Acute toxicity - Category 4, Oral
Hazardous to the aquatic environment, long-term (Chronic) - Category Chronic 2
H302 Harmful if swallowed
H411 Toxic to aquatic life with long lasting effects
P264 Wash ... thoroughly after handling.
P270 Do not eat, drink or smoke when using this product.
P273 Avoid release to the environment.
P301+P317 IF SWALLOWED: Get medical help.
P330 Rinse mouth.
P391 Collect spillage.
none
P501 Dispose of contents/container to an appropriate treatment and disposal facility in accordance with applicable laws and regulations, and product characteristics at time of disposal.
no data available
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
Skin contamination should be removed promptly by washing with soap and water. Contamination of the eyes should be treated immediately by prolonged flushing of the eyes with copious amounts of clean water. If dermal or ocular irritation persists, medical attention should be obtained without delay. Other herbicides
If material /is/ on fire or involved in /a/ fire do not extinguish fire unless flow can be stopped. Use water in flooding quantities as fog. Solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use "alcohol" foam, dry chemical or carbon dioxide. Carbamate pesticide, liquid, nos (compounds and preparations) (insecticides, other than agricultural, nec
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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.
A system for removing pesticides from the wash water produced by pesticide applicators as they clean their equipment has been developed. The first step is the flocculation/coagulation and sedimentation of the pesticide-contaminated wash water. The supernatant from the first step is then passed through activated carbon columns. Pesticides
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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Clear liquid
Slight aromatic odor
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272.8°C at 760mmHg
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118.8°C
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Miscible with common organic solvents, e.g. xylene, methyl isobutyl ketone, kerosene, acetone, ethanol
log Kow = 3.84 at 20 deg C
0.00596mmHg at 25°C
0.959g/cm3
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At pH 7, 50% loss occurs in 13 days at 40 deg C. Stable up to 200 deg C. Decomposed by sunlight.
Fire point: 124 deg c.
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When heated to decomposition it emits very toxic fumes of /nitrogen oxides and sulfur oxides/.
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AEROBIC: In soil, vernolate undergoes microbial decomposition to mercaptan, amine, carbon dioxide, and isopropanol(1). The half-life of vernolate in clay soil is 10-12 days(1). Vernolate has a short residual in soil with a typical field half-life of 12 days(2). The half-life in moist loam soil at 21-27 deg C was approximately 1.5 weeks(2). In sandy loam soil, the first and second aerobic soil half-lives were 40 days and 139 days(3). The half-life of vernolate (5 ppm) was 2-3 weeks both in Regina heavy clay (pH 7.5, 4.0% organic content) and Weyburn loam (pH 7.0, 6.5% organic content) at 25 deg C with water added to field capacity(4). Vernolate (1280 ppm) was 60% detoxified in 8 weeks at the optimal soil pH of 7.6 as determined by cucumber bioassays(5). Repeated vernolate use on a plot of soil resulted in enhanced degradation where adapted organisms degrade the pesticide faster(6).
An estimated BCF of 180 was calculated for vernolate(SRC), using a log Kow of 3.84(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is high(SRC), provided the compound is not metabolized by the organism(SRC).
Vernolate is adsorbed onto dry soil(1). An average Koc of 260 has been measured(1). The Koc values in 6 Hungarian soils (sandy loam, loam, and clay) ranged from 83 to 391(2). Measured Koc values of 259(3) and 214(4) have also been reported. According to a classification scheme(5), these Koc values suggest that vernolate is expected to have moderate to high mobility in soil. The leaching of vernolate incorporated in the upper 2 inch layer of soil was determined in 5 soils of widely different soil types having organic carbon contents ranging from 0.46 to 20.1% after two applications of 4 inches of water(6). Vernolate leached as far as the 6-9 inch layer in sandy loam (0.46% OC) and loamy sand (2.7% OC) soils, as far as the 3-6 inch layer in loam (3.2% OC) and clay (6.7% OC), and as far as the 0-3 inch layer in a peat soil (20.1% OC)(6). Leaching decreased with the clay content, as well as the organic carbon content of the soil(6).
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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: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Not dangerous goods. (For reference only, please check.)
IMDG: Not dangerous goods. (For reference only, please check.)
IATA: Not dangerous goods. (For reference only, please check.)
ADR/RID: Yes
IMDG: Yes
IATA: Yes
no data available
no data available