0890 100 010 - WURTH ENGINE GASKET

Chemwatch Material Safety Data Sheet

Issue Date: 12-Sep-2008

NC317ECP

CHEMWATCH 7504-18

Version No:4

Section 1 - CHEMICAL PRODUCT AND COMPANY IDENTIFICATION

PRODUCT NAME

0890 100 010 - WURTH ENGINE GASKET

PROPER SHIPPING NAME

FLAMMABLE LIQUID, TOXIC, N.O.S.
(contains ethyl acetate and m- cresol)

PRODUCT USE

The use of a quantity of material in an unventilated or confined space may result in
increased exposure and an irritating atmosphere developing. Before starting consider
control of exposure by mechanical ventilation. Used on engine gaskets to enhance sealing
quality.

SUPPLIER

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                  
                                      

Section 2 - HAZARDS IDENTIFICATION

STATEMENT OF HAZARDOUS NATURE

HAZARDOUS SUBSTANCE. DANGEROUS GOODS. According to the Criteria of NOHSC,
and the ADG Code.

POISONS SCHEDULE

S6

 

RISK SAFETY
Highly flammable. Keep locked up.
Harmful in contact with skin and if swallowed. Keep away from sources of ignition. No smoking.
Causes burns. Do not breathe gas/ fumes/ vapour/ spray.
Risk of serious damage to eyes. Avoid contact with eyes.
HARMFUL - May cause lung damage if swallowed. Wear suitable protective clothing.
Vapours may cause drowsiness and dizziness. Use only in well ventilated areas.
Keep container in a well ventilated place.
Do not empty into drains.
To clean the floor and all objects contaminated by this material use water and detergent.
Keep container tightly closed.
Take off immediately all contaminated clothing.
In case of accident or if you feel unwell IMMEDIATELY contact Doctor or Poisons Information Centre (show label if possible).
This material and its container must be disposed of as hazardous waste.

 

Section 3 - COMPOSITION / INFORMATION ON INGREDIENTS

NAME CAS RN %
ethyl acetate 141-78-6 20-40
ethanol 64-17-5 5-20
acetone 67-64-1 1-19
n- butyl acetate 123-86-4 1-14
m- cresol 108-39-4 1-4^
o- cresol 95-48-7 ^
p- cresol 106-44-5 ^
phenol 108-95-2 0-0.9^
xylenols 1300-71-6 <0.2^

Section 4 - FIRST AID MEASURES

SWALLOWED

· 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.

EYE

If this product comes in contact with the eyes:
· Immediately hold eyelids apart and flush the eye continuously with 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.
· Continue flushing until advised to stop by the Poisons Information Centre or a doctor, or for at least 15 minutes.
· Transport to hospital or doctor without delay.
· Removal of contact lenses after an eye injury should only be undertaken by skilled personnel.

SKIN

If skin contact occurs:
· Immediately remove all contaminated clothing, including footwear.
· Flush skin and hair with running water (and soap if available).
· Seek medical attention in event of irritation.

INHALED

· If fumes or combustion products are inhaled remove from contaminated area.
· 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.
· Apply artificial respiration if not breathing, preferably with a demand valve resuscitator, bag-valve mask device,
or pocket mask as trained. Perform CPR if necessary.
· Transport to hospital, or doctor.

NOTES TO PHYSICIAN

Treat symptomatically.

Section 5 - FIRE FIGHTING MEASURES

EXTINGUISHING MEDIA

· Alcohol stable foam.
· Dry chemical powder.
· BCF (where regulations permit).
· Carbon dioxide.
· Water spray or fog - Large fires only.

FIRE FIGHTING

· Alert Fire Brigade and tell them location and nature of hazard.
· May be violently or explosively reactive.
· Wear full body protective clothing with breathing apparatus.
· Prevent, by any means available, spillage from entering drains or water course.
· Consider evacuation (or protect in place).
· Fight fire from a safe distance, with adequate cover.
· 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.
· Avoid spraying water onto liquid pools.
· 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.
When any large container (including road and rail tankers) is involved in a fire,
consider evacuation by  1000  metres in all directions.

FIRE/EXPLOSION HAZARD

WARNING: In use may form flammable/ explosive vapour-air mixtures.
WARNING:
· Can become highly flammable in use.
· Avoid evaporation.
· Liquid and vapour are highly flammable.
· Severe fire hazard when exposed to heat, flame and/or oxidisers.
· Vapour may travel a considerable distance to source of ignition.
· Heating may cause expansion or decomposition leading to violent rupture of containers.
· On combustion, may emit toxic fumes of carbon monoxide (CO).
Combustion products include: carbon dioxide (CO2),  other pyrolysis products typical of
burning organic material.

FIRE INCOMPATIBILITY

· Avoid contamination with oxidising agents i.e. nitrates, oxidising acids, chlorine
bleaches, pool chlorine etc. as ignition may result.

HAZCHEM: 3WE

Section 6 - ACCIDENTAL RELEASE MEASURES

EMERGENCY PROCEDURES

MINOR SPILLS

· Remove all ignition sources.
· Clean up all spills immediately.
· Avoid breathing vapours and contact with skin and eyes.
· Control personal contact by using protective equipment.
· Contain and absorb small quantities with vermiculite or other absorbent material.
· Wipe up.
· Collect residues in a flammable waste container.

MAJOR SPILLS

·  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 full body protective clothing with breathing apparatus.
·  Prevent, by any means available, spillage from entering drains or water course.
·  Consider evacuation (or protect in place).
·  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 vapour.
·  Contain or absorb spill with sand, earth or vermiculite.
·  Use only spark-free shovels and explosion proof equipment.
·  Collect recoverable product into labelled containers for recycling.
·  Collect solid residues and seal in labelled drums for disposal.
·  Wash area and prevent runoff into drains.
·  After clean up operations, decontaminate and launder all protective clothing and 
equipment before storing and re-using.
·  If contamination of drains or waterways occurs, advise emergency services.

EMERGENCY RESPONSE PLANNING GUIDELINES (ERPG)

The maximum airborne concentration below which it is believed that nearly all individuals could be exposed
    for up to one hour WITHOUT experiencing or developing

  life-threatening health effects is:
    n-butyl acetate  3000ppm
    phenol           200ppm

  irreversible or other serious effects or symptoms which could impair an individual's ability to take
    protective action is:
    n-butyl acetate  200ppm
    phenol           50ppm

  other than mild, transient adverse effects without perceiving a clearly defined odour is:
    n-butyl acetate  5ppm
    phenol           10ppm

American Industrial Hygiene Association (AIHA)

Ingredients considered according to the following cutoffs
  Very Toxic (T+)  >= 0.1%          Toxic (T)       >= 3.0%
  R50              >= 0.25%         Corrosive (C)   >= 5.0%
  R51              >= 2.5%
else               >= 10%
where percentage is percentage of ingredient found in the mixture

 

Personal Protective Equipment advice is contained in Section 8 of the MSDS.

Section 7 - HANDLING AND STORAGE

PROCEDURE FOR HANDLING

Contains low boiling substance:
Storage in sealed containers may result in pressure buildup causing violent rupture of containers not rated
appropriately.
· Check for bulging containers.
· Vent periodically
· Always release caps or seals slowly to ensure slow dissipation of vapours.
· 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, heat or ignition sources.
· When handling, DO NOT eat, drink or smoke.
· Vapour may ignite on pumping or pouring due to static electricity.
· DO NOT use plastic buckets.
· Earth and secure metal containers when dispensing or pouring product.
· Use spark-free tools when handling.
· Avoid contact with incompatible materials.
· Keep containers securely sealed.
· 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.
· DO NOT allow clothing wet with material to stay in contact with skin.

SUITABLE CONTAINER

· Packing as supplied by manufacturer.
· Plastic containers may only be used if approved for flammable liquid.
· Check that containers are clearly labelled and free from leaks.
· For low viscosity materials (i) : Drums and jerry cans must be of the non-removable head type. (ii) : Where a can
is to be used as an inner package, the can must have a screwed enclosure.
· For materials with a viscosity of at least 2680 cSt. (23 deg. C)
· For manufactured product having a viscosity of at least 250 cSt. (23 deg. C)
· Manufactured product that requires stirring before use and having a viscosity of at least 20 cSt (25 deg. C)
(i) : Removable head packaging;
(ii) : Cans with friction closures and
(iii) : low pressure tubes and cartridges may be used.
· Where combination packages are used, and the inner packages are of glass, there must be sufficient inert
cushioning material in contact with inner and outer packages
· In addition, where inner packagings are glass and contain liquids of packing group I there must be sufficient
inert absorbent to absorb any spillage, unless the outer packaging is a close fitting moulded plastic box and the
substances are not incompatible with the plastic.

STORAGE INCOMPATIBILITY

· Avoid reaction with oxidising agents.

STORAGE REQUIREMENTS

· Store in original containers in approved flame-proof area.
· No smoking, naked lights, heat or ignition sources.
· DO NOT store in pits, depressions, basements or areas where vapours may be trapped.
· Keep containers securely sealed.
· Store away from incompatible materials in a cool, dry well ventilated area.
· Protect containers against physical damage and check regularly for leaks.
· Observe manufacturer's storing and handling recommendations.

Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

EXPOSURE CONTROLS

SourceMaterialTWA ppmTWA mg/m³STEL ppmSTEL mg/m³
________________________________________________________________
Australia Exposure Standardsethyl acetate (Ethyl acetate)2007204001440
Australia Exposure Standardsethanol (Ethyl alcohol)10001880
Australia Exposure Standardsacetone (Acetone)500118510002375
Australia Exposure Standardsn-butyl acetate (n-Butyl acetate)150713200950
Australia Exposure Standardsm-cresol (Cresol, all isomers)522
Australia Exposure Standardso-cresol (Cresol, all isomers)522
Australia Exposure Standardsp-cresol (Cresol, all isomers)522
Australia Exposure Standardsphenol (Phenol)14
ENDOELTABLE The following materials had no OELs on our records
• xylenols: CAS:1300-71-6

 

EMERGENCY EXPOSURE LIMITS

Material Revised IDLH Value (mg/m3) Revised IDLH Value (ppm)
ethyl acetate 2,000 [LEL]
ethanol 3,300 [LEL]
acetone 2,500 [LEL]
n-butyl acetate 1,700 [LEL]
NOTES Values marked LEL indicate that the IDLH was based on 10% of the lower explosive limit for safety considerations even though the relevant toxicological data indicated that irreversible health effects or impairment of escape existed only at higher concentrations.

 

MATERIAL DATA

Not available. Refer to individual constituents.

INGREDIENT DATA

ETHYL ACETATE:
   
   Odour Threshold Value: 6.4-50 ppm (detection), 13.3-75 ppm (recognition)
   The TLV-TWA provides a significant margin of safety from the standpoint of
   adverse health effects. Unacclimated subjects found the odour
   objectionably strong at 200 ppm. Mild nose, eye and throat irritation was
   experienced at 400 ppm. Workers exposed regularly at concentrations
   ranging from 375 ppm to 1500 ppm for several months showed no unusual
   signs or symptoms.

ETHANOL:
   For ethanol:
   Odour Threshold Value: 49-716 ppm (detection), 101 ppm (recognition)
   Eye and respiratory tract irritation do not appear to occur at exposure levels of less 
than 5000 ppm and the TLV-TWA is thought to provide an adequate margin of safety against 
such effects. Experiments in man show that inhalation of 1000 ppm caused slight symptoms 
of poisoning and 5000 ppm caused strong stupor and morbid sleepiness. Subjects exposed to 
5000 ppm to 10000 ppm experienced smarting of the eyes and nose and coughing. Symptoms 
disappeared within minutes. Inhalation also causes local irritating effects to the eyes 
and upper respiratory tract, headaches, sensation of heat intraocular tension, stupor, 
fatigue and a need to sleep. At 15000 ppm there was continuous lachrymation and coughing.

ACETONE:
   Odour Threshold Value: 3.6 ppm (detection), 699 ppm (recognition)
   Saturation vapour concentration: 237000 ppm @ 20 C
   NOTE: Detector tubes measuring in excess of 40 ppm, are available.
   Exposure at or below the recommended TLV-TWA is thought to protect the worker against 
mild irritation associated with brief exposures and the bioaccumulation, chronic 
irritation of the respiratory tract and headaches associated with long-term acetone 
exposures. The NIOSH REL-TWA is substantially lower and has taken into account slight 
irritation experienced by volunteer subjects at 300 ppm. Mild irritation to acclimatised 
workers begins at about 750 ppm - unacclimatised subjects will experience irritation at 
about 350-500 ppm but acclimatisation can occur rapidly. Disagreement between the peak 
bodies is based largely on the view by ACGIH that widespread use of acetone, without 
evidence of significant adverse health effects at higher concentrations, allows 
acceptance of a higher limit.
   Half-life of acetone in blood is 3 hours which means that no adjustment for shift-
length has to be made with reference to the standard 8 hour/day, 40 hours per week 
because body clearance occurs within any shift with low potential for accumulation.
   A STEL has been established to prevent excursions of acetone vapours that could cause 
depression of the central nervous system.
   Odour Safety Factor(OSF)
   OSF=38 (ACETONE).

N-BUTYL ACETATE:
   
   Odour Threshold Value: 0.0063 ppm (detection), 0.038-12 ppm (recognition)
   Exposure at or below the recommended TLV-TWA is thought to prevent
   significant irritation of the eyes and respiratory passages as well as
   narcotic effects. In light of the lack of substantive evidence regarding
   teratogenicity and a review of acute oral data a STEL is considered
   inappropriate.

PERSONAL PROTECTION

EYE

· Safety glasses with side shields.
· Chemical goggles.
· Contact lenses may pose a special hazard; soft contact lenses may absorb and 
concentrate irritants. A written policy document, describing the wearing of lens or 
restrictions on use, should be created for each workplace or task. This should include a 
review of lens absorption and adsorption for the class of chemicals in use and an account 
of injury experience. Medical and first-aid personnel should be trained in their removal 
and suitable equipment should be readily available. In the event of chemical exposure, 
begin eye irrigation immediately and remove contact lens as soon as practicable. Lens 
should be removed at the first signs of eye redness or irritation - lens should be 
removed in a clean environment only after workers have washed hands thoroughly. [CDC 
NIOSH Current Intelligence Bulletin 59].

HANDS/FEET

· Wear chemical protective gloves, eg. PVC.
· Wear safety footwear or safety gumboots, eg. Rubber.

OTHER

· Overalls.
· PVC Apron.
· PVC protective suit may be required if exposure severe.
· Eyewash unit.
· Ensure there is ready access to a safety shower.

RESPIRATOR

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 P -
1000 50 - AX-AUS P
5000 50 Airline * -
5000 100 - AX-2 P
10000 100 - AX-3 P
100+ Airline**
* - Continuous Flow ** - Continuous-flow or positive pressure demand. The local concentration of material, quantity and conditions of use determine the type of personal protective equipment required. For further information consult site specific CHEMWATCH data (if available), or your Occupational Health and Safety Advisor.

ENGINEERING CONTROLS

For flammable liquids and flammable gases, local exhaust ventilation or a process 
enclosure ventilation system may be required. Ventilation equipment should be explosion-
resistant.

Section 9 - PHYSICAL AND CHEMICAL PROPERTIES

APPEARANCE

Yellow highly flammable liquid with a characteristic odour; does not
mix with water.

PHYSICAL PROPERTIES

Does not mix with water.
Floats on water.

 

Molecular Weight: Not Applicable Boiling Range (ºC): 55
Melting Range (ºC): Not Available Specific Gravity (water=1): 0.97
Solubility in water (g/L): Immiscible pH (as supplied): Not Applicable
pH (1% solution): Not Applicable Vapour Pressure (kPa): 24.7 @ 20C
Volatile Component (%vol): >60 Evaporation Rate: Not Available
Relative Vapour Density (air=1): Not Available Flash Point (ºC): -19
Lower Explosive Limit (%): 2.1 Upper Explosive Limit (%): 15
Autoignition Temp (ºC): 370 Decomposition Temp (ºC): Not Available
State: LIQUID Viscosity: Not Available

Section 10 - CHEMICAL STABILITY AND REACTIVITY INFORMATION

CONDITIONS CONTRIBUTING TO INSTABILITY

· Presence of incompatible materials.
· Product is considered stable.
· Hazardous polymerisation will not occur.

Section 11 - TOXICOLOGICAL INFORMATION

POTENTIAL HEALTH EFFECTS

ACUTE HEALTH EFFECTS

SWALLOWED

Accidental ingestion of the material may be harmful; animal experiments indicate that ingestion of 
less than 150 gram may be fatal or may produce serious damage to the health of the individual.

EYE

The material may produce severe irritation to the eye causing pronounced inflammation. Repeated or 
prolonged exposure to irritants may produce conjunctivitis.

SKIN

Skin contact with the material may be harmful; systemic effects may result following absorption.
Entry into the blood-stream, through, for example, cuts, abrasions or lesions, may produce 
systemic injury with harmful effects. Examine the skin prior to the use of the material and ensure 
that any external damage is suitably protected.
The material may cause severe skin irritation after prolonged or repeated exposure and may produce 
on contact skin redness, swelling, the production of vesicles, scaling and thickening of the skin. 
Repeated exposures may produce severe ulceration.

INHALED

The material may produce respiratory tract irritation, and result in damage to the lung including 
reduced lung function.
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.

CHRONIC HEALTH EFFECTS

Prolonged or continuous skin contact with the liquid may cause defatting with drying, cracking, 
irritation and dermatitis following.
As with any chemical product, contact with unprotected bare skin; inhalation of vapour, mist or 
dust in work place atmosphere; or ingestion in any form, should be avoided by observing good 
occupational work practice.
Chronic exposure of o-cresol to the skin can cause facial peripheral nerve damage, impairment of 
renal function and even necrosis of the liver and kidneys.

TOXICITY AND IRRITATION

Not available. Refer to individual constituents.

ETHYL ACETATE:
unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.

TOXICITY IRRITATION
Oral (rat) LD50: 5620 mg/kg Eye (human): 400 ppm
Inhalation (rat) LC50: 1600 ppm/8h
Inhalation (human) TCLo: 400 ppm
Inhalation (Human) TCLo: 400 ppm/4h
Oral (Mouse) LD50: 4100 mg/kg
Intraperitoneal (Mouse) LD50: 709 mg/kg
Oral (Rabbit) LD50: 4935 mg/kg
Oral (Guinea) pig: LD50 5500 mg/kg
ETHANOL: unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Oral (rat) LD50: 7060 mg/kg Skin (rabbit):20 mg/24hr- Moderate
Oral (human) LDLo: 1400 mg/kg Skin (rabbit):400 mg (open)-Mild
Oral (man) TDLo: 50 mg/kg Eye (rabbit):100mg/24hr- Moderate
Oral (man) TDLo: 1.40 mg/kg Eye (rabbit): 500 mg SEVERE
Oral (woman) TDLo: 256 mg/kg/12 wks
Inhalation (rat) LC50: 20,000 ppm/10h
Inhalation (rat) LC50: 64000 ppm/4h
The material may cause skin irritation after prolonged or repeated exposure and may produce on contact skin redness, swelling, the production of vesicles, scaling and thickening of the skin. ACETONE: unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Oral (man) TDLo: 2857 mg/kg Eye (human): 500 ppm - Irritant
Oral (rat) LD50: 5800 mg/kg Eye (rabbit): 3.95 mg - SEVERE
Inhalation (human) TCLo: 500 ppm Eye (rabbit): 20mg/24hr -Moderate
Inhalation (man) TCLo: 12000 ppm/4 hr Skin (rabbit):395mg (open) - Mild
Inhalation (man) TCLo: 10 mg/m³/6 hr Skin (rabbit): 500 mg/24hr - Mild
Inhalation (rat) LC50: 50100 mg/m³/8 hr
Dermal (rabbit) LD50: 20000 mg/kg
The material may cause skin irritation after prolonged or repeated exposure and may produce on contact skin redness, swelling, the production of vesicles, scaling and thickening of the skin. for acetone: The acute toxicity of acetone is low. Acetone is not a skin irritant or sensitiser but is a defatting agent to the skin. Acetone is an eye irritant. The subchronic toxicity of acetone has been examined in mice and rats that were administered acetone in the drinking water and again in rats treated by oral gavage. Acetone- induced increases in relative kidney weight changes were observed in male and female rats used in the oral 13-week study. Acetone treatment caused increases in the relative liver weight in male and female rats that were not associated with histopathologic effects and the effects may have been associated with microsomal enzyme induction. Haematologic effects consistent with macrocytic anaemia were also noted in male rats along with hyperpigmentation in the spleen. The most notable findings in the mice were increased liver and decreased spleen weights. Overall, the no-observed-effect-levels in the drinking water study were 1% for male rats (900 mg/kg/d) and male mice (2258 mg/kg/d), 2% for female mice (5945 mg/kg/d), and 5% for female rats (3100 mg/kg/d). For developmental effects, a statistically significant reduction in foetal weight, and a slight, but statistically significant increase in the percent incidence of later resorptions were seen in mice at 15,665 mg/m3 and in rats at 26,100 mg/m3. The no-observable-effect level for developmental toxicity was determined to be 5220 mg/m3 for both rats and mice. Teratogenic effects were not observed in rats and mice tested at 26,110 and 15,665 mg/m3, respectively. Lifetime dermal carcinogenicity studies in mice treated with up to 0.2 mL of acetone did not reveal any increase in organ tumor incidence relative to untreated control animals. The scientific literature contains many different studies that have measured either the neurobehavioural performance or neurophysiological response of humans exposed to acetone. Effect levels ranging from about 600 to greater than 2375 mg/m3 have been reported. Neurobehavioral studies with acetone-exposed employees have recently shown that 8-hr exposures in excess of 2375 mg/m3 were not associated with any dose-related changes in response time, vigilance, or digit span scores. Clinical case studies, controlled human volunteer studies, animal research, and occupational field evaluations all indicate that the NOAEL for this effect is 2375 mg/m3 or greater. N-BUTYL ACETATE: unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Oral (rat) LD50: 13100 mg/kg Skin (rabbit): 500 mg/24h-Moderate
Dermal (rabbit) LD50: 3200 mg/kg* Eye (rabbit): 20 mg (open)-SEVERE
Inhalation (human) TCLo: 200 ppm Eye (rabbit): 20 mg/24h - Moderate
Inhalation (rat) LC50: 2000 ppm/4h Eye ( human): 300 mg
Inhalation (Human) TCLo: 200 ppm/4h * [PPG]
Oral (Rat) LD50: 10768 mg/kg
Inhalation (Rat) LC50: 390 ppm/4h
Intraperitoneal (Mouse) LD50: 1230 mg/kg
Oral (Rabbit) LD50: 3200 mg/kg
Oral (Guinea) pig: LD50 4700 mg/kg
Intraperitoneal (Guinea) pig: LD 1500 mg/kg
The material may produce severe irritation to the eye causing pronounced inflammation. Repeated or prolonged exposure to irritants may produce conjunctivitis. The material may cause skin irritation after prolonged or repeated exposure and may produce on contact skin redness, swelling, the production of vesicles, scaling and thickening of the skin.

 

MATERIAL CARCINOGEN REPROTOXIN SENSITISER SKIN
_______________ ____________ __________ __________ __________
ethanol ILOM
REPROTOXIN ILOM: ILO Agents toxic to the male reproductive system: ethanol

Section 12 - ECOLOGICAL INFORMATION

Marine Pollutant:  Not Determined

DO NOT discharge into sewer or waterways.
Water hazard classification (self assessment): 1 - slightly hazardous to water.
[Wurth]
Refer to data for ingredients, which follows:

ETHYL ACETATE:
log Pow (Verschueren 1983):                                           0.66/0.73
ThOD:                                                                 50.4
log Pow (Verschueren 1983):                                           0.66/0.73
BOD5:                                                                 15%
COD:                                                                  1.54 (83%)
ThOD:                                                                 1.82
Half- life Soil - High (hours):                                       168
Half- life Soil - Low (hours):                                        24
Half- life Air - High (hours):                                        353
Half- life Air - Low (hours):                                         35.3
Half- life Surface water - High (hours):                              168
Half- life Surface water - Low (hours):                               24
Half- life Ground water - High (hours):                               336
Half- life Ground water - Low (hours):                                48
Aqueous biodegradation - Aerobic - High (hours):                      168
Aqueous biodegradation - Aerobic - Low (hours):                       24
Aqueous biodegradation - Anaerobic - High (hours):                    672
Aqueous biodegradation - Anaerobic - Low (hours):                     96
Aqueous biodegradation - Removal secondary treatment - High (hours):  96%
Aqueous biodegradation - Removal secondary treatment - Low (hours):   99.90%
Photooxidation half- life water - High (hours):                       9.60E+05
Photooxidation half- life water - Low (hours):                        24090
Photooxidation half- life air - High (hours):                         353
Photooxidation half- life air - Low (hours):                          35.3
First order hydrolysis half- life (hours):                            1.77E+04
Acid rate constant [M(H+)- HR]- 1:                                    3.05E- 08
Base rate constant [MOH)- HR]- 1:                                     2.99E- 05

DO NOT discharge into sewer or waterways.
log Kow: 0.66-0.73
Half-life (hr) air: 200
Half-life (hr) H2O surface water: 10
Henry's atm m³ /mol: 1.20E-04
BOD 5 if unstated: 0.1-1.24,16-36%
COD: 1.54,83%
ThOD: 1.82

ETHANOL:
Fish LC50 (96hr.) (mg/l):                                             13480
Algae IC50 (72hr.) (mg/l):                                            1450
log Kow (Sangster 1997):                                              - 0.3
BOD5:                                                                 63%
ThOD:                                                                 2.1
Half- life Soil - High (hours):                                       24
Half- life Soil - Low (hours):                                        2.6
Half- life Air - High (hours):                                        122
Half- life Air - Low (hours):                                         12.2
Half- life Surface water - High (hours):                              26
Half- life Surface water - Low (hours):                               6.5
Half- life Ground water - High (hours):                               52
Half- life Ground water - Low (hours):                                13
Aqueous biodegradation - Aerobic - High (hours):                      26
Aqueous biodegradation - Aerobic - Low (hours):                       6.5
Aqueous biodegradation - Anaerobic - High (hours):                    104
Aqueous biodegradation - Anaerobic - Low (hours):                     26
Aqueous biodegradation - Removal secondary treatment - High (hours):  67%
Photooxidation half- life water - High (hours):                       3.20E+05
Photooxidation half- life water - Low (hours):                        8020
Photooxidation half- life air - High (hours):                         122
Photooxidation half- life air - Low (hours):                          12.2

When ethanol is released into the soil it readily and quickly biodegrades but may leach 
into ground water; most is lost by evaporation. When released into water the material 
readily evaporates and is biodegradable.
Ethanol does not bioaccumulate to an appreciable extent.
The material is readily degraded by reaction with photochemically produced hydroxy 
radicals; release into air will result in photodegradation and wet deposition.
Environmental Fate:
TERRESTRIAL FATE: An estimated Koc value of 1  indicates that ethanol is expected to have 
very high mobility in soil. Volatilisation of ethanol from moist soil surfaces is 
expected to be an important fate process given a Henry's Law constant of 5X10-6 atm-
m3/mole. The potential for volatilization of ethanol from dry soil surfaces may exist 
based upon an extrapolated vapor pressure of 59.3 mm Hg Biodegradation is expected to be 
an important fate process for ethanol based on half-lives on the order of a few days for 
ethanol in sandy soil/groundwater microcosms
AQUATIC FATE: An estimated Koc value of 1 indicates that ethanol is not expected to 
adsorb to suspended solids and sediment. Volatilisation from water surfaces is expected 
based upon a Henry's Law constant of 5X10-6 atm-m3/mole. Using this Henry's Law constant 
and an estimation method, volatilisation half-lives for a model river and model lake are 
3 and 39 days, respectively.An estimated BCF= 3, from a log Kow of -0.31 suggests 
bioconcentration in aquatic organisms is low. Hydrolysis and photolysis in sunlit surface 
waters is not expected to be an important environmental fate process for ethanol since 
this compound lacks functional groups that hydrolyse or absorb light under 
environmentally relevant conditions. Ethanol was degraded with half-lives on the order of 
a few days in aquatic studies conducted using microcosms constructed with a low organic 
sandy soil and groundwater, indicating it is unlikely to be persistent in aquatic 
environments(8).
ATMOSPHERIC FATE: Ethanol, which has an extrapolated vapor pressure of 59.3 mm Hg at 25 
deg C, is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase 
ethanol is degraded in the atmosphere by reaction with photochemically-produced hydroxyl 
radicals; the half-life for this reaction in air is estimated to be 5 days, calculated 
from its rate constant of 3.3X10-12 m3/molecule-sec at 25 deg C.
Ecotoxicity:
log Kow  : -0.31- -0.32
Half-life (hr) air  : 144
Half-life (hr) H2O surface water  : 144
Henry's atm m3 /mol: 6.29E-06
BOD 5 if unstated: 0.93-1.67,63%
COD  : 1.99-2.11,97%
ThOD  : 2.1.
DO NOT discharge into sewer or waterways.

ACETONE:
Fish LC50 (96hr.) (mg/l):                                             8300- 40000
Daphnia magna EC50 (48hr.) (mg/l):                                    10
log Kow (Prager 1995):                                                - 0.24
log Kow (Sangster 1997):                                              - 0.24
log Pow (Verschueren 1983):                                           - 0.24
BOD5:                                                                 122%
ThOD:                                                                 72
Half- life Soil - High (hours):                                       168
Half- life Soil - Low (hours):                                        24
Half- life Air - High (hours):                                        2790
Half- life Air - Low (hours):                                         279
Half- life Surface water - High (hours):                              168
Half- life Surface water - Low (hours):                               24
Half- life Ground water - High (hours):                               336
Half- life Ground water - Low (hours):                                48
Aqueous biodegradation - Aerobic - High (hours):                      168
Aqueous biodegradation - Aerobic - Low (hours):                       24
Aqueous biodegradation - Anaerobic - High (hours):                    672
Aqueous biodegradation - Anaerobic - Low (hours):                     96
Aqueous biodegradation - Removal secondary treatment - High (hours):  75%
Aqueous biodegradation - Removal secondary treatment - Low (hours):   54%
Aqueous photolysis half- life - High (hours):                         270
Photooxidation half- life water - High (hours):                       3.97E+06
Photooxidation half- life water - Low (hours):                        9.92E+04
Photooxidation half- life air - High (hours):                         2790
Photooxidation half- life air - Low (hours):                          279

Ketones are generally not degraded by hydrolysis. Based on its reactions in air, it seems 
likely that they undergo photolysis in water. It is probable that ketones will be 
biodegraded to an appreciable degree by micro-organisms in soil and water.
They are unlikely to bioconcentrate or biomagnify.
for acetone:
log Kow: -0.24
Half-life (hr) air: 312-1896
Half-life (hr) H2O surface water: 20
Henry's atm m3 /mol: 3.67E-05
BOD 5:  0.31-1.76,46-55%
COD: 1.12-2.07
ThOD: 2.2
BCF: 0.69
Environmental fate:
Acetone preferentially locates in the air compartment when released to the environment. A 
substantial amount of acetone can also be found in water, which is consistent with the 
high water to air partition coefficient and its small, but detectable, presence in rain 
water, sea water, and lake water samples. Very little acetone is expected to reside in 
soil, biota, or suspended solids. This is entirely consistent with the physical and 
chemical properties of acetone and with measurements showing a low propensity for soil 
absorption and a high preference for moving through the soil and into the ground water
In air, acetone is lost by photolysis and reaction with photochemically produced hydroxyl 
radicals; the estimated half-life of these combined processes is about 22 days. The 
relatively long half-life allows acetone to be transported long distances from its 
emission source.
Acetone is highly soluble and slightly persistent in water, with a half-life of about 20 
hours; it is minimally toxic to aquatic life.
Acetone released to soil volatilises although some may leach into the ground where it 
rapidly biodegrades.
Acetone does not concentrate in the food chain.
Acetone meets the OECD definition of readily biodegradable which requires that the 
biological oxygen demand (BOD) is at least 70% of the theoretical oxygen demand (THOD) 
within the 28-day test period
Drinking Water Standard: none available.
Soil Guidelines: none available.
Air Quality Standards: none available.
Ecotoxicity:
Testing shows that acetone exhibits a low order of toxicity
Fish LC50: brook trout 6070 mg/l; fathead minnow 15000 mg/l
Bird LC0 (5 day): Japanese quail, ring-neck pheasant 40,000 mg/l
Daphnia magna LC50 (48 h):  15800 mg/l; NOEC 8500 mg/l
Aquatic invertebrate 2100 - 16700 mg/l
Aquatic plant NOEC: 5400-7500 mg/l
Daphnia magna chronic NOEC 1660 mg/l
Acetone vapors were shown to be relatively toxic to two types insects and their eggs. The 
time to 50% lethality (LT50) was found to be 51.2 hr and 67.9 hr when the flour beetle 
(Tribolium confusum) and the flour moth (Ephestia kuehniella) were exposed to an airborne 
acetone concentration of 61.5 mg/m3. The LT50 values for the eggs were 30-50% lower than 
for the adult. The direct application of acetone liquid to the body of the insects or 
surface of the eggs did not, however, cause any mortality.
The ability of acetone to inhibit cell multiplication has been examined in a wide variety 
of microorganisms. The results have generally indicated mild to minimal toxicity with 
NOECs greater than 1700 mg/L for exposures lasting from 6 hr to 4 days. Longer exposure 
periods of 7 to 8 days with bacteria produced mixed results; but overall the data 
indicate a low degree of toxicity for acetone. The only exception to these findings were 
the results obtained with the flagellated protozoa (Entosiphon sulcatum) which yielded a 
3-day NOEC of 28 mg/L.
DO NOT discharge into sewer or waterways.

N-BUTYL ACETATE:
Fish LC50 (96hr.) (mg/l):           18
Daphnia magna EC50 (48hr.) (mg/l):  44
log Kow (Prager 1995):              1.82
Fish LC50 (96hr.) (mg/l):           100- 185
Daphnia magna EC50 (48hr.) (mg/l):  44
Algae IC50 (72hr.) (mg/l):          280
log Kow (Sangster 1997):            1.78
COD:                                78%

DO NOT discharge into sewer or waterways.
Half-life (hr) air: 144
Half-life (hr) H2O surface water: 178-27156
Henry's atm m³ /mol: 3.20E-04
BOD 5 if unstated: 0.15-1.02,7%
COD: 78%
ThOD: 2.207
BCF: 4-14
Toxicity Fish: LC50(96)100-185ppm
Toxicity invertebrate: cell mult. inhib.78-3700mg/L
Effects on algae and plankton: cell mult. inhib.21-280mg/L
Degradation Biological: sig
processes Abiotic: hydrol,RxnOH*

Section 13 - DISPOSAL CONSIDERATIONS

· Containers may still present a chemical hazard/ danger when empty.
· Return to supplier for reuse/ recycling if possible.
Otherwise:
· If container can not be cleaned sufficiently well to ensure that residuals do not
remain or if the container cannot be used to store the same product, then puncture
containers, to prevent re-use, and bury at an authorised landfill.
· Where possible retain label warnings and MSDS and observe all notices pertaining to the
product.
· Recycle wherever possible or consult manufacturer for recycling options.
· Consult State Land Waste Authority for disposal.
· Bury or incinerate residue at an approved site.
· Recycle containers if possible, or dispose of in an authorised landfill.

Section 14 - TRANSPORTATION INFORMATION

Labels Required: FLAMMABLE LIQUID,TOXIC
HAZCHEM: 3WE

UNDG:
Dangerous Goods Class: 3 Subrisk: 6.1
UN Number: 1992 Packing Group: II
Shipping Name:FLAMMABLE LIQUID, TOXIC, N.O.S. (contains ethyl acetate and m-cresol)

Air Transport IATA:

ICAO/IATA Class: 3 ICAO/IATA Subrisk: 6.1
UN/ID Number: 1992 Packing Group: II
Special provisions: A3
Shipping Name: FLAMMABLE LIQUID, TOXIC, N.O.S. *

Maritime Transport IMDG:

IMDG Class: 3 IMDG Subrisk: 6.1
UN Number: 1992 Packing Group: II
EMS Number: F-E,S-D Special provisions: 274 944
Limited Quantities: 1 L Marine Pollutant: Not Determined
Shipping Name: FLAMMABLE LIQUID, TOXIC, N.O.S.

Section 15 - REGULATORY INFORMATION

POISONS SCHEDULE: S6

REGULATIONS

0890 100 010 - Wurth Engine Gasket (CAS: None):
No regulations applicable

ethyl acetate (CAS: 141-78-6) is found on the following regulatory lists;
    Australia Exposure Standards
    Australia Hazardous Substances
    Australia High Volume Industrial Chemical List (HVICL)
    Australia Inventory of Chemical Substances (AICS)
    Australia National Pollutant Inventory
    GESAMP/EHS Composite List of Hazard Profiles - Hazard evaluation of substances transported by ships
    IMO IBC Code Chapter 17: Summary of minimum requirements
    IMO MARPOL 73/78 (Annex II) - List of Noxious Liquid Substances Carried in Bulk
    International Air Transport Association (IATA) Dangerous Goods Regulations
    International Council of Chemical Associations (ICCA) - High Production Volume List
    OECD Representative List of High Production Volume (HPV) Chemicals

ethanol (CAS: 64-17-5) is found on the following regulatory lists;
    Australia Exposure Standards
    Australia Hazardous Substances
    Australia High Volume Industrial Chemical List (HVICL)
    Australia Inventory of Chemical Substances (AICS)
    Australia National Pollutant Inventory
    Australia Standard for the Uniform Scheduling of Drugs and Poisons (SUSDP) - Schedule 5
    GESAMP/EHS Composite List of Hazard Profiles - Hazard evaluation of substances transported by ships
    IMO IBC Code Chapter 18: List of products to which the Code does not apply
    IMO MARPOL 73/78 (Annex II) - List of Other Liquid Substances
    IMO Provisional Categorization of Liquid Substances - List 1: Pure or technically pure products
    IMO Provisional Categorization of Liquid Substances - List 2: Pollutant only mixtures containing at least 99% by weight of components already assessed by IMO
    International Air Transport Association (IATA) Dangerous Goods Regulations
    International Council of Chemical Associations (ICCA) - High Production Volume List
    OECD Representative List of High Production Volume (HPV) Chemicals

acetone (CAS: 67-64-1) is found on the following regulatory lists;
    Australia - Victoria Occupational Health and Safety Regulations - Schedule 9: Materials at Major Hazard Facilities (And Their Threshold Quantity) Table 2
    Australia Exposure Standards
    Australia Hazardous Substances
    Australia High Volume Industrial Chemical List (HVICL)
    Australia Illicit Drug Reagents/Essential Chemicals - Category III
    Australia Inventory of Chemical Substances (AICS)
    Australia National Pollutant Inventory
    Australia Standard for the Uniform Scheduling of Drugs and Poisons (SUSDP) - Appendix E (Part 2)
    Australia Standard for the Uniform Scheduling of Drugs and Poisons (SUSDP) - Appendix F (Part 3)
    Australia Standard for the Uniform Scheduling of Drugs and Poisons (SUSDP) - Schedule 5
    GESAMP/EHS Composite List of Hazard Profiles - Hazard evaluation of substances transported by ships
    IMO IBC Code Chapter 18: List of products to which the Code does not apply
    IMO MARPOL 73/78 (Annex II) - List of Other Liquid Substances
    International Air Transport Association (IATA) Dangerous Goods Regulations
    OECD Representative List of High Production Volume (HPV) Chemicals
    United Nations Convention Against Illicit Traffic in Narcotic Drugs and Psychotropic Substances - Table II
    United Nations List of Precursors and Chemicals Frequently used in the Illicit Manufacture of Narcotic Drugs and Psychotropic Substances Under International Control - 
Table II

n-butyl acetate (CAS: 123-86-4) is found on the following regulatory lists;
    Australia - Victoria Occupational Health and Safety Regulations - Schedule 9: Materials at Major Hazard Facilities (And Their Threshold Quantity) Table 2
    Australia Exposure Standards
    Australia Hazardous Substances
    Australia High Volume Industrial Chemical List (HVICL)
    Australia Inventory of Chemical Substances (AICS)
    Australia Standard for the Uniform Scheduling of Drugs and Poisons (SUSDP) - Schedule 5
    GESAMP/EHS Composite List of Hazard Profiles - Hazard evaluation of substances transported by ships
    IMO IBC Code Chapter 17: Summary of minimum requirements
    IMO MARPOL 73/78 (Annex II) - List of Noxious Liquid Substances Carried in Bulk
    International Air Transport Association (IATA) Dangerous Goods Regulations
    International Council of Chemical Associations (ICCA) - High Production Volume List
    OECD Representative List of High Production Volume (HPV) Chemicals
    United Nations Convention Against Illicit Traffic in Narcotic Drugs and Psychotropic Substances - Table II

Section 16 - OTHER INFORMATION

REPRODUCTIVE HEALTH GUIDELINES

Ingredient                 ORG                 UF      Endpoi  CR      Adeq
                                                       nt              TLV
ethanol                    1880 mg/m3          NA      NA      NA      Yes
These exposure guidelines have been derived from a screening level of risk assessment and 
should not be construed as unequivocally safe limits. ORGS represent an 8-hour time-
weighted average unless specified otherwise.
CR = Cancer Risk/10000; UF = Uncertainty factor:
TLV believed to be adequate to protect reproductive health:
LOD: Limit of detection
Toxic endpoints have also been identified as:
D = Developmental; R = Reproductive; TC = Transplacental carcinogen
Jankovic J., Drake F.: A Screening Method for Occupational Reproductive
American Industrial Hygiene Association Journal 57: 641-649 (1996).

 

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: 12-Sep-2008

Print Date: 12-Sep-2008