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Disclaimer: These guidelines were developed under contract using generally accepted secondary sources. The protocol used by the contractor for surveying these data sources was developed by the National Institute for Occupational Safety and Health (NIOSH), the Occupational Safety and Health Administration (OSHA), and the Department of Energy (DOE). The information contained in these guidelines is intended for reference purposes only. None of the agencies have conducted a comprehensive check of the information and data contained in these sources. It provides a summary of information about chemicals that workers may be exposed to in their workplaces. The secondary sources used for supplements 111 and 1V were published before 1992 and 1993, respectively, and for the remainder of the guidelines the secondary sources used were published before September 1996. This information may be superseded by new developments in the field of industrial hygiene. Therefore readers are advised to determine whether new information is available.
OCCUPATIONAL SAFETY AND HEALTH GUIDELINE FOR NONANE
INTRODUCTION
This guideline summarizes pertinent information about nonane for workers and
employers as well as for physicians, industrial hygienists, and other
occupational safety and health professionals who may need such information to
conduct effective occupational safety and health programs. Recommendations
may be superseded by new developments in these fields; readers are therefore
advised to regard these recommendations as general guidelines and to
determine whether new information is available.
SUBSTANCE IDENTIFICATION
* Formula
C(9)H(20)
* Structure
(For Structure, see paper copy)
* Synonyms
n-Nonane; Shellsol 140; 2,2,5-trimethylhexane
* Identifiers
1. CAS No.: 111-84-2
2. RTECS No.: RA6115000
3. DOT UN: 1920 27
4. DOT label: Flammable Liquid
* Appearance and odor
Nonane is a colorless liquid with a mild gasoline-like odor. An
odor threshold of 47 parts per million (ppm) parts of air for nonane has been
reported .
CHEMICAL AND PHYSICAL PROPERTIES
* Physical data
1. Molecular weight: 128.26
2. Boiling point (at 760 mm Hg): 150.8 degrees C (303.4 degrees F)
3. Specific gravity (water = 1): 0.72 at 20 degrees C (68 degrees F)
4. Vapor density: 4.4
5. Freezing point: -53.5 degrees C (-64.3 degrees F)
6. Vapor pressure at 38 degrees C (100.4 degrees F): 10 mm Hg
7. Solubility: Insoluble in water; soluble in alcohol, ether, acetone,
benzene, and chloroform.
8. Evaporation rate: Data not available.
* Reactivity
1. Conditions contributing to instability: Heat, sparks, and open flames.
2. Incompatibilities: Nonane is incompatible with strong oxidizers.
3. Hazardous decomposition products: Toxic gases and vapors (such as
oxides of carbon, lower molecular weight hydrocarbon alkanes and alkenes) may
be released in a fire involving nonane.
4. Special precautions: None reported.
* Flammability
The National Fire Protection Association has assigned a flammability
rating of 3 (serious fire hazard) to nonane.
1. Flash point: 31 degrees C (88 degrees F) (closed cup)
2. Autoignition temperature: 205 degrees C (401 degrees F)
3. Flammable limits in air (percent by volume): Lower, 0.8; upper, 2.9
4. Extinguishant: For small fires use dry chemical, carbon dioxide, water
spray, or regular foam. Use water spray, fog, or regular foam to fight large
fires involving nonane.
Fires involving nonane should be fought upwind from the maximum
distance possible. Keep unnecessary people away; isolate the hazard area and
deny entry. Isolate the area for 1/2 mile in all directions if a tank, rail
car, or tank truck is involved in the fire. For a massive fire in a cargo
area, use unmanned hose holders or monitor nozzles; if this is impossible,
withdraw from the area and let the fire burn. Emergency personnel should
stay out of low areas. Vapors may travel to a source of ignition and flash
back. Vapors are an explosion and poison hazard indoors, outdoors, or in
sewers. Containers of nonane may explode in the heat of the fire and should
be moved from the fire area if it is possible to do so safely. If this is
not possible, cool fire-exposed containers from the sides with water until
well after the fire is out. Stay away from the ends of containers.
Personnel should withdraw immediately if a rising sound from a venting safety
device is heard or if there is discoloration of a container due to fire.
Firefighters should wear a full set of protective clothing and self-contained
breathing apparatus when fighting fires involving nonane.
EXPOSURE LIMITS
* OSHA PEL
The Occupational Safety and Health Administration (OSHA) does not
currently regulate nonane.
* NIOSH REL
The National Institute for Occupational Safety and Health (NIOSH)
has established a recommended exposure limit (REL) for nonane of 200 ppm
(1050 mg/m(3)) as a TWA for up to a 10-hour workday and a 40-hour workweek
[NIOSH 1992].
* ACGIH TLV
The American Conference of Governmental Industrial Hygienists
(ACGIH) has assigned nonane a threshold limit value (TLV) of 200 ppm (1050
mg/m(3)) as a TWA for a normal 8-hour workday and a 40-hour workweek [ACGIH
1994, p. 28].
* Rationale for Limits
The NIOSH limit is based on the risk of narcosis [NIOSH 1992].
The ACGIH limit is based on analogy to the narcotic effects of
octane [ACGIH 1991, p. 1139].
HEALTH HAZARD INFORMATION
* Routes of Exposure
Exposure to nonane can occur through inhalation, ingestion, and eye
or skin contact.
* Summary of toxicology
1. Effects on Animals: Nonane causes irritation and narcosis in
experimental animals. The 4-hr LC(50) in rats is 3,200 ppm [NIOSH 1991]. No
adverse effects were observed in rats exposed to 590 ppm of ()nonane for 6
hours/day, 5 days/week for 65 days [ACGIH 1991]. Exposure to 1,500 ppm
resulted in mild tremors, slight loss of coordination, and slight irritation
of the eyes [Clayton and Clayton 1981]. Nonane was not mutagenic in the Ames
mutagenicity assay [ACGIH 1991].
2. Effects on Humans: No data are available on the effects of nonane in
humans. The primary toxicological effects associated with inhalation of high
concentrations of aliphatic hydrocarbons such as nonane is depression of the
central nervous system [ACGIH 1991]. By analogy with heptane and octane,
nonane is expected to defat the skin, cause chemical dermatitis or, with
prolonged contact, cause necrolysis [ACGIH 1991].
* Signs and symptoms of exposure
1. Acute exposure: No signs or symptoms of acute exposure to nonane have
been reported in humans.
2. Chronic exposure: No signs or symptoms of chronic exposure to nonane
have been reported in humans.
EMERGENCY MEDICAL PROCEDURES
* Emergency medical procedures: [NIOSH to supply]
5. Rescue: Remove an incapacitated worker from further exposure and
implement appropriate emergency procedures (e.g., those listed on the
Material Safety Data Sheet required by OSHA's Hazard Communication Standard
[29 CFR 1910.1200]). All workers should be familiar with emergency
procedures, the location and proper use of emergency equipment, and methods
of protecting themselves during rescue operations.
EXPOSURE SOURCES AND CONTROL METHODS
The following operations may involve nonane and lead to worker exposures to
this substance:
* The manufacture and transportation of nonane * Use in the synthesis
of biodegradable detergents * Use as an ingredient of gasoline and
Stoddard solvent * Use as a distillation chaser * Use in organic
synthesis and as a solvent
Methods that are effective in controlling worker exposures to nonane,
depending on the feasibility of implementation, are as follows:
* Process enclosure * Local exhaust ventilation * General dilution
ventilation * Personal protective equipment
Workers responding to a release or potential release of a hazardous
substance must be protected as required by paragraph (q) of OSHA's Hazardous
Waste Operations and Emergency Response Standard [29 CFR 1910.120].
Good sources of information about control methods are as follows:
1. ACGIH [1992]. Industrial ventilation--a manual of recommended
practice. 21st() ed. Cincinnati, OH: American Conference of Governmental
Industrial Hygienists.
2. Burton DJ [1986]. Industrial ventilation--a self study companion.
Cincinnati, OH: American Conference of Governmental Industrial Hygienists.
3. Alden JL, Kane JM [1982]. Design of industrial ventilation systems.
New York, NY: Industrial Press, Inc.
4. Wadden RA, Scheff PA [1987]. Engineering design for control of
workplace hazards. New York, NY: McGraw-Hill.
5. Plog BA [1988]. Fundamentals of industrial hygiene. Chicago, IL:
National Safety Council.
MEDICAL SURVEILLANCE
OSHA is currently developing requirements for medical surveillance. When
these requirements are promulgated, readers should refer to them for
additional information and to determine whether employers whose employees are
exposed to nonane are required to implement medical surveillance procedures.
Medical Screening:
Workers who may be exposed to chemical hazards should be monitored in a
systematic program of medical surveillance that is intended to prevent
occupational injury and disease. The program should include education of
employers and workers about work-related hazards, early detection of adverse
health effects, and referral of workers for diagnosis and treatment. The
occurrence of disease or other work-related adverse health effects should
prompt immediate evaluation of primary preventive measures (e.g., industrial
hygiene monitoring, engineering controls, and personal protective equipment).
A medical surveillance program is intended to supplement, not replace, such
measures. To detect and control work-related health effects, medical
evaluations should be performed (1) before job placement, (2) periodically
during the term of employment, and (3) at the time of job transfer or
termination.
* Preplacement medical evaluation
Before a worker is placed in a job with a potential for exposure to
nonane, a licensed health care professional should evaluate and document the
worker's baseline health status with thorough medical, environmental, and
occupational histories, a physical examination, and physiologic and
laboratory tests appropriate for the anticipated occupational risks. These
should concentrate on the function and integrity of the skin and central
nervous system.
A preplacement medical evaluation is recommended to assess medical
conditions that may be aggravated or may result in increased risk when a
worker is exposed to nonane at or below the prescribed exposure limit. The
health care professional should consider the probable frequency, intensity,
and duration of exposure as well as the nature and degree of any applicable
medical condition. Such conditions (which should not be regarded as absolute
contraindications to job placement) include a history and other findings
consistent with diseases of the skin or central nervous system.
* Periodic medical evaluations
Occupational health interviews and physical examinations should be
performed at regular intervals during the employment period, as mandated by
any applicable Federal, State, or local standard. Where no standard exists
and the hazard is minimal, evaluations should be conducted every 3 to 5 years
or as frequently as recommended by an experienced occupational health
physician. Additional examinations may be necessary if a worker develops
symptoms attributable to nonane exposure. The interviews, examinations, and
medical screening tests should focus on identifying the adverse effects of
nonane on the skin or central nervous system. Current health status should
be compared with the baseline health status of the individual worker or with
expected values for a suitable reference population.
* Termination medical evaluations
The medical, environmental, and occupational history interviews, the
physical examination, and selected physiologic or laboratory tests that were
conducted at the time of placement should be repeated at the time of job
transfer or termination to determine the worker's medical status at the end
of his or her employment. Any changes in the worker's health status should
be compared with those expected for a suitable reference
population.
* Biological monitoring
Biological monitoring involves sampling and analyzing body tissues
or fluids to provide an index of exposure to a toxic substance or metabolite.
No biological monitoring test acceptable for routine use has yet been
developed for nonane.
WORKPLACE MONITORING AND MEASUREMENT
Determination of a worker's exposure to airborne nonane is made using a
charcoal tube (100/50 mg sections, 20/40 mesh). Samples are collected at a
maximum flow rate of 0.2 liter/minute until a maximum collection volume of 10
liters is reached. The sample is then treated with 99:1 carbon
disulfide:dimethylformamide. Analysis is conducted by gas chromatography
using a flame ionization detector. This method is described in the OSHA
Computerized Information System [OSHA 1994].
PERSONAL HYGIENE PROCEDURES
If nonane contacts the skin, workers should flush the affected areas
immediately with plenty of water, followed by washing with soap and water.
Clothing contaminated with nonane should be removed immediately, and
provisions should be made for the safe removal of the chemical from the
clothing. Persons laundering the clothes should be informed of the hazardous
properties of nonane, particularly its potential to be irritating to the eyes
and skin.
A worker who handles nonane should thoroughly wash hands, forearms, and face
with soap and water before eating, using tobacco products, using toilet
facilities, applying cosmetics, or taking medication.
Workers should not eat, drink, use tobacco products, apply cosmetics, or
take medication in areas where nonane or a solution containing nonane is
handled, processed, or stored.
STORAGE
Nonane should be stored in a cool, dry, well-ventilated area in tightly
sealed containers that are labeled in accordance with OSHA's Hazard
Communication Standard [29 CFR 1910.1200]. Containers of nonane should be
protected from physical damage, heat, sparks, and open flames, and should be
stored separately from strong oxidizing agents. Drums should be equipped
with self-closing valves, pressure vacuum bungs, and flame arresters. Only
non-sparking tools should be used to handle nonane. To prevent static
sparks, containers should be grounded and bonded for transfers. Because
containers that formerly contained nonane may still hold product residues,
they should be handled appropriately.
SPILLS AND LEAKS
In the event of a spill or leak involving nonane, persons not wearing
protective equipment and clothing should be restricted from contaminated
areas until cleanup has been completed. The following steps should be
undertaken following a spill or leak:
1. Do not touch the spilled material; stop the leak if it is possible to
do so without risk.
2. Notify safety personnel.
3. Remove all sources of heat and ignition.
4. Provide maximum explosion-proof ventilation.
5. Use non-sparking tools.
6. Water spray may be used to reduce vapors, but the spray may not prevent
ignition in closed spaces.
7. For small liquid spills, take up with sand or other noncombustible
absorbent material and use non-sparking tools to place material under a hood
or in an area with good ventilation to allow material to evaporate.
8. For large liquid spills, clean up the material if it is safe to do so
or build dikes far ahead of the spill to contain the nonane for later
reclamation or disposal. Keep material out of sewers or other confined places
where it could vaporize and form an explosion hazard.
SPECIAL REQUIREMENTS
U.S. Environmental Protection Agency (EPA) requirements for emergency
planning, reportable quantities of hazardous releases, community
right-to-know, and hazardous waste management may change over time. Users
are therefore advised to determine periodically whether new information is
available.
* Emergency planning requirements
Nonane is not subject to EPA emergency planning requirements under
the Superfund Amendments and Reauthorization Act (SARA) (Title III) in 42 USC
11022.
* Reportable quantity requirements for hazardous releases
Employers are not required by the emergency release notification
provisions in 40 CFR Part 355.40 to notify the National Response Center of an
accidental release of nonane; there is no reportable quantity for this
substance.
* Community right-to-know requirements
Employers are not required by EPA in 40 CFR Part 372.30 to submit a
Toxic Chemical Release Inventory form (Form R) to EPA reporting the amount of
nonane emitted or released from their facility annually.
* Hazardous waste management requirements
EPA considers a waste to be hazardous if it exhibits any of the
following characteristics: ignitability, corrosivity, reactivity, or
toxicity as defined in 40 CFR 261.21-261.24. Under the Resource Conservation
and Recovery Act (RCRA) [40 USC 6901 et seq.], EPA has specifically listed
many chemical wastes as hazardous. Although nonane is not specifically
listed as a hazardous waste under RCRA, EPA requires employers to treat waste
as hazardous if it exhibits any of the characteristics discussed
above.
Providing detailed information about the removal and disposal of
specific chemicals is beyond the scope of this guideline. The U.S.
Department of Transportation, EPA, and State and local regulations should be
followed to ensure that removal, transport, and disposal of this substance
are conducted in accordance with existing regulations. To be certain that
chemical waste disposal meets EPA regulatory requirements, employers should
address any questions to the RCRA hotline at (703) 412-9810 (in the
Washington, D.C. area) or toll-free at (800) 424-9346 (outside Washington,
D.C.). In addition, relevant State and local authorities should be contacted
for information on any requirements they may have for the waste removal and
disposal of this substance.
RESPIRATORY PROTECTION
* Conditions for respirator use
Good industrial hygiene practice requires that engineering controls
be used where feasible to reduce workplace concentrations of hazardous
materials to the prescribed exposure limit. However, some situations may
require the use of respirators to control exposure. Respirators must be worn
if the ambient concentration of nonane exceeds prescribed exposure limits.
Respirators may be used (1) before engineering controls have been installed,
(2) during work operations such as maintenance or repair activities that
involve unknown exposures, (3) during operations that require entry into
tanks or closed vessels, and (4) during emergencies. Workers should only use
respirators that have been approved by NIOSH and the Mine Safety and Health
Administration (MSHA).
* Respiratory protection program
Employers should institute a complete respiratory protection program
that, at a minimum, complies with the requirements of OSHA's Respiratory
Protection Standard [29 CFR 1910.134]. Such a program must include
respirator selection, an evaluation of the worker's ability to perform the
work while wearing a respirator, the regular training of personnel,
respirator fit testing, periodic workplace monitoring, and regular respirator
maintenance, inspection, and cleaning. The implementation of an adequate
respiratory protection program (including selection of the correct
respirator) requires that a knowledgeable person be in charge of the program
and that the program be evaluated regularly. For additional information on
the selection and use of respirators and on the medical screening of
respirator users, consult the latest edition of the NIOSH Respirator Decision
Logic [NIOSH 1987b] and the NIOSH Guide to Industrial Respiratory Protection
[NIOSH 1987a].
PERSONAL PROTECTIVE EQUIPMENT
Workers should use appropriate personal protective clothing and equipment
that must be carefully selected, used, and maintained to be effective in
preventing skin contact with nonane. The selection of the appropriate
personal protective equipment (PPE) (e.g., gloves, sleeves, encapsulating
suits) should be based on the extent of the worker's potential exposure to
nonane. There are no published reports on the resistance of various
materials to permeation by nonane.
To evaluate the use of various PPE materials with nonane, users should
consult the best available performance data and manufacturers'
recommendations. Significant differences have been demonstrated in the
chemical resistance of generically similar PPE materials (e.g., butyl)
produced by different manufacturers. In addition, the chemical resistance of
a mixture may be significantly different from that of any of its neat
components.
Any chemical-resistant clothing that is used should be periodically
evaluated to determine its effectiveness in preventing dermal contact. Safety
showers and eye wash stations should be located close to operations that
involve nonane.
Splash-proof chemical safety goggles or face shields (20 to 30 cm long,
minimum) should be worn during any operation in which a solvent, caustic, or
other toxic substance may be splashed into the eyes.
In addition to the possible need for wearing protective outer apparel (e.g.,
aprons, encapsulating suits), workers should wear work uniforms, coveralls,
or similar full-body coverings that are laundered each day. Employers should
provide lockers or other closed areas to store work and street clothing
separately. Employers should collect work clothing at the end of each work
shift and provide for its laundering. Laundry personnel should be informed
about the potential hazards of handling contaminated clothing and instructed
about measures to minimize their health risk.
Protective clothing should be kept free of oil and grease and should be
inspected and maintained regularly to preserve its effectiveness.
Protective clothing may interfere with the body's heat dissipation,
especially during hot weather or during work in hot or poorly ventilated work
environments.
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physical agents and biological exposure indices. Cincinnati, OH: American
Conference of Governmental Industrial Hygienists.
ACGIH [1991]. Documentation of the threshold limit values and biological
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