0890 110 - WURTH RUBBER CARE SPRAY
Chemwatch Independent Material Safety Data Sheet
Issue Date: 8-Jan-2010
NC317ECP
CHEMWATCH 7505-62
Version No:5
0890 110 - WURTH RUBBER CARE SPRAY
"Manufacturer's Code 0890 110"
AEROSOLS
■ Application is by spray atomisation from a hand held aerosol pack.
The use of a quantity of material in an unventilated or confined space may result in increased exposure and an irritating atmosphere developing.
Used for the protection of rubber surfaces.
Company: Wurth Pty Ltd
Address:
4 Redwood Drive (abn 48 002 487 096)
Dingley
VIC, 3172
AUS
Telephone: +61 3 9552 9552
Telephone: 1800 331 603
Emergency Tel: 1300 657 765
Fax: +61 3 9551 2994
HAZARDOUS SUBSTANCE. DANGEROUS GOODS. According to NOHSC Criteria, and ADG Code.
None
| RISK | SAFETY |
| ■ Extremely flammable. | ■ Keep away from sources of ignition. No smoking. |
| ■ Irritating to skin. | ■ Avoid contact with skin. |
| ■ Risk of explosion if heated under confinement. | ■ To clean the floor and all objects contaminated by this material use water and detergent. |
| ■ Toxic to aquatic organisms may cause long-term adverse effects in the aquatic environment. | ■ This material and its container must be disposed of in a safe way. |
| ■ Vapours may cause drowsiness and dizziness. | ■ If swallowed IMMEDIATELY contact Doctor or Poisons Information Centre (show this container or label). |
| ■ Use appropriate container to avoid environment contamination. | |
| ■ Avoid release to the environment. Refer to special instructions/ safety data sheets. | |
| ■ This material and its container must be disposed of as hazardous waste. |
| NAME | CAS RN | % |
| naphtha petroleum, light, hydrotreated | 64742-49-0. | 30-50 |
| isopropanol | 67-63-0 | 1-<20^ |
| hydrocarbon propellant | 68476-85-7. | NotSpec^ |
· Not considered a normal route of entry.
· Avoid giving milk or oils.
· Avoid giving alcohol.
· If swallowed do NOT induce vomiting.
· If vomiting occurs, lean patient forward or place on left side (head-down position, if possible) to maintain open airway and prevent aspiration.
· Observe the patient carefully.
· Never give liquid to a person showing signs of being sleepy or with reduced awareness; i.e. becoming unconscious.
· Give water to rinse out mouth, then provide liquid slowly and as much as casualty can comfortably drink.
· Seek medical advice.
■ If aerosols come in contact with the eyes:
· Immediately hold the eyelids apart and flush the eye with fresh running water.
· Ensure complete irrigation of the eye by keeping eyelids apart and away from eye and moving the eyelids by occasionally lifting the upper and lower lids.
· Seek medical attention without delay; if pain persists or recurs seek medical attention.
· Removal of contact lenses after an eye injury should only be undertaken by skilled personnel.
■ If solids or aerosol mists are deposited upon the skin:
· Flush skin and hair with running water (and soap if available).
· Remove any adhering solids with industrial skin cleansing cream.
· DO NOT use solvents.
· Seek medical attention in the event of irritation.
■ If aerosols, fumes or combustion products are inhaled:
· Remove to fresh air.
· Lay patient down. Keep warm and rested.
· Prostheses such as false teeth, which may block airway, should be removed, where possible, prior to initiating first aid procedures.
· If breathing is shallow or has stopped, ensure clear airway and apply resuscitation, preferably with a demand valve resuscitator, bag-valve mask device, or pocket mask as trained. Perform CPR if necessary.
· Transport to hospital, or doctor.
■ Treat symptomatically. For acute or short term repeated exposures to petroleum distillates or related hydrocarbons: · Primary threat to life, from pure petroleum distillate ingestion and/or inhalation, is respiratory failure. · Patients should be quickly evaluated for signs of respiratory distress (e.g. cyanosis, tachypnoea, intercostal retraction, obtundation) and given oxygen. Patients with inadequate tidal volumes or poor arterial blood gases (pO2 50 mm Hg) should be intubated. · Arrhythmias complicate some hydrocarbon ingestion and/or inhalation and electrocardiographic evidence of myocardial injury has been reported; intravenous lines and cardiac monitors should be established in obviously symptomatic patients. The lungs excrete inhaled solvents, so that hyperventilation improves clearance. · A chest x-ray should be taken immediately after stabilisation of breathing and circulation to document aspiration and detect the presence of pneumothorax. · Epinephrine (adrenalin) is not recommended for treatment of bronchospasm because of potential myocardial sensitisation to catecholamines. Inhaled cardioselective bronchodilators (e.g. Alupent, Salbutamol) are the preferred agents, with aminophylline a second choice. · Lavage is indicated in patients who require decontamination; ensure use of cuffed endotracheal tube in adult patients. [Ellenhorn and Barceloux: Medical Toxicology].
■ SMALL FIRE: · Water spray, dry chemical or CO2 LARGE FIRE: · Water spray or fog.
· Alert Fire Brigade and tell them location and nature of hazard. · May be violently or explosively reactive. · Wear breathing apparatus plus protective gloves. · Prevent, by any means available, spillage from entering drains or water course. · If safe, switch off electrical equipment until vapour fire hazard removed. · Use water delivered as a fine spray to control fire and cool adjacent area. · DO NOT approach containers suspected to be hot. · Cool fire exposed containers with water spray from a protected location. · If safe to do so, remove containers from path of fire. · Equipment should be thoroughly decontaminated after use. When any large container (including road and rail tankers) is involved in a fire, consider evacuation by 100 metres in all directions.
· Liquid and vapour are highly flammable. · Severe fire hazard when exposed to heat or flame. · Vapour forms an explosive mixture with air. · Severe explosion hazard, in the form of vapour, when exposed to flame or spark. · Vapour may travel a considerable distance to source of ignition. · Heating may cause expansion or decomposition with violent container rupture. · Aerosol cans may explode on exposure to naked flames. · Rupturing containers may rocket and scatter burning materials. · Hazards may not be restricted to pressure effects. · May emit acrid, poisonous or corrosive fumes. · On combustion, may emit toxic fumes of carbon monoxide (CO). Combustion products include: carbon dioxide (CO2), other pyrolysis products typical of burning organic material. Contains low boiling substance: Closed containers may rupture due to pressure buildup under fire conditions.
· Avoid contamination with oxidising agents i.e. nitrates, oxidising acids, chlorine bleaches, pool chlorine etc. as ignition may result.
2YE
Gas tight chemical resistant suit.
· Clean up all spills immediately. · Avoid breathing vapours and contact with skin and eyes. · Wear protective clothing, impervious gloves and safety glasses. · Shut off all possible sources of ignition and increase ventilation. · Wipe up. · If safe, damaged cans should be placed in a container outdoors, away from all ignition sources, until pressure has dissipated. · Undamaged cans should be gathered and stowed safely.
· Clear area of personnel and move upwind. · Alert Fire Brigade and tell them location and nature of hazard. · May be violently or explosively reactive. · Wear breathing apparatus plus protective gloves. · Prevent, by any means available, spillage from entering drains or water courses · No smoking, naked lights or ignition sources. · Increase ventilation. · Stop leak if safe to do so. · Water spray or fog may be used to disperse / absorb vapour. · Absorb or cover spill with sand, earth, inert materials or vermiculite. · If safe, damaged cans should be placed in a container outdoors, away from ignition sources, until pressure has dissipated. · Undamaged cans should be gathered and stowed safely. · Collect residues and seal in labelled drums for disposal.
Personal Protective Equipment advice is contained in Section 8 of the MSDS.
· Avoid all personal contact, including inhalation.
· Wear protective clothing when risk of exposure occurs.
· Use in a well-ventilated area.
· Prevent concentration in hollows and sumps.
· DO NOT enter confined spaces until atmosphere has been checked.
· Avoid smoking, naked lights or ignition sources.
· Avoid contact with incompatible materials.
· When handling, DO NOT eat, drink or smoke.
· DO NOT incinerate or puncture aerosol cans.
· DO NOT spray directly on humans, exposed food or food utensils.
· Avoid physical damage to containers.
· Always wash hands with soap and water after handling.
· Work clothes should be laundered separately.
· Use good occupational work practice.
· Observe manufacturer's storing and handling recommendations.
· Atmosphere should be regularly checked against established exposure standards to ensure safe working conditions are maintained.
· Aerosol dispenser.
· Check that containers are clearly labelled.
· Avoid reaction with oxidising agents.
· Keep dry to avoid corrosion of cans. Corrosion may result in container perforation and internal pressure may eject contents of can.
· Store in original containers in approved flammable liquid storage area.
· DO NOT store in pits, depressions, basements or areas where vapours may be trapped.
· No smoking, naked lights, heat or ignition sources.
· Keep containers securely sealed. Contents under pressure.
· Store away from incompatible materials.
· Store in a cool, dry, well ventilated area.
· Avoid storage at temperatures higher than 40 deg C.
· Store in an upright position.
· Protect containers against physical damage.
· Check regularly for spills and leaks.
· Observe manufacturer's storing and handling recommendations.
| Source | Material | TWA ppm | TWA mg/m³ | STEL ppm | STEL mg/m³ | Notes |
| ___________ | ___________ | _______ | _______ | _______ | _______ | _______ |
| Australia Exposure Standards | naphtha petroleum, light, hydrotreated (Petrol (gasoline)) | 900 | (see Chapter 16) | |||
| Australia Exposure Standards | isopropanol (Isopropyl alcohol) | 400 | 983 | 500 | 1230 | |
| Australia Exposure Standards | hydrocarbon propellant (LPG (liquified petroleum gas)) | 1000 | 1800 |
0890 110 - WURTH RUBBER CARE SPRAY: Not available NAPHTHA PETROLEUM, LIGHT, HYDROTREATED: ■ Odour Threshold Value: 34 ppm (detection), 97 ppm (recognition) NOTE: Detector tubes for benzene, measuring in excess of 0.5 ppm, are commercially available. The relative quality of epidemiological data and quantitative health risk assessments related to documented and theoretical leukaemic deaths constitute the basis of the TLV-recommendation. One study [Dow Chemical] demonstrates a significant fourfold increase in myelogenous leukaemia for workers exposed to average benzene concentrations of about 5 ppm for an average of 9 years and that 2 out of four individuals in the study who died from leukaemia were characterised as having been exposed to average benzene levels below 2 ppm. Based on such findings the estimated risk of leukaemia in workers exposed at daily benzene concentrations of 10 ppm for 40 years is 155 times that of unexposed workers; at 1 ppm the risk falls to 1.7 times whilst at 0.1 ppm the risk is about the same in the two groups. A revision of the TLV-TWA to 0.1 ppm was proposed in 1990 but this has been revised upwards as result of industry initiatives. Typical toxicities displayed following inhalation: · At 25 ppm (8 hours): no effect · 50-150 ppm: signs of intoxication within 5 hours · 500-1500 ppm: signs of intoxication within 1 hour · 7500 ppm: severe intoxication within 30-60 minutes · 20000 ppm: fatal within 5-10 minutes Some jurisdictions require that health surveillance be conducted on occupationally exposed workers. Some surveillance should emphasise (i) demography, occupational and medical history and health advice (ii) baseline blood sample for haematological profile (iii) records of personal exposure. for heptane (all isomers) The TLV-TWA is protective against narcotic and irritant effects which are greater than those of pentane or n-hexane but less than those of octane. The TLV-TWA applies to all isomers. Inhalation by humans of 1000 ppm for 6 minutes produced slight dizziness. Higher concentrations for shorter periods produce marked vertigo, incoordination and hilarity. Signs of central nervous system depression occur in the absence of mucous membrane irritation. Brief exposures to high levels (5000 ppm for 4 minutes) produce nausea, loss of appetite and a "gasoline-like" taste in the mouth that persists for many hours after exposure ceases. Odour threshold: 0.25 ppm. The TLV-TWA is protective against ocular and upper respiratory tract irritation and is recommended for bulk handling of gasoline based on calculations of hydrocarbon content of gasoline vapour. A STEL is recommended to prevent mucous membrane and ocular irritation and prevention of acute depression of the central nervous system. Because of the wide variation in molecular weights of its components, the conversion of ppm to mg/m3 is approximate. Sweden recommends hexane type limits of 100 ppm and heptane and octane type limits of 300 ppm. Germany does not assign a value because of the widely differing compositions and resultant differences in toxic properties. Odour Safety Factor (OSF) OSF=0.042 (gasoline). for petroleum distillates: CEL TWA: 500 ppm, 2000 mg/m3 (compare OSHA TWA).
■ No special equipment for minor exposure i.e. when handling small quantities. OTHERWISE: For potentially moderate or heavy exposures: · Safety glasses with side shields. · NOTE: Contact lenses pose a special hazard; soft lenses may absorb irritants and ALL lenses concentrate them.
· Neoprene rubber gloves. · No special equipment needed when handling small quantities. · OTHERWISE: · For potentially moderate exposures: · Wear general protective gloves, eg. light weight rubber gloves. · For potentially heavy exposures: · Wear chemical protective gloves, eg. PVC. and safety footwear.
■ No special equipment needed when handling small quantities. OTHERWISE: · Overalls. · Skin cleansing cream. · Eyewash unit. · Do not spray on hot surfaces. · The clothing worn by process operators insulated from earth may develop static charges far higher (up to 100 times) than the minimum ignition energies for various flammable gas-air mixtures. This holds true for a wide range of clothing materials including cotton. · Avoid dangerous levels of charge by ensuring a low resistivity of the surface material worn outermost. BRETHERICK: Handbook of Reactive Chemical Hazards.
■ Selection of the Class and Type of respirator will depend upon the level of breathing zone contaminant and the chemical nature of the contaminant. Protection Factors (defined as the ratio of contaminant outside and inside the mask) may also be important.
| Breathing Zone Level ppm (volume) | Maximum Protection Factor | Half-face Respirator | Full-Face Respirator |
| 1000 | 10 | AX-AUS | - |
| 1000 | 50 | - | AX-AUS |
| 5000 | 50 | Airline * | - |
| 5000 | 100 | - | AX-2 |
| 10000 | 100 | - | AX-3 |
| 100+ | Airline** |
■ CARE: Use of a quantity of this material in confined space or poorly ventilated area, where rapid build up of concentrated atmosphere may occur, could require increased ventilation and/or protective gear. General exhaust is adequate under normal conditions. If risk of overexposure exists, wear SAA approved respirator. Correct fit is essential to obtain adequate protection. Provide adequate ventilation in warehouse or closed storage areas.
■ Supplied as an aerosol pack. Contents under PRESSURE. Contains highly flammable hydrocarbon propellant. Yellow liquid spray with a characteristic odour; does not mix with water.
Liquid.
Gas.
Does not mix with water.
Floats on water.
| State | Liquid | Molecular Weight | Not Applicable |
| Melting Range (ºC) | Not Available | Viscosity | Not Available |
| Boiling Range (ºC) | Not Available | Solubility in water (g/L) | Immiscible |
| Flash Point (ºC) | -60 (propellant) | pH (1% solution) | Not Applicable |
| Decomposition Temp (ºC) | Not Available | pH (as supplied) | Not Applicable |
| Autoignition Temp (ºC) | 510 (propellant) | Vapour Pressure (kPa) | 300 @ 20C |
| Upper Explosive Limit (%) | 32 | Specific Gravity (water=1) | 0.63 |
| Lower Explosive Limit (%) | 1.4 | Relative Vapour Density (air=1) | Not Available |
| Volatile Component (%vol) | Not Available | Evaporation Rate | Not Available |
· Elevated temperatures.
· Presence of open flame.
· Product is considered stable.
· Hazardous polymerisation will not occur.
For incompatible materials - refer to Section 7 - Handling and Storage.
■ Not normally a hazard due to physical form of product. Considered an unlikely route of entry in commercial/industrial environments. Ingestion of petroleum hydrocarbons can irritate the pharynx, oesophagus, stomach and small intestine, and cause swellings and ulcers of the mucous. Symptoms include a burning mouth and throat; larger amounts can cause nausea and vomiting, narcosis, weakness, dizziness, slow and shallow breathing, abdominal swelling, unconsciousness and convulsions. Damage to the heart muscle can produce heart beat irregularities, ventricular fibrillation (fatal) and ECG changes. The central nervous system can be depressed. Light species can cause a sharp tingling of the tongue and cause loss of sensation there. Aspiration can cause cough, gagging, pneumonia with swelling and bleeding.
■ Not considered to be a risk because of the extreme volatility of the gas. Direct eye contact with petroleum hydrocarbons can be painful, and the corneal epithelium may be temporarily damaged. Aromatic species can cause irritation and excessive tear secretion.
■ This material can cause inflammation of the skin oncontact in some persons. The material may accentuate any pre-existing dermatitis condition. Repeated exposure may cause skin cracking, flaking or drying following normal handling and use. Spray mist may produce discomfort. Open cuts, abraded or irritated skin should not be exposed to this material. Aromatic hydrocarbons may produce sensitivity and redness of the skin. They are not likely to be absorbed into the body through the skin but branched species are more likely to.
■ Inhalation of vapours may cause drowsiness and dizziness. This may be accompanied by sleepiness, reduced alertness, loss of reflexes, lack of co-ordination, and vertigo. The vapour is discomforting. WARNING:Intentional misuse by concentrating/inhaling contents may be lethal. Inhalation hazard is increased at higher temperatures. Inhalation of high concentrations of gas/vapour causes lung irritation with coughing and nausea, central nervous depression with headache and dizziness, slowing of reflexes, fatigue and inco-ordination.
■ Constant or exposure over long periods to mixed hydrocarbons may produce stupor with dizziness, weakness and visual disturbance, weight loss and anaemia, and reduced liver and kidney function. Skin exposure may result in drying and cracking and redness of the skin. Chronic exposure to lighter hydrocarbons can cause nerve damage, peripheral neuropathy, bone marrow dysfunction and psychiatric disorders as well as damage the liver and kidneys. WARNING: Aerosol containers may present pressure related hazards.
■ Not available. Refer to individual constituents. NAPHTHA PETROLEUM, LIGHT, HYDROTREATED: ■ unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
| Gasoline (NB: Overall evaluation upgraded from 3 to 2B with supporting evidence from other relevant data) | International Agency for Research on Cancer (IARC) - Agents Reviewed by the IARC Monographs | Group | 2B |
| Petroleum solvents | International Agency for Research on Cancer (IARC) - Agents Reviewed by the IARC Monographs | Group | 3 |
Refer to data for ingredients, which follows: NAPHTHA PETROLEUM, LIGHT, HYDROTREATED: 0890 110 - WURTH RUBBER CARE SPRAY: ■ DO NOT discharge into sewer or waterways. ■ Toxic to aquatic organisms. 0890 110 - WURTH RUBBER CARE SPRAY: /53#90wgk Water hazard class 1 (self-assessment): slightly hazardous to water. [Wurth] NAPHTHA PETROLEUM, LIGHT, HYDROTREATED: ■ Do NOT allow product to come in contact with surface waters or to intertidal areas below the mean high water mark. Do not contaminate water when cleaning equipment or disposing of equipment wash-waters. Wastes resulting from use of the product must be disposed of on site or at approved waste sites. ■ May cause long-term adverse effects in the aquatic environment. ■ For High Benzene Naphthas (HBNs) category: Environmental fate: The chemical components in HBNs are relatively volatile, and if released they would be expected to partition to the air phase to a significant extent. In the air, they are subject to rapid physical degradation through hydroxyl radical attack. Therefore, as a result of both biological and physical degradation processes, these products are not expected to persist in the environment Read across biodegradation data show that products in the HBNs have the potential to exhibit a high extent of biodegradability. The carbon number of products in this category ranges primarily between C5 to C11. Results for several chemicals, including benzene, with carbon numbers in this range that are contained by these products have been shown to biodegrade from 63 to 100% after 14 or 28 days, while results for several comparable, complex products containing several components range from 21 to 96% after 28 days. Hydrocarbons are not expected to hydrolyse at a measurable rate. Ecotoxicity: Read across aquatic toxicity data show that HBNs have the potential to produce a moderate level of toxicity in freshwater algae and acute toxicity in freshwater fish and invertebrates. The aquatic toxicity data fall within a narrow range of values regardless of their varying chemical class content and carbon number range. This is not unexpected, because the constituent chemicals of products in this category are neutral organic hydrocarbons whose toxic mode of action is non-polar narcosis. The mechanism of short-term toxicity for these chemicals is disruption of biological membrane function. The existing fish toxicity database for narcotic chemicals supports a critical body residue (CBR, the internal concentration that causes mortality) of between approximately 2-8 mmol/kg fish (wet weight) , supporting the assessment that these chemicals have equal potencies. When normalized to lipid content, the CBR is approximately 50 umol of hydrocarbon/g of lipid for most organisms . Because the products in this category are all complex mixtures containing relatively similar series of homologous chemicals, their short-term toxicities are expected to fall within the range of toxicity demonstrated by the individual chemicals. The fish and invertebrate acute and alga toxicity values for individual chemicals and complex products similar to those in this category fall within a range of approximately 1-64 mg/L and overlap between the three trophic levels. Because HBNs will range in paraffin, alkene, and/or aromatic carbon number content within approximately C5 to C11, a range in toxicity for products in this category is expected. Experimental data, this category will exhibit a moderate range of acute toxicity to fish and invertebrates and a moderate range of toxicity to algae. For representative chemicals and products, experimental acute fish toxicity values range between 2.5 to 46 mg/L for two species while acute invertebrate toxicity values range between 0.9 to 32 mg/L for one species . In comparison, alga toxicity values for one species range between 1.0 to 64 mg/L (for biomass and growth rate endpoints), while alga NOELR values range between 1.0 to 51 mg/L (for biomass or growth rate endpoints). ■ For benzene: log Kow: 1.95-2.15 log Koc: 1.7-2 Koc: 85 log Kom: 1.04-2.56 Half-life (hr) air: 2.4-501 Half-life (hr) H2O surface water: 4.81-384 Half-life (hr) H2O ground: 240-17280 Half-life (hr) soil: 48-922 Henry's Pa m3 /mol: 441-595 Henry's atm m3 /mol: 5.43E-03 BOD 5 if unstated: 2.18 COD: 0.25-2.8 ThOD: 3.1 BCF: 3.5-3.9 Log BCF: 0.54-1.48 Drinking Water Standards: hydrocarbon total: 10 ug/l (UK max.); benzene: 10 ug/l (WHO guideline) Soil Guidelines: Dutch Criteria: 0.05 mg/kg (detection limit) target; 1 mg/kg (intervention) Air Quality Standards: 1 ppb averaging time 1 year (UK) No safe level recommended due to carcinogenic properties (WHO Guideline) If benzene is released to the atmosphere it remains predominantly in the vapour phase. Vapour phase benzene is not subject to direct photolysis but reacts with photochemically produced hydroxyl radicals (half-life approximately 13.4 days). Reaction time in polluted atmospheres which contain nitrogen oxide (NO) or sulfur dioxide (SO2) is accelerated (half-life 4-6 hours); products of photooxidation include phenol, nitrophenols, nitrobenzene, formic acid and peroxyacetyl nitrates. In water, benzene is rapidly volatilised (half-life 2.7 hours). In soil benzene undergoes rapid volatilisation; it is not absorbed, to any appreciable degree, by sediments. Benzene does not bioaccumulate in the food chain. Environmental Fate Terrestrial fate: A Koc value of 85, indicates that benzene is expected to have high mobility in soil. Volatilisation of benzene from moist soil surfaces is expected to be an important fate process given a Henry's Law constant of 5.43xX10-3 atm-cu m/mole. The potential for volatilisation of benzene from dry soil surfaces may exist based upon a vapor pressure of 94.8 mm Hg. Benzene is expected to biodegrade in soils based on a biodegradation study in a base-rich para-brownish soil where 20 ppm benzene was 24% degraded in 1 week, 44% in 5 weeks, and 47% in 10 weeks. Anaerobic degradation of benzene in soil is not expected to be an important loss process based on various studies. In one study of chemical biotransformation under nitrate- and sulfate-reducing conditions, benzene was found to be stable for 60 days. In a related study, benzene did not undergo biodegradation in situ nor in laboratory controlled soil samples under denitrifying conditions. Aquatic fate: The Koc value of 85, indicates that benzene is not expected to adsorb to sediment and suspended solids in water. Volatilisation from water surfaces is expected based upon the Henry's Law constant. Using this Henry's Law constant, volatilisation half-lives for a model river and model lake are estimated to be 1 hr and 3.5 days, respectively. Anaerobic degradation of benzene in water is not expected to be an important loss process based on various studies. In one study of chemical biotransformation under nitrate- and sulfate-reducing conditions, benzene was found to be stable for 60 days. In aqueous solution, benzene will react with hydroxyl radical at a reaction rate of 7.8x10+9 L/mol sec; using the average OH radical concentration (1.0x10-17 molec/cu cm), benzene would have a half-life of 103 days. A BCF ranging from 1.1-20 suggests the potential for bioconcentration in aquatic organisms is low. Aquatic fate: Evaporation was the primary loss mechanism in winter in a mesocosm experiment which simulated a northern bay where the half-life was 13 days. In spring and summer the half-lives were 23 and 3.1 days, respectively. In these cases biodegradation plays a major role and takes about 2 days. However, acclimation is critical and this takes much longer in the colder water in spring. According to one experiment, benzene has a half-life of 17 days due to photodegradation which could contribute to benzene's removal. In situations of cold water, poor nutrients, or other conditions less conducive to microbial growth, photolysis will play a important role in degradation. The half-life of benzene in sea water is about 5 hrs based on its high Henry's Law constant of 5.56x10-3 atm-cu m/mole. Atmospheric fate: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere benzene, which has a vapour pressure of 94.8 mm Hg at 25 deg C, is expected to exist solely as a vapor in the ambient atmosphere. Vapour-phase benzene is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals; the half-life for this reaction in air is estimated to be 13 days, calculated from its rate constant of 1.23x10-12 cu cm/molecule-sec at 25 deg C. The half-life in polluted atmospheres which contain nitrogen oxides or sulfur dioxide has been observed to shorten to 4-6 hrs. Vapour-phase benzene is also degraded in the atmosphere by atmospheric ozone radicals at an extremely slow rate; the half-life for this reaction in air is estimated to be 170,000 days. The reaction rate of benzene with nitrate radical in the atmosphere is estimated to be less than 0.3x10-16 cu cm/molecule sec at 25 deg C; the half-life for this reaction in air is estimated to be greater than or equal to 111 days based on an average concentration of nitrate radicals of 2.4x10+8 molec/cu cm. Benzene has a maximum absorbance frequency of 253 nm suggesting that direct photolysis will not be an important degradation process. Due to benzene's high water solubility, it may be removed from the atmosphere by rainfall Ecotoxicity: Fish LC50 (96 h): bass (Morone saxatilis) 5.8-11 mg/l Fish LC50 24-96 h) fathead minnow (Pimephales promelus) 33-35 mg/l (softwater); 24-32 mg/l (hardwater); bluegill sunfish (Lepomis macrochirus) 22 mg/l; goldfish (Carassius auratus) 36 mg/l (softwater); mosquito fish (Gambusia affinis) 395 mg/l Fish LC50 (24-48 h): bluegill sunfish (Lepomis macrochirus) 20 mg/l Fish LC50 (24 h): goldfish (Carassius auratus) 46 mg/l; blue gill sunfish (Lepomis macrochirus) 34 mg/l Fish LC100 (2 h): blue gill sunfish (Lepomis macrochirus) 60 mg/l Fish LC50 (14 d): guppy (Poecilia reticulata) 63 mg/l Fish LC50 (1 h): brown trout yearlings (Salmo trutta) 12 mg/l (static assay) Ciliate LC100 (24 h): Tetrahymena pyriformis 12.8 mmole/l Grass shrimp (Palaemonetes pugio) LC50 (96 h): 27 ppm Shrimp (Crangon fransicorum) LC50 (96 h): 20 mg/l Crab larvae (Cancer magister) LC50 (96 h): 108 ppm Mexican axolotl (Ambystoma mexicanum) LC50 (48 h): 370 mg/l (3-4 weeks after hatching) Clawed toad LC50 (48 h): 190 mg/l (3-4 weeks after hatching). ■ For n-heptane: log Kow : 4.66 Koc : 2400-8100 Half-life (hr) air : 52.8 Half-life (hr) H2O surface water : 2.9-312 Henry's atm m3 /mol: 2.06 BOD 5 if unstated: 1.92 COD : 0.06 BCF : 340-2000 log BCF : 2.53-3.31 Environmental fate: Photolysis or hydrolysis of n-heptane are not expected to be important environmental fate processes. Biodegradation of n-heptane may occur in soil and water, however volatilisation and adsorption are expected to be more important fate processes. A high Koc (2400-8200) indicates n-heptane will be slightly mobile to immobile in soil. In aquatic systems n-heptane may partition from the water column to organic matter in sediments and suspended solids. The bioconcentration of n-heptane may be important in aquatic environments. the Henry's Law constant suggests rapid volatilisation from environmental waters and surface soils. The volatilisation half-lives from a model river and a model pond (the latter considers the effect of adsorption) have been estimated to be 2.9 hr and 13 days, respectively. n-Heptane is expected to exist entirely in the vapour phase in ambient air. Reactions with photochemically produced hydroxyl radicals in the atmosphere have been shown to be important (estimated half-life of 2.4 days calculated from its rate constant of 7.15x10-12 cu cm/molecule-sec at 25 deg C). Data also suggests that night-time reactions with nitrate radicals may contribute to the atmospheric transformation of n-heptane, especially in urban environments. n-Heptane does not contain chromophores that absorb at wavelengths >290 nm and therefore is not expected to be susceptible to direct photolysis by sunlight An estimated BCF of 2,000 using log Kow suggests the potential for bioconcentration in aquatic organisms is very high. Based on 100% degradation after 4 days in water inoculated with gasoline contaminated soil and 100% degradation after 25 days in water inoculated with activated sewage sludge, biodegradation is expected to be an important fate process for n-heptane in water. Ecotoxicity: Fish LC50 (48 h): goldfish (Carrasius auratus) 4 mg/l; golden orfe (Idus melanotus) 2940 mg/l; western mosquitofish (Gambusia affinis) 4924 mg/l Daphnia LC50 (24 h): >10 mg/l Daphnia EC50 (96 h): 82 mg/l (immobilisation) Opposum shrimp (Mysidopsis bahia) LC50 (96 h): 0.1 mg/l Snail EC50 (96 h): 472 mg/l.
· DO NOT allow wash water from cleaning or process equipment to enter drains.
· It may be necessary to collect all wash water for treatment before disposal.
· In all cases disposal to sewer may be subject to local laws and regulations and these should be considered first.
· Where in doubt contact the responsible authority.
· Consult State Land Waste Management Authority for disposal.
· Discharge contents of damaged aerosol cans at an approved site.
· Allow small quantities to evaporate.
· DO NOT incinerate or puncture aerosol cans.
· Bury residues and emptied aerosol cans at an approved site.
Labels Required: FLAMMABLE GAS
2YE (ADG7)
| Class or division: | 2 | Subsidiary risk: | None |
| UN No.: | 1950 | UN packing group: | None |
| Special provisions: | 63; 190; 277; 327; 344 | Packing Instructions: | None |
| Notes: | None | Limited quantities: | See SP 277 |
| Portable tanks and bulk containers - Instructions: | None | Portable tanks and bulk containers - Special provisions: | None |
| Packagings and IBCs - Packing instruction: | P003; LP02 | Packagings and IBCs - Special packing provisions: | PP17, PP87, L2 |
| Class or division: | 2 | Subsidiary risk: | None |
| UN No.: | 1950 | UN packing group: | None |
| ICAO/IATA Class: | 2.1 | ICAO/IATA Subrisk: | None |
| UN/ID Number: | 1950 | Packing Group: | - |
| Special provisions: | A145 |
| IMDG Class: | 2.1 | IMDG Subrisk: | SP63 |
| UN Number: | 1950 | Packing Group: | None |
| EMS Number: | F-D,S-U | Special provisions: | 63 190 277 327 959 |
| Limited Quantities: | See SP277 |
None
Regulations for ingredients
"Australia Hazardous Substances","Australia High Volume Industrial Chemical List (HVICL)","Australia Inventory of Chemical Substances (AICS)","International Council of Chemical Associations (ICCA) - High Production Volume List","OECD Representative List of High Production Volume (HPV) Chemicals"
| Ingredient Name | CAS |
| hydrocarbon propellant | 68476-85-7, 68476-86-8 |
■ Classification of the preparation and its individual components has drawn on official and authoritative sources as well as independent review by the Chemwatch Classification committee using available literature references.
A list of reference resources used to assist the committee may be found at:
www.chemwatch.net/references.
■ The (M)SDS is a Hazard Communication tool and should be used to assist in the Risk Assessment. Many factors determine whether the reported Hazards are Risks in the workplace or other settings. Risks may be determined by reference to Exposures Scenarios. Scale of use, frequency of use and current or available engineering controls must be considered.
This document is copyright. Apart from any fair dealing for the purposes of private study, research, review or
criticism, as permitted under the Copyright Act, no part may be reproduced by any process without written
permission from CHEMWATCH. TEL (+61 3) 9572 4700.
Issue Date: 8-Jan-2010
Print Date: 27-Jan-2010
This is the end of the MSDS.