDIAMINE (9 total), please visit the HSDB record page.

TERRESTRIAL FATE: Based on a classification scheme(1), an average Koc value of 4766(2) indicates that ethylenediamine is expected to have slight mobility in soil(SRC). Volatilization of ethylenediamine from moist soil surfaces is not expected to be an important fate process(SRC) given a Henry's Law constant of 1.73X10-9 atm-cu m/mole(3). The potential for volatilization of ethylenediamine from dry soil surfaces may exist based upon a vapor pressure of 12.1 mm Hg(4). However, adsorption to soil may attenuate volatilization(SRC). Based on screening studies(5-7), biodegradation is expected to be the most important degradation process for this compound but no experimental rates in soil are available. Ethylenediamine may also form stable complexes with metal ions(8) in soil, but again, experimental data are lacking(SRC).

AQUATIC FATE: Based on a classification scheme(1), an average Koc value of 4766(2) indicates that ethylenediamine is expected to adsorb to suspended solids and sediment in water(SRC). Volatilization from water surfaces is not expected(3) based upon a Henry's Law constant of 1.73X10-9 atm-cu m/mole(4). As ethylenediamine has two primary amine groups, at the pH range found in most environmental waters, it is expected to be partially protonated; the dissociated form will not volatilize. According to a classification scheme(5), an estimated BCF of less than 1(SRC), from its log Kow(6) and a regression-derived equation(7), suggests the potential for bioconcentration in aquatic organisms is low. Based on screening studies(8-10), biodegradation is expected to be the most important degradation process for this compound but no experimental rates in water are available. Complexation of ethylenediamine with transition metals(11) in the water or reaction with humic materials(12) is possible(SRC).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), ethylenediamine, which has a vapor pressure of 12.1 mm Hg at 25 °C(2), is expected to exist solely as a vapor. Vapor-phase ethylenediamine is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC); the half-life for this reaction in air is estimated to be 6 hours(SRC), calculated from its rate constant of 6.3x10-11 cu cm/molecule-sec at 25 °C(3) using a structure estimation method(3). As ethylenediamine is miscible in water(4), washout by rain will also be an important removal process(SRC).

The substance can be absorbed into the body by inhalation, through the skin and by ingestion.

inhalation, skin absorption, ingestion, skin and/or eye contact

Cough. Sore throat. Shortness of breath. Burning sensation. Wheezing. Shortness of breath.

Redness. Pain. Burning sensation. Skin burns.

Redness. Pain. Blurred vision. Severe burns.

Burns in mouth and throat. Sore throat. Burning sensation. Abdominal pain. Shock or collapse.

irritation nose, respiratory system; sensitization dermatitis; asthma; liver, kidney damage

... A complete history and physical exam /is required/ ... to detect existing conditions that might place the exposed employee at increased risk, and to establish a baseline for future health monitoring. Persons with a history of asthma, allergies, or unknown sensitization to ethylenediamine would be expected to be at incr risk from exposure. Exam of the resp system, liver, and kidneys should be stressed. The skin should be examined for evidence of chronic disorders. ... Should be repeated on an annual basis.

Ethylenediamine has two primary amine groups and at the pH range found in most soils it is expected to be partially protonated given a pKa1 of 10.7 and a pKa2 of 7.6(1). An average Koc of 4766 (range=2071 to 6160) was measured for ethylenediamine in six different soils; five were from the vadose zone and one from an aquifer (saturated zone)(2). pH values ranged from 6.0 to 9.6 and the fraction of organic carbon from 0.0024 to 0.0391 for this group of soils. Soils with increased cation exchange capacity and organic content had greater affinity for ethylenediamine(2).

Ethylenediamine (CAS # 107-15-3) was evaluated for acute oral toxicity in groups of Fischer 344 rats (5/sex/group) administered single oral doses of 200, 400, 800, 1200, and 1800 mg/kg bodyweight as a monohydrochloride or dichlorohydride salt in water. Mortality was attributed to treatment at doses of 1800 mg/kg (9/10) and 1200 mg/kg (2/10); An LD50 was not calculated. Clinical signs observed in the 1200 mg/kg group included emaciation, bluish extremities and diarrhea. Upon necropsy, no gross pathology was observed.

This action promulgates standards of performance for equipment leaks of Volatile Organic Compounds (VOC) in the Synthetic Organic Chemical Manufacturing Industry (SOCMI). The intended effect of these standards is to require all newly constructed, modified, and reconstructed SOCMI process units to use the best demonstrated system of continuous emission reduction for equipment leaks of VOC, considering costs, non air quality health and environmental impact and energy requirements. Ethylenediamine is produced, as an intermediate or a final product, by process units covered under this subpart.

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. Ethylenediamine is an extremely hazardous substance (EHS) subject to reporting requirements when stored in amounts in excess of its threshold planning quantity (TPQ) of 10,000 lbs.

Persons in charge of vessels or facilities are required to notify the National Response Center (NRC) immediately, when there is a release of this designated hazardous substance, in an amount equal to or greater than its reportable quantity of 5000 lb or 2270 kg. The toll free number of the NRC is (800) 424-8802; In the Washington D.C. metropolitan area (202) 426-2675. The rule for determining when notification is required is stated in 40 CFR 302.4 (section IV. D.3.b).

Ethylenediamine is designated as a hazardous substance under section 311(b)(2)(A) of the Federal Water Pollution Control Act and further regulated by the Clean Water Act Amendments of 1977 and 1978. These regulations apply to discharges of this substance. This designation includes any isomers and hydrates, as well as any solutions and mixtures containing this substance.

Ethylenediamine

1

20000

Toxic chemical that can be released at a facility.

Used in the manufacture of chelating agents, fungicides, waxes, polyamide resins, and corrosion inhibitors. [ACGIH] Used as an emulsifier, an inhibitor in antifreeze solutions, and an additive to pharmaceuticals and textile lubricants; [Merck Index] Used in photography (color developing baths); [www.ci.tucson.az.us/arthazards/medium.html]

Textiles (Fiber & Fabric Manufacturing) [Category: Industry]

For Ethylenediamine (USEPA/OPP Pesticide Code: 004205) there are 0 labels match. /SRP: Not registered for current use in the U.S., but approved pesticide uses may change periodically and so federal, state and local authorities must be consulted for currently approved uses./

Solvent for casein, albumin, shellac, and sulfur; emulsifier; stabilizing rubber latex; as inhibitor in antifreeze solutions; in textile lubricants; pharmaceutic aid (aminophylline injection stabilizer)

In prepn of dyes, synthetic waxes, resins, insecticides and asphalt wetting agents

Use in manuf of weed killers; use in manuf of surfactants, emulsifying agents, wetting agents, dispersants, corrosion inhibitors, detergents, and textile surface treatments

(1972) 7.31X10+9 G

(1975) 1.43X10+9 G

(1984) 1.13X10+10 g

(1972) NEGLIGIBLE

(1975) 2.33X10+8 G

(1984) 1.09X10+9 g

2023: 100,000,000 - <500,000,000 lb

1,2-Diaminoethane is produced in large quantities, 26,509,000 kg in 1993.

(1972) 2.70X10+10 G

(1975) 3.0X10+10 G

CHEMICAL PROFILE: Ethylenediamine. Exports (mainly for carbamate fungicides), 45%; chelating agents (mainly EDA tetraacetic acid tetrasodium salt), 25%; oil and gas additives, 5%; polyamides, 5%; aminoethylethanol-amine-based surfactants, 5%; ethylene (bis)stearamide, 5%; others, including urethane additives, 10%.

CHEMICAL PROFILE: Ethylenediamine. Demand: 1987: 75 million lb; 1988: 77 million lb; 1992 /projected/: 85 million lb. (Includes exports, but not imports, totalling 4 to 5 million lb in 1987, or potential demand for the new Air Products facility).

Chemical Profile: Ethylenediamine. Exports (mainly for carbamate fungicides and tetraacetylethylenediamine (TAED)), 45%; chelating agents (mainly ethylenediaminetetraacetic acid (EDTA) and tetrasodium salt), 25%; lube oil and gas additives, 5%; nonreactive polyamide resins, 5%; aminoethylethanolamine-based surfactants, 5%; ethylene(bis)stearamide, 5%; others, including urethane additives, 10%.

Chemical Profile: Ethylenediamine. Demand: 1990: 80 million pounds; 1991: 82 million pounds; 1995: 90 million pounds. (Includes exports, which in 1990 are estimated at about 35 million pounds).

Lube oil additives, 35%; wet strength resins, 12%; chelating agents, 11%; epoxy curing agents, 9%; surfactants, 8%; polyamide resins, 6%; oil field chemicals, 5%; miscellaneous, including ethylene bis(stearamide), 14% /Ethyleneamines including EDA/

Catalytic reaction of ethylene glycol or ethylene dichloride and ammonia (Ni or Cu catalysts are used)

Ethylenediamine is produced mainly by reacting ethylene chloride with aqueous or liquid ammonia at about 100 °C.

The reaction of ethanolamine with ammonia ... In a continuous procedure, ethanolamine, ammonia, and hydrogen are passed over a cobalt catalyst at 20 MPa and 150-230 °C.

Reaction of ethylene oxide with ammonia

USEPA/OPP Pesticide Code 004205; Trade Names: Busan 881, component of (with 039002 and 063301), NCI-C60402.

Grades: Technical; USP, 97%; soln of various strenghts.

Grades or Purity: 99+%

Computer and Electronic Product Manufacturing

1,2-Ethanediamine: ACTIVE

Method of purification is redistillation

Guard against sticking of ground-glass joint due to strong alkaline.