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Move the victim into fresh air. If breathing is difficult, give oxygen. If not breathing, give artificial respiration and consult a doctor immediately. Do not use mouth to mouth resuscitation if the victim ingested or inhaled the chemical.
Take off contaminated clothing immediately. Wash off with soap and plenty of water. Consult a doctor.
Rinse with pure water for at least 15 minutes. Consult a doctor.
Rinse mouth with water. Do not induce vomiting. Never give anything by mouth to an unconscious person. Call a doctor or Poison Control Center immediately.
no data available
1. wash contaminated skin with soap & water. 2. flush contaminated eyes with copious amounts of fresh water for 15 minutes. 3. ingestions of small amounts (less than 10 mg/kg body weight) occurring less than an hour before treatment, are probably best treated by: a. syrup of ipecac, followed by 1-2 glasses of water. dose for adults & children over 12 years: 30 ml. dose for children under 12 years: 15 ml. b. activated charcoal: ... after vomiting stops. c. sodium or magnesium sulfate, 0.25 g/kg in tap water. pesticides of low or moderate toxicity
Use dry chemical, carbon dioxide or alcohol-resistant foam.
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Wear self-contained breathing apparatus for firefighting if necessary.
Avoid dust formation. Avoid breathing mist, gas or vapours.Avoid contacting with skin and eye. Use personal protective equipment.Wear chemical impermeable gloves. Ensure adequate ventilation.Remove all sources of ignition. Evacuate personnel to safe areas.Keep people away from and upwind of spill/leak.
Prevent further spillage or leakage if it is safe to do so. Do not let the chemical enter drains. Discharge into the environment must be avoided.
Collect and arrange disposal. Keep the chemical in suitable and closed containers for disposal. Remove all sources of ignition. Use spark-proof tools and explosion-proof equipment. Adhered or collected material should be promptly disposed of, in accordance with appropriate laws and regulations.
Handling in a well ventilated place. Wear suitable protective clothing. Avoid contact with skin and eyes. Avoid formation of dust and aerosols. Use non-sparking tools. Prevent fire caused by electrostatic discharge steam.
Store the container tightly closed in a dry, cool and well-ventilated place. Store apart from foodstuff containers or incompatible materials.
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Ensure adequate ventilation. Handle in accordance with good industrial hygiene and safety practice. Set up emergency exits and the risk-elimination area.
Wear tightly fitting safety goggles with side-shields conforming to EN 166(EU) or NIOSH (US).
Wear fire/flame resistant and impervious clothing. Handle with gloves. Gloves must be inspected prior to use. Wash and dry hands. The selected protective gloves have to satisfy the specifications of EU Directive 89/686/EEC and the standard EN 374 derived from it.
If the exposure limits are exceeded, irritation or other symptoms are experienced, use a full-face respirator.
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Light gray powder.
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196-201°C
266.5°C at 760mmHg
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115°C
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In water, 2.73X10+3 mg/l @ 23 deg C.
log Kow = 0.77
0.00862mmHg at 25°C
1.439g/cm3
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Cancer classification: Group D-Not classifiable as to human carcinogenicity.
no data available
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AEROBIC: 2,6-Dichlorobenzamide, present at 100 mg/l, reached 0%, 0.5%, 1.25%, 2.25%, 3.25%, 3.5%, and 5% degradation in 0, 25, 75, 105, 155, 180, and 300 days, respectively, using a grab soil inoculum(1). Using an organic rich soil (mixed with 50% sand) grab inoculum, 2,6-dichlorobenzamide, present at 400 mg/l, reached 0%, 3%, 6%, and 10% degradation after 0, 13, 46, and 206 days, respectively(1). 0%, 6%, and 16% of 2,6-dichlorobenzamide (initial concn = 400 mg/l) degraded after 0, 13, 205 days, respectively, using a grab sample of clay soil mixed with 50% sand(1). Using a clay-lime soil grab sample, 0.4%, 0.9%, 3%, and 6.1% of 2,6-dichlorobenzamide (initial concn = 1 mg/l) degraded after 4, 12, 51, and 110 days of incubation, respectively(2). These studies suggest that 2,6-dichlorobenzamide does not biodegrade rapidly in the environment(SRC).
A BCF of 10 was measured for Golden Ide fish after a 3 day equilibration period(1). According to a classification scheme(2), this BCF suggests the potential for bioconcentration in aquatic organisms is low(SRC). The BCF for algae ranges from <10 to 320 after a 1 day equilibration period(1,3).
A Koc of 30 was measured for 2,6-dichlorobenzamide on activated sludge(1). According to a classification scheme(2), this Koc value suggests that 2,6-dichlorobenzamide is expected to have very high mobility in soil(SRC). After aerobic ageing of dichlobenil on a treated silt loam soil column, 2,6-dichloronezamide, its degradate, was detected in the 25-30 cm segment at a concn of 28% of applied dichlobenil(3). In field study, an established commercial orchard (Town of Huron, NY) was treated with dichlobenil at 6 lb ai/A; the degradate 2,6-dichlorobenzamide was detected to a depth of 72 inches (max sampling depth)(3). Thus, 2,6-dichlorobenzamide is expected to leach into groundwater through soil(3).
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The material can be disposed of by removal to a licensed chemical destruction plant or by controlled incineration with flue gas scrubbing. Do not contaminate water, foodstuffs, feed or seed by storage or disposal. Do not discharge to sewer systems.
Containers can be triply rinsed (or equivalent) and offered for recycling or reconditioning. Alternatively, the packaging can be punctured to make it unusable for other purposes and then be disposed of in a sanitary landfill. Controlled incineration with flue gas scrubbing is possible for combustible packaging materials.
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: no data available
IMDG: no data available
IATA: no data available
ADR/RID: No
IMDG: No
IATA: No
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