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· CALL 911. Then call emergency response telephone number on shipping paper. If shipping paper not available or no answer, refer to appropriate telephone number listed on the inside back cover.

· ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from immediate area.

INHALATION: Call for medical aid. Remove the victim to fresh air. If not breathing give artificial respiration. If breathing is difficult, give oxygen.

General First Aid:

To fight fire, use foam, carbon dioxide, dry chemical.

If material on fire or involved in fire: Do not extinguish fire unless flow can be stopped or safely confined. 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 foam, dry chemical, or carbon dioxide. Keep run-off water out of sewers and water sources.

SRP: At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices.

The following wastewater treatment technologies have been investigated for n-propyl benzene: concentration process: biological treatment.

If material 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 knock-down vapors.

Personnel protection: Avoid breathing vapors. Keep upwind. ... Avoid bodily contact with the material. ... 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. ... If contact with the material anticipated, wear appropriate chemical protective clothing.

Excerpt from ERG Guide 128 [Flammable Liquids (Water-Immiscible)]:

Immediate precautionary measure

3.7 [ppm]

41 [ppm]

240 [ppm]

WEC50 Mytilus edulis (mussels) 0.86 mg/l (0.69-1.07 mg/l) (toxicant concn in water required to reduce feeding rate by 50%).

TEC50 Mytilus edulis (mussels) 27.0 mg/kg (22.7-32.1 mg/kg) (toxicant conc in mussel tissue required to reduce feeding rate by 50%).

TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 955(SRC), determined from molecular connectivity indices(2), and measured values of 495 to 725(3,4) indicates that n-propylbenzene is expected to have low mobility in soil(SRC). Volatilization of n-propylbenzene from moist soil surfaces is expected to be an important fate process(7) given a Henry's Law constant of 1.05X10-2 atm-cu m/mole(5). The potential for volatilization of n-propylbenzene from dry soil surfaces may exist(SRC) based upon a vapor pressure of 3.42 mm Hg(6). Biodegradation from soil may occur based on results from activated sludge studies(8).

AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 955(SRC), determined from molecular connectivity indices(2), as well as measured Koc values ranging from 495 to 725(3,4), indicate that n-propylbenzene is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(5) based upon a Henry's Law constant of 1.05X01-2 atm-cu m/mole(6). Using this Henry's Law constant and an estimation method(5), volatilization half-lives for a model river and model lake are 1 hr and 4 days, respectively(SRC). Volatilization half-lives of 1.3 to 19 days have been predicted for the Narraganset Bay near RI where volatilization is expected to be the major removal process(10). Aquatic hydrolysis is not an important fate process(SRC) due to the lack of hydrolyzable functional groups(5). According to a classification scheme(7), an estimated BCF of 138(SRC), from its log Kow of 3.69(8) and a regression-derived equation(9), suggests the potential for bioconcentration in aquatic organisms is moderate. Biodegradation from water may occur based on activated sludge studies, with theoretical BODs ranging from 21.8 to 43.7%(11,12).

ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), n-propylbenzene, which has a vapor pressure of 3.42 mm Hg at 25 °C(2), is expected to exist solely as a vapor in the ambient atmosphere. Vapor-phase n-propylbenzene is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC); the half-life for this reaction in air is estimated to be 2 days(SRC), calculated from its rate constant of 5.0X10-12 cu cm/molecule-sec at 25 °C(3). The detection of n-propylbenzene in rainwater samples(4) suggests that physical removal from the atmosphere by wet deposition is possible(SRC).

n-Propylbenzene has been qualitatively detected in various wastewaters from the following industries: petroleum refining, textile mills, auto and other laundries, plastics mfg, and publicly owned treatment works(1). Leachate from 4 hazardous waste landfills in Germany contained n-propylbenzene levels of 10-700 ug/l(3). An n-propylbenzene concn of 69 mg/cu m was detected in gas emissions from a landfill in Great Britain(4). An aqueous effluent from a US petroleum refinery had a n-propylbenzene concn of 13 ng/g(5). n-Propylbenzene is a component of leachate from a landfill in Germany, being detected up to a distance of 56 m(5). Maximum concns of n-propylbenzene in the off-gas at aerated grit chambers in two Ontario, Canada municipal wastewater treatment plants were 205 and 203 ug/l(6).

Based upon dynamometer tests, the avg n-propylbenzene emission rate from gasoline-powered engines is 1.2 mg/km(1). Emission rates for n-propylbenzene from motor vehicles was calculated to be 34 mg/l of fuel consumed based on measurements made inside and outside a Los Angeles roadway tunnel(2). It is also a component of exhaust emissions from four-stroke lawn mower engines: n-propylbenzene comprised 0.57% of total organic emissions from baseline gasoline and 0.55% of total organic emissions in reformulated gasoline(3). Four stroke outboard motors are also a source of n-propylbenzene into surface waters(4).

n-Propylbenzene has also been detected as a possible volatile (C3-benzene) from furniture coatings for wood-based materials(1) and as a volatile emission from building materials (concn): linoleum tile (2.3 ug-sq m/hr); black rubber molding (0.96 ug-sq m/hr); vinyl edge molding (0.34 ug-sq m/hr); large diameter telephone cable (0.65 ug-sq m/hr); small diameter telephone cable (0.79 ug-sq m/hr); polystyrene foam insulation (0.70 ug-sq m/hr); cove adhesive (110 ug-sq m/hr); latex caulk (2.7 ug-sq m/hr); carpet (0.49 ug-sq m/hr)(2).

A Koc of 725 was measured for n-propylbenzene using a surface sediment collected from the Tamar estuary(1). A similar Koc of 676 was measured in a humic acid column via HPLC(2). Adsorption percentages ranging from 0.16 to 5.58% were measured in soil column studies using three different soil types and a sludge sample(3). Using a structure estimation method based on molecular connectivity indices(4), the Koc for n-propylbenzene can be estimated to be 955(SRC). According to a classification scheme(5), these estimated and measured Koc values suggest that n-propylbenzene is expected to have low mobility in soil.

SOURCE DOMINATED: n-Propylbenzene was detected in tunnel air at 0.037 g/kg (traffic) and 0.052 (congested) from the Craeybeckx highway tunnel in Antwerp Belgium(1).

URBAN/SUBURBAN: An evaluated database of US air monitoring data for the years 1970-1987 contains the following data for n-propylbenzene (concn is reported as daily median conc): suburban sites-213 samples, 0.123 ppb; urban sites-520 samples, 0.167 ppb(1). Air samples collected in Tulsa, OK in Jul 1978 contained n-propylbenzene levels of 0-0.9 ppb(2); samples from Rio Blanco County, CO (Jul 1978) had levels of 0.5-1.6 ppb(2). Ambient air samples collected in Long Beach, Burbank, Azuza, Los Angeles and Inglewood, CA (date no reported) contained n-propylbenzene levels of 0.001-0.011 ppm(3). The avg concn in the ambient air of Sydney, Australia between Sep 1979 and June 1980 (140 samples) was 0.4 ppb(4). The n-propylbenzene concn in Los Angeles, CA air range from 1-3 ppb during Sep-Nov 1981 monitoring(5).

URBAN/SUBURBAN: The avg concns of n-propylbenzene in the air of Vienna, Austria during Oct 1986 to Feb 1987 monitoring were 0.6 ppb (background), 2.2 ppb (suburbs), and 4.8 ppb (streets)(1). An avg n-propylbenzene concn of 2 ppb was monitored in Los Angeles, CA air during the fall of 1966(2). Levels ranging from 0.2-61.1 ppb were detected in the ambient air of Houston, TX during 1973 and 1974 monitoring(3). Air samples from Atlanta, GA contained n-propylbenzene at a concn of <5 ppbC(4).

RURAL/REMOTE: An evaluated database of US air monitoring data for the years 1970-1987 contained the following data for n-propylbenzene (conc is reported as daily median conc): remote sites-2 samples, 0.056 ppb; rural sites-2 samples, 0.056 ppb(1). Samples from the Smokey Mountains (Sept 1978) had levels of 0-0.6 ppb(2).

INDOOR AIR: n-Propylbenzene was detected in 85% of the indoor air of 26 houses in Helsinki, Finland(1). The median concn in a normal house was 0.62 ug/cu m(1). In "sick houses", 10.5% contained n-propylbenzene at 5-10% greater than average; 2.6% houses contained 10-50% greater than average, and 2.6% houses contained 200-1000% greater than average concn of n-propylbenzene(1).

... IRRITATING TO MUCOUS MEMBRANES, EYES, NOSE, THROAT & SKIN. SYSTEMICALLY, IT CAUSES DEPRESSION OF CNS, HEADACHE, ANOREXIA, MUSCULAR WEAKNESS, INCOORDINATION, NAUSEA, VERTIGO, MENTAL CONFUSION, & UNCONSCIOUSNESS.

The action of the alkylbenzenes under conditions of acute exposure resembles those of the general anesthetics. /Alkylbenzenes/

Incineration of organic, petroleum or coal wastes, and combustion of fuels will release n-propylbenzene to the atmosphere(1). General uses of asphalt and naphtha and use as a solvent will release n-propylbenzene to the environment(1). n-Propylbenzene is emitted in the exhaust from gasoline and diesel engines(2). Outboard motors and motor boats have been identified as sources of n-propylbenzene emissions to water(3,4). n-Propylbenzene can be released to the environment in leachates and vapor emissions from landfills(5,6).

n-Propylbenzene's production and use as a solvent and use in textile dyeing(1) may result in its release to the environment through various waste streams(SRC).

(CA) CALIFORNIA 260 ug/l

(FL) FLORIDA 280 ug/l

(NH) NEW HAMPSHIRE 260 ug/L