5875 SDS
===================================================================================================================
Section 1 -- PRODUCT AND COMPANY IDENTIFICATION
===================================================================================================================
HMIS CODES
Health 2
5875 Flammability 3
Reactivity 1
MANUFACTURER'S NAME: ADDRESS:
Cumberland Products Incorporated 50 Commerce Parkway
Hodgenville, KY 42748
EMERGENCY PHONE : (800) 424 - 9300 DATE PRINTED : 11/27/2013
INFORMATION PHONE : (800) 223 - 1918
FAX NUMBER : (800) 500 – 9812
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Section 2 -- COMPOSITION/INFORMATION ON HAZARDOUS INGREDIENTS
% by WT CAS No. INGREDIENT UNITS VP
===================================================================================================================
5 - 20% 108-65-6 Glycol Ether PM Acetate 3.7
ACGIH TLV N/E
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
1 - 5% 79-20-9 Methyl Acetate 228
ACGIH TLV 200 ppm (TWA)
ACGIH STEL 250 ppm (TWA)
OSHA PEL 200 ppm (TWA)
OSHA STEL N/E
NIOSH 200 ppm (TWA)
NIOSH ST 250 ppm
NIOSH IDLH 3100 ppm
5 - 20% 67-64-1 Acetone 180
ACGIH TLV 500 ppm (TWA)
ACGIH STEL 750 ppm
OSHA PEL 1000 ppm (TWA)
OSHA STEL N/E
NIOSH REL:250 ppm (TWA)
NIOSH IDLH 2500 ppm (10%)
1 - 5% 110-43-0 Methyl-n-Amyl Ketone 3
ACGIH TLV 50 ppm (TWA)
ACGIH STEL N/E
OSHA PEL 100 ppm (TWA)
OSHA STEL N/E
NIOSH 200 ppm (TWA)
NIOSH IDLH 800 ppm
0.1 - 1% 108-83-8 Diisobutyl Ketone (DIBK) 2
ACGIH TLV 200 ppm (TWA)
OSHA PEL 50 ppm (TWA)
NIOSH REL: 25 ppm (TWA)
NIOSH IDLH: 500 ppm
0.1 - 1% 8052-41-3 Mineral Spirits 2.000
ACGIH TLV 100 ppm (TWA)
OSHA PEL 500 ppm (TWA)
NIOSH REL: 350 mg/m3 (TWA)
NIOSH C 1800 mg/m3 (15-minute)
NIOSH IDLH: 20,000 mg/m3
0.1 - 1% 1330-20-7 Xylene 8
ACGIH TLV 100 ppm (TWA)
ACGIH STEL 2.5 mg/m3
OSHA PEL 2.5 mg/m3
OSHA STEL
5 - 20% 98-56-6 Parachlorobenzotrifluoride 5.3
ACGIH TLV 100 ppm (TWA)
ACGIH STEL 125 ppm (TWA)
OSHA PEL 100 ppm (TWA)
OSHA STEL N/E
1 - 5% 95-63-6 1,2,4-Trimethylbenzene N/A
ACGIH TLV N/E
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
0.1 - 1% 98-82-8 Isopropyl Benzene 8
ACGIH TLV 50 ppm
ACGIH STEL N/E
OSHA PEL 50 ppm
OSHA STEL N/E
1 - 5% 64742-95-6 Solvent Naphtha, petroleum, light aromatic .8
ACGIH TLV N/E
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
1 - 5% 65997-17-3 Silica, amorphous, precipitated and gel N/A
ACGIH TLV TWA: 10 mg/m3 inhalable
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
0.1 - 1% Mixture Diethylbenzene Isomer Mixture 1.3 mbar
ACGIH TLV
ACGIH STEL
OSHA PEL
OSHA STEL
0.1 - 1% 41556-26-7 Bis(1,2,2,6,6-Pentamethyl-4-piperidinyl) Sebacate
ACGIH TLV
ACGIH STEL
OSHA PEL
OSHA STEL
0.1 - 1% 104810-48-2 Poly Alcohol
ACGIH TLV N/E
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
0.1 - 1% 104810-47-1 Poly alcohol
ACGIH TLV N/E
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
0.1 - 1% 82919-37-7 Methyl 1,2,2,6,6-pentamethyl-4-piperidyl sebacate .0001
ACGIH TLV N/E
ACGIH STEL N/E
OSHA PEL N/E
OSHA STEL N/E
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Section 3 -- HAZARDS IDENTIFICATION
===================================================================================================================
ROUTES OF EXPOSURE:
Exposure may be by INHALATION and/or SKIN or EYE contact, depending on conditions of use. To minimize exposure, follow recommendations for proper use, ventilation, and personal protective equipment.
EFFECTS OF OVEREXPOSURE:
Irritation of eyes, skin and upper respiratory system. May cause nervous system depression. Extreme overexposure may result in unconsciousness and possibly death.
SIGNS AND SYMPTOMS OF OVEREXPOSURE:
Headache, dizziness, nausea, and loss of coordination are indications of excessive exposure to vapors or spray mists. Redness and itching or burning sensation may indicate eye or excessive skin exposure.
MEDICAL CONDITIONS AGGRAVATED BY EXPOSURE:
None generally recognized.
CANCER INFORMATION:
FOR COMPLETE DISCUSSION OF TOXICOLOGY DATA REFER TO SECTION 11.
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Section 4 -- FIRST AID MEASURES
===================================================================================================================
If INHALED:
If affected, remove from exposure. Restore breathing. Keep warm and quiet.
If on SKIN:
Wash affected area thoroughly with soap and water. Remove contaminated clothing and launder before re-use.
If in EYES:
Flush eyes with large amounts of water for 15 minutes. Get medical attention.
If SWALLOWED:
Do not induce vomiting. Get medical attention immediately.
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Section 5 -- FIRE FIGHTING MEASURES
===================================================================================================================
FLASH POINT LEL UEL
-4 F 0.8 16.0
EXTINGUISHING MEDIA:
Use National Fire Protection Association (NFPA) Class B extinguishers (carbon dioxide, dry chemical, or universal aqueous film forming foam) designed to extinguish NFPA Class IB flammable liquid fires. Water spray may be ineffective. Water spray may be used to cool closed containers to prevent pressure build-up and possible auto ignition or explosion when exposed to extreme heat.
UNUSUAL FIRE AND EXPLOSION HAZARDS:
Containers may explode when exposed to extreme heat. Application to hot surfaces requires special precautions. During emergency conditions overexposure to decomposition products may cause a health hazard. Symptoms may not be immediately apparent. Obtain medical attention.
SPECIAL FIRE FIGHTING PROCEDURES:
Full protective equipment including self-contained breathing apparatus should be used. Water spray may be ineffective. If water is used, fog nozzles are preferable. Water may be used to cool closed containers to prevent pressure build-up and possible auto ignition or explosion when exposed to extreme heat.
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Section 6 -- ACCIDENTAL RELEASE MEASURES
===================================================================================================================
STEPS TO BE TAKEN IN CASE MATERIAL IS RELEASED OR SPILLED:
Provide maximum ventilation. Only personnel equipped with proper respiratory, skin, and eye protection should be permitted in the area. Remove all sources of ignition. Take up spilled material with sand, vermiculite, or other noncombustible absorbent material and place in clean, empty containers for disposal. Only the spilled material and the absorbent should be placed in this container.
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Section 7 -- HANDLING RELEASE MEASURES
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PRECAUTIONS TO BE TAKEN IN HANDLING AND STORAGE:
Keep away from heat, sparks, and open flame. Vapors will accumulate readily and may ignite explosively. During use and until all vapors are gone: Keep area ventilated - Do not smoke - Extinguish all flames, pilot lights, and heaters - Turn off stoves, electric tools and appliances, and other sources of ignition. Consult NFPA Code. Use approved bonding and grounding procedures. Do not expose to temperature above 120F. Heat from sunlight, radiators, stoves, hot water, and other heat sources could cause container to burst. Do not take internally. Keep out of the reach of children.
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Section 8 -- EXPOSURE CONTROLS / PERSONAL PROTECTION
===================================================================================================================
PRECAUTIONS TO BE TAKEN IN USE:
Use only with adequate ventilation. Avoid contact with skin and eyes. Avoid breathing vapor and spray mist. Wash hands after using. This coating may contain materials classified as nuisance particulates (listed "as Dust" in section 2) which may be present at hazardous levels only during sanding or abrading of
the dried film. If no specific dusts are listed in section 2, the applicable limits for nuisance dust are ACGIII TLV 10 mg/m3 (total dust), 3 mg/m3 (respirable fraction), OSHA PEL 15 mg/m3 (total dust), 5 mg/m3 (respirable fraction). Removal of old paint by sanding, scraping, or other means may generate dust or fumes that contain lead.
VENTILATION:
Local exhaust preferable. General exhaust acceptable if the exposure to materials in section 2 is maintained below applicable exposure limits. Refer to OSHA Standards 1910.94, 1910.107, 1910.108.
RESPIRATORY PROTECTION:
If personal exposure cannot be controlled below applicable limits by ventilation, wear a properly fitted organic vapor/particulate respirator approved by NIOSH/MSHA for protection against materials in section 2. When sanding or abrading the dried film, wear a dust/mist respirator approved by NIOSH/MSHA for dust which may be generated from this product, underlying paint, or the abrasive.
PROTECTIVE GLOVES:
None required for normal application of these products where minimal skin contact is expected. For long repeated contact, wear chemical resistant gloves.
EYE PROTECTION:
Wear safety spectacles with unperforated side shields.
OTHER PRECAUTIONS:
Intentional misuse by deliberately concentrating and inhaling the contents can be harmful of fatal.
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Section 9 -- PHYSICAL AND CHEMICAL PROPERTIES
===================================================================================================================
PRODUCT WEIGHT 10.862 lb/gal 1302 g/l
SPECIFIC GRAVITY 1.300
BOILING POINT 0 - 662 F -18 - 350 C
VOLATILES 48.1 % by wt 61.2 % by vol
EVAPORATION RATE Same as ether
VAPOR DENSITY Heavier than air
REGULATORY VOC 2.64 lb/gal 317 g/l
ACTUAL VOC 1.55 lb/gal 185 g/l
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Section 10 -- STABILITY AND REACTIVITY
===================================================================================================================
STABILITY:
This product is normally stable and will not undergo hazardous reactions.
CONDITIONS TO AVOID:
None Known.
INCOMPATIBILITY:
Avoid contact with strong alkalies, strong mineral acids, or strong oxidizing agents.
HAZARDOUS DECOMPOSITION PRODUCTS:
Carbon monoxide, carbon dioxide, oxides of sulfur, oxides of barium, lowers molecular weight polymer fractions.
HAZARDOUS POLYMERIZATION:
None Known.
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Section 11 -- TOXICOLOGICAL INFORMATION
===================================================================================================================
CAS No. Ingredient Name
------------------------------------------------------------------------------------------------------------
108-65-6 Glycol Ether PM Acetate
IARC Classification Not Established
Acute Inhalation Effects: Rabbit, oral, LD 50 : >5 gm/kg
Chronic Effects: None Listed
Acute Oral Effects: Rat, oral, LD50: 8532 mg/kg
79-20-9 Methyl Acetate
IARC Classification Not Established
Oral: LD50: >5000 mg/kg, rat
Dermal: LD50: >2000 mg/kg, rat
Inhalation: LC50: >49 mg/l, rat 4h
Skin Irritation: Non-irritant
Species Rabbit
Method OECD 404
Eye Irritation: Irritant
Species Rabbit eye
Method OECD 405
In vitro Mutagenicity: Ames test-negative with and without
metabolic activation
In vitro Mutagenicity: Mutagenicity (micronucleus test)-negative
Rat Inhalation
67-64-1 Acetone
IARC Classification Not Established
Acute oral toxicity: LD50 Rat: 5,800 mg/kg
Acute inhalation toxicity: LC Lo Rat: 16000 ppm, 4h
Acute dermal toxicity: LD50 Rabbit: 20,000 mg/kg
110-43-0 Methyl n-Amyl Ketone
IARC Classification Not Established
Acute oral toxicity LD50 Rat: 1670 mg/kg
Acute inhalation toxicity LC Lo Rat: 4000 ppm, (4h)
Acute dermal toxicity LD50 Rabbit: 13000 mg/kg
108-83-8 Diisobutyl Ketone (DIBK)
IARC Classification Not Established
Oral rat, LD50: 5750 mg/kg;
skin rabbit, LD50: 16 g/kg.
Human data: 25 ppm/15 minutes (standard Draize)
produced mild eye irritation.
8052-41-3 Mineral Spirits
LC50 RAT 4HR N/E
LD50 RAT N/E
IARC Classification Not Established
Eye - Standard Draize Test Rabbit, Dose: 500 mg/24H; Reaction: Moderate
1330-20-7 Xylene
IARC Classification Group 3
Acute oral toxicity: LD50 Rat: 4.300 mg/kg
Acute inhalation toxicity: No data available
Acute dermal toxicity: LD50 Rabbit: (>) 2,000 mg/kg
98-56-6 Parachlorobenzotrifluoride
IARC Classification Not Established
LD50: 11500 mg/kg Oral Rat
LC50: 20 gm/m³
95-63-6 1,2,4-Trimethylbenzene
IARC Classification Not Established
Acute oral toxicity LD50: 3,400 - 6,000 mg/kg (Rat)
Acute inhalation toxicity LC50: 18,000 mg/m3, 4 h (Rat)
Acute dermal toxicity LD50: > 3,160 mg/kg (rabbit)
Skin irritation rabbit, Moderately irritating
Eye irritation Rat, Slightly irritating
Sensitisation dermal: non-sensitizer (Guinea pig,
Maximization Test)
Repeated dose toxicity 20 Days, inhalation: NOAEL: < 100 ppm,
(rat, ) CNS depression.28 Days, oral: NOAEL: < 500 mg/kg, (rat,)Changes in:
kidney
Mutagenicity Genetic Toxicity in Vitro:
Ames: negative (Salmonella typhimurium,
Metabolic Activation: with/without)
Genetic Toxicity in Vivo: Sister
Chromatid Exchange: (mouse, )
Positive and negative results were seen
in various in vivo studies.
Cytogenetic assay: (Rat, )negative
Developmental Toxicity/Teratogenicity
rat, female, inhalation, daily, NOAEL
(teratogenicity): 0.19%, No Teratogenic
effects observed at doses tested., No
fetotoxicity observed at doses tested.
98-82-8 Isopropyl Benzene
LC50 RAT 4HR 8000 ppm/4H
LD50 RAT 1400 mg/kg
IARC Classification Not Established
64742-95-6 Solvent Naphtha, petroleum, light aromatic
IARC Classification Not Established
Acute oral toxicity LD50: 3,500 mg/kg (rat, female)
LD50: > 5,000 mg/kg (rat, Male/Female)
Acute inhalation toxicity LC50: 10.2 mg/l, 4 h (rat)
LC50: 5.2 mg/l, 4 h (rat)
Acute dermal toxicity LD50: > 3,160 mg/kg (rabbit)
Skin irritation rabbit, Draize, Exposure Time: 24 h,
Slightly irritating
Eye irritation rabbit, Draize, Exposure Time: 24 h,
Slightly irritating
Sensitization dermal: non-sensitizer (guinea pig,
Maximization Test) dermal: non-sensitizer
(Human, Other method)
Repeated dose toxicity 90 D, Inhalation: NOAEL: 6.6 mg/l, (rat)
14 D, dermal: NOAEL: 3,750 mg/kg,(rabbit)
Mutagenicity
Genetic Toxicity in Vitro: Ames: negative (Salmonella typhimurium,
Metabolic Activation: with/without)
Carcinogenicity mouse, male, dermal, 2 Y, negative
rat, Male/Female, inhalation, 109 w, 6
hrs/day 7 days/week, positive, Kidney
carcinomas were found in male rats only
at all dose levels.
Toxicity to Reproduction/Fertility Two generation study, inhalation,
6 hrs/day 7 days/week, (rat, Male/Female)
NOAEL (F1): 500 ppm,
NOAEL (F2): 500 ppm
No effects on Reproductive parameters
observed at doses tested.
Three generation study,
inhalation, 6 hrs/day 7 days/week, (rat,
Male/Female) No effects on Reproductive
parameters observed at doses tested.
Developmental Toxicity/Teratogenicity rat, female, inhalation, NOAEL
(teratogenicity): > 1,573 ppm, No
Teratogenic effects observed at
doses tested.
65997-17-3 Silica, amorphous, precipitated and gel
LC50 RAT 4HR N/E
IARC Classification Not Established
Mixture Diethylbenzene Isomer Mixture
LD50 RAT 3 gm/kg
IARC Classification Not Established
41556-26-7 Bis(1,2,2,6,6-Pentamethyl-4-piperidinyl) Sebacate
IARC Classification Not Established
104810-48-2 Poly Alcohol
LC50 RAT 4HR N/E
LD50 RAT N/E
IARC Classification Not Established
104810-47-1 Poly alcohol
LC50 RAT 4HR N/E
LD50 RAT N/E
IARC Classification Not Established
82919-37-7 Methyl 1,2,2,6,6-pentamethyl-4-piperidyl sebacate
IARC Classification Not Established
Acute toxicity
Oral: LD50/rat: > 2,000 mg/kg
Skin irritation: rabbit: non-irritant
Eye irritation : rabbit: non-irritant
Sensitization: guinea pig: sensitizing (OECD Guideline
406)
IARC Reference
IARC Group 1: The agent is carcinogenic to humans
This category is used when there is sufficient evidence of carcinogenicity in humans. Exceptionally, an agent may be placed in this category when evidence of carcinogenicity in humans is less than sufficient but
there is sufficient evidence of carcinogenicity in experimental animals and strong evidence in exposed humans that the agent acts through a relevant mechanism of carcinogenicity.
IARC Group 2A: The agent is probably carcinogenic to humans.
This category is used when there is limited evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals. In some cases, an agent may be classified in this category when there is inadequate evidence of carcinogenicity in humans and sufficient evidence of carcinogenicity in experimental animals and strong evidence that the carcinogenesis is mediated by a mechanism that also operates in humans. Exceptionally, an agent may be classified in this category solely on the basis of limited evidence of carcinogenicity in humans. An agent may be assigned to this category if it clearly belongs, based on mechanistic considerations, to a class of agents for which one or more members have been classified in Group 1 or Group 2A.
IARC Group 2B: The agent is possibly carcinogenic to humans.
This category is used for agents for which there is limited evidence of carcinogenicity in humans and less than sufficient evidence of carcinogenicity in experimental animals. It may also be used when there is inadequate evidence of carcinogenicity in humans but there is sufficient evidence of carcinogenicity in experimental animals. In some instances, an agent for which there is inadequate evidence of carcinogenicity in humans and less than sufficient evidence of carcinogenicity in experimental animals together with supporting evidence from mechanistic and other relevant data may be placed in this group. An agent may be classified in this category solely on the basis of strong evidence from mechanistic and other relevant data.
IARC Group 3: The agent is not classifiable as to its carcinogenicity to humans.
This category is used most commonly for agents for which the evidence of carcinogenicity is inadequate in humans and inadequate or limited in experimental animals. Exceptionally, agents for which the evidence of carcinogenicity is inadequate in humans but sufficient in experimental animals may be placed in this category when there is strong evidence that the mechanism of carcinogenicity in experimental animals does not operate in humans. Agents that do not fall into any other group are also placed in this category. An evaluation in Group 3 is not a determination of non-carcinogenicity or overall safety. It often means that
further research is needed, especially when exposures are widespread or the cancer data are consistent with differing interpretations.
IARC Group 4: The agent is probably not carcinogenic to humans.
This category is used for agents for which there is evidence suggesting lack of carcinogenicity in humans and in experimental animals. In some instances, agents for which there is inadequate evidence of carcinogenicity in humans but evidence suggesting lack of carcinogenicity in experimental animals, consistently and strongly supported by a broad range of mechanistic and other relevant data, may be classified in this group.
===================================================================================================================
Section 12 -- ECOLOGICAL INFORMATION
CAS No. Ingredient Name
===================================================================================================================
108-65-6 Glycol Ether PM Acetate
Ecotoxicity: Rainbow Trout LC50: 100-180mg/L; Daphnia Magna
LC50: >400mg/L
Environmental Fate: Biodegradable over time with low
bioconcentration potential and a high
mobility rate in the soil.
Environmental Degradation: Biodegradation 84% after 28 days (OECD
test No. 301F)
79-20-9 Methyl Acetate
Toxicity to fish LC50: >250mg/l (96h)
Species Brachidanio rerio (zebra fish)
Method OECH 203
Toxicity to daphnia EC50: >1000 mg/l (48h)
Species Daphnia magna
Method OECD 202
Toxicity to Algae EC50: >120 mg/l (72h)
Species Scenedesmus subspicatus
Method OECD 201
Biodegradation 70% (28d)
Method OECD 301 D
67-64-1 Acetone
Aquatic toxicity
Acute and Prolonged Toxicity to Fish: No data available
Acute Toxicity to Aquatic Invertebrates: No data available
Environmental fate and pathways: No data available
110-43-0 Methyl n-Amyl Ketone
Aquatic toxicity
Acute and Prolonged Toxicity to Fish No data
Acute Toxicity to Aquatic Invertebrates No data
Enviornmental fate and pathways No data
108-83-8 Diisobutyl Ketone (DIBK)
Environmental Fate: When released into the soil, this
material may leach into groundwater. When
released into the soil, this material may
evaporate to a moderate extent. When
released into the soil, this material may
biodegrade to a moderate extent. When
released into water, this material may
evaporate to a moderate extent. When
released into water, this material may
biodegrade to a moderate extent. When
released into the water, this material is
expected to have a half-life between 1
and 10 days. This material has an
estimated bioconcentration factor (BCF)
of less than 100. This material is not
expected to significantly bioaccumulate.
When released into the air, this material
is expected to be readily degraded by
reaction with photochemically produced
hydroxyl radicals. When released into the
air, this material is expected to have a
half-life of less than 1 day.
Environmental Toxicity: No information found.
8052-41-3 Mineral Spirits
Environmental Fate: No information found.
Environmental Toxicity: No information found.
1330-20-7 Xylene
Biodegradability: No data available
Bioaccumulation: No Data Available
Ecotoxicity effects
Toxicity to fish: 96h LC50 Flathead minnow (oimephales
promelas); 23.53-29.97 mg/l
Method: Static
Mortality
Toxicity to daphnia and other aquatic Invertebrates: 24h LC50 Water flea (Daphnia
magna): > 100.00 -<1,000.00 mg/l
Method: Static
Mortality
Toxicity to algae: No data available
Toxicity to bacteria: No data available
Biochemical Oxygen Demand (COD): No data available
Chemical Oxygen Demand (COD): No data available
Additional ecological information: No data available
98-56-6 Parachlorobenzotrifluoride
AQUATIC ECOTOX DATA Fish: LC50 (96 hr.} (Rainbow trout} 13.5 mg/L
LC50 (96 hr.} (Bluegill sunfish} 12.0
mg/L
MATC (31 day} (Fathead minnow}
>0.54 <1.4 mg/L*
*Triethylene glycol used as solvent
carrier
BCF (48 hr.} (Bluegill sunfish} 121.8 &
202.0
Invertebrates: LC50 (48 hr.) (Water flea) 12.4 mg/L
MATC (21 day) (Water flea)
>0.03 < 0.05 mg/L*
*Acetone used as solvent carrier
Plants: IC50 (72 hr.) (Green & Blue-green algae)
500 mg/L
TERRESTRIAL ECOTOX DATA No data available
ENVIRONMENTAL FATE DATA
Biotic:
Biodegradation: inconclusive- due to volatility
Abiotic:
Atmospheric lifetime: estimated to be 65.9 days for OH radical
reaction
Log Kow 3.7
Koc 420- 530
Water Sol. @ 23 C 29.1
p-Chlorobenzotrifluoride (PCBTF) will
preferentially partition to the
atmosphere,
due to its high volatility. It
has been estimated that 99.93% of a 100
Kg spill would end up in the atmosphere,
While only 0.06% would partition to water
(M. Garlanda, 1990) .The aqueous
solubility of PCBTF (29.1 mg/L) would
also tend to limit its potential impact
to exposed aquatic systems. PCBTF has
exhibited significant toxicity to aquatic
species under laboratory conditions, but
is unlikely to exhibit a similar degree
of acute toxicity under environmental
conditions due to the aforementioned
solubility and volatility issues. The
moderate level of bioaccumulation
measured in laboratory tests will also be
subject to environmental mitigation due
to PCBTF's physical/chemical properties.
PCBTF should rapidly volatilize from dry
and moist soils. Volatility, and relative
environmental partitioning
characteristics, make it unlikely that
PCBTF represents a significant threat to
aquatic or terrestrial environments.
95-63-6 1,2,4-Trimethylbenzene
Biochemical Oxygen Demand (BOD) ca. 190 mg/l
Chemical Oxygen Demand (COD) ca. 440 mg/g
Bioaccumulation Cyprinus carpio (Carp), 31 - 207 BCF
Acute and Prolonged Toxicity to Fish LC50: 7.72 mg/l (Fathead minnow
(Pimephales promelas), 96 h)
Acute Toxicity to Aquatic Invertebrates EC50: 3.6 mg/l (Water flea (Daphnia
magna), 48 h)
98-82-8 Isopropyl Benzene
64742-95-6 Solvent Naphtha, petroleum, light aromatic
Biochemical Oxygen Demand (BOD) 5 Days, 190 mg/l
Chemical Oxygen Demand (COD) 440 mg/g
Acute and Prolonged Toxicity to Fish LC50: 320 - 435 mg/l (Golden orfe
(Leuciscus idus), 48 h)
LC50: 9.22 mg/l (Rainbow (Donaldson)Trout
(Oncorhynchus mykiss), 96 h)
Acute Toxicity to Aquatic Invertebrates EC50: 170 mg/l (Water flea (Daphnia
magna), 24 h)
EC50: 226 mg/l (Water flea (Daphnia
magna), 24 h) Toxicity to Aquatic Plants
EC50: 56 mg/l, (Green algae (Selenastrum
capricornutum), 72 h)
EC50: 19 mg/l, (Green algae (Selenastrum
capricornutum), 72 h)
Toxicity Other Non-Mammal Terrestial Species > 2,250 mg/kg, (Bobwhite quail)
65997-17-3 Silica, amorphous, precipitated and gel
Mixture Diethylbenzene Isomer Mixture
41556-26-7 Bis(1,2,2,6,6-Pentamethyl-4-piperidinyl) Sebacate
104810-48-2 Poly Alcohol
104810-47-1 Poly alcohol
82919-37-7 Methyl 1,2,2,6,6-pentamethyl-4-piperidyl sebacate
Environmental fate and transport
Biodegradation: Moderately/partially biodegradable.
Evaluation: Not readily biodegradable (by OECD
criteria).
Environmental toxicity
Acute and prolonged toxicity to fish: OECD 203; ISO 7346; 92/69/EEC, C.1
sunfish/LC50 (96 h): 0.97 mg/l
OECD 203; ISO 7346; 92/69/EEC, C.1
Rainbow trout/LC50 (96 h): 7.9 mg/l
Acute toxicity to aquatic invertebrates: OECD Guideline 202, part 1 Daphnia
magna/EC50 (24 h): 20 mg/l
Toxicity to microorganisms: OECD Guideline 209 activated sludge/EC50
(3 h): > 100 mg/l
===================================================================================================================
Section 13 -- DISPOSAL CONSIDERATIONS
===================================================================================================================
WASTE DISPOSAL METHOD:
Waste from this product may be hazardous as defined under the Resource Conservation and Recovery Act (RCRA) 40 CFR 261. Do not incinerate. Depressurize container. Dispose of in accordance with Federal, State, and Local regulations regarding pollution.
Section 14 -- TRANSPORT INFORMATION
Proper Shipping Name: Consumer Commodity
NOS Technical Name: ORM-D
Hazard Class: N/A
UN Number: N/A
Packing Group: N/A
Section 15 -- REGULATORY INFORMATION
Canadian Regulations:
CEPA (Canadian Environmental Protection Act):
All substances in this product are listed on the Canadian Domestic Substance List (DSL) or are not required to be listed.
US Regulations:
This product contains the following substances subject to the reporting requirements of Section 313 of Title III of the Superfund Amendments and Reauthorization Act of 1986 and 40 CFR Part 372.
SARA 313:
CAS No. CHEMICAL/COMPOUND % by WT
------------------------------------------------------------------------------------------------------------
8052-41-3 Mineral Spirits 0.8
1330-20-7 Xylene 0.2
98-82-8 Isopropyl Benzene 0.1
CALIFORNIA PROPOSITION 65
WARNING: This product contains chemicals known to the State of California to cause cancer and birth defects or other reproductive harm.
TSCA CERTIFICATION:
U.S. TSCA: This product and/or all of its components are listed on the U.S. TSCA Inventory or is otherwise exempt form TSCA Inventory reporting requirements.
===================================================================================================================
Section 16 -- OTHER INFORMATION
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DISCLAIMER:
Do not handle until the manufacturer's safety precautions have been read and understood. Regulations require that all employees be trained on Material Safety Data Sheets for all products with which they come in contact. While we believe that the data contained herein is accurate and derived from qualified sources, the data are not to be taken as a warranty or representation for which we assume legal responsibility. They are offered solely for your consideration, investigation, and verification. Any use of these data and information must be determined by the user to be in accordance with applicable federal, state, provincial, and local laws and regulations.
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ENVIRONMENTAL DATA SHEET
All data given below are MAXIMUM THEORETICAL VALUES based on the product AS CURRENTLY FORMULATED. Variations
may occur on individual batches due to adjustments made during production.
PRODUCT NUMBER
CP-5875
PRODUCT NAME
2.8 Vintage Hot Rod White (Satin)
PRODUCT WEIGHT SPECIFIC GRAVITY FLASH POINT
10.862 lb/gal 1.300 -4 F
VOLATILE INGREDIENTS CERC. SARA HAPS PCT PCT
NAME CAS No. 313 112 by by
TC Wt Vol
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Methyl Acetate 79-20-9 X 3.1 4.3
Methyl n-Amyl Ketone 110-43-0 X 3.0 4.8
Mineral Spirits 8052-41-3 X 0.8 1.3
Xylene 1330-20-7 X X X 0.2 0.3
Isopropyl Benzene 98-82-8 X X 0.1 0.2
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VOLATILE ORGANIC COMPOUNDS
A. Coating Density 10.86 lb/gal 1302 g/l
B. Total Volatiles 48.1 % by wt 61.2 % by vol
Exempt Volatiles 33.9 % by wt 41.5 % by vol
Water 0.0 % by wt 0.0 % by vol
C. Organic Volatiles 14.2 % by wt 19.7 % by vol
D. Percent Non-Volatile 51.9 % by wt 38.8 % by vol
E. Regulatory VOC 2.64 lb/gal 317 g/l
Actual VOC 1.55 lb/gal 185 g/l
Solids 5.63 lb/gal 675 g/l
WASTE DISPOSAL
Waste from this product may be hazardous as defined under the Resource Conservation and Recovery Act (RCRA) 40 CFR 261. Waste must be tested for ignitability to determine the applicable EPA hazardous waste numbers. The addition of reducers or other additives to this product may substantially alter the above data. Since conditions of use are outside our control, we make no warranties, express or implied, and assume no liability in connection with any use of this information.