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                  0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 1 of 24



Section 1 - CHEMICAL PRODUCT AND COMPANY IDENTIFICATION


PRODUCT NAME
0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS

STATEMENT OF HAZARDOUS NATURE
Considered a Hazardous Substance according to the criteria of the New
Zealand Hazardous Substances New Organisms legislation.

OTHER NAMES



PROPER SHIPPING NAME
AEROSOLS

PRODUCT USE
Spray paint for applying to surfaces.
Application is by spray atomisation from a hand held aerosol pack.

SUPPLIER
Company: Wurth New Zealand Limited
Address:
42 Hobill Avenue
Manukau City
Auckland
NZL
Telephone: 0800 683 040
Fax: 0800 100 104



Section 2 - HAZARDS IDENTIFICATION


GHS Classification
Acute Toxicity (Inhalation) Category 3
Carcinogen Category 2
Eye Irritation Category 2A
Flammable Aerosol Category 1
Reproductive Toxicity Category 1B
Respiratory Irritation Category 3
Skin Corrosion/Irritation Category 3

EMERGENCY OVERVIEW

HAZARD
DANGER
Determined by Chemwatch using GHS/HSNO criteria:
2.1.2A 6.1C 6.3B 6.4A 6.7B 6.8A
May cause respiratory irritation
Extremely flammable aerosol
Toxic if inhaled
Causes mild skin irritation
Causes serious eye irritation
Suspected of causing cancer


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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 2 of 24
Section 2 - HAZARDS IDENTIFICATION

May damage the unborn child

PRECAUTIONARY STATEMENTS

Prevention
Obtain special instructions before use.
Do not spray on an open flame or other ignition source.
Wash hands thoroughly after handling.
Avoid breathing dust/fume/gas/mist/vapours/spray.
Use only outdoors or in a well ventilated area.
Pressurized container: Do not pierce or burn, even after use.
Keep away from heat/sparks/open flame - No smoking.
Do not handle until all safety precautions have been read and understood.
Use personal protective equipment as required.

Response
IF IN EYES: Rinse cautiously with water for several minutes. Remove contact lenses, if
present and easy to do. Continue rinsing.
If skin irritation occurs, seek medical advice/attention.
If exposed or concerned: Get medical attention advice.
If eye irritation persists, get medical advice/attention.
Wear eye/face protection.
Specific treatment: refer to Label or MSDS.
Eliminate all ignition sources if safe to do so.
Leaking gas fire: Do not extinguish, unless leak can be stopped safely
IF INHALED: Remove to fresh air and keep at rest in a position comfortable for breathing.
Call a POISON CENTER or doctor/physician if you feel unwell.
Keep container tightly closed.

Storage
Store locked up.
Protect from sunlight and do not expose to temperatures exceeding 50??C/122??F.

Disposal
Dispose of contents and container in accordance with relevant legislation.


Section 3 - COMPOSITION / INFORMATION ON INGREDIENTS

NAME CAS RN %
acetone 67-64-1 20-50
n- butyl acetate 123-86-4 1-40
propylene glycol monomethyl ether acetate, alpha- isomer 108-65-6 1-20
xylene 1330-20-7 1-12
titanium dioxide 13463-67-7 1-10
carbon black 1333-86-4 1-10
n- butanol 71-36-3 1-5
hydrocarbon propellant 68476-85-7. 2-40


Section 4 - FIRST AID MEASURES

NEW ZEALAND POISONS INFORMATION CENTRE 0800 POISON (0800 764 766)
NZ EMERGENCY SERVICES: 111

SWALLOWED
For advice, contact a Poisons Information Centre or a doctor.
路 If swallowed do NOT induce vomiting.


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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 3 of 24
Section 4 - FIRST AID MEASURES

路 If vomiting occurs, lean patient forward or place on left side (head-down position, if
possible) to maintain open airway and prevent aspiration.
路 Observe the patient carefully.
路 Never give liquid to a person showing signs of being sleepy or with reduced awareness;
i.e. becoming unconscious
路 Give water to rinse out mouth, then provide liquid slowly and as much as casualty can
comfortably drink.
路 Seek medical advice.

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

SKIN
If solids or aerosol mists are deposited upon the skin:
路 Flush skin and hair with running water (and soap if available).
路 Remove any adhering solids with industrial skin cleansing cream.
路 DO NOT use solvents.
路 Seek medical attention in the event of irritation.

INHALED
路 If fumes or combustion products are inhaled remove from contaminated area.
路 Lay patient down. Keep warm and rested.
路 Prostheses such as false teeth, which may block airway, should be removed, where
possible, prior to initiating first aid procedures.
路 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.
路 Transport to hospital, or doctor.

NOTES TO PHYSICIAN
For acute or short term repeated exposures to petroleum distillates or related
hydrocarbons:
路 Primary threat to life, from pure petroleum distillate ingestion and/or inhalation, is
respiratory failure.
路 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.
路 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.
路 A chest x-ray should be taken immediately after stabilisation of breathing and
circulation to document aspiration and detect the presence of pneumothorax.
路 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.
路 Lavage is indicated in patients who require decontamination; ensure use of cuffed
endotracheal tube in adult patients. [Ellenhorn and Barceloux: Medical Toxicology].




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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 4 of 24


Section 5 - FIRE FIGHTING MEASURES


EXTINGUISHING MEDIA
路 Water spray or fog.
路 Foam.
路 Dry chemical powder.
路 BCF (where regulations permit).
路 Carbon dioxide.

FIRE FIGHTING
路 Alert Fire Brigade and tell them location and nature of hazard.
路 May be violently or explosively reactive.
路 Wear breathing apparatus plus protective gloves.
路 Prevent, by any means available, spillage from entering drains or water course.
路 If safe, switch off electrical equipment until vapour fire hazard removed.
路 Use water delivered as a fine spray to control fire and cool adjacent area.
路 DO NOT approach containers suspected to be hot.
路 Cool fire exposed containers with water spray from a protected location.
路 If safe to do so, remove containers from path of fire.
路 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.

FIRE/EXPLOSION HAZARD
路 Liquid and vapour are highly flammable.
路 Severe fire hazard when exposed to heat or flame.
路 Vapour forms an explosive mixture with air.
路 Severe explosion hazard, in the form of vapour, when exposed to flame or spark.
路 Vapour may travel a considerable distance to source of ignition.
路 Heating may cause expansion or decomposition with violent container rupture.
路 Aerosol cans may explode on exposure to naked flames.
路 Rupturing containers may rocket and scatter burning materials.
路 Hazards may not be restricted to pressure effects.
路 May emit acrid, poisonous or corrosive fumes.
路 On combustion, may emit toxic fumes of carbon monoxide (CO).
Other combustion products include:.
carbon dioxide (CO2).

FIRE INCOMPATIBILITY
Avoid contamination with strong oxidising agents as ignition may result.

Personal Protective Equipment
Breathing apparatus.
Gas tight chemical resistant suit.
Limit exposure duration to 1 BA set 30 mins.


Section 6 - ACCIDENTAL RELEASE MEASURES


EMERGENCY PROCEDURES

MINOR SPILLS
路 Clean up all spills immediately.
路 Avoid breathing vapours and contact with skin and eyes.
路 Wear protective clothing, impervious gloves and safety glasses.
路 Shut off all possible sources of ignition and increase ventilation.
路 Wipe up.
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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 5 of 24
Section 6 - ACCIDENTAL RELEASE MEASURES

路 If safe, damaged cans should be placed in a container outdoors, away from all ignition
sources, until pressure has dissipated.
路 Undamaged cans should be gathered and stowed safely.

MAJOR SPILLS
路 Clear area of personnel and move upwind.
路 Alert Fire Brigade and tell them location and nature of hazard.
路 May be violently or explosively reactive.
路 Wear breathing apparatus plus protective gloves.
路 Prevent, by any means available, spillage from entering drains or water courses
路 No smoking, naked lights or ignition sources.
路 Increase ventilation.
路 Stop leak if safe to do so.
路 Water spray or fog may be used to disperse / absorb vapour.
路 Absorb or cover spill with sand, earth, inert materials or vermiculite.
路 If safe, damaged cans should be placed in a container outdoors, away from ignition
sources, until pressure has dissipated.
路 Undamaged cans should be gathered and stowed safely.
路 Collect residues and seal in labelled drums for disposal.

PROTECTIVE ACTIONS FOR SPILL
PROTECTIVE ACTION ZONE

half
evacuation
downwind
direction
distance
down wind distance
wind isolation
distance
direction
half
evacuation downwind
INITIAL direction distance
ISOLATION
ZONE

From IERG (Canada/Australia)
Isolation Distance -
Downwind Protection Distance 8 metres
IERG Number 49

FOOTNOTES
1 PROTECTIVE ACTION ZONE is defined as the area in which people are at risk of harmful exposure. This zone
assumes that random changes in wind direction confines the vapour plume to an area within 30 degrees on
either side of the predominant wind direction, resulting in a crosswind protective action distance equal
to the downwind protective action distance.
2 PROTECTIVE ACTIONS should be initiated to the extent possible, beginning with those closest to the spill
and working away from the site in the downwind direction. Within the protective action zone a level of
vapour concentration may exist resulting in nearly all unprotected persons becoming incapacitated and
unable to take protective action and/or incurring serious or irreversible health effects.
3 INITIAL ISOLATION ZONE is determined as an area, including upwind of the incident, within which a high
probability of localised wind reversal may expose nearly all persons without appropriate protection to
life-threatening concentrations of the material.
4 SMALL SPILLS involve a leaking package of 200 litres (55 US gallons) or less, such as a drum (jerrican or
box with inner containers). Larger packages leaking less than 200 litres and compressed gas leaking from
a small cylinder are also considered "small spills".
LARGE SPILLS involve many small leaking packages or a leaking package of greater than 200 litres, such as
a cargo tank, portable tank or a "one-tonne" compressed gas cylinder.
5 Guide 126 is taken from the US DOT emergency response guide book.

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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 6 of 24
Section 6 - ACCIDENTAL RELEASE MEASURES

6 IERG information is derived from CANUTEC - Transport Canada.

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:
acetone 8500 ppm
n-butyl acetate 3000 ppm
propylene glycol monomethyl ether acetate, alpha-isomer 600 ppm
xylene 900 ppm
titanium dioxide 500 mg/m鲁
carbon black 500 mg/m鲁
hydrocarbon propellant 2000 ppm

irreversible or other serious effects or symptoms which could impair an individual's ability to take
protective action is:
acetone 8500 ppm
n-butyl acetate 200 ppm
propylene glycol monomethyl ether acetate, alpha-isomer 250 ppm
xylene 200 ppm
titanium dioxide 15 mg/m鲁
carbon black 17.5 mg/m鲁
hydrocarbon propellant 2000 ppm

other than mild, transient adverse effects without perceiving a clearly defined odour is:
acetone 1000 ppm
n-butyl acetate 5 ppm
propylene glycol monomethyl ether acetate, alpha-isomer 150 ppm
xylene 150 ppm
titanium dioxide 15 mg/m鲁
carbon black 10.5 mg/m鲁
hydrocarbon propellant 2000 ppm

The threshold concentration below which most people will experience no appreciable risk of health effects:
acetone 1000 ppm
n-butyl acetate 5 ppm
propylene glycol monomethyl ether acetate, alpha-isomer 50 ppm
xylene 100 ppm
titanium dioxide 15 mg/m鲁
carbon black 3.5 mg/m鲁
hydrocarbon propellant 1000 ppm

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.




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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 7 of 24


Section 7 - HANDLING AND STORAGE


PROCEDURE FOR HANDLING
路 Avoid all personal contact, including inhalation.
路 Wear protective clothing when risk of exposure occurs.
路 Use in a well-ventilated area.
路 Prevent concentration in hollows and sumps.
路 DO NOT enter confined spaces until atmosphere has been checked.
路 Avoid smoking, naked lights or ignition sources.
路 Avoid contact with incompatible materials.
路 When handling, DO NOT eat, drink or smoke.
路 DO NOT incinerate or puncture aerosol cans.
路 DO NOT spray directly on humans, exposed food or food utensils.
路 Avoid physical damage to containers.
路 Always wash hands with soap and water after handling.
路 Work clothes should be laundered separately.
路 Use good occupational work practice.
路 Observe manufacturer's storing and handling recommendations.
路 Atmosphere should be regularly checked against established exposure standards to ensure
safe working conditions are maintained.

SUITABLE CONTAINER
路 Aerosol dispenser.
路 Check that containers are clearly labelled.

STORAGE INCOMPATIBILITY
Avoid storage with oxidisers.

STORAGE REQUIREMENTS
路 Store in original containers in approved flame-proof area.
路 DO NOT store in pits, depressions, basements or areas where vapours may be trapped.
路 No smoking, naked lights, heat or ignition sources.
路 Keep containers securely sealed. Contents under pressure.
路 Store away from incompatible materials.
路 Store in a cool, dry, well ventilated area in an upright position.
路 Avoid storage at temperatures higher than 40 deg C.
路 Protect containers against physical damage and check regularly for leaks.
路 Observe manufacturer's storing and handling recommendations.


Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION


EXPOSURE CONTROLS
Source Material TWA ppm TWA mg/m鲁 STEL ppm STEL mg/m鲁Peak ppm Peak mg/m鲁 TWA F/CC
_________ _________ _____ _____ _____ _____ _____ _____ _____
New acetone 500 1, 185 1, 000 2, 375
Zealand (Acetone)
Workplace
Exposure
Standards
(WES)
New n- butyl 150 713 200 950
Zealand acetate
Workplace (n- Butyl
Exposure acetate)
Standards
(WES)
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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 8 of 24
Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

Source Material TWA ppm TWA mg/m鲁 STEL ppm STEL mg/m鲁Peak ppm Peak mg/m鲁 TWA F/CC
_________ _________ _____ _____ _____ _____ _____ _____ _____

New xylene 50 217
Zealand (Xylene)
Workplace
Exposure
Standards
(WES)
New xylene 50 217
Zealand (Xylene)
Workplace
Exposure
Standards
(WES)
New xylene 50 217
Zealand (Xylene)
Workplace
Exposure
Standards
(WES)
New xylene 50 217
Zealand (Xylene)
Workplace
Exposure
Standards
(WES)
New titanium 10(d)
Zealand dioxide
Workplace (Titanium
Exposure dioxide)
Standards
(WES)
New carbon 3
Zealand black
Workplace (Carbon
Exposure black)
Standards
(WES)
New n- butanol 50 150
Zealand (n- Butyl
Workplace alcohol)
Exposure
Standards
(WES)
New hydrocarbo 1, 000 1, 800
Zealand n
Workplace propellant
Exposure (LPG
Standards (Liquefied
(WES) petroleum
gas))


EMERGENCY EXPOSURE LIMITS
Material Revised IDLH Value (mg/m3) Revised IDLH Value (ppm)
acetone 2, 500 [LEL]
n- butyl acetate 1, 700 [LEL]
xylene 900
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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 9 of 24
Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

titanium dioxide 5, 000
carbon black 1, 750
n- butanol 1, 400 [LEL]
hydrocarbon propellant 2, 000 [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.


ODOUR SAFETY FACTOR (OSF)
OSF=0.16 (hydrocarbon propellant)
Exposed individuals are NOT reasonably expected to be warned, by smell, that the Exposure
Standard is being exceeded.
Odour Safety Factor (OSF) is determined to fall into either Class C, D or E.
The Odour Safety Factor (OSF) is defined as:
OSF= Exposure Standard (TWA) ppm/ Odour Threshold Value (OTV) ppm
Classification into classes follows:

Class OSF Description
A 550 Over 90% of exposed individuals
are aware by smell that the
Exposure Standard (TLV- TWA for
example) is being reached, even
when distracted by working
activities
B 26- 550 As " A" for 50- 90% of persons
being distracted
C 1- 26 As " A" for less than 50% of
persons being distracted
D 0.18- 1 10- 50% of persons aware of
being tested perceive by smell
that the Exposure Standard is
being reached
E <0.18 As " D" for less than 10% of
persons aware of being tested

.

MATERIAL DATA
None assigned. Refer to individual constituents.

INGREDIENT DATA
PROPYLENE GLYCOL MONOMETHYL ETHER ACETATE, ALPHA-ISOMER:
TITANIUM DIOXIDE:
XYLENE:
Sensory irritants are chemicals that produce temporary and undesirable side-effects on
the eyes, nose or throat. Historically occupational exposure standards for these
irritants have been based on observation of workers' responses to various airborne
concentrations. Present day expectations require that nearly every individual should be
protected against even minor sensory irritation and exposure standards are established
using uncertainty factors or safety factors of 5 to 10 or more. On occasion animal no
-observable-effect-levels (NOEL) are used to determine these limits where human results
are unavailable. An additional approach, typically used by the TLV committee (USA) in
determining respiratory standards for this group of chemicals, has been to assign ceiling
values (TLV C) to rapidly acting irritants and to assign short-term exposure limits (TLV
STELs) when the weight of evidence from irritation, bioaccumulation and other endpoints
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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 10 of 24
Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

combine to warrant such a limit. In contrast the MAK Commission (Germany) uses a five
-category system based on intensive odour, local irritation, and elimination half-life.
However this system is being replaced to be consistent with the European Union (EU)
Scientific Committee for Occupational Exposure Limits (SCOEL); this is more closely
allied to that of the USA.
OSHA (USA) concluded that exposure to sensory irritants can:
路 cause inflammation
路 cause increased susceptibility to other irritants and infectious agents
路 lead to permanent injury or dysfunction
路 permit greater absorption of hazardous substances and
路 acclimate the worker to the irritant warning properties of these substances thus
increasing the risk of overexposure.

ACETONE:
N-BUTANOL:
N-BUTYL ACETATE:
Exposed individuals are reasonably expected to be warned, by smell, that the Exposure
Standard is being exceeded.
Odour Safety Factor (OSF) is determined to fall into either Class A or B.
The Odour Safety Factor (OSF) is defined as:
OSF= Exposure Standard (TWA) ppm/ Odour Threshold Value (OTV) ppm
Classification into classes follows:

Class OSF Description
A 550 Over 90% of exposed individuals
are aware by smell that the
Exposure Standard (TLV- TWA for
example) is being reached, even
when distracted by working
activities
B 26- 550 As " A" for 50- 90% of persons
being distracted
C 1- 26 As " A" for less than 50% of
persons being distracted
D 0.18- 1 10- 50% of persons aware of
being tested perceive by smell
that the Exposure Standard is
being reached
E <0.18 As " D" for less than 10% of
persons aware of being tested

.

HYDROCARBON PROPELLANT:
XYLENE:
Exposed individuals are NOT reasonably expected to be warned, by smell, that the
Exposure Standard is being exceeded.
Odour Safety Factor (OSF) is determined to fall into either Class C, D or E.
The Odour Safety Factor (OSF) is defined as:
OSF= Exposure Standard (TWA) ppm/ Odour Threshold Value (OTV) ppm
Classification into classes follows:

Class OSF Description
A 550 Over 90% of exposed individuals
are aware by smell that the
Exposure Standard (TLV- TWA for
example) is being reached, even
when distracted by working
activities
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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 11 of 24
Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

B 26- 550 As " A" for 50- 90% of persons
being distracted
C 1- 26 As " A" for less than 50% of
persons being distracted
D 0.18- 1 10- 50% of persons aware of
being tested perceive by smell
that the Exposure Standard is
being reached
E <0.18 As " D" for less than 10% of
persons aware of being tested

.

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.

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.

PROPYLENE GLYCOL MONOMETHYL ETHER ACETATE, ALPHA-ISOMER:

Saturated vapour concentration: 4868 ppm at 20 C.
A two-week inhalation study found nasal effects to the nasal mucosa in
animals at concentrations up to 3000 ppm. Differences in the teratogenic
potential of the alpha (commercial grade) and beta isomers of PGMEA may
be explained by the formation of different metabolites. The beta-isomer is
thought to be oxidised to methoxypropionic acid, a homologue to
methoxyacetic acid which is a known teratogen. The alpha- form is
conjugated and excreted.
PGMEA mixture (containing 2% to 5% beta isomer) is a mild skin and eye
irritant, produces mild central nervous system effects in animals at
3000 ppm and produces mild CNS impairment and upper respiratory tract
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0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 12 of 24
Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

and eye irritation in humans at 1000 ppm. In rats exposed to 3000 ppm
PGMEA produced slight foetotoxic effects (delayed sternabral ossification)
- no effects on foetal development were seen in rabbits exposed at 3000 ppm.

XYLENE:
IDLH Level: 900 ppm
Odour Threshold Value: 20 ppm (detection), 40 ppm (recognition)
NOTE: Detector tubes for o-xylene, measuring in excess of 10 ppm, are
available commercially. (m-xylene and p-xylene give almost the same
response)
Xylene vapour is an irritant to the eyes, mucous membranes and skin and
causes narcosis at high concentrations. Exposure to doses sufficiently high
to produce intoxication and unconsciousness also produces transient liver
and kidney toxicity. Neurologic impairment is NOT evident amongst
volunteers inhaling up to 400 ppm though complaints of ocular and upper
respiratory tract irritation occur at 200 ppm for 3 to 5 minutes.
Exposure to xylene at or below the recommended TLV-TWA and STEL is thought
to minimise the risk of irritant effects and to produce neither significant
narcosis or chronic injury. An earlier skin notation was deleted because
percutaneous absorption is gradual and protracted and does not
substantially contribute to the dose received by inhalation.

TITANIUM DIOXIDE:
It is the goal of the ACGIH (and other Agencies) to recommend TLVs (or their
equivalent) for all substances for which there is evidence of health effects at airborne
concentrations encountered in the workplace.
At this time no TLV has been established, even though this material may produce
adverse health effects (as evidenced in animal experiments or clinical experience).
Airborne concentrations must be maintained as low as is practically possible and
occupational exposure must be kept to a minimum.
NOTE: The ACGIH occupational exposure standard for Particles Not Otherwise Specified
(P.N.O.S) does NOT apply.
WARNING: This substance has been classified by the IARC as Group 2B: Possibly
Carcinogenic to Humans.
IDLH Level: 5000 mg/m3
Animal studies at 10 mg/m3 show no significant fibrosis, possibly reversible
tissue reaction and the architecture of lung air spaces remains intact.

CARBON BLACK:
The TLV-TWA is recommended to minimise complaints of excessive dirtiness
and applies only to commercially produced carbon blacks or to soots
derived from combustion sources containing absorbed polycyclic aromatic
hydrocarbons (PAHs). When PAHs are present in carbon black (measured as
the cyclohexane-extractable fraction) NIOSH has established a REL-TWA of
0.1 mg/m3 and considers the material to be an occupational carcinogen.
The NIOSH REL-TWA was "selected on the basis of professional judgement
rather than on data delineating safe from unsafe concentrations of PAHs".
This limit was justified on the basis of feasibility of measurement and
not on a demonstration of its safety.

N-BUTANOL:

Odour Threshold Value: 0.12-3.4 ppm (detection), 1.0-3.5 ppm (recognition)
NOTE: Detector tubes for n-butanol, measuring in excess of 5 ppm are
commercially available.
Exposure at or below the TLV-TWA is thought to provide protection against
hearing loss due to vestibular and auditory nerve damage in younger
workers and to protect against the significant risk of headache and
irritation.
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Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

25 ppm may produce mild irritation of the respiratory tract
50 ppm may produce headache and vertigo.
Higher concentrations may produce marked irritation, sore throat,
coughing, nausea, shortness of breath, pulmonary injury and central
nervous system depression characterised by headache, dizziness, dullness
and drowsiness.
6000 ppm may produce giddiness, prostration, narcosis, ataxia, and death.

PERSONAL PROTECTION

EYE
路 Safety glasses with side shields; or as required,
路 Chemical goggles.
路 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
No special equipment needed when handling small quantities.
OTHERWISE: Wear general protective gloves, eg. light weight rubber gloves. Or as required
: Wear chemical protective gloves, eg. PVC. Wear safety footwear.

OTHER
No special equipment needed when handling small quantities.
OTHERWISE:
路 Overalls.
路 Skin cleansing cream.
路 Eyewash unit.
路 Do not spray on hot surfaces.

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 Maximum Protection Half- face Respirator Full- Face Respirator
ppm (volume) Factor
1000 10 AX- AUS -
1000 50 - AX- AUS
5000 50 Airline * -
5000 100 - AX- 2
10000 100 - AX- 3
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.


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Section 8 - EXPOSURE CONTROLS / PERSONAL PROTECTION

ENGINEERING CONTROLS
General exhaust is adequate under normal operating 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.


Section 9 - PHYSICAL AND CHEMICAL PROPERTIES


APPEARANCE
Red liquid with a characteristic solvent odour; does not mix with water.
Supplied as an aerosol pack. Contents under PRESSURE. Contains highly flammable
hydrocarbon propellant.

PHYSICAL PROPERTIES
Liquid.
Gas.
Does not mix with water.

Molecular Weight: Not Applicable Boiling Range (掳 Not Av ailable
C):
Melting Range (掳 Not Available
C): Specific Gravity (water= 1): Not Available
Solubility in water (g/L): Immiscible pH (as supplied): Not Applicable
pH (1% solution): Not Applicable Vapour Pressure (kPa): 26.8
Volatile Component (%vol): Not Available Evaporation Rate: Not Available
Relative Vapour Density (air=1): Not Available Flash Point (掳 - 4
C):
Lower Explosive Limit (%): 2.3 Upper Explosive Limit (%): 13
Autoignition Temp (掳 315
C): Decomposition Temp (掳 Not Av ailable
C):
State: Liquid Viscosity: Not Available

log Kow (Prager 1995): - 0.24
log Kow (Sangster 1997): - 0.24
log Kow: -0.24
log Kow (Prager 1995): 1.82
log Kow (Sangster 1997): 1.78
log Kow (Prager 1995): 3.12- 3.20
log Kow (Prager 1995): 0.88
log Kow (Sangster 1997): 0.84
log Kow: 0.88


Section 10 - CHEMICAL STABILITY AND REACTIVITY INFORMATION


CONDITIONS CONTRIBUTING TO INSTABILITY
路 Elevated temperatures.
路 Presence of open flame.
路 Product is considered stable.
路 Hazardous polymerisation will not occur.


Section 11 - TOXICOLOGICAL INFORMATION


POTENTIAL HEALTH EFFECTS

ACUTE HEALTH EFFECTS




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Section 11 - TOXICOLOGICAL INFORMATION

SWALLOWED
Although ingestion is not thought to produce harmful effects (as classified under EC
Directives), the material may still be damaging to the health of the individual,
following ingestion, especially where pre-existing organ (e.g liver, kidney) damage is
evident. Present definitions of harmful or toxic substances are generally based on doses
producing mortality rather than those producing morbidity (disease, ill-health).
Gastrointestinal tract discomfort may produce nausea and vomiting. In an occupational
setting however, ingestion of insignificant quantities is not thought to be cause for
concern.
Ingestion may result in nausea, pain, vomiting. Vomit entering the lungs by aspiration
may cause potentially lethal chemical pneumonitis.
Considered an unlikely route of entry in commercial/industrial environments.

EYE
Evidence exists, or practical experience predicts, that the material may cause eye
irritation in a substantial number of individuals and/or may produce significant ocular
lesions which are present twenty-four hours or more after instillation into the eye(s) of
experimental animals.
Repeated or prolonged eye contact may cause inflammation characterised by temporary
redness (similar to windburn) of the conjunctiva (conjunctivitis); temporary impairment
of vision and/or other transient eye damage/ulceration may occur.
The material may produce severe irritation to the eye causing pronounced inflammation.
Repeated or prolonged exposure to irritants may produce conjunctivitis.

SKIN
The material is not thought to produce adverse health effects or skin irritation
following contact (as classified by EC Directives using animal models). Nevertheless,
good hygiene practice requires that exposure be kept to a minimum and that suitable
gloves be used in an occupational setting.
Toxic effects may result from skin absorption.
The material may accentuate any pre-existing skin condition.
The material may cause skin irritation after prolonged or repeated exposure and may
produce a contact dermatitis (nonallergic). This form of dermatitis is often
characterised by skin redness (erythema) and swelling the epidermis. Histologically there
may be intercellular oedema of the spongy layer (spongiosis) and intracellular oedema of
the epidermis.

INHALED
The material is not thought to produce respiratory irritation (as classified by EC
Directives using animal models). Nevertheless inhalation, of the material, especially for
prolonged periods, may produce respiratory discomfort and occasionally, distress.
Inhalation hazard is increased at higher temperatures.
Acute effects from inhalation of high concentrations of vapour are pulmonary irritation,
including coughing, with nausea; central nervous system depression - characterised by
headache and dizziness, increased reaction time, fatigue and loss of co-ordination.
If exposure to highly concentrated solvent atmosphere is prolonged this may lead to
narcosis, unconsciousness, even coma and possible death.
WARNING:Intentional misuse by concentrating/inhaling contents may be lethal.

CHRONIC HEALTH EFFECTS
On the basis, primarily, of animal experiments, concern has been expressed that the
material may produce carcinogenic or mutagenic effects; in respect of the available
information, however, there presently exists inadequate data for making a satisfactory
assessment.
Principal routes of exposure are by accidental skin and eye contact and by inhalation of
vapours especially at higher temperatures.
Chronic solvent inhalation exposures may result in nervous system impairment
and liver and blood changes. [PATTYS].
WARNING: Aerosol containers may present pressure related hazards.
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Section 11 - TOXICOLOGICAL INFORMATION


TOXICITY AND IRRITATION
Not available. Refer to individual constituents.

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/m鲁/6 hr Skin (rabbit): 500 mg/24hr - Mild
Inhalation (rat) LC50: 50100 mg/m鲁/8 hr
Dermal (rabbit) LD50: 20000 mg/kg

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 a contact dermatitis (nonallergic). This form of dermatitis is often
characterised by skin redness (erythema) and swelling the epidermis. Histologically there
may be intercellular oedema of the spongy layer (spongiosis) and intracellular oedema of
the epidermis.

PROPYLENE GLYCOL MONOMETHYL ETHER ACETATE, ALPHA-ISOMER:
unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Oral (rat) LD50: 8532 mg/kg Nil Reported
Dermal (rabbit) LD50: >5000 mg/kg* * [CCINFO]
Inhalation (rat) LC50: 4345 ppm/6h
A BASF report (in ECETOC ) showed that inhalation exposure to 545 ppm PGMEA
(beta isomer) was associated with a teratogenic response in rabbits; but
exposure to 145 ppm and 36 ppm had no adverse effects.
The beta isomer of PGMEA comprises only 10% of the commercial material, the
remaining 90% is alpha isomer. Hazard appears low but emphasizes the need
for care in handling this chemical. [I.C.I]

XYLENE:
unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Oral (human) LDLo: 50 mg/kg Skin (rabbit):500 mg/24h Moderate
Oral (rat) LD50: 4300 mg/kg Eye (human): 200 ppm Irritant
Inhalation (human) TCLo: 200 ppm Eye (rabbit): 87 mg Mild
Inhalation (man) LCLo: 10000 ppm/6h Eye (rabbit): 5 mg/24h SEVERE
Inhalation (rat) LC50: 5000 ppm/4h
Oral (Human) LD: 50 mg/kg
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Section 11 - TOXICOLOGICAL INFORMATION

Inhalation (Human) TCLo: 200 ppm/4h
Intraperitoneal (Rat) LD50: 2459 mg/kg
Subcutaneous (Rat) LD50: 1700 mg/kg
Oral (Mouse) LD50: 2119 mg/kg
Intraperitoneal (Mouse) LD50: 1548 mg/kg
Intravenous (Rabbit) LD: 129 mg/kg
Inhalation (Guinea) pig: LC 450 ppm/4h
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 a contact dermatitis (nonallergic). This form of dermatitis is often
characterised by skin redness (erythema) and swelling the epidermis. Histologically there
may be intercellular oedema of the spongy layer (spongiosis) and intracellular oedema of
the epidermis.
The substance is classified by IARC as Group 3:
NOT classifiable as to its carcinogenicity to humans.
Evidence of carcinogenicity may be inadequate or limited in animal testing.
Reproductive effector in rats

TITANIUM DIOXIDE:
unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Skin (human) 0.3: mg/3d- I Mild
The material may produce moderate eye irritation leading to inflammation. Repeated or
prolonged exposure to irritants may produce conjunctivitis.
The material may cause skin irritation after prolonged or repeated exposure and may
produce a contact dermatitis (nonallergic). This form of dermatitis is often
characterised by skin redness (erythema) and swelling epidermis. Histologically there may
be intercellular oedema of the spongy layer (spongiosis) and intracellular oedema of the
epidermis.

CARBON BLACK:
unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Inhalation (rat) TCLo: 50 mg/m鲁/6h/90D- I Nil Reported
Inhalation (rat) TCLo: 7 mg/m鲁
Dermal (rabbit) LD50: >3000 mg/kg
WARNING: This substance has been classified by the IARC as Group 2B: Possibly
Carcinogenic to Humans.

N-BUTANOL:
unless otherwise specified data extracted from RTECS - Register of Toxic Effects of Chemical Substances.
TOXICITY IRRITATION
Oral (rat) LD50: 790 mg/kg Skin (rabbit): 405 mg/24h- Moderate
Inhalation (human) TCLo: 25 ppm Eye (human): 50 ppm - Irritant
Inhalation (rat) LC50: 8000 ppm/4h Eye (rabbit): 1.6 mg- SEVERE
Dermal (rabbit) LD50: 3400 mg/kg Eye (rabbit): 24 mg/24h- SEVERE
Inhalation (human) TCLo: 86000 mg/m鲁

HYDROCARBON PROPELLANT:
Not available. Refer to individual constituents.


Section 12 - ECOLOGICAL INFORMATION

Marine Pollutant:Not Determined
Water hazard class 1 (self assessment): slightly hazardous to water.
Refer to data for ingredients, which follows:


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Section 12 - ECOLOGICAL INFORMATION

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

DO NOT discharge into sewer or waterways.
log Kow: -0.24
Half-life (hr) air: 312-1896
Half-life (hr) H2O surface water: 20
Henry's atm m鲁 /mol: 3.67E-05
BOD 5 if unstated: 0.31-1.76,46-55%
COD: 1.12-2.07
ThOD: 2.2
BCF: 0.69
Toxicity Fish: LC50(96) 5540-13000mg/L
Toxicity invertebrate: cell mult. inhib. 28-7500mg/L
Bioaccumulation: not sig
Nitrif. inhib.: 75% decr. at 840mg/L
Anaerobic effects: sig degrad
Degradation Biological: sig
processes Abiotic: Rxn OH*,photodissoc
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.
Drinking Water Standard: none available.
Soil Guidelines: none available.
Air Quality Standards: none available.

N-BUTYL ACETATE:
Fish LC50 (96hr.) (mg/l): 18
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Section 12 - ECOLOGICAL INFORMATION

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 m鲁 /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*

PROPYLENE GLYCOL MONOMETHYL ETHER ACETATE, ALPHA-ISOMER:
DO NOT discharge into sewer or waterways.

XYLENE:
Fish LC50 (96hr.) (mg/l): 13.5
BCF<100: 2.14- 2.20
log Kow (Prager 1995): 3.12- 3.20
Half- life Soil - High (hours): 672
Half- life Soil - Low (hours): 168
Half- life Air - High (hours): 44
Half- life Air - Low (hours): 2.6
Half- life Surface water - High (hours): 672
Half- life Surface water - Low (hours): 168
Half- life Ground water - High (hours): 8640
Half- life Ground water - Low (hours): 336
Aqueous biodegradation - Aerobic - High (hours): 672
Aqueous biodegradation - Aerobic - Low (hours): 168
Aqueous biodegradation - Anaerobic - High (hours): 8640
Aqueous biodegradation - Anaerobic - Low (hours): 4320
Photolysis maximum light absorption - High (nano- m): 269.5
Photolysis maximum light absorption - Low (nano- m): 265
Photooxidation half- life water - High (hours): 2.70E+08
Photooxidation half- life water - Low (hours): 3.90E+05
Photooxidation half- life air - High (hours): 44
Photooxidation half- life air - Low (hours): 2.6

The lower molecular weight hydrocarbons are expected to form a "slick" on the surface of
waters after release in calm sea conditions. This is expected to evaporate and enter the
atmosphere where it will be degraded through reaction with hydroxy radicals.

Some of the material will become associated with benthic sediments, and it is likely to
be spread over a fairly wide area of sea floor. Marine sediments may be either aerobic or
anaerobic. The material, in probability, is biodegradable, under aerobic conditions
(isomerised olefins and alkenes show variable results). Evidence also suggests that the
hydrocarbons may be degradable under anaerobic conditions although such degradation in
benthic sediments may be a relatively slow process.


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Section 12 - ECOLOGICAL INFORMATION

Under aerobic conditions the material will degrade to water and carbon dioxide, while
under anaerobic processes it will produce water, methane and carbon dioxide.

Based on test results, as well as theoretical considerations, the potential for
bioaccumulation may be high. Toxic effects are often observed in species such as blue
mussel, daphnia, freshwater green algae, marine copepods and amphipods.
Drinking Water Standards:
hydrocarbon total: 10 ug/l (UK max.).
DO NOT discharge into sewer or waterways.
The material is classified as an ecotoxin* because the Fish LC50 (96 hours) is less than
or equal to 0.1 mg/l

* Classification of Substances as Ecotoxic (Dangerous to the Environment)
Appendix 8, Table 1
Compiler's Guide for the Preparation of International Chemical Safety Cards: 1993
Commission of the European Communities.

TITANIUM DIOXIDE:
DO NOT discharge into sewer or waterways.

CARBON BLACK:
DO NOT discharge into sewer or waterways.

N-BUTANOL:
Fish LC50 (96hr.) (mg/l): 1910- 1940
Daphnia magna EC50 (48hr.) (mg/l): 1983
Algae IC50 (72hr.) (mg/l): 650
log Kow (Prager 1995): 0.88
log Kow (Sangster 1997): 0.84
log Pow (Verschueren 1983): 0.88
Half- life Soil - High (hours): 168
Half- life Soil - Low (hours): 24
Half- life Air - High (hours): 87.7
Half- life Air - Low (hours): 8.8
Half- life Surface water - High (hours): 168
Half- life Surface water - Low (hours): 24
Half- life Ground water - High (hours): 1296
Half- life Ground water - Low (hours): 48
Aqueous biodegradation - Aerobic - High (hours): 168
Aqueous biodegradation - Aerobic - Low (hours): 24
Aqueous biodegradation - Anaerobic - High (hours): 1296
Aqueous biodegradation - Anaerobic - Low (hours): 96
Aqueous biodegradation - Removal secondary treatment - High (hours): 99%
Aqueous biodegradation - Removal secondary treatment - Low (hours): 31%
Photooxidation half- life water - High (hours): 104000
Photooxidation half- life water - Low (hours): 2602
Photooxidation half- life air - High (hours): 87.7
Photooxidation half- life air - Low (hours): 8.8

DO NOT discharge into sewer or waterways.
log Kow: 0.88
Koc: 71.6
Half-life (hr) air: 5-52
Half-life (hr) H2O surface water: 2.4-3022
Henry's atm m鲁 /mol: 5.57E-06
BOD 5 if unstated: 1.1-2.04,33%
COD: 1.9,92%
ThOD: 2.594
Toxicity Fish: LD100(24)1.4g/L,LC50(96)1.91g/L
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Section 12 - ECOLOGICAL INFORMATION

Toxicity invertebrate: cell mult. inhib.8-650mg/L
Bioacculmulation: not sig
Nitrif. inhib.: 50% inhib at 8200mg/L
Effects on algae and plankton: cell mult. inhib.100-875mg/L
Degradation Biological: sig
processes Abiotic: RxnOH*

HYDROCARBON PROPELLANT:
The lower molecular weight hydrocarbons are expected to form a "slick" on the surface of
waters after release in calm sea conditions. This is expected to evaporate and enter the
atmosphere where it will be degraded through reaction with hydroxy radicals.

Some of the material will become associated with benthic sediments, and it is likely to
be spread over a fairly wide area of sea floor. Marine sediments may be either aerobic or
anaerobic. The material, in probability, is biodegradable, under aerobic conditions
(isomerised olefins and alkenes show variable results). Evidence also suggests that the
hydrocarbons may be degradable under anaerobic conditions although such degradation in
benthic sediments may be a relatively slow process.

Under aerobic conditions the material will degrade to water and carbon dioxide, while
under anaerobic processes it will produce water, methane and carbon dioxide.

Based on test results, as well as theoretical considerations, the potential for
bioaccumulation may be high. Toxic effects are often observed in species such as blue
mussel, daphnia, freshwater green algae, marine copepods and amphipods.
Drinking Water Standards:
hydrocarbon total: 10 ug/l (UK max.).
DO NOT discharge into sewer or waterways.


Section 13 - DISPOSAL CONSIDERATIONS

路 Consult State Land Waste Management Authority for disposal.
路 Discharge contents of damaged aerosol cans at an approved site.
路 Allow small quantities to evaporate.
路 DO NOT incinerate or puncture aerosol cans.
路 Bury residues and emptied aerosol cans at an approved site.


Section 14 - TRANSPORTATION INFORMATION




Labels Required: FLAMMABLE GAS
HAZCHEM: 2Y

UNDG:
Dangerous Goods Class: 2.1 Subrisk: None
UN Number: 1950 Packing Group: None
Shipping Name:AEROSOLS




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Section 14 - TRANSPORTATION INFORMATION

Air Transport IATA:
ICAO/IATA Class: 2.1 ICAO/IATA Subrisk: None
UN/ID Number: 1950 Packing Group: None
ERG Code: 10L
Shipping name:AEROSOLS

Maritime Transport IMDG:
IMDG Class: 2.1 IMDG Subrisk: SP63
UN Number: 1950 Packing Group: None
EMS Number: F- D, S- U Marine Pollutant: Not Determined
Shipping name:AEROSOLS



Section 15 - REGULATORY INFORMATION


REGULATIONS
0893 333 020 - Wurth Lacquer Spray Red High Gloss (CAS No: None):
No regulations applicable

acetone (CAS: 67-64-1) is found on the following regulatory lists;
IMO MARPOL 73/78 (Annex II) - List of Other Liquid Substances
New Zealand Hazardous Substances Transfer Notice 2004 - Schedule I, List of Substances (Dangerous Goods) to be transferred
New Zealand Poisons Schedule
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
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;
IMO MARPOL 73/78 (Annex II) - List of Noxious Liquid Substances Carried in Bulk
International Council of Chemical Associations (ICCA) - High Production Volume List
New Zealand Hazardous Substances Transfer Notice 2004 - Schedule I, List of Substances (Dangerous Goods) to be transferred
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals
United Nations Convention Against Illicit Traffic in Narcotic Drugs and Psychotropic Substances - Table II

propylene glycol monomethyl ether acetate, alpha-isomer (CAS: 108-65-6) is found on the following regulatory lists;
International Council of Chemical Associations (ICCA) - High Production Volume List
New Zealand Hazardous Substances Transfer Notice 2004 - Schedule I, List of Substances (Dangerous Goods) to be transferred
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals

xylene (CAS: 1330-20-7) is found on the following regulatory lists;
IMO MARPOL 73/78 (Annex II) - List of Noxious Liquid Substances Carried in Bulk
International Agency for Research on Cancer (IARC) Carcinogens
International Council of Chemical Associations (ICCA) - High Production Volume List
New Zealand Biological Exposure Indices
New Zealand Hazardous Substances Transfer Notice 2004 - Schedule I, List of Substances (Dangerous Goods) to be transferred
New Zealand Poisons Schedule
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals
WHO Guidelines for Drinking-water Quality - Guideline values for chemicals that are of health significance in drinking-water

titanium dioxide (CAS: 13463-67-7) is found on the following regulatory lists;
CODEX General Standard for Food Additives (GSFA) - Additives Permitted for Use in Food in General, Unless Otherwise Specified, in Accordance with GMP
International Agency for Research on Cancer (IARC) Carcinogens
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals
titanium dioxide (CAS: 1317-70-0) is found on the following regulatory lists;
OECD Representative List of High Production Volume (HPV) Chemicals
titanium dioxide (CAS: 1317-80-2) is found on the following regulatory lists;
OECD Representative List of High Production Volume (HPV) Chemicals

carbon black (CAS: 1333-86-4) is found on the following regulatory lists;
International Agency for Research on Cancer (IARC) Carcinogens
International Council of Chemical Associations (ICCA) - High Production Volume List
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals

n-butanol (CAS: 71-36-3) is found on the following regulatory lists;


continued...
0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 23 of 24
Section 15 - REGULATORY INFORMATION
IMO MARPOL 73/78 (Annex II) - List of Other Liquid Substances
International Council of Chemical Associations (ICCA) - High Production Volume List
New Zealand Hazardous Substances Transfer Notice 2004 - Schedule I, List of Substances (Dangerous Goods) to be transferred
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals

hydrocarbon propellant (CAS: 68476-85-7) is found on the following regulatory lists;
New Zealand Hazardous Substances Transfer Notice 2004 - Schedule I, List of Substances (Dangerous Goods) to be transferred
New Zealand Transferred List of Single Component Substances
New Zealand Workplace Exposure Standards (WES)
OECD Representative List of High Production Volume (HPV) Chemicals
hydrocarbon propellant (CAS: 68476-86-8) is found on the following regulatory lists;
OECD Representative List of High Production Volume (HPV) Chemicals

No data available for propylene glycol monomethyl ether acetate, alpha-isomer as CAS: 84540-57-8.
No data available for titanium dioxide as CAS: 12188-41-9.


Specific advice on controls required for materials used in
New Zealand can be found at
http://www.ermanz.govt.nz/search/registers.html


Section 16 - OTHER INFORMATION

NEW ZEALAND POISONS INFORMATION CENTRE
0800 POISON (0800 764 766)
NZ EMERGENCY SERVICES: 111



INGREDIENTS WITH MULTIPLE CAS NUMBERS

Ingredient Name CAS
propylene glycol monomethyl ether acetate, 108- 65- 6, 84540- 57- 8
alpha- isomer
titanium dioxide 13463- 67- 7, 1317- 70- 0, 1317- 80- 2, 12188-
41- 9
hydrocarbon propellant 68476- 85- 7, 68476- 86- 8


REPRODUCTIVE HEALTH GUIDELINES
Ingredient ORG UF
Endpoi CR Adeq
nt TLV
xylene 1.5 mg/m3 10 D NA -
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.

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.

continued...
0893 333 020 - WURTH LACQUER SPRAY RED HIGH GLOSS
Chemwatch Material Safety Data Sheet
Issue Date: 28-Jan-2005 CHEMWATCH 4598-22
NA477ECP Version No:3
CD 2007/2 Page 24 of 24
Section 16 - OTHER INFORMATION

Issue Date: 28-Jan-2005
Print Date: 24-Jul-2007

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