N-BUTYL ALCOHOL

N-BUTYL ALCOHOL
CASRN: 71-36-3
http://toxnet.nlm.nih.gov/cgi-bin/sis/search/f?./temp/~BAAc8a4qL:1

Human Health Effects:

Human Toxicity Excerpts:

Symptomatology: 1. Central nervous system: headache, muscle weakness, giddiness, ataxia, confusion, delirium, coma. 2. Gastrointestinal: nausea, vomiting, diarrhea (odor of the alcohol in excreta). 3. Irritation of skin, eyes, throat from vapor or liquid. Cough and dyspnea. 4. Death from resp failure. 5. Disturbances of cardiac rhythm. 6. Occasional complications: a. Gastrointestinal hemorrhage b. Renal damage with glycosuria c. Liver damage d. Cardiac failure e. Pulmonary edema. /Alcohols (higher)/
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. II-173]**PEER REVIEWED**

CIRCUMSTANTIAL EVIDENCE POINTS TO BUTYL ALCOHOL VAPOR AS CAUSE OF A SPECIAL VACUOLAR KERATITIS IN HUMAN BEINGS. ... IN SOME PATIENTS VACUOLAR KERATOPATHY CAUSES NO COMPLAINTS, BUT IN THE MOST SEVERELY AFFECTED IT HAS BEEN ASSOCIATED WITH PAIN & TEARING, CHARACTERISTICALLY MOST MARKED ON FIRST OPENING EYES IN MORNING.
[Grant, W.M. Toxicology of the Eye. 3rd ed. Springfield, IL: Charles C. Thomas Publisher, 1986. 162]**PEER REVIEWED**

A 10 yr study was conducted of men exposed to 1-butanol in an industrial setting. ... The concentration of 1-butanol was 200 ppm or more, and corneal inflammation was occasionally observed. Ocular symptoms included a burning sensation, blurring of vision, lachrymation, and photophobia. Symptoms became more severe toward the end of the work week.
[Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994. 2640]**PEER REVIEWED**

ITS VAPORS IRRITATE & CAUSE COUGH. ... MAY CAUSE IRRITATION OF MUCOUS MEMBRANES, CONTACT DERMATITIS, HEADACHE, DIZZINESS, DROWSINESS.
[The Merck Index. 10th ed. Rahway, New Jersey: Merck Co., Inc., 1983. 214]**PEER REVIEWED**

TRANSIENT MILD EDEMA OF CONJUNCTIVA OF THE EYE & A SLIGHTLY REDUCED ERYTHROCYTE COUNT MAY OCCUR ABOVE 200 PPM.
[International Labour Office. Encyclopaedia of Occupational Health and Safety. 4th edition, Volumes 1-4 1998. Geneva, Switzerland: International Labour Office, 1998.,p. 104.33]**PEER REVIEWED**

... SERIOUS SYSTEMIC EFFECTS ... IN THE FORM OF AUDITORY NERVE & VESTIBULAR INJURY HAVE BEEN REPORTED IN WORKERS OUTSIDE THE USA (FRANCE AND MEXICO).
[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I,II, III. Cincinnati, OH: ACGIH, 1991. 170]**PEER REVIEWED**

AS EXTRAPOLATED FROM RAT DATA ... 3 TO 7 OZ REPRESENTS REASONABLE EST OF SINGLE ORAL MEAN LETHAL DOSE OF ANY BUTYL ALCOHOL IN MAN. /ALCOHOLS, HIGHER/
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. III-13]**PEER REVIEWED**

ETHANOL & CERTAIN SHORT-CHAIN ARYL (BENZYL) & ALIPHATIC (PROPYL, BUTYL) ALCOHOLS PRODUCED UP TO 10 FOLD INCR IN CYCLIC AMP CONCN IN PURIFIED HUMAN PERIPHERAL BLOOD LYMPHOCYTES. ETHANOL CONCN AS LOW AS 80 MG/DL PRODUCED SIGNIFICANT ELEVATIONS IN LYMPHOCYTE CYCLIC AMP.
[ATKINSON JP ET AL; J CLIN INVEST 60 (2): 284-94 (1977)]**PEER REVIEWED**

... BUTYL ALCOHOLS ... HAVE PRODUCED FEW CASES OF POISONING IN INDUSTRY BECAUSE OF THEIR LOW VOLATILITY. /BUTYL ALCOHOLS/
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

A CASE IS REPORTED OF OCCUPATIONALLY ACQUIRED SENSITIVITY TO ISOPROPYL ALCOHOL IN WHICH, ON TESTING WITH GAS CHROMATOGRAPHICALLY PURIFIED MATERIAL, POSITIVE PATCH TEST REACTIONS WERE FOUND TO 1-PROPANOL, 1-BUTANOL, 2-PROPANOL, 2-BUTANOL.
[LUDWIG E, HAUSEN BM; CONTACT DERMATITIS 3 (5): 240-4 (1977)]**PEER REVIEWED**

THE ACTIVITY OF PARTIALLY PURIFIED HUMAN ERYTHROCYTE ACID PHOSPHATASE (EAPASE) WAS ENHANCED 4-FOLD BY N-BUTANOL. THE EXTENT OF HUMAN PROSTATIC ACID PHOSPHATASE (PAPASE) ACTIVATION BY N-PROPANOL WAS LOWER THAN THAT OF EAPASE. EAPASE & PAPASE ACTIVATION BY ALIPHATIC ALCOHOLS, INCLUDING N-BUTANOL WAS NONCOMPETITIVE.
[SAWADA H ET AL; CHEM PHARM BULL (TOKYO) 28 (12): 3466-72 (1980)]**PEER REVIEWED**

In high concn in the air it can cause CNS depression.
[Sullivan, J.B. Jr., G.R. Krieger (eds.). Hazardous Materials Toxicology-Clinical Principles of Environmental Health. Baltimore, MD: Williams and Wilkins, 1992. 1106]**PEER REVIEWED**

Short-term exposure of humans to n-butanol produces a variety of CNS effects, including headaches, giddiness, ataxia, confusion, delirium & possible coma. Muscle weakness may also be observed. Possible gastrointestinal effects include nausea & vomiting. In addition, butanol liquid or vapors cause irritation to the skin & membranes in the eyes & upper respiratory tract.
[Snyder, R. (ed.). Ethel Browning's Toxicity and Metabolism of Industrial Solvents. Second Edition. Volume 3 Alcohols and Esters. New York, NY: Elsevier, 1992. 40]**PEER REVIEWED**

 

Skin, Eye and Respiratory Irritations:

May cause irritation of mucous membranes.
[The Merck Index. 10th ed. Rahway, New Jersey: Merck Co., Inc., 1983. 214]**PEER REVIEWED**

Vapor: Irritating to eyes, nose and throat; ... Liquid: Irritating to skin and eyes.
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

It is a strong irritant of the mucous membranes, eyes, skin & respiratory tract.
[Sullivan, J.B. Jr., G.R. Krieger (eds.). Hazardous Materials Toxicology-Clinical Principles of Environmental Health. Baltimore, MD: Williams and Wilkins, 1992. 1106]**PEER REVIEWED**

 

Medical Surveillance:

Employees should be screened for history of certain medical conditions ... /skin, liver, kidney, eye, or chronic respiratory diseases central and peripheral nervous systems/ which might place the employee at increased risk from butyl alcohol exposure. ... Any employee developing the ... conditions should be referred for further medical exam.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 1]**PEER REVIEWED**

Blood n-butanol concn should not exceed 0.08 mg/l during exposure at the threshold limit value of 50 ppm.
[Baselt, R.C. Biological Monitoring Methods for Industrial Chemicals. 2nd ed. Littleton, MA: PSG Publishing Co., Inc. 1988. 51]**PEER REVIEWED**

 

Probable Routes of Human Exposure:

THE PRODN OR, IN SOME CASES, USE OF THE FOLLOWING ... MAY OFFER EXPOSURE TO N-BUTYL ALCOHOL: ARTIFICIAL LEATHER, BUTYL ESTERS, RUBBER CEMENT, DYES, FRUIT ESSENCES, LACQUERS, MOTION PICTURE & PHOTOGRAPHIC FILMS, RAINCOATS, PERFUMES, PYROXYLIN PLASTICS, RAYON, SAFETY GLASS, SHELLAC, VARNISH & WATER PROOFED CLOTH.
[Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994. 2636]**PEER REVIEWED**

Use and liberation during spray, brush, or dip application of surface coatings. Use in adhesive and as a solvent adhesive in the manufacture of garments from polyvinyl butyral coated fabric. Liberation during the manufacture of derivatives of butyl alcohol, including chemicals, herbicides, ore flotation agents, urea and melamine formaldehyde resins, and pharmaceuticals. Use as a solvent or as a diluent in the manufacture of brake fluids, detergents, denatured alcohol, and surface coatings, and as a swelling agent in textiles. It is also used as an azeotrophic dehydrating agent and blending agent in laboratory analysis, and liberation as a by-product in furfural tetrahydrofuran conversion.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 3]**PEER REVIEWED**

NIOSH (NOES Survey 1981-83) has statistically estimated that 794,284 workers (115,385 of these are female) are potentially exposed to n-butyl alcohol in the US(1). Occupational exposure may occur through inhalation and dermal contact with this compound at workplaces where n-butyl alcohol is produced or used(SRC). The concentration of n-butyl alcohol in expired air from 8 individuals employed as sprayers during the varnishing of automobiles ranged from 1.3-35.0 ug/hr(2). n-Butyl alcohol was identified, not quantified, in 29 air samples from printing shops and 18 painting shops in Belgium(3). n-Butyl alcohol was detected at a mean concn of 1.6 ug/cu m in 73 samples of exhaled breath from 111 Belgian workers exposed to a solvent mixture(4). The general population is exposed to n-butyl alcohol through the ingestion of foods that contain this compound and inhalation of ambient air(SRC).
[(1) NIOSH; National Occupational Exposure Survey (NOES) (1989) (2) Conkle JP et al; Arch Environ Health 30: 290-5 (1975) (3) Veulemans H et al; Ind Hyg Assoc J 48: 671-76 (1987) (4) Veulemans H et al; Scand J Work Environ Health 13: 239-42 (1987)]**PEER REVIEWED**

 

Body Burden:

n-Butyl alcohol was identified, not quantified, in human blood(1) and mother's milk(2). n-Butyl alcohol was detected in human breath samples at concns of 1-10 ppb(3). The concentration of n-butanol in expired air from 8 individuals ranged from 1.3-35.0 ug/hr(4). n-Butyl alcohol was detected at concns of 0.02 and 0.08 ng/l in 2 samples of the expired air of 54 individuals(5). n-Butyl alcohol was detected at a mean concn of 1.6 ug/cu m in the exhaled breath of Belgian workers exposed to a solvent mixture(6).
[(1) Bonin MA et al; Amer Chem Soc, Div Env Chem, 206th ACS Nat Meet., 33: 21-24 (1993) (2) Pellizzari ED et al; Bull Environ Contam Toxicol 28: 322-28 (1982) (3) Fenske JD, Paulson SE; J Air Waste Manage Assoc 49: 594-98 (1999) (4) Conkle JP et al; Arch Environ Health 30: 290-5 (1975) (5) Krotoszynski BK et al; J Anal Toxicol 3: 225-34 (1979) (6) Veulemans H et al; Scand J Work Environ Health 13: 239-42 (1987)]**PEER REVIEWED**

 

Minimum Fatal Dose Level:

AS EXTRAPOLATED FROM RAT DATA ... 3 TO 7 OZ REPRESENTS REASONABLE EST OF SINGLE ORAL MEAN LETHAL DOSE OF ANY BUTYL ALCOHOL IN MAN. /ALCOHOLS, HIGHER/
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. III-13]**PEER REVIEWED**

Antidote and Emergency Treatment:

Basic Treatment: Establish a patent airway. Suction if necessary. Watch for signs of respiratory insufficiency and assist ventilations if necessary. Administer oxygen by nonrebreather mask at 10 to 15 L/min. Monitor for shock and treat if necessary ... . Monitor for pulmonary edema and treat if necessary ... . Anticipate seizures and treat if necessary ... . For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with normal saline during transport ... . Do not use emetics. For ingestion, rinse mouth and administer 5 ml/kg up to 200 ml of water for dilution if the patient can swallow, has a strong gag reflex, and does not drool. Administer activated charcoal ... . /Higher alcohols (>3 carbons) and related compounds/
[Bronstein, A.C., P.L. Currance; Emergency Care for Hazardous Materials Exposure. 2nd ed. St. Louis, MO. Mosby Lifeline. 1994.,p. 200-01]**PEER REVIEWED**

Advanced Treatment: Consider orotracheal or nasotracheal intubation for airway control in the patient who is unconscious or has severe pulmonary edema. Positive-pressure ventilation techniques, with a bag-valve-mask device, may be beneficial. Monitor cardiac rhythm and treat arrhythmias as necessary ... . Start an IV with D5W /SRP: "To keep open", minimal flow rate/. Use lactated Ringer's if signs of hypovolemia are present. Watch for signs of fluid overload. Monitor for signs of hypoglycemia (decreased LOC, tachycardia, pallor, dilated pupils, diaphoresis, and/or dextrose strip or glucometer readings below 50 mg) and administer 50% dextrose if necessary ... . Treat seizures with diazepam (Valium) ... . For hypotension with signs of hypovolemia, administer fluid cautiously. Consider vasopressors if patient is hypotensive with a normal fluid volume. Watch for signs of fluid overload ... . Consider drug therapy for pulmonary edema ... . Use proparacaine hydrochloride to assist eye irrigation ... . /Higher alcohols (>3 carbons) and related compounds/
[Bronstein, A.C., P.L. Currance; Emergency Care for Hazardous Materials Exposure. 2nd ed. St. Louis, MO. Mosby Lifeline. 1994. 201]**PEER REVIEWED**

 

Animal Toxicity Studies:

 

 

Evidence for Carcinogenicity:

CLASSIFICATION: D: not classifiable as to human carcinogenicity. BASIS FOR CLASSIFICATION: Based on no human and no animal cancer data. HUMAN CARCINOGENICITY DATA: None. ANIMAL CARCINOGENICITY DATA: None.
[U.S. Environmental Protection Agency's Integrated Risk Information System (IRIS) on n-Butanol (71-36-3) Available from: http://www.epa.gov/ngispgm3/iris on the Substance File List as of March 15, 2000]**PEER REVIEWED**

 

Non-Human Toxicity Excerpts:

LIKE THE OTHER BUTYL ALCOHOLS, TERTIARY BUTYL ALCOHOL IS A ... /CNS DEPRESSANT/, STRONGER IN ANIMALS THAN BUTANOL-1 OR ISOBUTYL ALCOHOL.
[Browning, E. Toxicity and Metabolism of Industrial Solvents. New York: American Elsevier, 1965. 354]**PEER REVIEWED**

/CNS DEPRESSANT/ ... DOSE. (I) BY ORAL ADMIN FOR RABBITS, DEEP & RAPID ... /CNS DEPRESSION/ FOLLOWED A DOSAGE OF 2.1 TO 2.44 G/KG. (II) BY IP INJECTION, FOR MICE, 0.76 ML/KG ... (III) BY INHALATION, FOR MICE, 6600 PPM. ... RABBITS GIVEN ORALLY 1 TO 1.5 G/KG SHOWED MODERATE REDUCTION OF SENSITIVITY & WITHIN 20 TO 30 MIN SLIGHT PARALYSIS. WITH DOSAGE OF 1.6-2.0 G/KG THEY SHOWED PRIMARY EXCITEMENT, AND AFTER 15 MIN COMPLETE PARALYSIS, ANALGESIA, DIMINISHED CORNEAL, PUPILLARY & CILIARY REFLEXES, REDN OF BODY TEMP & RESPIRATION, WITH HIGHER DOSAGES, NYSTAGMUS, SALIVATION & DEEP ... /CNS DEPRESSION/ LASTING 36 HR.
[Browning, E. Toxicity and Metabolism of Industrial Solvents. New York: American Elsevier, 1965. 345]**PEER REVIEWED**

ANIMALS EXPOSED TO N-BUTYL ALCOHOL IN AIR MAY MANIFEST ... ATAXIA, PROSTRATION, & ... /CNS DEPRESSION/. ... DEATHS FROM ACUTE OVEREXPOSURE ARE BELIEVED DUE TO RESPIRATORY FAILURE. ... GUINEA PIGS EXPOSED TO 100 PPM, 4 HR/DAY 6 DAYS/WK FOR 64 EXPOSURES SHOWED A DECR IN NUMBER OF RED BLOOD COUNT & RELATIVE & ABSOLUTE LYMPHOCYTOSIS, SOME EVIDENCE OF LUNG HEMORRHAGE, ALBUMINURIA, EARLY DEGENERATIVE CHANGES OF THE LIVER, & CORTICAL & TUBULAR DEGENERATION IN THE KIDNEYS. MICE SUBJECTED TO 130 HR OF TOTAL EXPOSURE (UNSTATED NUMBER OF HR PER DAY FOR SEVERAL DAYS) TO A CONCN OF 8000 PPM (24.3 MG/L OF AIR) /SHOWED CNS DEPRESSION/ ... REPEATEDLY BUT GAINED IN WEIGHT & SURVIVED. REVERSIBLE FATTY CHANGES WERE OBSERVED IN THE LIVERS OF THE MICE.
[Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994. 2639]**PEER REVIEWED**

LIQ N-BUTYL ALCOHOL TESTED BY APPLYING DROP TO RABBIT EYES CAUSED MODERATE TEMPORARY INJURY, GRADED 7 ON SCALE OF 1 TO 10 AFTER 24 HR. /10 IS MOST SEVERE INJURY/
[Grant, W.M. Toxicology of the Eye. 3rd ed. Springfield, IL: Charles C. Thomas Publisher, 1986. 162]**PEER REVIEWED**

TREATMENTS OF RABBIT SARCOPLASMIC RETICULUM VESICLES WITH AQUEOUS /SOLUTIONS OF/ C1-C7 N-ALCOHOLS INHIBITED CALCIUM UPTAKE & ENHANCED ATP ACTIVITY. /C1-C7 N-ALCOHOLS/
[KONDO M, KASAI M; BIOCHIM BIOPHYS ACTA 311 (3): 391-9 (1973)]**PEER REVIEWED**

THE SUCCESS RATE OF A CONDITIONED RESPONSE IN GOLDFISH WAS TESTED AS A FUNCTION OF TIME AFTER SINGLE ADDITIONS OF N-BUTANOL AT DIFFERENT CONCENTRATIONS. FOLLOWING A STEP INCR IN ALC CONCN TO GOLDFISH, INITIAL CONDITIONAL RESPONSE SUCCESS RATE DECR & WAS RELATED BOTH TO INITIAL CONCN & TO SIZE OF THE STEP. AFTER SINGLE STEPS TO FINAL CONCN OF 15 MMOLE THERE WAS NO EVIDENCE OF RECOVERY BY 5 HR. AT 20 MMOLE FISH WERE FULLY ANESTHETIZED.
[HILL MW ET AL; J COMP PHYSIOL 142 (1): 61-5 (1981)]**PEER REVIEWED**

SHORT & LONG CHAIN ALCOHOLS CAUSED NERVE BLOCK IN GUINEA PIG LATERAL OLFACTORY TRACT (15-20 MIN FOR N-BUTANOL).
[HESKETH TR ET AL; J PHYSIOL (LONDON) 278: 5P-6P (1978)]**PEER REVIEWED**

Studies of the neuronal effects of aliphatic alcohols of varying chain lengths were done on sciatic nerve preparations of Xenopus laevis, in order to obtain information on the action mechanisms of anesthetics. With regard to their ability to reduce the permeability constants for sodium ions and potassium ions, the alcohols ranked as follows: octanol greater than heptanol greater than or equal to 2-octanol greater than butanol greater than propyl alcohol greater than ethyl alcohol.
[Aarhem P, Van Helden D; Acta Physiol Scand 119 (1): 105-7 (1983)]**PEER REVIEWED**

In mouse striatal membranes, ethyl alcohol, propyl alcohol, & butyl alcohol all increased adenylate cyclase activity in the presence of 5-guanylylimidodiphosphate (nucleotide-binding protein), & their effects on adenylate cyclase activity were linearly correlated with their respective carbon chain lengths.
[Luthin GR, Tabakoff B; J Pharmacol Exp Ther 228 (3): 579-87 (1984)]**PEER REVIEWED**

Alcohol exposure produced a dose dependent elevation and then decline in specific prolactin binding in membrane preparations from ventral prostate glands of adult rats. 1-Butanol produced a maximal 37-42% increase in prolactin binding at a concn of 1.0%. The value of the microviscosity parameter decreased by 10-13% after a 15 min exposure of prostatic membranes to 1.0% butanol. Evidently, in vitro fluidization of prostatic membrane modifies prolactin binding capacity.
[Dave JR, Witorsch RJ; Biochem Biophys Res Commun 113 (1): 220-8 (1983)]**PEER REVIEWED**

Injection of n-butyl alcohol into the yolk sac of fertile eggs prior to incubation was used to determine toxicity. Butyl alcohol produced marked teratogenic effects in the chick embryo, such as damage to eyes, kidney, and nerves. Injection doses ranged from 0.17 to 234 mg/egg.
[McLaughlin J et al; Am Ind Hyg Assoc J 25 (3): 282-4 (1964)]**PEER REVIEWED**

The butyl alcohols are ... 2 to 5 times more toxic than ethanol when tested acutely in the rat. ... Toxic symptoms from butyl ... alcohol are usually more severe and more prolonged than those in ethanol intoxication. /Alcohols, higher/
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. III-13]**PEER REVIEWED**

IN THE RAT ... THE ORDER OF INCREASING LETHALITY BY SINGLE DOSE ORAL ADMIN IS AS FOLLOWS: ETHYL, ISOPROPYL AND SEC-BUTYL, N-BUTYL, TERT-BUTYL, ISOBUTYL, & AMYL ALCOHOLS.
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. III-12]**PEER REVIEWED**

Changes in the cytochrome p450 enzyme systems were investigated in the liver, kidney, and lung of rats exposed to n-butanol and its isomers at 2000 ppm for 3 days and at 500 ppm for 5 days. A pronounced increase in the microsomal p450 was observed in the kidney, with sec and tert butanol causing 47% and 36% increases, respectively. The lung and liver microsomal p450 was unaltered. The induction of p450 was greater at lower concentration. A longer duration of exposure is required for the enzyme induction in the kidney, whereas the concentration is an imporatant factor for its induction in the liver.
[Aarstad K et al; Arch Toxicol Suppl 8: 418-21 (1985)]**PEER REVIEWED**

LOCAL ANESTHETICS AND ALCOHOLS INHIBITED MITOCHONDRIAL ELECTRON TRANSPORT AT SEVERAL POINTS ALONG THE CHAIN. N-BUTANOL & BENZYL ALC INHIBITED EACH OF SEGMENTS OF RAT LIVER & BEEF HEART MITOCHONDRIAL ELECTRON TRANSPORT CHAIN ASSAYED; THESE INCL CYTOCHROME C OXIDASE, DUROHYDROQUINONE OXIDASE, SUCCINATE OXIDASE & DEHYDROGENASE, NADH OXIDASE, SUCCINATE-CYTOCHROME C OXIDOREDUCTASE, & OTHERS.
[CHAZOTTE B, VANDERKOOI G; BIOCHIM BIOPHYS ACTA 636 (2): 153-61 (1981)]**PEER REVIEWED**

A CORRELATION BETWEEN HYPNOTIC POTENCY OF ALIPHATIC ALC & ABILITIES TO DISRUPT STRUCTURE OF NEURONAL MEMBRANE IN VITRO WAS ESTABLISHED. SIGNIFICANT REDN IN ORDER PARAMETER WERE OBSERVED @ NERVE BLOCKING CONCN. THE FOLLOWING ALCOHOLS WERE INVESTIGATED: ETHANOL, PROPANOL, 2-PROPANOL, BUTANOL, 2-BUTANOL, 2-METHYL-1-PROPANOL, 2-METHYL-2-PROPANOL. DISORDERING POTENCY OF EACH ALCOHOL WAS CLOSELY RELATED TO ITS MEMBRANE SOLUBILITY, BASED ON OIL/WATER PARTITION COEFFICIENT.
[LYON RC ET AL; J PHARMACOL EXP THER 218 (3): 669-75 (1981)]**PEER REVIEWED**

... Rats were not killed in 4 hr of inhalation exposure to n-butyl alcohol at 8000 ppm. ... No /CNS depressant/ or irritative effects are to be anticipated at 100 ppm.
[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I,II, III. Cincinnati, OH: ACGIH, 1991. 170]**PEER REVIEWED**

 

Non-Human Toxicity Values:

LD50 Rat oral 790 mg/kg
[Kirk-Othmer Encyclopedia of Chemical Technology. 3rd ed., Volumes 1-26. New York, NY: John Wiley and Sons, 1978-1984.,p. 4(78) 343]**PEER REVIEWED**

LC50 Rat inhalation 8000 ppm/4 hr
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

LD50 Rat iv 310 mg/kg
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

LD50 Mouse ip 603 mg/kg
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

LD50 Mouse iv 377 mg/kg
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

LD50 Rabbit dermal 3400 mg/kg
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

 

Ecotoxicity Values:

LC50 Pimephales promelas (fathead minnow) 1730 mg/l/96 hr (95% confidence limit 1630-1840 mg/l); age 33 days old, water hardness 47.7 mg/l (CaCO3), temp 24.7 deg C, pH 7.64, dissolved oxygen 6.3 mg/l, alkalinity 45.5 mg/l (CaCO3) Static bioassay
[Brooke, L.T., D.J. Call, D.T. Geiger and C.E. Northcott (eds.). Acute Toxicities of Organic Chemicals to Fathead Minnows (Pimephales Promelas). Superior, WI: Center for LakeSuperior Environmental Studies Univ. of Wisconsin Superior, 1984. 108]**PEER REVIEWED**

LC50 Pimephales promelas (fathead minnow) 1950, 1950, 1950, 1950, & 1910 mg/l at 1, 24, 48, 72, & 96 hr, respectively, at 18 to 22 deg C (Static bioassay in Lake Superior water)
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

LC50 Pimephales promelas (fathead minnow) 1940, 1940, 1940, 1940, & 1940 mg/l at 1, 24, 48, 72, & 96 hr, respectively, at 18 to 22 deg C (Static bioassay in reconstituted water)
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

Toxicity Threshold (Cell Multiplication Inhibition Test) Scenedesmus quadricauda (green algae) 875 mg/l
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

Toxicity Threshold (Cell Multiplication Inhibition Test) Microcystis aeruginosa (algae) 100 mg/l
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

Toxic Dose Chlorella pyrenoidosa (algae) 8,500 mg/l
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

Toxicity Threshold (Cell Multiplication Inhibition Test): Uronema parduczi Chatton-Lwoff (protozoa) 8.0 mg/l
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

Toxicity Threshold (Cell Multiplication Inhibition Test): Entosiphon sulcatum (protozoa) 55 mg/l
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 301]**PEER REVIEWED**

EC50 Daphnia magna (daphnid) 2337 mg/l/24 hr, toxic effect: lost ability to swim
[Kuhn R et al; Water Res 23 (4): 495-99 (1989)]**PEER REVIEWED**

EC50 Daphnia magna (daphnid) 1983 mg/l/48 hr, toxic effect: lost ability to swim
[Kuhn R et al; Water Res 23 (4): 495-99 (1989)]**PEER REVIEWED**

 

Metabolism/Pharmacokinetics:

 

 

Metabolism/Metabolites:

Cytochrome p450 isozyme 3a, isolated from hepatic microsomes of rabbits treated chronically with ethyl alcohol, had a unique substrate specificity when compared with isozymes 2, 3b, 3c, and 4. Form 3a has unusually high activity in the p-hydroxylation of aniline and in the oxidation of alcohols to aldehydes. Isozyme 3a catalyzes the oxidation of methyl alcohol, propyl alcohol, and butanol as well as ethyl alcohol.
[Morgan ET et al; J Biol Chem 257 (23): 13951-7 (1982)]**PEER REVIEWED**

In rats, n-butanol is extensively metabolized; within 24 hr of a single oral dose, 83% had been converted to carbon dioxide.
[Baselt, R.C. Biological Monitoring Methods for Industrial Chemicals. 2nd ed. Littleton, MA: PSG Publishing Co., Inc. 1988. 51]**PEER REVIEWED**

METABOLISM OF ETHANOL, PROPANOL, ISOPROPANOL, BUTANOL, ISOBUTANOL, SEC-BUTANOL, & TERT-BUTANOL WAS STUDIED AFTER ORAL ADMIN IN RABBITS. BLOOD PH WAS ON THE ACID SIDE WITH PROPANOL, BUTANOL, & ISOBUTANOL, AND ON THE ALKALINE SIDE WITH ISOPROPANOL & SEC-BUTANOL, BUT NO CHANGE WAS OBSERVED WITH ETHANOL & TERT-BUTANOL. BUTANOL & ISOBUTANOL HAD THE LOWEST RATE OF URINARY EXCRETION. ACETALDEHYDE AND ACETIC ACID WERE DETECTED AS THE URINARY METABOLITES OF ETHANOL AND PROPANOL, WHEREAS ISOBUTYRALDEHYDE & ISOVALERIC ACID WERE THE METABOLITES OF ISOBUTANOL.
[SAITO M; NICHIDAI IGAKU ZASSHI 34 (8-9): 569-85 (1975)]**PEER REVIEWED**

Butanol is oxidized to butyraldehyde via alcohol dehydrogenase, with the concomitant reduction of NAD+ to NADH. This reaction is limited both by the amount of enzyme & by the rate of reoxidation of NADH to NAD+ via mitochondrial respiration. Butyraldehyde is further oxidized to butyrate via mitochondrial aldehyde dehydrogenases. The butyrate is activated to butyryl CoA, which is combusted via mitochondrial B-oxidation to carbon dioxide. Butanol may also be oxidized to butyraldehyde via cytochrome p450 & the supply of NADPH available for mixed-function oxidation. The contribution of this latter pathway is probably minor, as is the case for ethanol.
[Snyder, R. (ed.). Ethel Browning's Toxicity and Metabolism of Industrial Solvents. Second Edition. Volume 3 Alcohols and Esters. New York, NY: Elsevier, 1992. 40]**PEER REVIEWED**

 

Absorption, Distribution & Excretion:

BUTANOL IS ABSORBED THROUGH THE LUNG, THE GI TRACT AND SKIN.
[Snyder, R. (ed.). Ethel Browning's Toxicity and Metabolism of Industrial Solvents. Second Edition. Volume 3 Alcohols and Esters. New York, NY: Elsevier, 1992. 39]**PEER REVIEWED**

TWELVE SUBJECTS WERE EXPOSED TO 300 OR 600 MG/CU M OF N-BUTYL ALCOHOL IN INSPIRED AIR DURING REST AND DURING EXERCISE ON A BICYCLE ERGOMETER. EXPOSURE LASTED 2 HR. THE ARTERIAL BLOOD CONCENTRATION WAS LOW. THE CONCENTRATION IN THE LAST PART OF THE EXPIRED AIR, IE, THE ALVEOLAR CONCENTRATION, WAS LOW. THE QUOTIENT OF ALVEOLAR CONCENTRATION WAS LOW IN RELATION TO THE LOW PERCENTAGE UPTAKE. THE HIGH SOLUBILITY OF BUTYL ALCOHOL IN WATER MAY EXPLAIN THE RESULTS.
[ASTRAND I ET AL; SCAND J WORK ENVIRON HEALTH 2 (3): 165-75 (1976)]**PEER REVIEWED**

Volunteers exposed to n-butanol for 2 hr at air concn of 100 and 200 ppm developed blood concn that never exceeded 1.0 mg/l, whether at rest or during excercise. Exposure to an air concn of 50 ppm for 2 hr resulted in blood levels less than 0.08 mg/l.
[Baselt, R.C. Biological Monitoring Methods for Industrial Chemicals. 2nd ed. Littleton, MA: PSG Publishing Co., Inc. 1988. 51]**PEER REVIEWED**

In rats, n-butanol is extensively metabolized; within 24 hr of a single oral dose, 83% had been converted to carbon dioxide, 4% excreted in the urine and 12% remained in the body.
[Baselt, R.C. Biological Monitoring Methods for Industrial Chemicals. 2nd ed. Littleton, MA: PSG Publishing Co., Inc. 1988. 51]**PEER REVIEWED**

Urine was analyzed immediately, 1, 2, 8, and 9 hr after drinking (during 2 hr) 3.75 ml/kg of beverages containing orange juice, 15 or 40% ethanol, and and 1 g/l of 1-propanol, 2-propanol, 1-butanol, 2-butanol, isobutyl alcohol or a mixture of 1-propanol & isobutyl alcohol. Maximum urine levels /in mg/l/ were found 1 hr after drinking ended: 1-propanol 5.04, 2-propanol 3.36, 1-butanol 0.43, 2-butanol 2.55, isobutyl alcohol ... 1.7-2.03 mg/l. Urine treatment with beta-glucuronidase before analysis indicated that significant amounts of the alcohols were excreted as glucuronides, esp isobutyl alcohol. 2-Propanol and 2-butanol were the slowest to be metabolized. When mixtures of alcohols were given, the concentrations of isobutyl alcohol glucuronides were high with the mixtures containing 5 and 15% ethanol, and decreased at 40% ethanol.
[Bonte W et al; Blutalkohol 18 (6): 412-26 (1981)]**PEER REVIEWED**

1-Butanol is readily absorbed through the lungs, skin, and intestinal tract. Once absorbed, 1-butanol disappears rapidly from the blood and is distributed to various tissues with no evidence of bioaccumulation.
[Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994. 2637]**PEER REVIEWED**

 

Mechanism of Action:

The effects of n-butyl and t-butyl alcohol on the respiration of electrically stimulated and unstimulated slices of rat brain cortical tissue were studied. n-Butyl alcohol, at a concn of 9 mM, and t-butyl alcohol, at a concn of 41 mM, reduced the respiration of stimulated tissue by about 11.5%, and depressed respiration of unstimulated tissue. It is concluded that the alcohols ... act primarily by interfering with mechanisms closely related to the excitation cycle in conducting membranes.
[Lindbohm R, Wallgren H; Acta Pharmacol et Toxicol 19 (1): 53-8 (1962)]**PEER REVIEWED**

 

Interactions:

... Ethanol, isopropanol, n-butanol, sec-butanol, and tert-butanol ... exert a ... potentiating effect on the acute inhalation toxicity of carbon tetrachloride. ... Interaction between isopropanol & carbon tetrachloride was documented in an industrial accident ... where workers exposed to both agents exhibited hepatotoxicity. With ethanol the potentiation seems to be due to the presence of the unmetabolized alcohol; however, with isopropanol the effect seems to be caused by the presence of both unmetabolized alcohol and acetone. The results obtained with n-butanol resemble those of ethanol, whereas with 2-butanol they resemble those of isopropanol ...
[Doull, J., C.D.Klassen, and M.D. Amdur (eds.). Casarett and Doull's Toxicology. 3rd ed., New York: Macmillan Co., Inc., 1986. 303]**PEER REVIEWED**

POTENTIATES BACTERICIDAL EFFECTS OF ALCOHOL, ETHYL & ALCOHOL, PROPYL.
[Rossoff, I.S. Handbook of Veterinary Drugs. New York: Springer Publishing Company, 1974. 7]**PEER REVIEWED**

IN VITRO ... WITH RAT LIVER SLICES BIOTRANSFORMATION OF CHLORAL HYDRATE TO TRICHLOROETHANOL WAS FOUND TO BE ENHANCED MORE EFFECTIVELY BY N-PROPANOL AND N-BUTANOL THAN BY ETHANOL.
[The Chemical Society. Foreign Compound Metabolism in Mammals. Volume 2: A Review of the Literature Published Between 1970 and 1971. London: The Chemical Society, 1972. 462]**PEER REVIEWED**

... IN ANIMALS, ETHYL ALCOHOL DOES NOT PROTECT AGAINST TOXICITY OF N-BUTANOL ... THIS MAY BE DUE TO FACT THAT N-BUTANOL IS EXCELLENT SUBSTRATE FOR ALCOHOL DEHYDROGENASE OR THAT METABOLIC PRODUCTS OF N-BUTANOL ARE NOT MAJOR CAUSE OF TOXICITY.
[Doull, J., C.D. Klaassen, and M. D. Amdur (eds.). Casarett and Doull's Toxicology. 2nd ed. New York: Macmillan Publishing Co., 1980. 481]**PEER REVIEWED**

PRETREATMENT WITH N-BUTANOL 30 MIN BEFORE ALLOXAN (100 MG/KG) PROTECTS MICE FROM PERMANENT HYPERGLYCEMIC EFFECTS (MEASURED AT 72 HR) OF ALLOXAN.
[SCHAUBERGER CW ET AL; J PHARMACOL EXP THER 201 (2): 450-5 (1977)]**PEER REVIEWED**

 

Pharmacology:

 

 

Therapeutic Uses:

MEDICATION (VET): BACTERICIDE USED IN TREATMENT OF FROTHY BLOAT.
[Rossoff, I.S. Handbook of Veterinary Drugs. New York: Springer Publishing Company, 1974. 7]**PEER REVIEWED**

... n-Butyl alcohol has been admin to patients for the control of postoperative pain in otolaryngeal surgery and for an unexplained anti-hemorrhagic effect ... in those with far advanced cancer.
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. III-13]**PEER REVIEWED**

A saturated aq soln has been given intravenously to many patients in vol up to 300 ml per day for reducing postoperative pain, for ocular conditions in 68 patients, without note of any untoward effect on the eyes or central nervous system.
[Grant, W.M. Toxicology of the Eye. 3rd ed. Springfield, IL: Charles C. Thomas Publisher, 1986. 162]**PEER REVIEWED**

 

Interactions:

... Ethanol, isopropanol, n-butanol, sec-butanol, and tert-butanol ... exert a ... potentiating effect on the acute inhalation toxicity of carbon tetrachloride. ... Interaction between isopropanol & carbon tetrachloride was documented in an industrial accident ... where workers exposed to both agents exhibited hepatotoxicity. With ethanol the potentiation seems to be due to the presence of the unmetabolized alcohol; however, with isopropanol the effect seems to be caused by the presence of both unmetabolized alcohol and acetone. The results obtained with n-butanol resemble those of ethanol, whereas with 2-butanol they resemble those of isopropanol ...
[Doull, J., C.D.Klassen, and M.D. Amdur (eds.). Casarett and Doull's Toxicology. 3rd ed., New York: Macmillan Co., Inc., 1986. 303]**PEER REVIEWED**

POTENTIATES BACTERICIDAL EFFECTS OF ALCOHOL, ETHYL & ALCOHOL, PROPYL.
[Rossoff, I.S. Handbook of Veterinary Drugs. New York: Springer Publishing Company, 1974. 7]**PEER REVIEWED**

IN VITRO ... WITH RAT LIVER SLICES BIOTRANSFORMATION OF CHLORAL HYDRATE TO TRICHLOROETHANOL WAS FOUND TO BE ENHANCED MORE EFFECTIVELY BY N-PROPANOL AND N-BUTANOL THAN BY ETHANOL.
[The Chemical Society. Foreign Compound Metabolism in Mammals. Volume 2: A Review of the Literature Published Between 1970 and 1971. London: The Chemical Society, 1972. 462]**PEER REVIEWED**

... IN ANIMALS, ETHYL ALCOHOL DOES NOT PROTECT AGAINST TOXICITY OF N-BUTANOL ... THIS MAY BE DUE TO FACT THAT N-BUTANOL IS EXCELLENT SUBSTRATE FOR ALCOHOL DEHYDROGENASE OR THAT METABOLIC PRODUCTS OF N-BUTANOL ARE NOT MAJOR CAUSE OF TOXICITY.
[Doull, J., C.D. Klaassen, and M. D. Amdur (eds.). Casarett and Doull's Toxicology. 2nd ed. New York: Macmillan Publishing Co., 1980. 481]**PEER REVIEWED**

PRETREATMENT WITH N-BUTANOL 30 MIN BEFORE ALLOXAN (100 MG/KG) PROTECTS MICE FROM PERMANENT HYPERGLYCEMIC EFFECTS (MEASURED AT 72 HR) OF ALLOXAN.
[SCHAUBERGER CW ET AL; J PHARMACOL EXP THER 201 (2): 450-5 (1977)]**PEER REVIEWED**

 

Minimum Fatal Dose Level:

AS EXTRAPOLATED FROM RAT DATA ... 3 TO 7 OZ REPRESENTS REASONABLE EST OF SINGLE ORAL MEAN LETHAL DOSE OF ANY BUTYL ALCOHOL IN MAN. /ALCOHOLS, HIGHER/
[Gosselin, R.E., R.P. Smith, H.C. Hodge. Clinical Toxicology of Commercial Products. 5th ed. Baltimore: Williams and Wilkins, 1984.,p. III-13]**PEER REVIEWED**

 

Environmental Fate & Exposure:

 

 

Environmental Fate/Exposure Summary:

n-Butyl alcohol's production and use as a solvent for many natural resins, an ingredient in paint removers and industrial cleaners may result in its release to the environment through various waste streams. n-Butyl alcohol is an aroma component of apples and is also found in many foods. If released to air, a vapor pressure of 7 mm Hg at 25 deg C indicates n-butyl alcohol will exist solely as a vapor in the ambient atmosphere. Vapor-phase n-butyl alcohol will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals; the half-life for this reaction in air is estimated to be 46 hours. If released to soil, n-butyl alcohol is expected to have high mobility based upon an estimated Koc of 72. Volatilization from moist soil surfaces is expected to be an important fate process based upon a Henry's Law constant of 8.8X10-6 atm-cu m/mole. n-Butyl alcohol may volatilize from dry soil surfaces based upon its vapor pressure. The biodegradation half-life of n-butyl alcohol in a sub-surface soil was approximately 7 days. If released into water, n-butyl alcohol is not expected to adsorb to suspended solids and sediment in water based upon the estimated Koc. Volatilization from water surfaces is expected to be an important environmental fate process based upon this compound's Henry's Law constant. Estimated volatilization half-lives for a model river and model lake are 2 and 29 days, respectively. In a river die-away test, n-butyl alcohol achieved 33% of its theoretical BOD in 5 days, suggesting biodegradation will be an important fate process in water. An estimated BCF of 3 suggests the potential for bioconcentration in aquatic organisms is low. Hydrolysis is not expected to be an important environmental fate process since this compound lacks functional groups that hydrolyze under environmental conditions. Occupational exposure may occur through inhalation and dermal contact with this compound at workplaces where n-butyl alcohol is produced or used. The general population is exposed to n-butyl alcohol through the ingestion of foods that contain this compound and inhalation of ambient air. (SRC)
**PEER REVIEWED**

 

Probable Routes of Human Exposure:

THE PRODN OR, IN SOME CASES, USE OF THE FOLLOWING ... MAY OFFER EXPOSURE TO N-BUTYL ALCOHOL: ARTIFICIAL LEATHER, BUTYL ESTERS, RUBBER CEMENT, DYES, FRUIT ESSENCES, LACQUERS, MOTION PICTURE & PHOTOGRAPHIC FILMS, RAINCOATS, PERFUMES, PYROXYLIN PLASTICS, RAYON, SAFETY GLASS, SHELLAC, VARNISH & WATER PROOFED CLOTH.
[Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994. 2636]**PEER REVIEWED**

Use and liberation during spray, brush, or dip application of surface coatings. Use in adhesive and as a solvent adhesive in the manufacture of garments from polyvinyl butyral coated fabric. Liberation during the manufacture of derivatives of butyl alcohol, including chemicals, herbicides, ore flotation agents, urea and melamine formaldehyde resins, and pharmaceuticals. Use as a solvent or as a diluent in the manufacture of brake fluids, detergents, denatured alcohol, and surface coatings, and as a swelling agent in textiles. It is also used as an azeotrophic dehydrating agent and blending agent in laboratory analysis, and liberation as a by-product in furfural tetrahydrofuran conversion.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 3]**PEER REVIEWED**

NIOSH (NOES Survey 1981-83) has statistically estimated that 794,284 workers (115,385 of these are female) are potentially exposed to n-butyl alcohol in the US(1). Occupational exposure may occur through inhalation and dermal contact with this compound at workplaces where n-butyl alcohol is produced or used(SRC). The concentration of n-butyl alcohol in expired air from 8 individuals employed as sprayers during the varnishing of automobiles ranged from 1.3-35.0 ug/hr(2). n-Butyl alcohol was identified, not quantified, in 29 air samples from printing shops and 18 painting shops in Belgium(3). n-Butyl alcohol was detected at a mean concn of 1.6 ug/cu m in 73 samples of exhaled breath from 111 Belgian workers exposed to a solvent mixture(4). The general population is exposed to n-butyl alcohol through the ingestion of foods that contain this compound and inhalation of ambient air(SRC).
[(1) NIOSH; National Occupational Exposure Survey (NOES) (1989) (2) Conkle JP et al; Arch Environ Health 30: 290-5 (1975) (3) Veulemans H et al; Ind Hyg Assoc J 48: 671-76 (1987) (4) Veulemans H et al; Scand J Work Environ Health 13: 239-42 (1987)]**PEER REVIEWED**

 

Body Burden:

n-Butyl alcohol was identified, not quantified, in human blood(1) and mother's milk(2). n-Butyl alcohol was detected in human breath samples at concns of 1-10 ppb(3). The concentration of n-butanol in expired air from 8 individuals ranged from 1.3-35.0 ug/hr(4). n-Butyl alcohol was detected at concns of 0.02 and 0.08 ng/l in 2 samples of the expired air of 54 individuals(5). n-Butyl alcohol was detected at a mean concn of 1.6 ug/cu m in the exhaled breath of Belgian workers exposed to a solvent mixture(6).
[(1) Bonin MA et al; Amer Chem Soc, Div Env Chem, 206th ACS Nat Meet., 33: 21-24 (1993) (2) Pellizzari ED et al; Bull Environ Contam Toxicol 28: 322-28 (1982) (3) Fenske JD, Paulson SE; J Air Waste Manage Assoc 49: 594-98 (1999) (4) Conkle JP et al; Arch Environ Health 30: 290-5 (1975) (5) Krotoszynski BK et al; J Anal Toxicol 3: 225-34 (1979) (6) Veulemans H et al; Scand J Work Environ Health 13: 239-42 (1987)]**PEER REVIEWED**

 

Natural Pollution Sources:

REPORTED PRESENT IN PEPPERMINT OIL FROM BRAZIL, ACHILLEA AGERATUM, TEA, & IN APPLE AROMA.
[Fenaroli's Handbook of Flavor Ingredients. Volume 2. Edited, translated, and revised by T.E. Furia and N. Bellanca. 2nd ed. Cleveland: The Chemical Rubber Co., 1975. 62]**PEER REVIEWED**

 

Artificial Pollution Sources:

n-Butyl alcohol's production and use as a solvent for many natural resins, an ingredient in paint removers and industrial cleaners(1) may result in its release to the environment through various waste streams(SRC).
[(1) Budvari S, ed; Merck Index. 12th ed. Whitehouse Station, NJ: Merck & Co. p 256 (1996)]**PEER REVIEWED**

 

Environmental Fate:

TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 72(SRC), determined from a log Kow of 0.88(2) and a regression-derived equation(3), indicates that n-butyl alcohol is expected to have high mobility in soil(SRC). Volatilization of n-butyl alcohol from moist soil surfaces is expected to be an important fate process(SRC) given a Henry's Law constant of 8.8X10-6 atm-cu m/mole(4). The potential for volatilization of n-butyl alcohol from dry soil surfaces may exist based upon a vapor pressure of 7 mm Hg(5). The biodegradation half-life of n-butyl alcohol in a sub-surface soil from Blacksburg, VA was approximately 7 days(6).
[(1) Swann RL et al; Res Rev 85: 17-28 (1983) (2) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Heller SR, consult. ed., Washington, DC: Amer Chem Soc p. 10 (1995) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9 (1990) (4) Buttery RG et al; J Agric Food Chem 17: 385-89 (1969) (5) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals Data Compilation Washington, DC: Taylor and Francis (1989) (6) Morris MS; Diss Abstr Int B 49: 2766 (1988)]**PEER REVIEWED**

AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 72(SRC), determined from a log Kow of 0.88(2) and a regression-derived equation(3), indicates that n-butyl alcohol is not expected to adsorb to suspended solids and sediment in water(SRC). Volatilization from water surfaces is expected to be an important fate process(3) based upon a Henry's Law constant of 8.8X10-6 atm-cu m/mole(4). Using this Henry's Law constant and an estimation method(3), volatilization half-lives for a model river and model lake are 2 and 29, days respectively(SRC). According to a classification scheme(5), an estimated BCF of 3(SRC), from its log Kow(2) and a regression-derived equation(6), suggests the potential for bioconcentration in aquatic organisms is low. In a river die-away test, n-butyl alcohol achieved 33% of its theoretical BOD in 5 days(7), suggesting biodegradation will be an important fate process in water(SRC).
[(1) Swann RL et al; Res Rev 85: 17-28 (1983) (2) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Heller SR, consult. ed., Washington, DC: Amer Chem Soc p. 10 (1995) (3) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9, 15-1 to 15-29 (1990) (4) Buttery RG et al; J Agric Food Chem 17: 385-89 (1969) (5) Franke C et al; Chemosphere 29: 1501-14 (1994) (6) Meylan WM et al; Environ Toxicol Chem 18: 664-72 (1999) (7) Dore M et al; Trib Cebedeau 28: 3-11 (1975)]**PEER REVIEWED**

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), n-butyl alcohol, which has a vapor pressure of 7 mm Hg at 25 deg C(2), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase n-butyl alcohol is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC). The half-life for the reaction in air with hydroxyl radicals is estimated to be 46 hours(SRC), calculated from its rate constant of 8.3X10-12 cu cm/molecule-sec at 25 deg C(3).
[(1) Bidleman TF; Environ Sci Technol 22: 361-367 (1988) (2) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals Data Compilation Washington, DC: Taylor and Francis (1989) (3) Atkinson R; J Phys Chem Ref Data Monograph 1 (1989)]**PEER REVIEWED**

 

Environmental Biodegradation:

n-Butyl alcohol biodegrades rapidly in screening tests using a sewage or activated sludge inoculum. n-Butyl alcohol reached 66% of its theoretical BOD in a sewage sludge during a 5 day incubation period(1) and 33% of its theoretical BOD using an inoculum from polluted surface water(2). The first-order rate constant for the degradation of n-butyl alcohol in soils was reported as 2X10-6 sec-1(3). This corresponds to a half-life of approximately 4 days(SRC). The first-order biodegradation rate constant of n-butyl alcohol in an activated sludge inoculum was reported as 9.59X10-3 hour-1(4). This corresponds to a half-life of about 3 days(SRC). The biodegradation half-life of n-butyl alcohol in a sub-surface soil from Blacksburg, VA was approximately 7 days(5). The biodegradation half-life of n-butyl alcohol in a basic sandy silt loam from Texas was reported as 1 day and the half-life of n-butyl alcohol in an acidic sandy loam from Mississippi was reported as 8.5 days(6).
[(1) Bridie AL et al; Water Res 13: 627-30 (1979) (2) Dore M et al; Trib Cebedeau 28: 3-11 (1975) (3) Schering M; Environ Sci Technol 31: 2891-97 (1997) (4) Yonezawa Y, Urushigawa Y; Chemosphere 8: 139-42 (1979) (5) Morris MS; Diss Abstr Int B 49: 2766 (1988) (6) Loehr RC; Treatability Potential For EPA Listed Hazardous Wastes In Soil. ADA, OK: USEPA Robert S Kerr Environ Res Lab, USEPA/600/2-89/011 (1989)]**PEER REVIEWED**

AEROBIC: Thirty-eight process wastewaters and 37 organic substances identified in the wastewater of the Kashima (Japan) petrochemical complex were subjected to the activated sludge degradability test. The test used the activated sludge of the Fukashiba (Japan) industrial wastewater treatment plant, which was acclimatized to the wastewater and organic substances. Water in the test container was sampled during aeration at 0 hr and 24 hr later. After 1 day of acclimation, 100 mg/l of n-butyl alcohol resulted in a chemical oxygen demand of 82% and 93% total organic carbon(1).
[(1) Matsui S et al; Water Sci Technol 20: 201-10 (1989)]**PEER REVIEWED**

 

Environmental Abiotic Degradation:

The rate constant for the vapor-phase reaction of n-butyl alcohol with photochemically-produced hydroxyl radicals has been measured as 8.3X10-12 cu cm/molecule-sec at 25 deg C(1). This corresponds to an atmospheric half-life of about 46 hours at an atmospheric concentration of 5X10+5 hydroxyl radicals per cu cm(1). n-Butyl alcohol is not expected to undergo hydrolysis in the environment due to the lack of hydrolyzable functional groups(2) nor to directly photolyze due to the lack of absorption in the environmental UV spectrum (>290 nm).
[(1) Atkinson R; J Phys Chem Ref Data Monograph 1 (1989) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 7-4, 7-5 (1990)]**PEER REVIEWED**

 

Environmental Bioconcentration:

An estimated BCF of 3 was calculated for n-butyl alcohol(SRC), using a log Kow of 0.88(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is low(SRC).
[(1) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Heller SR, consult. ed., Washington, DC: Amer Chem Soc p. 10 (1995) (2) Meylan WM et al; Environ Toxicol Chem 18: 664-72 (1999) (3) Franke C et al; Chemosphere 29: 1501-14 (1994)]**PEER REVIEWED**

 

Soil Adsorption/Mobility:

The Koc of n-butyl alcohol is estimated as 72(SRC), using a log Kow of 0.88(1) and a regression-derived equation(2). According to a classification scheme(3), this estimated Koc value suggests that n-butyl alcohol is expected to have high mobility in soil(SRC).
[(1) Hansch C et al; Exploring QSAR. Hydrophobic, Electronic, and Steric Constants. ACS Prof Ref Book. Heller SR, consult. ed., Washington, DC: Amer Chem Soc p. 10 (1995) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 4-9 (1990) (3) Swann RL et al; Res Rev 85: 17-28 (1983)]**PEER REVIEWED**

 

Volatilization from Water/Soil:

The Henry's Law constant for n-butyl alcohol is 8.8X10-6 atm-cu m/mole(1). This Henry's Law constant indicates that n-butanol is expected to volatilize from water surfaces(2). Based on this Henry's Law constant, the volatilization half-life from a model river (1 m deep, flowing 1 m/sec, wind velocity of 3 m/sec)(2) is estimated as 2 days(SRC). The volatilization half-life from a model lake (1 m deep, flowing 0.05 m/sec, wind velocity of 0.5 m/sec)(2) is estimated as 29 days(SRC). n-Butyl alcohol's Henry's Law constant(1) indicates that volatilization from moist soil surfaces may occur(SRC). The potential for volatilization of n-butanol from dry soil surfaces may exist based upon a vapor pressure of 7 mm Hg(3).
[(1) Buttery RG et al; J Agric Food Chem 17: 385-89 (1969) (2) Lyman WJ et al; Handbook of Chemical Property Estimation Methods. Washington, DC: Amer Chem Soc pp. 15-1 to 15-29 (1990) (3) Daubert TE, Danner RP; Physical and Thermodynamic Properties of Pure Chemicals Data Compilation Washington, DC: Taylor and Francis (1989)]**PEER REVIEWED**

 

Environmental Water Concentrations:

SURFACE WATER: n-Butyl alcohol was detected in surface water from Tatsuno City, Japan at 318 ppb(1). n-Butyl alcohol was identified, but not quantified, in water samples from Lake Ontario(2).
[(1) Yasuhara A et al; Environ Sci Technol 15: 570-3 (1981) (2) Great Lakes Water Quality Board; An Inventory of Chemical Substances Identified in the Great Lakes Ecosystem Vol.1 (1983)]**PEER REVIEWED**

 

Effluent Concentrations:

Effluents from an unidentified petrochemical company contained about 16.0 mg/l n-butyl alcohol and discharged approximately 90 lbs n-butyl alcohol/day(1). n-Butyl alcohol was identified, not quantified, in the volatile emissions of furniture coatings(2). n-Butyl alcohol was detected at concns ranging from 0.1 to 238 mg/cu m in landfill gas from 7 waste disposal sites in the United Kingdom(3). n-Butyl alcohol was identified, not quantified, in the volatile emissions of common garden waste(4). n-Butyl alcohol was identified, not quantified, in the volatile emissions of freshly laid carpets(5) and landfill compost(6).
[(1) Keith LH; Sci Total Environ 3: 87-102 (1974) (2) Salthammer T; Indoor Air 7: 189-97 (1997) (3) Allen MR et al; Environ Sci Technol 31: 1054-61 (1997) (4) Wilkins K, Larsen K; Chemosphere 32: 2049-55 (1996) (5) Hodgson AT et al; J Air Waste Manage Assoc 43: 316-24 (1993) (6) Kryzmien M et al; J Air Waste Manage Assoc 49: 804-13 (1999)]**PEER REVIEWED**

 

Atmospheric Concentrations:

n-Butyl alcohol was identified, not quantified, in forest air in the Southern Black Forest of Germany(1). n-Butyl alcohol was detected in the air of Tucson, AZ at a mean concn of 5.7 ppb (February-September, 1982) and two rural sites 40 km away at a mean concn of 3.7 ppb (August-September, 1982)(2). n-Butyl alcohol was detected at mean concns of less than 0.2 ppb and 1.63 ppb in 2 industrial sites in Boston, MA and Houston, TX, respectively(3). n-Butyl alcohol was detected at a school (indoor air) in Denmark at an avg concn of 7 ug/cu m(4). n-Butyl alcohol was identified, not quantified, in the indoor air of homes where a Swedish oil floor finish called "Glitsa" was recently applied(5). n-Butyl alcohol was identified, not quantified, in 29 air samples from printing shops and 18 painting shops in Belgium(6).
[(1) Juttner F; Chemosphere 15: 985-92 (1986) (2) Snider JR, Dawson GA; J Geophys Res 90: 3797-805 (1985) (3) Kelly TJ, Callahan PJ; Environ Sci Technol 27: 1146-53 (1993) (4) Brown SK et al; Indoor Air 4: 123-34 (1994) (5) van Netten C et al; Bull Environ Contam Toxicol 40: 672-677 (1988) (6) Veulemans H et al; Ind Hyg Assoc J 48: 671-76 (1987)]**PEER REVIEWED**

 

Food Survey Values:

n-Butyl alcohl was identified, not quantified, in the volatile emissions of roasted filberts(1), raw beef(2), Frankfurter sausages(3) and roasted almonds(4). n-Butyl alcohol was detected in soybeans at concns of 199.9 to 1,586.2 ug/kg(5). The volatile emission rate of n-butanol from Bisbee apples harvested from the state of Washington was 8.6 to 35.1 picoliters/kg-hr(6).
[(1) Kinlin TE et al; J Agric Food Chem 20: 1021 (1972) (2) King MF et al; J Agric Food Chem 41: 1974-81 (1993) (3) Chevance FV, Farmer LJ; J Agric Food Chem 47: 5151-60 (1999) (4) Cantalejo MH; J Agric Food Chem 45: 1853-60 (1997) (5) Chung HY; J Agric Food Chem 47: 2690-96 (1999) (6) Mattheis JP et al; J Agric Food Chem 39: 1902-1906 (1991)]**PEER REVIEWED**

 

Fish/Seafood Concentrations:

n-Butyl alcohol was found in a sample of mussel at a concn of 0.27 ppm(1). The mussel sample was collected off the coast of Japan(1).
[(1) Yashuhara A, Morita M; Chemosphere 16: 2559-65 (1987)]**PEER REVIEWED**

 

Milk Concentrations:

n-Butanol was identified, not quantified, in 3 of 12 samples of mother's milk(1).
[(1) Pellizzari ED et al; Bull Environ Contam Toxicol 28: 322-28 (1982)]**PEER REVIEWED**

 

Environmental Standards & Regulations:

 

 

FIFRA Requirements:

Residues of n-butanol are exempted from the requirement of a tolerance when used as a solvent or cosolvent in accordance with good agricultural practices as inert (or occasionally active) ingredients in pesticide formulations applied to growing crops or to raw agricultural commodities after harvest.
[40 CFR 180.1001(c) (7/1/2000)]**PEER REVIEWED**

n-Butanol is exempted from the requirement of a tolerance when used as a solvent for blended emulsifiers in accordance with good agricultural practice as inert (or occasionally active) ingredients in pesticide formulations applied to animals.
[40 CFR 180.1001(e) (7/1/2000)]**PEER REVIEWED**

 

CERCLA Reportable Quantities:

Persons in charge of vessels or facilities are required to notify the National Response Center (NRC) immediately, when there is a release of this designated hazardous substance, in an amount equal to or greater than its reportable quantity of 5000 lb or 2270 kg. The toll free number of the NRC is (800) 424-8802; In the Washington D.C. metropolitan area (202) 426-2675. The rule for determining when notification is required is stated in 40 CFR 302.4 (section IV. D.3.b).
[40 CFR 302.4 (7/1/2000)]**PEER REVIEWED**

 

RCRA Requirements:

U031; As stipulated in 40 CFR 261.33, when n-butyl alcohol, as a commercial chemical product or manufacturing chemical intermediate or an off-specification commercial chemical product or a manufacturing chemical intermediate, becomes a waste, it must be managed according to Federal and/or State hazardous waste regulations. Also defined as a hazardous waste is any residue, contaminated soil, water, or other debris resulting from the cleanup of a spill, into water or on dry land, of this waste. Generators of small quantities of this waste may qualify for partial exclusion from hazardous waste regulations (40 CFR 261.5).
[40 CFR 261.33 (7/1/2000)]**PEER REVIEWED**

F003; When n-butyl alcohol is a spent solvent, it is classified as a hazardous waste from a nonspecific source (F003), as stated in 40 CFR 261.31, and must be managed according to State and/or Federal hazardous waste regulations.
[40 CFR 261.31 (7/1/2000]**PEER REVIEWED**

 

Atmospheric Standards:

This action promulgates standards of performance for equipment leaks of Volatile Organic Compounds (VOC) in the Synthetic Organic Chemical Manufacturing Industry (SOCMI). The intended effect of these standards is to require all newly constructed, modified, and reconstructed SOCMI process units to use the best demonstrated system of continuous emission reduction for equipment leaks of VOC, considering costs, non air quality health and environmental impact and energy requirements. n-Butyl alcohol is produced, as an intermediate or a final product, by process units covered under this subpart.
[40 CFR 60.489 (7/1/2000)]**PEER REVIEWED**

 

State Drinking Water Guidelines:

(MI) MICHIGAN 910 ug/l
[USEPA/Office of Water; Federal-State Toxicology and Risk Analysis Committee (FSTRAC). Summary of State and Federal Drinking Water Standards and Guidelines (11/93)] **QC REVIEWED**

(MN) MINNESOTA 700 ug/l
[USEPA/Office of Water; Federal-State Toxicology and Risk Analysis Committee (FSTRAC). Summary of State and Federal Drinking Water Standards and Guidelines (11/93)] **QC REVIEWED**

(FL) FLORIDA 700 ug/l
[USEPA/Office of Water; Federal-State Toxicology and Risk Analysis Committee (FSTRAC). Summary of State and Federal Drinking Water Standards and Guidelines (11/93)] **QC REVIEWED**

 

FDA Requirements:

n-Butyl alcohol (without residue) may be used in inks for marking food supplements in tablet form, gum, and confectionery.
[21 CFR 73.1 (4/1/2000)]**PEER REVIEWED**

 

Allowable Tolerances:

Residues of n-butanol are exempted from the requirement of a tolerance when used as a solvent or cosolvent in accordance with good agricultural practices as inert (or occasionally active) ingredients in pesticide formulations applied to growing crops or to raw agricultural commodities after harvest.
[40 CFR 180.1001(c) (7/1/2000)]**PEER REVIEWED**

n-Butanol is exempted from the requirement of a tolerance when used as a solvent for blended emulsifiers in accordance with good agricultural practice as inert (or occasionally active) ingredients in pesticide formulations applied to animals.
[40 CFR 180.1001(e) (7/1/2000)]**PEER REVIEWED**

 

Chemical/Physical Properties:

 

 

Molecular Formula:

C4-H10-O
[The Merck Index. 10th ed. Rahway, New Jersey: Merck Co., Inc., 1983. 214]**PEER REVIEWED**

 

Molecular Weight:

74.12
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 3-100]**PEER REVIEWED**

 

Color/Form:

Colorless liquid
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Odor:

HARSH FUSEL ODOR WITH BANANA
[Furia, T.E. (ed.). CRC Handbook of Food Additives. 2nd ed. Volume 2. Boca Raton, Florida: CRC Press, Inc., 1980. 261]**PEER REVIEWED**

ODOR SIMILAR TO AMYL ALCOHOL
[Fenaroli's Handbook of Flavor Ingredients. Volume 2. Edited, translated, and revised by T.E. Furia and N. Bellanca. 2nd ed. Cleveland: The Chemical Rubber Co., 1975. 62]**PEER REVIEWED**

Rancid, sweet
[Verschueren, K. Handbook of Environmental Data on Organic Chemicals. 3rd ed. New York, NY: Van Nostrand Reinhold Co., 1996. 351]**PEER REVIEWED**

Strong characteristic, mildly alcoholic odor
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Taste:

BANANA, FUSEL TASTE
[Furia, T.E. (ed.). CRC Handbook of Food Additives. 2nd ed. Volume 2. Boca Raton, Florida: CRC Press, Inc., 1980. 261]**PEER REVIEWED**

DRY, BURNING TASTE
[Fenaroli's Handbook of Flavor Ingredients. Volume 2. Edited, translated, and revised by T.E. Furia and N. Bellanca. 2nd ed. Cleveland: The Chemical Rubber Co., 1975. 62]**PEER REVIEWED**

5.00X10-1 ppm (taste detection in water, gas chromatically pure)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

 

Boiling Point:

117.7 deg C
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 3-100]**PEER REVIEWED**

 

Melting Point:

-89.8 deg C
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 3-100]**PEER REVIEWED**

 

Corrosivity:

Attack some forms of plastics, rubber, and coatings
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 2]**PEER REVIEWED**

 

Critical Temperature & Pressure:

Critical temperature: 563 K; critical pressure: 4.414 MPa
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 6-53]**PEER REVIEWED**

 

Density/Specific Gravity:

0.8098 @ 20 deg C/4 deg C
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 3-100]**PEER REVIEWED**

 

Dissociation Constants:

pKa= 16.10
[Serjeant, E.P., Dempsey B.; Ionisation Constants of Organic Acids in Aqueous Solution. International Union of Pure and Applied Chemistry (IUPAC). IUPACChemical Data Series No. 23, 1979. New York, New York: Pergamon Press, Inc. 989]**PEER REVIEWED**

 

Heat of Combustion:

639.53 kg cal/g mol wt at 25 deg C
[Weast, R.C. (ed.) Handbook of Chemistry and Physics. 69th ed. Boca Raton, FL: CRC Press Inc., 1988-1989.,p. D-274]**PEER REVIEWED**

 

Heat of Vaporization:

52.35 kJ/mol @ 25 deg C
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 6-112]**PEER REVIEWED**

 

Octanol/Water Partition Coefficient:

log Kow= 0.88
[Hansch, C., Leo, A., D. Hoekman. Exploring QSAR - Hydrophobic, Electronic, and Steric Constants. Washington, DC: American Chemical Society., 1995. 10]**PEER REVIEWED**

 

Solubilities:

In water, 6.32X10+4 mg/l @ 25 deg C
[Tewari YG et al; J Res NBS 87: 155-8 (1982)]**PEER REVIEWED**

Miscible with many organic solvents
[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996. 255]**PEER REVIEWED**

Very soluble in acetone; miscible with ethanol and ethyl ether
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 3-100]**PEER REVIEWED**

> 10% in benzene
[Weast, R.C. and M.J. Astle. CRC Handbook of Data on Organic Compounds. Volumes I and II. Boca Raton, FL: CRC Press Inc. 1985.,p. V1 347]**PEER REVIEWED**

 

Spectral Properties:

Index of refraction: 1.3993 @ 20 deg C/D
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 3-100]**PEER REVIEWED**

Specific rotation: +9.8 at 20 deg C/D (water)
[Weast, R.C. (ed.) Handbook of Chemistry and Physics. 69th ed. Boca Raton, FL: CRC Press Inc., 1988-1989.,p. C-168]**PEER REVIEWED**

IR: 4807 (Coblentz Society Spectral Collection)
[Lide, D.R., G.W.A. Milne (eds.). Handbook of Data on Organic Compounds. Volume I. 3rd ed. CRC Press, Inc. Boca Raton ,FL. 1994.,p. V2 1909]**PEER REVIEWED**

1H NMR: SAD 7200 (Sadtler Research Laboratories Spectral Collection)
[Lide, D.R., G.W.A. Milne (eds.). Handbook of Data on Organic Compounds. Volume I. 3rd ed. CRC Press, Inc. Boca Raton ,FL. 1994.,p. V2 1909]**PEER REVIEWED**

13C NMR: STOT 140 (Stothers, Cabon-13 NMR Spectroscopy, Academic Press, New York)
[Lide, D.R., G.W.A. Milne (eds.). Handbook of Data on Organic Compounds. Volume I. 3rd ed. CRC Press, Inc. Boca Raton ,FL. 1994.,p. V2 1909]**PEER REVIEWED**

MS: NIST 19177 (NIST/EPA/MCDC Mass Spectral Database 1990 version); NBS 23 (National Bureau of Standards)
[Lide, D.R., G.W.A. Milne (eds.). Handbook of Data on Organic Compounds. Volume I. 3rd ed. CRC Press, Inc. Boca Raton ,FL. 1994.,p. V2 1909]**PEER REVIEWED**

Raman: SAD 180 (Sadtler Research Laboratories Spectral Collection)
[Lide, D.R., G.W.A. Milne (eds.). Handbook of Data on Organic Compounds. Volume I. 3rd ed. CRC Press, Inc. Boca Raton ,FL. 1994.,p. V2 1909]**PEER REVIEWED**

 

Surface Tension:

26.28 dynes/cm @ 10 deg C; 24.93 dynes/cm @ 25 deg C; 22.69 dynes/cm @ 50 deg C
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 6-146]**PEER REVIEWED**

 

Vapor Density:

2.6 (Air= 1)
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

 

Vapor Pressure:

7.0 mm Hg @ 25 deg C
[Daubert, T.E., R.P. Danner. Physical and Thermodynamic Properties of Pure Chemicals Data Compilation. Washington, D.C.: Taylor and Francis, 1989.]**PEER REVIEWED**

 

Relative Evaporation Rate:

0.46 (butyl acetate= 1)
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 2]**PEER REVIEWED**

 

Viscosity:

36.1 cP at -50.9 deg C; 5.186 cP at 0 deg C; 2.544 cP at 25 deg C; 0.533 cP at 100 deg C
[Lide, DR (ed.). CRC Handbook of Chemistry and Physics. 81st Edition. CRC Press LLC, Boca Raton: FL 2000,p. 6-182]**PEER REVIEWED**

 

Other Chemical/Physical Properties:

Highly refractive liq
[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996. 255]**PEER REVIEWED**

Leaves transitory greasy spot on paper.
[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996. 255]**PEER REVIEWED**

PERCENT IN SATURATED AIR 0.86 (25 DEG C); DENSITY OF SATURATED AIR: 1.01 (AIR= 1)
[Clayton, G. D. and F. E. Clayton (eds.). Patty's Industrial Hygiene and Toxicology: Volume 2A, 2B, 2C: Toxicology. 3rd ed. New York: John Wiley Sons, 1981-1982. 4572]**PEER REVIEWED**

Heat of fusion: 29.93 cal/g= 125.23 J/g= 9,282 J/mol
[Weast, R.C. (ed.) Handbook of Chemistry and Physics. 69th ed. Boca Raton, FL: CRC Press Inc., 1988-1989.,p. C-667]**PEER REVIEWED**

Sat concn in air 20 g/cu m at 20 deg C; 39 g/cu m at 30 deg C
[Verschueren, K. Handbook of Environmental Data on Organic Chemicals. 3rd ed. New York, NY: Van Nostrand Reinhold Co., 1996. 351]**PEER REVIEWED**

Liquid heat capacity= 0.566 BTU/lb-F @ 75 deg F; Liquid thermal conductivity= 1.028 BTU-inch/hr-sq ft-F @ 75 deg F; Saturated vapor density= 0.00145 lb/cu ft @ 75 deg F; Ideal gas heat capacity= 0.354 BTU/lb-F @ 75 deg F
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

Ionization potential= 10.01 eV
[NIOSH. Pocket Guide to Chemical Hazards. 2nd Printing. DHHS (NIOSH) Publ. No. 85-114. Washington, D.C.: U.S. Dept. of Health and Human Services, NIOSH/Supt.of Documents, GPO, February 1987. 64]**PEER REVIEWED**

Observed and estimated solubility of naphthalene in 1-butanol at 40 deg C: 0.116 mole fraction (observed) & 0.111 mole fraction (estimated)
[Lyman, W.J., W.F. Reehl, D.H. Rosenblatt. Handbook of Chemical Property Estimation Methods-Environmental Behavior of Organic Compounds. New York, NY: McGraw-Hill Book Company, 1982.,p. 3-21]**PEER REVIEWED**

Hydroxyl radical reaction rate constant = 8.3X10-12 cu cm/molecule-sec @ 25 deg C
[Atkinson R; J Phys Chem Ref Data Monograph 1 (1989)]**PEER REVIEWED**

Coefficient of cubical expansion: 0.00093/deg C, 0.00052/deg F; specific heat of liquid: 0.563 cal/g at 20 deg c; wt/gal: 6.756 lb at 20 deg C
[Flick, E.W. Industrial Solvents Handbook. 3rd ed. Park Ridge, NJ: Noyes Publications, 1985. 229]**PEER REVIEWED**

Forms binary azeotropes with 1-bromo-3-methylbutane, butyl acetate, butyl ether, butyl formate, butyl vinyl ether, camphene, chlorobenzene, 1-chloro-3-methylbutane, cyclohexane, cyclohexene, dibutyl ether, 1,3-dimethylcyclohexane, 2,5-dimethylhexane, ethyl borate, ethyl butyrate, ethyl carbonate, ethyl isobutyrate, heptane, hexane, 2-hexanone, 3-hexanone, 1-iodo-3-methylbutane, isoamyl formate, isobutyl acetate, isobutyl ether, isopropyl isobutyrate, isopropyl sulfide, methylcyclohexane, methylcyclopentane, methyl isovalerate, 4-methyl-2-pentanone, octane, paraldehyde, alpha-pinene, pyridine, styrene, tetrachloroethylene, toluene, o-xylene, p-xylene
[Flick, E.W. Industrial Solvents Handbook. 3rd ed. Park Ridge, NJ: Noyes Publications, 1985. 231]**PEER REVIEWED**

Forms ternary azeotropes with water, butyl acetate; water, butyl chloroacetate; water, butyl ether; water, butyl formate; water, carbon tetrachloride
[Flick, E.W. Industrial Solvents Handbook. 3rd ed. Park Ridge, NJ: Noyes Publications, 1985. 231]**PEER REVIEWED**

Dielectric constant: 17.8 at 20 deg C; 8.2 at 118 deg C; dipole moment: 1.66 (gas, at 20 deg C in benzene)
[Dean, J.A. Handbook of Organic Chemistry. New York, NY: McGraw-Hill Book Co., 1987.,p. 4-49]**PEER REVIEWED**

Enthalpies of formation: -78.18 kcal/mole (liquid); -65.65 kcal/mole (gas)
[Dean, J.A. Handbook of Organic Chemistry. New York, NY: McGraw-Hill Book Co., 1987.,p. 5-8]**PEER REVIEWED**

Gibbs (free) energies of formation: -38.84 kcal/mole (liquid); -36.04 kcal/mole (gas)
[Dean, J.A. Handbook of Organic Chemistry. New York, NY: McGraw-Hill Book Co., 1987.,p. 5-8]**PEER REVIEWED**

Entropies: 54.1 cal/deg-mole (liquid); 86.7 cal/deg-mole (gas)
[Dean, J.A. Handbook of Organic Chemistry. New York, NY: McGraw-Hill Book Co., 1987.,p. 5-8]**PEER REVIEWED**

Heat capacities: 42.31 cal/deg-mole (liquid); 26.29 cal/deg-mole (gas)
[Dean, J.A. Handbook of Organic Chemistry. New York, NY: McGraw-Hill Book Co., 1987.,p. 5-8]**PEER REVIEWED**

Electrical conductivity: 9.12X10-9/ohm.cm
[Kirk-Othmer Encyclopedia of Chemical Technology. 3rd ed., Volumes 1-26. New York, NY: John Wiley and Sons, 1978-1984.,p. 4(78) 338]**PEER REVIEWED**

Diffusion coefficient: 0.025 sq m/hr in air at 0 deg C and 1 atm
[Kirk-Othmer Encyclopedia of Chemical Technology. 3rd ed., Volumes 1-26. New York, NY: John Wiley and Sons, 1978-1984.,p. 1(78) 87]**PEER REVIEWED**

Burns with strongly luminous flame.
[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996. 255]**PEER REVIEWED**

Henry's Law constant = 8.8X10-6 atm-cu m/mole @ 25 deg C
[Buttery RG et al; J Agric Food Chem 17: 385-89 (1969)]**PEER REVIEWED**

 

Chemical Safety & Handling:

 

 

DOT Emergency Guidelines:

Fire or explosion: Highly flammable: Will be easily ignited by heat, sparks or flames. Vapors may form explosive mixtures with air. Vapors may travel to source of ignition and flash back. Most vapors are heavier than air. They will spread along ground and collect in low confined areas (sewers, basements, tanks). Vapor explosion hazard indoors, outdoors or in sewers. Some may polymerize (P) explosively when heated or involved in a fire. Runoff to sewer may create fire or explosion hazard. Containers may explode when heated. Many liquids are lighter than water.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

Health: May cause toxic effects if inhaled or absorbed through skin. Inhalation or contact with material may irritate or burn skin and eyes. Fire will produce irritating, corrosive and/or toxic gases. Vapors may cause dizziness or suffocation. Runoff from fire control or dilution water may cause pollution.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

Public safety: Call Emergency Response Telephone Number ... . Isolate spill or leak area immediately for at least 50 to lOO meters (160 to 330 feet) in all directions. Keep unauthorized personnel away. Stay upwind. Keep out of low areas. Ventilate closed spaces before entering.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

Protective clothing: Wear positive pressure self-contained breathing apparatus (SCBA). Structural firefighters' protective clothing will only provide limited protection.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

Evacuation: Large spill: Consider initial downwind evacuation for at least 300 meters (1000 feet). Fire: If tank, rail car or tank truck is involved in a fire, isolate for 800 meters (1/2 mile) in all directions; also, consider initial evacuation for 800 meters (1/2 mile) in all directions.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

Fire: Caution: All these products have a very low flash point: Use of water spray when fighting fire may be inefficient. Small fires: Dry chemical, CO2, water spray or alcohol-resistant foam. Do not use dry chemical extinguishers to control fires involving nitromethane or nitroethane. Large fires: Water spray, fog or alcohol-resistant foam. Do not use straight streams. Move containers from fire area if you can do it without risk. Fire involving tanks or car/trailer loads: Fight fire from maximum distance or use unmanned hose holders or monitor nozzles. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. Always stay away from the ends of tanks. For massive fire, use unmanned hose holders or monitor nozzles; if this is impossible, withdraw from area and let fire burn.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

Spill or leak: Eliminate all ignition sources (no smoking, flares, sparks or flames in immediate area). All equipment used when handling the product must be grounded. Do not touch or walk through spilled material. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. A vapor suppressing foam may be used to reduce vapors. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. Use clean non-sparking tools to collect absorbed material. Large spills: Dike far ahead of liquid spill for later disposal. Water spray may reduce vapor; but may not prevent ignition in closed spaces.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

First aid: Move victim to fresh air. Call emergency medical care. Apply artificial respiration if victim is not breathing. Administer oxygen if breathing is difficult. Remove and isolate contaminated clothing and shoes. In case of contact with substance, immediately flush skin or eyes with running water for at least 20 minutes. Wash skin with soap and water. Keep victim warm and quiet. Effects of exposure (inhalation, ingestion or skin contact) to substance may be delayed. Ensure that medical personnel are aware of the material(s) involved, and take precautions to protect themselves.
[U.S. Department of Transportation. 1996 North American Emergency Response Guidebook. A Guidebook for First Responders During the Initial Phase of aHazardous Materials/Dangerous Goods Incident. U.S. Department of Transportation (U.S. DOT) Research and Special Programs Administration, Office of HazardousMaterials Initiatives and Training (DHM-50), Washington, D.C. (1996).,p. G-129]**PEER REVIEWED**

 

Odor Threshold:

Water odor threshold: 7.1 mg/l. Air odor threshold: 0.83 ppm. Odor safety class: B. B= odor safety factor 26-550. 50-90% of distracted persons perceive warning of TLV.
[Amoore JE, Hautala E; J Appl Toxicol 3 (6): 272-90 (1983)]**PEER REVIEWED**

2.50 ppm (detection in water, chemically pure)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

2.77 ppm (detection in air, chemically pure)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

2.88 ppm (detection in air, chemically pure)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

2.86X10-9 moles/l (detection in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

1.10X10-13 molecules/cu cm (detection in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

3.00X10-1 ppm (detection in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

1.00 ppm (recognition in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

1.20X10-1 ppm (detection in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

4.10X10-1 ppm (detection in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

8.20X10+10 molecules/cu cm (in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

6.80X10-1 ppm (detection in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

1.80 ppm (recognition in air, purity not specified)
[Fazzalari, F.A. (ed.). Compilation of Odor and Taste Threshold Values Data. ASTM Data Series DS 48A (Committee E-18). Philadelphia, PA: American Society for Testing and Materials, 1978. 23]**PEER REVIEWED**

Odor Thresholds 0.3600 mg/cu m (low) 150.000 mg/cu m (high).
[Ruth JH; Am Ind Hyg Assoc J 47: A-142-51 (1986)]**PEER REVIEWED**

 

Skin, Eye and Respiratory Irritations:

May cause irritation of mucous membranes.
[The Merck Index. 10th ed. Rahway, New Jersey: Merck Co., Inc., 1983. 214]**PEER REVIEWED**

Vapor: Irritating to eyes, nose and throat; ... Liquid: Irritating to skin and eyes.
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

It is a strong irritant of the mucous membranes, eyes, skin & respiratory tract.
[Sullivan, J.B. Jr., G.R. Krieger (eds.). Hazardous Materials Toxicology-Clinical Principles of Environmental Health. Baltimore, MD: Williams and Wilkins, 1992. 1106]**PEER REVIEWED**

 

Fire Potential:

FLAMMABLE LIQUID. MODERATELY EXPLOSIVE WHEN EXPOSED TO FLAME.
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

 

NFPA Hazard Classification:

Health: 1. 1= Materials that, on exposure, would cause irritation, but only minor residual injury, including those requiring the use of an approved air-purifying respirator. These materials are only slightly hazardous to health and only breathing protection is needed.
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

Flammability: 3. 3= This degree includes Class IB and IC flammable liquids and materials that can be easily ignited under almost all normal temperature conditions. Water may be ineffective in controlling or extinguishing fires in such materials.
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

Reactivity: 0. 0= This degree includes materials that are normally stable, even under fire exposure conditions, and that do not react with water. Normal fire fighting procedures may be used.
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

 

Flammable Limits:

Lower flammable limit: 1.4% by volume; Upper flammable limit: 11.2% by volume
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

 

Flash Point:

98 deg F, 37 deg C (closed cup)
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

Closed cup flash point: 28.89 degrees C
[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I,II, III. Cincinnati, OH: ACGIH, 1991. 170]**PEER REVIEWED**

 

Autoignition Temperature:

650 DEG F (343 DEG C)
[Fire Protection Guide to Hazardous Materials. 12 ed. Quincy, MA: National Fire Protection Association, 1997.,p. 325-20]**PEER REVIEWED**

 

Fire Fighting Procedures:

Do not extinguish fire unless flow can be stopped. Use water in flooding quantities as fog. Solid streams of water may be ineffective. Cool all affected containers with flooding quantities of water. Apply water from as far a distance as possible. Use "alcohol" foam, dry chemical or carbon dioxide.
[Prager, J.C. Environmental Contaminant Reference Databook Volume 1. New York, NY: Van Nostrand Reinhold, 1995. 353]**PEER REVIEWED**

 

Toxic Combustion Products:

Toxic gases and vapors (such as carbon monoxide) may be released in a fire involving butyl alcohol.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 2]**PEER REVIEWED**

 

Firefighting Hazards:

Flashback along vapor trail may occur.
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

 

Explosive Limits & Potential:

MODERATELY EXPLOSIVE WHEN EXPOSED TO FLAME.
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

Vapor may explode if ignited in an enclosed area.
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

Lower: 1.45% by vol in air; upper 11.25% by vol in air
[Flick, E.W. Industrial Solvents Handbook. 3rd ed. Park Ridge, NJ: Noyes Publications, 1985. 229]**PEER REVIEWED**

 

Hazardous Reactivities & Incompatibilities:

WHEN METHANOL ... USED TO RINSE A PESTLE & MORTAR WHICH HAD BEEN USED TO GRIND COARSE CHROMIUM TRIOXIDE, IMMEDIATE IGNITION OCCURRED, DUE TO VIGOROUS OXIDATION OF SOLVENT. THE SAME OCCURRED WITH ... BUTANOL.
[Arena, J.M. and Drew, R.H. (eds.) Poisoning-Toxicology, Symptoms, Treatments. 5th ed. Springfield, IL: Charles C. Thomas Publisher, 1986. 1023]**PEER REVIEWED**

Butanol, used as a solvent in an autoclave preparation at 100 deg C, severely attacked the aluminum gasket, liberating hydrogen which caused a sharp rise in pressure. Other alcohols would behave similarly ... .
[Bretherick, L. Handbook of Reactive Chemical Hazards. 4th ed. Boston, MA: Butterworth-Heinemann Ltd., 1990 22]**PEER REVIEWED**

Contact with strong oxidizers may cause fire and explosion.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 2]**PEER REVIEWED**

Strong oxidizers, strong mineral acids, alkali metals, halogens.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Hazardous Decomposition:

When heated to decomp it emits acrid smoke and fumes.
[Lewis, R.J. Sax's Dangerous Properties of Industrial Materials. 9th ed. Volumes 1-3. New York, NY: Van Nostrand Reinhold, 1996. 559]**PEER REVIEWED**

Decomposition products: toxic gases & vapors (e.g., carbon monoxide) may be released in a fire involving n-butyl alcohol.
[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I,II, III. Cincinnati, OH: ACGIH, 1991. 170]**PEER REVIEWED**

 

Immediately Dangerous to Life or Health:

1400 ppm [Based on 10% of the lower explosion limit for safety considerations even though the relevant toxicological data indicated irreversible health effects or impairment of escape existed only at higher concentrations.]
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Protective Equipment & Clothing:

Employees should be provided with and required to use impervious clothing, gloves, face shields (eight-inch minimum), and other appropriate protective clothing necessary to prevent repeated or prolonged skin contact with liquid butyl alcohol.
[Prager, J.C. Environmental Contaminant Reference Databook Volume 1. New York, NY: Van Nostrand Reinhold, 1995. 353]**PEER REVIEWED**

Breakthough times are less (usually significantly less) than one hour as reported by two or more testers, for natural rubber.
[ACGIH; Guidelines Select of Chem Protect Clothing Volume #1 Field Guide p.61 (1983)]**PEER REVIEWED**

For neoprene, nitrile rubber, and polyvinyl chloride (PVC), the breakthrough times are greater than one hr as reported by two or more testers.
[ACGIH; Guidelines Select of Chem Protect Clothing Volume #1 Field Guide p.61 (1983)]**PEER REVIEWED**

Wear appropriate chemical protective gloves, boots and goggles.
[Association of American Railroads. Emergency Handling of Hazardous Materials in Surface Transportation. Washington, D.C.: Assoc. of American Railroads,Hazardous Materials Systems (BOE), 1987. 106]**PEER REVIEWED**

If the use of respirators is necessary, the only respirators permitted are those that have been approved by the Mine Safety and Health Administration (formerly Mining Enforcement and Safety Administration), or by the National Institute for Occupational Safety and Health.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 2]**PEER REVIEWED**

Some data (usually from immersion tests) suggesting breakthrough times greater than one hour are not likely for polyvinyl alcohol (PVA). No data for butyl rubber (butyl), neoprene/styrene butadiene rubber(neo./SBR), polyethylene (PE), chlorinated polyethylene (CPE), polyethane (PU), styrene-butadiene (SBR) and viton.
[ACGIH; Guidelines Select of Chem Protect Clothing Volume #1 Field Guide p.61 (1983)]**PEER REVIEWED**

Wear appropriate personal protective clothing to prevent skin contact.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

Wear appropriate eye protection to prevent eye contact.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

Recommendations for respirator selection. Max concn for use: 1250 ppm. Respirator Class(es): Any supplied-air respirator operated in a continuous flow mode. Eye protection needed. Any powered, air-purifying respirator with organic vapor cartridge(s). Eye protection needed.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

Recommendations for respirator selection. Max concn for use: 1400 ppm. Respirator Class(es): Any chemical cartridge respirator with a full facepiece and organic vapor cartridge(s). Any air-purifying, full-facepiece respirator (gas mask) with a chin-style, front- or back-mounted organic vapor canister. Any powered, air-purifying respirator with a tight-fitting facepiece and organic vapor cartridge(s). Eye protection needed. Any self-contained breathing apparatus with a full facepiece. Any supplied-air respirator with a full facepiece.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

Recommendations for respirator selection. Condition: Emergency or planned entry into unknown concn or IDLH conditions: Respirator Class(es): Any self-contained breathing apparatus that has a full facepiece and is operated in a pressure-demand or other positive-pressure mode. Any supplied-air respirator that has a full facepiece and is operated in a pressure-demand or other positive-pressure mode in combination with an auxiliary self-contained breathing apparatus operated in pressure-demand or other positive-pressure mode.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

Recommendations for respirator selection. Condition: Escape from suddenly occurring respiratory hazards: Respirator Class(es): Any air-purifying, full-facepiece respirator (gas mask) with a chin-style, front- or back-mounted organic vapor canister. Any appropriate escape-type, self-contained breathing apparatus.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Preventive Measures:

Contact lenses should not be worn when working with this chemical.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

SRP: The scientific literature for the use of contact lenses in industry is conflicting. The benefit or detrimental effects of wearing contact lenses depend not only upon the substance, but also on factors including the form of the substance, characteristics and duration of the exposure, the uses of other eye protection equipment, and the hygiene of the lenses. However, there may be individual substances whose irritating or corrosive properties are such that the wearing of contact lenses would be harmful to the eye. In those specific cases, contact lenses should not be worn. In any event, the usual eye protection equipment should be worn even when contact lenses are in place.
**PEER REVIEWED**

SRP: Local exhaust ventilation should be applied wherever there is an incidence of point source emissions or dispersion of regulated contaminants in the work area. Ventilation control of the contaminant as close to its point of generation is both the most economical and safest method to minimize personnel exposure to airborne contaminants.
**PEER REVIEWED**

Employees should wash promptly when skin is wet or contaminated. Remove clothing immediately if wet or contaminated to avoid flammability hazard.
[Sittig, M. Handbook of Toxic and Hazardous Chemicals and Carcinogens, 1985. 2nd ed. Park Ridge, NJ: Noyes Data Corporation, 1985. 160]**PEER REVIEWED**

Respirators may be used when engineering and work practice controls are not technically feasible, when such controls are in the process of being installed, or when they fail and need to be supplemented. Respirators may also be used for operations which require entry into tanks or closed vessels, and in emergency situations. ... Clothing wet with liquid butyl alcohol should be placed in closed containers for storage until it can be discarded or until provision is made for the removal of butyl alcohol from the clothing. If the clothing is to be laundered or otherwise cleaned to remove the butyl alcohol, the person performing the operation should be informed of butyl alcohol's hazardous properties. Any clothing which becomes wet with liquid butyl alcohol should be removed immediately and not reworn until the butyl alcohol is removed from the clothing.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 2]**PEER REVIEWED**

If material /is/ not on fire and not involved in fire: Keep sparks, flames, and other sources of ignition away. Keep material out of water sources and sewers. Build dikes to contain flow as necessary. Attempt to stop leak if without undue personnel hazard. Use water spray to disperse vapors and dilute standing pools of liquid.
[Association of American Railroads. Emergency Handling of Hazardous Materials in Surface Transportation. Washington, D.C.: Assoc. of American Railroads,Hazardous Materials Systems (BOE), 1987. 106]**PEER REVIEWED**

Avoid breathing vapors. Keep upwind. ... Do not handle broken packages unless wearing appropriate personal protective equipment. Wash away any material which may have contacted the body with copious amounts of water or soap and water.
[Association of American Railroads. Emergency Handling of Hazardous Materials in Surface Transportation. Washington, D.C.: Assoc. of American Railroads,Hazardous Materials Systems (BOE), 1987. 106]**PEER REVIEWED**

SRP: Contaminated protective clothing should be segregated in such a manner so that there is no direct personal contact by personnel who handle, dispose, or clean the clothing. Quality assurance to ascertain the completeness of the cleaning procedures should be implemented before the decontaminated protective clothing is returned for reuse by the workers. Contaminated clothing should not be taken home at end of shift, but should remain at employee's place of work for cleaning.
**PEER REVIEWED**

Employees who handle liquid isobutyl alcohol should wash their hands before eating or smoking. /Isobutyl alcohol/
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 3]**PEER REVIEWED**

The worker should immediately wash the skin when it becomes contaminated.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

Work clothing that becomes wet should be immediately removed due to its flammability hazard.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Shipment Methods and Regulations:

No person may /transport,/ offer or accept a hazardous material for transportation in commerce unless that person is registered in conformance ... and the hazardous material is properly classed, described, packaged, marked, labeled, and in condition for shipment as required or authorized by ... /the hazardous materials regulations (49 CFR 171-177)./
[49 CFR 171.2 (7/1/2000)]**PEER REVIEWED**

The International Air Transport Association (IATA) Dangerous Goods Regulations are published by the IATA Dangerous Goods Board pursuant to IATA Resolutions 618 and 619 and constitute a manual of industry carrier regulations to be followed by all IATA Member airlines when transporting hazardous materials.
[IATA. Dangerous Goods Regulations. 41st Ed.Montreal, Canada and Geneva, Switzerland: International Air Transport Association, Dangerous Goods Regulations, 2000. 124]**PEER REVIEWED**

The International Maritime Dangerous Goods Code lays down basic principles for transporting hazardous chemicals. Detailed recommendations for individual substances and a number of recommendations for good practice are included in the classes dealing with such substances. A general index of technical names has also been compiled. This index should always be consulted when attempting to locate the appropriate procedures to be used when shipping any substance or article.
[IMDG; International Maritime Dangerous Goods Code; International Maritime Organization p.3314 (1998)]**PEER REVIEWED**

 

Storage Conditions:

Store in cool, unlighted place away from ... explosives ... organic peroxides, poisons and radioactive materials.
[ITII. Toxic and Hazarous Industrial Chemicals Safety Manual. Tokyo, Japan: The International Technical Information Institute, 1982. 84]**PEER REVIEWED**

Preserve in tight containers, and prevent exposure to excessive heat.
[USP Convention. The United States Pharmacopeia 21st Revision/The National Formulary 16th ed. Rockville, MD: United States Pharmacopeial Convention, Inc.,Jan. 1, 1985 (plus Supplements 1-6). 1538]**PEER REVIEWED**

 

Cleanup Methods:

1. REMOVE ALL IGNITION SOURCES. 2. VENTILATE AREA OF SPILL OR LEAK. 3. FOR SMALL QUANTITIES ABSORB ON PAPER TOWELS. EVAPORATE IN SAFE PLACE (SUCH AS FUME HOOD). ALLOW SUFFICIENT TIME FOR EVAPORATING VAPORS TO ... CLEAR HOOD DUCTWORK. BURN PAPER IN SUITABLE LOCATION AWAY FROM COMBUSTIBLE MATERIALS.
[Prager, J.C. Environmental Contaminant Reference Databook Volume 1. New York, NY: Van Nostrand Reinhold, 1995. 353]**PEER REVIEWED**

Waste water treatment: Activated carbon: adsorbability: 0.107 g/g C, 53.4% reduction, influent: 1,000 mg/l, effl: 466 mg/l; reverse osmosis: 41.3% rejection from a 0.01 M soln; stabilization pond design: toxicity correction factor: 2.0 at 4,000 mg/l influent; anaerobic lagoon: 22 lb Chemical Oxygen Demand (COD)/day/1,000 cu ft: influent: 170 mg/l, effluent: 75 mg/l; 48 lb COD/day/1,000 cu ft: influent: 170 mg/l, effluent: 80 mg/l
[Verschueren, K. Handbook of Environmental Data of Organic Chemicals. 2nd ed. New York, NY: Van Nostrand Reinhold Co., 1983. 300]**PEER REVIEWED**

 

Disposal Methods:

Generators of waste (equal to or greater than 100 kg/mo) containing this contaminant, EPA hazardous waste number U031; F003, must conform with USEPA regulations in storage, transportation, treatment and disposal of waste.
[40 CFR 240-280, 300-306, 702-799 (7/1/2000)]**PEER REVIEWED**

Incineration, landfill: Incinerate by atomizing into a suitable combustion chamber. Bury adsorbed waste in an approved landfill.
[United Nations. Treatment and Disposal Methods for Waste Chemicals (IRPTC File). Data Profile Series No. 5. Geneva, Switzerland: United Nations Environmental Programme, Dec. 1985. 117]**PEER REVIEWED**

1. ABSORBING IN VERMICULITE, DRY SAND, EARTH OR SIMILAR MATERIAL & DISPOSING IN SECURED SANITARY LANDFILL. 2. ATOMIZING IN SUITABLE COMBUSTION CHAMBER.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 4]**PEER REVIEWED**

Good candidate for liquid injection incineration, with a temperature range of 650 to 1600 deg C, and a residence time of 0.1 to 2 seconds. Also, a good candidate for rotary kiln incineration, with a temperature range of 820 to 1600 deg C, and a residence time of seconds. Additionally, a good candidate for fluidized bed incineration, with a temperature range of 450 to 980 deg C, and a residence time of seconds. /From table/
[USEPA; Engineering Handbook for Hazardous Waste Incineration p.3-4 (1981) EPA 68-03-3025]**PEER REVIEWED**

n-Butyl alcohol is a waste chemical stream constituent which may be subjected to ultimate disposal by controlled incineration. /From table/
[USEPA; Engineering Handbook for Hazardous Waste Incineration p.2-4 (1981) EPA 68-03-3025]**PEER REVIEWED**

 

Occupational Exposure Standards:

 

 

OSHA Standards:

Permissible Exposure Limit: Table Z-1 8-hr Time Weighted Avg: 100 ppm (300 mg/cu m).
[29 CFR 1910.1000 (7/1/2000)]**PEER REVIEWED**

Vacated 1989 OSHA PEL Ceiling limit: 50 ppm (150 mg/cu m), skin designation, is still enforced in some states.
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 360]**PEER REVIEWED**

 

Threshold Limit Values:

Ceiling Limit 50 ppm, skin
[American Conference of Governmental Industrial Hygienists. TLVs and BEIs. Threshold Limit Values for Chemical Substances and Physical Agents and Biological Exposure Indices. Cincinnati, OH. 2000. 21]**PEER REVIEWED**

Notice of Intended Change for 2000: These substances, with their corresponding values and notations, comprise those for which a limit has been proposed for the first time or for which a change in the Adopted listing has been proposed. In each case, the proposed values should be considered trial values for the year following ratification by the ACGIH Board of Directors. If, during the year, no evidence comes t light that questions the appropriateness of these proposals, the value will be reconsidered for adoption as TLVs. Time Weighted Avg (TWA): 20 ppm; Short Term Exposure Limit (STEL): 50 ppm.
[American Conference of Governmental Industrial Hygienists. TLVs and BEIs. Threshold Limit Values for Chemical Substances and Physical Agents and Biological Exposure Indices. Cincinnati, OH. 2000. 73]**PEER REVIEWED**

 

NIOSH Recommendations:

Recommended Exposure Limit: (15 Min) Ceiling value: 50 ppm (150 mg/cu m) [skin].
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Immediately Dangerous to Life or Health:

1400 ppm [Based on 10% of the lower explosion limit for safety considerations even though the relevant toxicological data indicated irreversible health effects or impairment of escape existed only at higher concentrations.]
[NIOSH. NIOSH Pocket Guide to Chemical Hazards. DHHS (NIOSH) Publication No. 97-140. Washington, D.C. U.S. Government Printing Office, 1997. 38]**PEER REVIEWED**

 

Other Occupational Permissible Levels:

Max allowable concn (MAC) USSR 10 mg/cu m
[International Labour Office. Encyclopedia of Occupational Health and Safety. Vols. I&II. Geneva, Switzerland: International Labour Office, 1983. 109]**PEER REVIEWED**

 

Manufacturing/Use Information:

 

 

Major Uses:

... is employed as a solvent for paints, lacquers & varnishes, natural & synthetic resins, gums, vegetable oils, dyes & alkaloids. It is used as an intermediate in the manufacture of pharmaceuticals & chemicals, & employed in industries producing artificial leather, textiles, safety glass, rubber cement, shellac, raincoats, photographic films & perfumes.
[International Labour Office. Encyclopaedia of Occupational Health and Safety. 4th edition, Volumes 1-4 1998. Geneva, Switzerland: International Labour Office, 1998.,p. 104.32]**PEER REVIEWED**

MEDICATION (VET)
**PEER REVIEWED**

Solvent for oils & fats, waxes, resins, shellac, varnishes & rubbers; raw material for butyl acetate
[ITII. Toxic and Hazarous Industrial Chemicals Safety Manual. Tokyo, Japan: The International Technical Information Institute, 1982. 84]**PEER REVIEWED**

CHEM INT FOR ETHYLENE GLYCOL MONOBUTYL ETHER, PLASTICIZERS INCL DIBUTYL PHTHALATE; CHEM INT FOR BUTYLAMINES, 2,4-D ESTERS
[SRI]**PEER REVIEWED**

REPORTED USES: NON-ALCOHOLIC BEVERAGES 12 PPM; ALCOHOLIC BEVERAGES 1.0 PPM; ICE CREAM, ICES, ETC 7.0 PPM; CANDY 34 PPM; BAKED GOODS 32 PPM; CREAM 4.0 PPM
[Fenaroli's Handbook of Flavor Ingredients. Volume 2. Edited, translated, and revised by T.E. Furia and N. Bellanca. 2nd ed. Cleveland: The Chemical Rubber Co., 1975. 62]**PEER REVIEWED**

MEDICATION
**PEER REVIEWED**

Manufacture of hydraulic fluids; detergent formulations; dehydrating agent; intermediate for glycol ethers; preparation of esters, especially butyl acetate
[Lewis, R.J., Sr (Ed.). Hawley's Condensed Chemical Dictionary. 13th ed. New York, NY: John Wiley & Sons, Inc. 1997. 175]**PEER REVIEWED**

Used in alkyd resin coatings; provide diluent for formulating brake fluids suitable for use in passenger cars; used as an extractant in the mfr of antibiotics, vitamins, & hormones
[Kirk-Othmer Encyclopedia of Chemical Technology. 4th ed. Volumes 1: New York, NY. John Wiley and Sons, 1991-Present.,p. V4 (92) 696]**PEER REVIEWED**

As stabilizing agent.
[Kirk-Othmer Encyclopedia of Chemical Technology. 4th ed. Volumes 1: New York, NY. John Wiley and Sons, 1991-Present.,p. V4 (92) 696]**PEER REVIEWED**

Application in surface coatings; in adhesive & as a solvent adhesive in the manufacture of garments from polyvinyl butyral coated fabric; in the manufacture of derivatives of butyl alcohol, incl chemicals, herbicides, ore flotation agents, urea & melamine formaldehyde resins, & pharmaceuticals. Denatured alcohol, a swelling agent in textiles, is also used as an azeotrophic dehydrating agent & blending agent in laboratory analysis.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 3]**PEER REVIEWED**

... In microscopy for preparing paraffin imbedding materials.
[American Conference of Governmental Industrial Hygienists, Inc. Documentation of the Threshold Limit Values and Biological Exposure Indices. 6th ed. Volumes I,II, III. Cincinnati, OH: ACGIH, 1991. 170]**PEER REVIEWED**

 

Manufacturers:

BASF Corp., 3000 Continental Drive-North, Mount Olive, NJ 07828-1234, (973) 426-2600; Production site: Freeport, TX 77541
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

Celanese LTD., 86 Morris Avenue, Summit, NJ 07901, (972) 443-4000; Production site: Baytown, TX 77520
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

CONDEA Vista Co., 900 Threadneedle, Houston, TX 77079-2900, (281) 588-3000; Production site: Lake Charles, LA 70669
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

Eastman Chemical Co., P.O. Box 511, Kingsport, TN 37662, (423) 229-2196; Production site: Longview, TX 75607
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

Shell Chemical Co., One Shell Plaza, P.O. Box 2463 Houston, TX 77252-2463, (713) 241-6161; Production site: Deer Park, TX 77536
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

Texmark Chemicals, 900 Clinton Drive, Galena Park, TX 77547, (713) 455-1206; Production site: Galena Park, TX 77547
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

Union Carbide Corp., 39 Old Ridgebury Rd., Danbury, CT 06817-0001, (203) 794-2000; Production sites: Texas City, TX 77590; Taft, LA 70057
[SRI International. 2000 Directory of Chemical Producers -- United States. SRI Consulting, Menlo Park: CA 2000 494]**PEER REVIEWED**

 

Methods of Manufacturing:

The prinicipal commercial source of 1-butanol is n-butraldehyde, obtained from the oxo reaction of propylene, followed by hydrogenation in the presence of a catalyst. ... produced from ethanol via successive dehydrogenation to acetaldehyde, followed by an aldol process.
[Clayton, G.D., F.E. Clayton (eds.) Patty's Industrial Hygiene and Toxicology. Volumes 2A, 2B, 2C, 2D, 2E, 2F: Toxicology. 4th ed. New York, NY: John Wiley & Sons Inc., 1993-1994. 2636]**PEER REVIEWED**

... OBTAINED BY FERMENTATION OF GLYCEROL, MANNITE, STARCHES, & SUGARS IN GENERAL, USING BACILLUS BUTYLICUS SOMETIMES SYNERGIZED BY PRESENCE OF CLOSTRIDIUM ACETOBUTYRICUM, SYNTHETICALLY, FROM ACETYLENE.
[Fenaroli's Handbook of Flavor Ingredients. Volume 2. Edited, translated, and revised by T.E. Furia and N. Bellanca. 2nd ed. Cleveland: The Chemical Rubber Co., 1975. 62]**PEER REVIEWED**

... manufacture from ethylene oxide and triethylaluminum ... manufacture by carbohydrate fermentation, by hydrogenation of butyraldehyde, from crotonaldehyde.
[Budavari, S. (ed.). The Merck Index - An Encyclopedia of Chemicals, Drugs, and Biologicals. Whitehouse Station, NJ: Merck and Co., Inc., 1996. 255]**PEER REVIEWED**

Ethyl alcohol may be converted directly to 1-butanol at 325 deg C and 13 MPa (128 atm) over magnesium oxide/copper oxide. A mixture of butanol, hexyl and octyl alcohols, acetaldehyde, butyraldehyde, and crontonaldehyde is obtained when ethanol and hydrogen are passed over magnesium oxide at 200 deg C and 10 MPa (99 atm). Butyl bromide can be hydrolyzed at 130-180 deg C at 350-700 kPa (3.5-6.9 atm) to give a mixture of butanol and dibutyl ether; the dibutyl ether can be converted to 81% butanol by heating with 48% aq hydrobromic acid in an autoclave at 150 deg C. An 82% yield of 1-butanol can be obtained from a low temp reduction of n-butyraldehyde with sodium borohydride. At 200-300 deg C and 10 MPa (99 atm), furan has been reduced in the presence of copper chromite-barium chromite catalyst to butanol in 70% yields.
[Kirk-Othmer Encyclopedia of Chemical Technology. 3rd ed., Volumes 1-26. New York, NY: John Wiley and Sons, 1978-1984.,p. V4 (78) 342]**PEER REVIEWED**

... Ethylmagnesium chloride undergoes reaction with two equivalents of ethylene oxide to yield both n-butyl alcohol (80% yield) and ethylene chlorohydrin (70% yield) ... .
[Kirk-Othmer Encyclopedia of Chemical Technology. 3rd ed., Volumes 1-26. New York, NY: John Wiley and Sons, 1978-1984.,p. V12 (80) 42]**PEER REVIEWED**

 

Formulations/Preparations:

GRADE OR PURITY: 99+%
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

ACS reagent grade
[USP Convention. The United States Pharmacopeia 21st Revision/The National Formulary 16th ed. Rockville, MD: United States Pharmacopeial Convention, Inc.,Jan. 1, 1985 (plus Supplements 1-6). 1367]**PEER REVIEWED**

 

Impurities:

0.10% water by wt (max)
[Flick, E.W. Industrial Solvents Handbook. 3rd ed. Park Ridge, NJ: Noyes Publications, 1985. 229]**PEER REVIEWED**

 

Consumption Patterns:

20% AS A SOLVENT FOR SURFACE COATINGS; 14% FOR SYNTHESIS OF GLYCOL ETHERS (INCL ETHYLENE GLYCOL MONOBUTYL ETHER); 12% FOR PLASTICIZERS (INCL DIBUTYL PHTHALATE); 20% FOR N-BUTYL ACETATE; 10% EXPORTED; 7% FOR SYNTHESIS OF N-BUTYL ACRYLATE; 15% FOR MISC APPLCNS (INCL SYNTHESIS OF BUTYLAMINES AND 2,4-D ESTERS) (1972)
[SRI]**PEER REVIEWED**

30% FOR BUTYL ACRYLATES AND METHACRYLATE; 23% FOR GLYCOL ETHERS; 12.5% FOR BUTYL ACETATE; 12.5% FOR SOLVENT; 8% FOR PLASTICIZERS; 5% FOR AMINO RESINS; 1% FOR AMINES; 1% MISCELLANEOUS; 7% FOR EXPORTS (1984)
[CHEMICAL PROFILE: N-BUTANOL, 1985]**PEER REVIEWED**

CHEMICAL PROFILE: n-Butanol. Butylacrylate and methacrylate, 28%; glycol ethers, 20%; solvent use, 12%; butyl acetate, 10%; plasticizers, 6%; amino resins, 3%; amines, 1%; miscellaneous, 2%; exports, 18%.
[Kavaler AR; Chemical Marketing Reporter 232 (19): 58 (1987)]**PEER REVIEWED**

CHEMICAL PROFILE: n-Butanol. Demand: 1986: 1,000 million lb; 1987: 1,100 million lb; 1991 /projected/: 1,150 million lb (Includes exports; imports are negligible).
[Kavaler AR; Chemical Marketing Reporter 232 (19): 58 (1987)]**PEER REVIEWED**

Demand: (1998) 1.8 billion lb; (1999) 1.85 billion lb; (2000) 2 billion lb
[ChemExpo; Chemical Marketing Reporter. Chemical Profile on n-Butanol. July 5, 1999. NY, NY: Schnell Pub Co. Available from the Database Query page at http://www.chemexpo.com/news/newsframe.cfm?framebody=/news/profile.cfm as of Dec 11, 2000.]**PEER REVIEWED**

 

U. S. Production:

(1972) 2.68X10+11 G
[SRI]**PEER REVIEWED**

(1975) 2.22X10+11 G
[SRI]**PEER REVIEWED**

(1984) 4.12X10+11 g
[USITC. SYN ORG CHEM-U.S. PROD/SALES 1984 p.257]**PEER REVIEWED**

(1986) 8.57X10+8 lb
[USITC. SYN ORG CHEM-U.S. PROD. PRELIMINARY FEBRUARY 1988 (SERIES C/P 87-5)]**PEER REVIEWED**

(1987) 1.15X10+9 lb
[USITC. SYN ORG CHEM-U.S. PROD/SALES 1987 p.15-5]**PEER REVIEWED**

(1992) 1.26 billion lb
[Chem & Engineering News 72 (15): 13 (4/11/94)]**PEER REVIEWED**

(1993) 1.33 billion lb
[Chem & Engineering News 72 (15): 13 (4/11/94)]**PEER REVIEWED**

 

U. S. Imports:

(1972) NEGLIGIBLE
[SRI]**PEER REVIEWED**

(1975) 1.48X10+10 G
[SRI]**PEER REVIEWED**

(1984) 4.69X10+8 g
[BUREAU OF THE CENSUS. US IMPORTS FOR CONSUMPTION AND GENERAL IMPORTS 1984 p.1-359]**PEER REVIEWED**

(1986) 1.71X10+5 lb /Butyl alcohol, NSPF/
[BUREAU OF THE CENSUS. US IMPORTS FOR CONSUMPTION AND GENERAL IMPORTS 1986 P.1-527]**PEER REVIEWED**

(1998) 25 million lb
[ChemExpo; Chemical Marketing Reporter. Chemical Profile on n-Butanol. July 5, 1999. NY, NY: Schnell Pub Co. Available from the Database Query page at http://www.chemexpo.com/news/newsframe.cfm?framebody=/news/profile.cfm as of Dec 11, 2000.]**PEER REVIEWED**

 

U. S. Exports:

(1972) 2.68X10+10 G
[SRI]**PEER REVIEWED**

(1975) 2.99X10+10 G
[SRI]**PEER REVIEWED**

(1984) 1.83X10+10 g
[BUREAU OF THE CENSUS. US EXPORTS, SCHEDULE E, 1984 p.2-75]**PEER REVIEWED**

(1987) 1.77X10+7 lb
[BUREAU OF THE CENSUS. US EXPORTS, SCHEDULE E, DECEMBER 1987, P.2-78]**PEER REVIEWED**

(1988) 1.13X10+7 lb
[BUREAU OF THE CENSUS. US EXPORTS, SCHEDULE E, DECEMBER 1988, P.2-81]**PEER REVIEWED**

Annual average exports for 1994-1998 were 286 million lb
[ChemExpo; Chemical Marketing Reporter. Chemical Profile on n-Butanol. July 5, 1999. NY, NY: Schnell Pub Co. Available from the Database Query page at http://www.chemexpo.com/news/newsframe.cfm?framebody=/news/profile.cfm as of Dec 11, 2000.]**PEER REVIEWED**

 

Laboratory Methods:

 

 

Clinical Laboratory Methods:

N-BUTANOL CAN BE SEPARATED FROM BIOLOGICAL LIQ AFTER INJECTION ONTO PACKED GAS-CHROMATOGRAPHIC COLUMNS ... SEPARATED VOLATILE COMPONENT MAY BE IDENTIFIED BY ITS GAS-CHROMATOGRAPHIC RETENTION TIME & QUANTITATED BY MEANS OF GAS CHROMATOGRAPH DETECTOR RESPONSE. N-BUTANOL HAS A RELATIVE RETENTION TIME OF 6.60 MIN (ETHANOL= 1.9 MIN).
[Sunshine, Irving (ed.) Methodology for Analytical Toxicology. Cleveland: CRC Press, Inc., 1975. 407]**PEER REVIEWED**

The detection of n-butanol in 50-100 ul blood serum is performed by capillary gas chromatograpy. Detection limit is 10 ug/l.
[Wolf M et al; Blutalkohol 22 (4): 321-32 (1985)]**PEER REVIEWED**

 

Analytic Laboratory Methods:

OSW Method 8260B. Volatile Organic Compounds by Gas Chromatography/Mass Spectrometry (GC/MS): Capillary Column Technique. No detection limit.
[USEPA; EMMI. EPA's Environmental Monitoring Methods Index. Version 1.1. PC# 4082. Rockville, MD: Government Institutes (1997)]**PEER REVIEWED**

OSW Method 8015B. Nonhalogenated Organics Using GC/FID. No detection limit.
[USEPA; EMMI. EPA's Environmental Monitoring Methods Index. Version 1.1. PC# 4082. Rockville, MD: Government Institutes (1997)]**PEER REVIEWED**

NIOSH Method 1401. Determination of Alcohols by Gas Chromatography, Using a Flame Ionization Detector. Detection limit 1 mg/cu m.
[U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health. NIOSH Manual of Analytical Methods. 4th ed.Methods A-Z & Supplements. Washington, DC: U.S. Government Printing Office, Aug 1994.]**PEER REVIEWED**

A modified variant of the purge-and-trap gas chromatographic analysis of volatile organic carbon compounds in water was designed. Samples ... are purged ... in an ultrapure helium gas stream using an open loop arrangement. Volatile eluates are trapped onto selective adsorbents packed inside stainless steel tubes connected in series. After stripping, ... the adsorbent tubes are disconnected, fitted with analytical desorption caps and sequentially desorbed ... on a thermal desorber. The desorbed organics are trapped ... on a packed cold trap prior to flash volatilization of the volatiles across a fused silica transfer line onto a capillary column. The method /uses/ flame ionization and ion trap detection and is capable of quantitation down to 5 ng/l per component. The recoveries of n-butyl alcohol from water at 30 and 60 deg C were 58 and 84%, respectively.
[Bianchi A et al; J Chromatogr 467 (1): 111-28 (1989)]**PEER REVIEWED**

 

Sampling Procedures:

... Sampling ... may be performed by collection of n-butyl alcohol vapors using an adsorption tube.
[Mackison, F. W., R. S. Stricoff, and L. J. Partridge, Jr. (eds.). NIOSH/OSHA - Occupational Health Guidelines for Chemical Hazards. DHHS(NIOSH) PublicationNo. 81-123 (3 VOLS). Washington, DC: U.S. Government Printing Office, Jan. 1981. 3]**PEER REVIEWED**

A SIMPLIFIED QUANTITATIVE METHOD IS DESCRIBED FOR COLLECTION OF ORGANIC POLLUTANTS IN AIR ON A POROUS POLYMER TRAP.
[PARSONS JS, MITZNER S; ENVIRON SCI TECHNOL 9 (12): 1053-8 (1975)]**PEER REVIEWED**

NIOSH 1401: Analyte: n-butyl alcohol; Matrix: air; Sampler: solid sorbent tube (coconut shell charcoal, 100 mg/50 mg); Flow rate: 0.01 to 0.2 l/min; Vol: min: 1 l, max: 10 l; Stability: unknown; store in freezer /Alcohols II, n-butyl alcohol/
[U.S. Department of Health and Human Services, Public Health Service. Centers for Disease Control, National Institute for Occupational Safety and Health. NIOSHManual of Analytical Methods, 3rd ed. Volumes 1 and 2 with 1985 supplement, and revisions. Washington, DC: U.S. Government Printing Office, February 1984.,p. V1 1401-1]**PEER REVIEWED**

 

Special References:

 

 

Special Reports:

Brusewitz S, Wennberg A; Arbetarskyddsstyrelsen (1984). Criteria document for setting exposure limits for butanol and butyl acetate.

 

Synonyms and Identifiers:

 

 

Synonyms:

ALCOOL BUTYLIQUE (FRENCH)
**PEER REVIEWED**

BUTANOL
**PEER REVIEWED**

N-BUTANOL
**PEER REVIEWED**

N-BUTAN-1-OL
**PEER REVIEWED**

BUTAN-1-OL
**PEER REVIEWED**

BUTANOLEN (DUTCH)
**PEER REVIEWED**

BUTANOL (FRENCH)
**PEER REVIEWED**

BUTANOLO (ITALIAN)
**PEER REVIEWED**

BUTYL ALCOHOL
**PEER REVIEWED**

BUTYL HYDROXIDE
**PEER REVIEWED**

BUTYLOWY ALKOHOL (POLISH)
**PEER REVIEWED**

BUTYRIC ALCOHOL
**PEER REVIEWED**

CCS 203
**PEER REVIEWED**

FEMA NUMBER 2178
**PEER REVIEWED**

HEMOSTYP
**PEER REVIEWED**

1-HYDROXYBUTANE
**PEER REVIEWED**

METHYLOLPROPANE
**PEER REVIEWED**

NBA
**PEER REVIEWED**

NORMAL PRIMARY BUTYL ALCOHOL
**PEER REVIEWED**

PROPYLCARBINOL
**PEER REVIEWED**

PROPYLMETHANOL
**PEER REVIEWED**

 

Formulations/Preparations:

GRADE OR PURITY: 99+%
[U.S. Coast Guard, Department of Transportation. CHRIS - Hazardous Chemical Data. Volume II. Washington, D.C.: U.S. Government Printing Office, 1984-5.]**PEER REVIEWED**

ACS reagent grade
[USP Convention. The United States Pharmacopeia 21st Revision/The National Formulary 16th ed. Rockville, MD: United States Pharmacopeial Convention, Inc.,Jan. 1, 1985 (plus Supplements 1-6). 1367]**PEER REVIEWED**

 

Shipping Name/ Number DOT/UN/NA/IMO:

UN 1120; Butanol

IMO 3.3; Butanol

NA 1120; Butyl alcohol

 

Standard Transportation Number:

49 091 17; Butyl alcohol

49 091 17; n-butyl alcohol

 

EPA Hazardous Waste Number:

U031; A toxic waste when a discarded commercial chemical product or manufacturing chemical intermediate or an off-specification commercial chemical product or manufacturing chemical intermediate.

F003; A hazardous waste from nonspecific sources when a spent solvent.

 

RTECS Number:

NIOSH/EO1400000

 

Administrative Information:

 

 

Hazardous Substances Databank Number: 48

Last Revision Date: 20020213

Last Review Date: Reviewed by SRP on 5/10/2001

http://www.nycwasteless.com/gov-bus/citysense/edefinitions.htm
Acute Health Effects:
Can irritate skin, causing a burning sensation or rash on contact. Can irritate and burn eyes, leading to tearing and damage. Inhalation can cause coughing, wheezing, and shortness of breath, headache, nausea, vomiting, and dizziness; higher levels can cause unconsciousness and irregular heartbeat.

Chronic Health Effects:
Repeated contact may cause drying and cracking of skin. Exposure can damage liver, heart, kidneys, hearing, and sense of balance.

 

N-butyl Alcohol
... Health effects: Exposure to n-butyl alcohol can cause death from respiratory
failure and cardiac failure. Exposure can occur through ...
http://www.nsc.org/library/chemical/N-butyla.htm
More Results From: www.nsc.org

BUTYL ALCOHOL, NORMAL
... CAS No Percent Hazardous -----
n-Butyl Alcohol 71-36 ... Potential Health Effects ...
http://www.jtbaker.com/msds/b5860.htm
More Results From: www.jtbaker.com

Erowid Alcohol Vault : Info #5 - n-Butyl Alcohol
... HAZARD INFORMATION Acute Health Effects The following acute (short term) health
effects may occur immediately or shortly after exposure to n-Butyl Alcohol: * ...
http://www.erowid.org/chemicals/alcohol/alcohol_info5.shtml
More Results From: www.erowid.org

Product Lines Application Guide Solvent Physical Properties ...
... 3, 1, 2. n-Butyl Alcohol, 2, 3, 1, 3. n-Butyl ... 4, 1, 1. Petroleum Ether, 1, 4, 1, 1.
n-Propyl Alcohol, ... Susceptibility for causing adverse acute or chronic health effects ...
http://www.bandj.com/BJProduct/HealthSafety/Health2.html
More Results From: www.bandj.com

tec: Publishing Item: Details: Solvents: health effects
... 6 Methyl alcohol 1, 4, 11 Propyl alcohol 1 Butyl alcohol 1, 11 Methyl ethyl ketone
1a 150 Methyl n-butyl ... that it is safe, nor are all the health effects ...
http://www.nccnsw.org.au/member/tec/projects/tcye/detail/Household/Solv_healt_42.html

CHEMICAL REFERENCE FOR N-BUTANOL
... 1-BUTANOL ; N-BUTYL ALCOHOL The ... and Toxics (OPPT) Chemical Fact Sheets provide a
summary on chemical exposure, health and environmental effects ...
http://www.epa.gov/enviro/html/emci/chemref/71363.html
More Results From: www.epa.gov

Matheson Tri-Gas MSDS N-Butyl Alcohol
... SECTION 2 COMPOSITION, INFORMATION ON INGREDIENTS COMPONENT: N-BUTYL ALCOHOL CAS ... Vapor
may cause flash fire. POTENTIAL HEALTH EFFECTS: INHALATION ...
http://www.matheson-trigas.com/msds/NButylAlcohol.htm
More Results From: www.matheson-trigas.com

n-Butyl Alcohol
... NAME: n-Butyl Alcohol SYNONYM(s): Butyl alcohol; 1 ... corneal inflammation, blurred vision,
lacrimation, photophobia; dry, cracked skin HEALTH EFFECTS ...
http://www.osha-slc.gov/dts/chemicalsampling/data/CH_222900.html
More Results From: www.osha-slc.gov

Custom Agricultural Formulators: Products: Spray Adjuvants: ...
... Chemical CAS Number TLV or PEL. Ethoxylated Alcohol Phosphate N-Butyl Alcohol
71-36-3 100/ppm III. ... V. PHYSIOLOGICAL & HEALTH EFFECTS. ...
http://www.customagformulators.com/spray/blender.htm

n-Butyl Alcohol
n-Butyl Alcohol. 10/29/86. ... Health. Effects: Inhalation: May cause dizziness
or unconsciousness. Skin: May cause irritation. ...
http://www.camd.lsu.edu/msds/b/nbutyl_alcohol.htm
More Results From: www.camd.lsu.edu

Glassodur-Special Converter for 21-Line (PDF)
... Butyl acetate 123-86-4 40-60 n-Butyl alcohol 71-36-3 20-30 Ingredients determined
not to be hazardous to 100 HEALTH HAZARD INFORMATION Health Effects Acute ...
http://www.health.adelaide.edu.au/ComMed/consulting/eap/522-44.pdf
More Results From: www.health.adelaide.edu.au

Air Quality: The Need For Action
... 1,301,219. Chronic Toxicity, Environmental Toxicity. N-Butyl Alcohol. ... Toxics Release
Inventory Database, 1999; human health and environmental effects ...
http://www.texasep.org/html/air/air_1nfa.html

Consumer Information: 1996-06 Toxic Air Contaminant ... (PDF)
... in this evaluation include carcinogenic and noncarcinogenic health effects ... Molybdenum
trioxide Bromine compounds (inorganic) n-Butyl alcohol Butyl ...
http://www.arb.ca.gov/toxics/tac/appendxa.pdf
More Results From: www.arb.ca.gov

Air
... Direct health effects. ... ranking of air emission MODERATE priority contaminants based
on health ... Acetic acid, Ammonia. Bromine, Butyl acrylate, n-Butyl alcohol. ...
http://environment-network.com/training/aspects/concerns/air.htm

C-Health - Disease in Depth
... 10 Aluminum Lake, n-butyl alcohol, propylene ... 3A alcohol, pharmaceutical shellac, ethyl
alcohol, isopropyl alcohol ... Other reported side effects include: dizziness; ...
http://www.mediresource.net/canoe/health/DrugInfo.asp?BrandNameID=348
More Results From: www.mediresource.net

Material Safety Data Sheet (PDF)
... PEL TLV Acetone 67-64-1 1000 ppm 500 ppm n-Butyl Alcohol 71 ... Routes of Exposure: Inhalation
Skin Contact Eye Contact Potential Acute Health Effects ...
http://www.zinsser.com/pdf/MSDS/_spraysh.pdf
More Results From: www.zinsser.com

Alcohol
Basic Health Information: facts1: basic facts about alcohol. alcohol-effects.html:
specific effects related to the blood alcohol concentration; aging-and-alcohol ...
http://paranoia.lycaeum.org/alcohol/

BYPRODUCT AND RECYCLED SOLVENTS FOR SALE
... Like all chlorinated solvents, it has now been associated with untoward health effects
and is rarely used in consumer products. ... n-BUTYL ALCOHOL ...
http://www.chem-surf.com/recycling/solvents.html

MATERIAL SAFETY DATA SHEET Conductive carbon paint (PDF)
... Hexylene Glycol 107-41-5 3% n-Butyl ... Dimethoxymethane 109-87-5 1% tert-Butyl Alcohol
75 ... 2 Conductive carbon paint HEALTH HAZARD INFORMATION Health Effects ...
http://www.proscitech.com/msds/i003.pdf

Joan Rothlein, PhD
... EM (1977) Biochemical and cytogenic effects in ... Health 3:769-1076. ... Gasoline, Acrolein,
Chlorine, tert-Butyl Alcohol ... Hydrogen Cyanide, Methyl Chloride, Methyl n ...
http://www.ohsu.edu/croet/rothlein/rothlein.html

Great Lakes Chemical Corporation and the Pathfinders Camp