Heads up: There are no suggested sections in this chapter.
Heads up: There are no amended sections in this chapter.
Authority: 29 U.S.C. 653, 655, 657; Secretary of Labor's Order No. 12-71 (36 FR 8754), 8-76 (41 FR 25059), 9-83 (48 FR 35736), 1-90 (55 FR 9033), 6-96 (62 FR 111), 3-2000 (65 FR 50017), 5-2002 (67 FR 50017), 5-2007 (72 FR 31159), 4-2010 (75 FR 55355), or 1-2012 (77 FR 3912), as applicable; and 29 CFR part 1911.

[55 FR 46054, Nov. 1, 1990; 58 FR 35308. June 30, 1993; 61 FR 9227, March 7, 1996; 61 FR 31427, June 20, 1996; 63 FR 1152, Jan. 8, 1998; 64 FR 13909, March 23, 1999; 71 FR 16672, April, 3, 2006; 72 FR 71069, Dec. 14, 2007; 73 FR 75584, Dec. 12, 2008; 74 FR 46356, Sept. 9, 2009; 78 FR 35566, June 13, 2013]
A solid substance used in an abrasive blasting operation.
A complete enclosure which rotates on an axis, or which has an internal moving tread to tumble the parts, in order to expose various surfaces of the parts to the action of an automatic blast spray.
A complete enclosure in which blasting operations are performed and where the operator works inside of the room to operate the blasting nozzle and direct the flow of the abrasive material.
An air purifying respirator, commonly referred to as a dust or a fume respirator, which removes most of the dust or fume from the air passing through the device.
An enclosure where the operator stands outside and operates the blasting nozzle through an opening or openings in the enclosure.
Air of such purity that it will not cause harm or discomfort to an individual if it is inhaled for extended periods of time.
A device or combination of devices for separating dust from the air handled by an exhaust ventilation system.
A system for removing contaminated air from a space, comprising two or more of the following elements (a) enclosure or hood, (b) duct work, (c) dust collecting equipment, (d) exhauster, and (e) discharge stack.
Airborne dust in sizes capable of passing through the upper respiratory system to reach the lower lung passages.
An enclosure where the pieces to be cleaned are positioned on a rotating table and are passed automatically through a series of blast sprays.
The forcible application of an abrasive to a surface by pneumatic pressure, hydraulic pressure, or centrifugal force.
A respirator contstructed so that it covers the wearer's head, neck, and shoulders to protect him from rebounding abrasive.
Abrasives and the surface coatings on the materials blasted are shattered and pulverized during blasting operations and the dust formed will contain particles of respirable size. The composition and toxicity of the dust from these sources shall be considered in making an evaluation of the potential health hazards.
Organic abrasives which are combustible shall be used only in automatic systems. Where flammable or explosive dust mixtures may be present, the construction of the equipment, including the exhaust system and all electric wiring, shall conform to the requirements of American National Standard Installation of Blower and Exhaust Systems for Dust, Stock, and Vapor Removal or Conveying, Z33.1-1961 (NFPA 91-1961) which is incorporated by reference as specified in § 1910.6, and subpart S of this part. The blast nozzle shall be bonded and grounded to prevent the build up of static charges. Where flammable or explosive dust mixtures may be present, the abrasive blasting enclosure, the ducts, and the dust collector shall be constructed with loose panels or explosion venting areas, located on sides away from any occupied area, to provide for pressure relief in case of explosion, following the principles set forth in the National Fire Protection Association Explosion Venting Guide, NFPA 68-1954, which is incorporated by reference as specified in § 1910.6.
The concentration of respirable dust or fume in the breathing zone of the abrasive-blasting operator or any other worker shall be kept below the levels specified in 1910.1000.
Blast-cleaning enclosures shall be exhaust ventilated in such a way that a continuous inward flow of air will be maintained at all openings in the enclosure during the blasting operation.
All air inlets and access openings shall be baffled or so arranged that by the combination of inward air flow and baffling the escape of abrasive or dust particles into an adjacent work area will be minimized and visible spurts of dust will not be observed.
The rate of exhaust shall be sufficient to provide prompt clearance of the dust-laden air within the enclosure after the cessation of blasting.
Before the enclosure is opened, the blast shall be turned off and the exhaust system shall be run for a sufficient period of time to remove the dusty air within the enclosure.
Safety glass protected by screening shall be used in observation windows, where hard deep-cutting abrasives are used.
Slit abrasive-resistant baffles shall be installed in multiple sets at all small access openings where dust might escape, and shall be inspected regularly and replaced when needed.
Doors shall be flanged and tight when closed.
Doors on blast-cleaning rooms shall be operable from both inside and outside, except that where there is a small operator access door, the large work access door may be closed or opened from the outside only.
The construction, installation, inspection, and maintenance of exhaust systems shall conform to the principles and requirements set forth in American National Standard Fundamentals Governing the Design and Operation of Local Exhaust Systems, Z9.2-1960, and ANSI Z33.1-1961, which are incorporated by reference as specified in § 1910.6.
When dust leaks are noted, repairs shall be made as soon as possible.
The static pressure drop at the exhaust ducts leading from the equipment shall be checked when the installation is completed and periodically thereafter to assure continued satisfactory operation. Whenever an appreciable change in the pressure drop indicates a partial blockage, the system shall be cleaned and returned to normal operating condition.
The air exhausted from blast-cleaning equipment shall be discharged through dust collecting equipment. Dust collectors shall be set up so that the accumulated dust can be emptied and removed without contaminating other working areas.
In installations where the abrasive is recirculated, the exhaust ventilation system for the blasting enclosure shall not be relied upon for the removal of fines from the spent abrasive instead of an abrasive separator. An abrasive separator shall be provided for the purpose.
Employers must use only respirators approved by the National Institute for Occupational Safety and Health (NIOSH) under 42 CFR part 84 to protect employees from dust produced during abrasive-blasting operations.
Properly fitted particulate filter respirators, commonly referred to as dust-filter respirators, may be used for short, intermittent, or occasional dust exposures such as cleanup, dumping of dust collectors, or unloading shipments of sand at a receiving point, when it is not feasible to control the dust by enclosure, exhaust ventilation, or other means. The respirators used must be approved by NIOSH under 42 CFR part 84 for protection against the specific type of dust encountered.
Dust-filter respirators may be used to protect the operator of outside abrasive-blasting operations where nonsilica abrasives are used on materials having low toxicities.
Dust-filter respirators shall not be used for continuous protection where silica sand is used as the blasting abrasive, or toxic materials are blasted.
For employees who use respirators required by this section, the employer must implement a respiratory protection program in accordance with 29 CFR 1910.134.
Operators shall be equipped with heavy canvas or leather gloves and aprons or equivalent protection to protect them from the impact of abrasives. Safety shoes shall be worn to protect against foot injury where heavy pieces of work are handled.
Protective footwear must comply with the requirements specified by 29 CFR 1910.136(b)(1).
Equipment for protection of the eyes and face shall be supplied to the operator when the respirator design does not provide such protection and to any other personnel working in the vicinity of abrasive blasting operations. This equipment shall conform to the requirements of 1910.133.
Abrasive-blasting respirators shall be worn by all abrasive-blasting operators:
When working inside of blast-cleaning rooms, or
When using silica sand in manual blasting operations where the nozzle and blast are not physically separated from the operator in an exhaust ventilated enclosure, or
Where concentrations of toxic dust dispersed by the abrasive blasting may exceed the limits set in 1910.1000 and the nozzle and blast are not physically separated from the operator in an exhaust-ventilated enclosure.
Air for abrasive-blasting respirators shall be free of harmful quantities of dusts, mists, or noxious gases, and must meet the requirements for supplied-air quality and use specified in 29 CFR 1910.134(i).
Dust shall not be permitted to accumulate on the floor or on ledges outside of an abrasive-blasting enclosure, and dust spills shall be cleaned up promptly. Aisles and walkways shall be kept clear of steel shot or similar abrasive which may create a slipping hazard.
This paragraph (a) applies to all operations where an abrasive is forcibly applied to a surface by pneumatic or hydraulic pressure, or by centrifugal force. It does not apply to steam blasting, or steam cleaning, or hydraulic cleaning methods where work is done without the aid of abrasives.
Organic-bonded wheels, the thickness of which is not more than one forty-eighth of their diameter for those up to, and including, 20 inches in diameter, and not more than one-sixtieth of their diameter for those larger than 20 inches in diameter, used for a multitude of operations variously known as cutting, cutting off, grooving, slotting, coping, and jointing, and the like. The wheels may be "solid" consisting of organic-bonded abrasive material throughout, "steel centered" consisting of a steel disc with a rim of organic-bonded material molded around the periphery, or of the "inserted tooth" type consisting of a steel disc with organic-bonded abrasive teeth or inserts mechanically secured around the periphery.
The part of an exhaust system piping that is connected directly to the hood or enclosure.
A movable fixture, upon which the part to be ground or polished is placed.
A pipe into which one or more branch pipes enter and which connects such branch pipes to the remainder of the exhaust system.
All power-driven rotatable discs faced with abrasive materials, artificial or natural, and used for grinding or polishing on the side of the assembled disc.
The loss in static pressure caused by air flowing into a duct or hood. It is usually expressed in inches of water gauge.
A system consisting of branch pipes connected to hoods or enclosures, one or more header pipes, an exhaust fan, means for separating solid contaminants from the air flowing in the system, and a discharge stack to outside.
All power-driven rotatable grinding or abrasive wheels, except disc wheels as defined in this standard, consisting of abrasive particles held together by artificial or natural bonds and used for peripheral grinding.
The partial or complete enclosure around the wheel or disc through which air enters an exhaust system during operation.
A grinding machine carrying two power-driven, rotatable, coaxial, horizontal spindles upon the inside ends of which are mounted abrasive disc wheels used for grinding two surfaces simultaneously.
A grinding machine carrying an abrasive disc wheel upon one or both ends of a power-driven, rotatable single horizontal spindle.
All power-driven rotatable wheels composed all or in part of textile fabrics, wood, felt, leather, paper, and may be coated with abrasives on the periphery of the wheel for purposes of polishing, buffing, and light grinding.
Any power-driven rotatable grinding, polishing, or buffing wheel mounted in such manner that it may be manually manipulated.
All power-driven rotatable wheels made from wire or bristles, and used for scratch cleaning and brushing purposes.
Any power-driven rotatable grinding, polishing, or buffing wheel mounted in such a manner that the wheel with its supporting framework can be manipulated over stationary objects.
The kinetic pressure in the direction of flow necessary to cause a fluid at rest to flow at a given velocity. It is usually expressed in inches of water gauge.
A grinding machine having a vertical, rotatable power-driven spindle carrying a horizontal abrasive disc wheel.
All power-driven, flexible, coated bands used for grinding, polishing, or buffing purposes.
Wherever dry grinding, dry polishing or buffing is performed, and employee exposure, without regard to the use of respirators, exceeds the permissible exposure limits prescribed in 1910.1000 or other sections of this part, a local exhaust ventilation system shall be provided and used to maintain employee exposures within the prescribed limits.
Hoods connected to exhaust systems shall be used, and such hoods shall be designed, located, and placed so that the dust or dirt particles shall fall or be projected into the hoods in the direction of the air flow. No wheels, discs, straps, or belts shall be operated in such manner and in such direction as to cause the dust and dirt particles to be thrown into the operator's breathing zone.
Scratch-brush wheels and all buffing and polishing wheels mounted on floor stands, pedestals, benches, or special-purpose machines shall have not less than the minimum exhaust volume shown in Table G-5.

TABLE G-5 - BUFFING AND POLISHING WHEELS
Wheel diameter
(inches)
Wheel width
(inches)
Minimum exhaust
volume (feet (3) /min.)
To 9 2 300
Over 9 to 16 3 500
Over 16 to 19 4 610
Over 19 to 24 5 740
Over 24 to 30 6 1,040
Over 30 to 36 6 1,200
Grinding wheels or discs for horizontal single-spindle disc grinders shall be hooded to collect the dust or dirt generated by the grinding operation and the hoods shall be connected to branch pipes having exhaust volumes as shown in Table G-6.

TABLE G-6 - HORIZONTAL SINGLE-SPINDLE DISC GRINDER
Disc diameter (inches) Exhaust volume
(ft. (3)/min.)
Up to 12 220
Over 12 to 19 390
Over 19 to 30 610
Over 30 to 36 880
Where the work is outside the hood, air volumes must be increased as shown in American Standard Fundamentals Governing the Design and Operation of Local Exhaust Systems, Z9.2-1960 (section 4, exhaust hoods).
Grinding wheels or discs for horizontal double-spindle disc grinders shall have a hood enclosing the grinding chamber and the hood shall be connected to one or more branch pipes having exhaust volumes as shown in Table G-7.

TABLE G-7 - HORIZONTAL DOUBLE-SPINDLE DISC GRINDER
Disc diameter (inches) Exhaust volume
(ft. (3) /min.)
Up to 19    610
Over 19 to 25    880
Over 25 to 30 1,200
Over 30 to 53 1,770
Over 53 to 72 6,280
Grinding wheels or discs for vertical single-spindle disc grinders shall be encircled with hoods to remove the dust generated in the operation. The hoods shall be connected to one or more branch pipes having exhaust volumes as shown in Table G-8.

TABLE G-8 - VERTICAL SPINDLE DISC GRINDER
Disc
diameter
(inches)
One-half or more
of disc covered
Disc not covered
Number
(1)
Exhaust
foot (3) /min
Number
(1)
Exhaust
foot (3)/min
Up to 20 1 500 2 780
Over 20 to 30 2 780 2 1,480
Over 30 to 53 2 1,770 4 3,530
Over 53 to 72 2 3,140 5 6,010
Footnote(1) Number of exhaust outlets around periphery of hood, or equal distribution provided by other means.
Grinding and polishing belts shall be provided with hoods to remove dust and dirt generated in the operations and the hoods shall be connected to branch pipes having exhaust volumes as shown in Table G-9.

TABLE G-9 - GRINDING AND POLISHING BELTS
Belts width (inches) Exhaust
volume
(ft. (3) /min.)
Up to 3 220
Over 3 to 5 300
Over 5 to 7 390
Over 7 to 9 500
Over 9 to 11 610
Over 11 to 13 740
Cradles and swing-frame grinders. Where cradles are used for handling the parts to be ground, polished, or buffed, requiring large partial enclosures to house the complete operation, a minimum average air velocity of 150 feet per minute shall be maintained over the entire opening of the enclosure. Swing-frame grinders shall also be exhausted in the same manner as provided for cradles. (See fig. G-3)

FIGURE G-3 A METHOD OF APPLYING AN EXHAUST ENCLOSURE TO SWING-FRAME GRINDERS
Note: Baffle to reduce front opening as much as possible.
Grinding wheels on floor stands, pedestals, benches, and special-purpose grinding machines and abrasive cutting-off wheels shall have not less than the minimum exhaust volumes shown in Table G-4 with a recommended minimum duct velocity of 4,500 feet per minute in the branch and 3,500 feet per minute in the main. The entry losses from all hoods except the vertical-spindle disc grinder hood, shall equal 0.65 velocity pressure for a straight takeoff and 0.45 velocity pressure for a tapered takeoff. The entry loss for the vertical-spindle disc grinder hood is shown in figure G-1 (following 1910.94(b)).

For any wheel wider than wheel diameters shown in Table G-4, increase the exhaust volume by the ratio of the new width to the width shown.

Example:
   If wheel width = 4 1/2 inches, then
          4.5 divided by 4 X 610 = 686 (rounded to 690).

FIGURE G-1 VERTICAL SPINDLE DISC GRINDER EXHAUST HOOD AND BRANCH PIPE CONNECTIONS

Figure G-1 -- Vertical Spindle Disc Grinder Exhaust Hood
      and Branch Pipe Connections
Dia. D inches (cm) Exhaust E Volume
Exhausted
at 4,500
ft/min
ft (3)/min
Note


Min. Max. No
Pipes
Dia.
20 1 41/4 500 When
one-half
or more
of the
disc can
be hooded,
use
exhaust
ducts as
shown at
the left.
Over 20 30 2 4 780
Over 30 72 2 6 1,770
Over 53 72 2 8 3,140
20 2 4 780 When no
hood can
be used
over
disc,
use
exhaust
ducts
as
shown
at left.
Over 20 20 2 4 780
Over 30 30 2 51/2 1,480
Over 53 53
72
4
5
6
7
3,530
6,010
Entry loss = 1.0 slot velocity pressure + 0.5 branch velocity pressure. Minimum slot velocity = 2,000 ft/min -- 1/2-inch (1.27 cm) slot width.


TABLE G-4 - GRINDING AND ABRASIVE CUTTING-OFF WHEELS
Wheel diameter
(inches)
Wheel width (inches) Minimum exhaust
volume (feet (3)/min.)
To 9 1 1/2 220
Over 9 to 16 2 390
Over 16 to 19 3 500
Over 19 to 24 4 610
Over 24 to 30 5 880
Over 30 to 36 6 1,200
Exhaust systems for grinding, polishing, and buffing operations should be designed in accordance with American Standard Fundamentals Governing the Design and Operation of Local Exhaust Systems, Z9.2-1960.
All exhaust systems shall be provided with suitable dust collectors.
Exhaust systems for grinding, polishing, and buffing operations shall be tested in the manner described in American Standard Fundamentals Governing the Design and Operation of Local Exhaust Systems, Z9.2-1960.
It is the dual function of grinding and abrasive cutting-off wheel hoods to protect the operator from the hazards of bursting wheels, as well as to provide a means for the removal of dust and dirt generated. All hoods shall be not less in structural strength than specified in Tables O-1 and O-9 of § 1910.215.
Due to the variety of work and types of grinding machines employed, it is necessary to develop hoods adaptable to the particular machine in question, and such hoods shall be located as close as possible to the operation.
Swing-frame grinders shall be provided with exhaust booths as indicated in figure G-3.
Portable grinding operations, whenever the nature of the work permits, shall be conducted within a partial enclosure. The opening in the enclosure shall be no larger than is actually required in the operation and an average face air velocity of not less than 200 feet per minute shall be maintained.
Vertical-spindle disc grinders shall be encircled with a hood so constructed that the heavy dust is drawn off a surface of the disc and the lighter dust exhausted through a continuous slot at the top of the hood as shown in figure G-1.
Hoods for polishing and buffing and scratch-brush wheels shall be constructed to conform as closely to figure G-4 as the nature of the work will permit.

FIGURE G-4 STANDARD BUFFING AND POLISHING HOOD

Standard Buffing and Polishing Hood
Wheel dimension, inches Exhaust
outlet,
inches
E

Volume
of air
at
4,500
ft/min
Diameter Width, Max
Min = d Max = D
Over 9 9
16
2
3
31/2
4
300
500
Over 16 19 4 5 610
Over 19 24 5 1/2 740
Over 24 30 6 61/2 1,040
Over 30 36 6 7 1,200
   Entry loss = 0.15 velocity pressure for tapered takeoff; 0.65 velocity pressure for straight takeoff.
Cradle grinding and polishing operations shall be performed within a partial enclosure similar to figure G-5. The operator shall be positioned outside the working face of the opening of the enclosure. The face opening of the enclosure should not be any greater in area than that actually required for the performance of the operation and the average air velocity into the working face of the enclosure shall not be less than 150 feet per minute.

FIGURE G-5 CRADLE POLISHING OR GRINDING ENCLOSURE


Entry loss = 0.45 velocity pressure for tapered takeoff.
Hoods for horizontal single-spindle disc grinders shall be constructed to conform as closely as possible to the hood shown in figure G-6. It is essential that there be a space between the back of the wheel and the hood, and a space around the periphery of the wheel of at least 1 inch in order to permit the suction to act around the wheel periphery. The opening on the side of the disc shall be no larger than is required for the grinding operation, but must never be less than twice the area of the branch outlet.

FIGURE G-6 HORIZONTAL SINGLE-SPINDLE DISC GRINDER EXHAUST HOOD AND BRANCH PIPE CONNECTIONS

Dia D inches
Exhaust E
dia.
inches

Volume
exhausted
at 4,500
ft/min
ft(3)/min
Min. Max.
Over 12 12
19
3
4
220
390
Over 19 30 5 610
Over 30 36 6 880
   NOTE: If grinding wheels are used for disc grinding purposes, hoods must conform to structural strength and materials as described in 9.1.

Entry loss = 0.45 velocity pressure for tapered takeoff.
Horizontal double-spindle disc grinders shall have a hood encircling the wheels and grinding chamber similar to that illustrated in figure G-7. The openings for passing the work into the grinding chamber should be kept as small as possible, but must never be less than twice the area of the branch outlets.

FIGURE G-7 HORIZONTAL DOUBLE-SPINDLE DISC GRINDER EXHAUST HOOD AND BRANCH PIPE CONNECTIONS


Disc dia.inches Exhaust E Volume
exhausted
at
4,500
ft/min.
ft(3)/min
Note
Min. Max. No
Pipes
Dia.
19 1 5 610 When
width "W"
permits,
exhaust
ducts
should
be as
near
heaviest
grinding
as
possible.
Over 19 25 1
6 880
Over 25 30 1 7 1200
Over 30 53 2 6 1770
Over 53 72 4 8 6280
Entry loss = 0.45 velocity pressure for tapered takeoff.
Grinding and polishing belt hoods shall be constructed as close to the operation as possible. The hood should extend almost to the belt, and 1-inch wide openings should be provided on either side. Figure G-8 shows a typical hood for a belt operation.

FIGURE G-8 A TYPICAL HOOD FOR A BELT OPERATION

Belt width W. inches (centimeters) Exhaust Volume
ft.[1] /min
Up to 3 220
3 to 5 300
5 to 7 390
7 to 9 500
9 to 11 610
11 to 13 740
   Minimum duct velocity = 4,500 ft/min branch, 3,500 ft/min main.
   Entry loss = 0.45 velocity pressure for tapered takeoff; 0.65 velocity pressure for straight takeoff.
Exhaust hoods for floor stands, pedestals, and bench grinders shall be designed in accordance with figure G-2. The adjustable tongue shown in the figure shall be kept in working order and shall be adjusted within one-fourth inch of the wheel periphery at all times.

FIGURE G-2 STANDARD GRINDER HOOD

Wheel dimension, inches Exhaust
outlet,
inches
E

Volume
of air
at
4,500
ft/min
Diameter Width, Max
Min= d Max= D
Over 9 9
16
11/2
2
3
4
220
390
Over 16 19 3 41/2 500
Over 19 24 4 5 610
Over 24 30 5 6 880
Over 30 36 6 7 1,200
   Entry loss = 0.45 velocity pressure for tapered takeoff 0.65 velocity pressure for straight takeoff.
This paragraph (b), prescribes the use of exhaust hood enclosures and systems in removing dust, dirt, fumes, and gases generated through the grinding, polishing, or buffing of ferrous and nonferrous metals.
Spray-finishing operations are employment of methods wherein organic or inorganic materials are utilized in dispersed form for deposit on surfaces to be coated, treated, or cleaned. Such methods of deposit may involve either automatic, manual, or electrostatic deposition but do not include metal spraying or metallizing, dipping, flow coating, roller coating, tumbling, centrifuging, or spray washing and degreasing as conducted in self-contained washing and degreasing machines or systems.
A spray room is a room in which spray-finishing operations not conducted in a spray booth are performed separately from other areas.
Minimum maintained velocity is the velocity of air movement which must be maintained in order to meet minimum specified requirements for health and safety.
Spray booths are defined and described in § 1910.107(a).
Spray booths or spray rooms are to be used to enclose or confine all operations. Spray-finishing operations shall be located as provided in sections 201 through 206 of the Standard for Spray Finishing Using Flammable and Combustible Materials, NFPA No. 33-1969.
Spray booths shall be designed and constructed in accordance with § 1910.107(b)(1) through (b)(4) and (b)(6) through (b)(10). for a more detailed discussion of fundamentals relating to this subject, see ANSI Z9.2-1960, which is incorporated by reference as specified in § 1910.6.
Lights, motors, electrical equipment, and other sources of ignition shall conform to the requirements of § 1910.107(b)(10) and (c).
In no case shall combustible material be used in the construction of a spray booth and supply or exhaust duct connected to it.
Baffles, distribution plates, and dry-type overspray collectors shall conform to the requirements of § 1910.107(b)(4) and (b)(5).
Overspray filters shall be installed and maintained in accordance with the requirements of § 1910.107(b)(5), and shall only be in a location easily accessible for inspection, cleaning, or replacement.
Where effective means, independent of the overspray filters, are installed which will result in design air distribution across the booth cross section, it is permissible to operate the booth without the filters in place.
For wet or water-wash spray booths, the water-chamber enclosure, within which intimate contact of contaminated air and cleaning water or other cleaning medium is maintained, if made of steel, shall be 18 gage or heavier and adequately protected against corrosion.
Chambers may include scrubber spray nozzles, headers, troughs, or other devices. Chambers shall be provided with adequate means for creating and maintaining scrubbing action for removal of particulate matter from the exhaust air stream.
Collecting tanks shall be of welded steel construction or other suitable non-combustible material. If pits are used as collecting tanks, they shall be concrete, masonry, or other material having similar properties.
Tanks shall be provided with weirs, skimmer plates, or screens to prevent sludge and floating paint from entering the pump suction box. Means for automatically maintaining the proper water level shall also be provided. Fresh water inlets shall not be submerged. They shall terminate at least one pipe diameter above the safety overflow level of the tank.
Tanks shall be so constructed as to discourage accumulation of hazardous deposits.
Pump manifolds, risers, and headers shall be adequately sized to insure sufficient water flow to provide efficient operation of the water chamber.
Unobstructed walkways shall not be less than 6 1/2 feet high and shall be maintained clear of obstruction from any work location in the booth to a booth exit or open booth front. In booths where the open front is the only exit, such exits shall be not less than 3 feet wide. In booths having multiple exits, such exits shall not be less than 2 feet wide, provided that the maximum distance from the work location to the exit is 25 feet or less. Where booth exits are provided with doors, such doors shall open outward from the booth.
Spray rooms, including floors, shall be constructed of masonry, concrete, or other noncombustible material.
Spray rooms shall be adequately ventilated so that the atmosphere in the breathing zone of the operator shall be maintained in accordance with the requirements of paragraph (c)(6)(ii) of this section.
Spray rooms used for production spray-finishing operations shall conform to the requirements for spray booths.
Spray rooms shall have noncombustible fire doors and shutters.
Ventilation shall be provided in accordance with provisions of § 1910.107(d), and in accordance with the following:
Where a fan plenum is used to equalize or control the distribution of exhaust air movement through the booth, it shall be of sufficient strength or rigidity to withstand the differential air pressure or other superficially imposed loads for which the equipment is designed and also to facilitate cleaning. Construction specifications shall be at least equivalent to those of paragraph (c)(5)(iii) of this section.
Exhaust ductwork shall be adequately supported throughout its length to sustain its weight plus any normal accumulation in interior during normal operating conditions and any negative pressure exerted upon it.
Exhaust ductwork shall be sized in accordance with good design practice which shall include consideration of fan capacity, length of duct,number of turns and elbows, variation in size, volume, and character of materials being exhausted. See American National Standard Z9.2-1960 for further details and explanation concerning elements of design.
Longitudinal joints in sheet steel ductwork shall be either lock-seamed, riveted, or welded. For other than steel construction, equivalent securing of joints shall be provided.
Circumferential joints in ductwork shall be substantially fastened together and lapped in the direction of airflow. At least every fourth joint shall be provided with connecting flanges, bolted together, or of equivalent fastening security.
Inspection or clean-out doors shall be provided for every 9 to 12 feet of running length for ducts up to 12 inches in diameter, but the distance between cleanout doors may be greater for larger pipes. A clean-out door or doors shall be provided for servicing the fan, and where necessary, a drain shall be provided.
Where ductwork passes through a combustible roof or wall, the roof or wall shall be protected at the point of penetration by open space or fire-resistive material between the duct and the roof or wall. When ducts pass through firewalls, they shall be provided with automatic fire dampers on both sides of the wall, except that three-eighth-inch steel plates may be used in lieu of automatic fire dampers for ducts not exceeding 18 inches in diameter.
Ductwork used for ventilating any process covered in this standard shall not be connected to ducts ventilating any other process or any chimney or flue used for conveying any products of combustion.
Inlet or supply ductwork used to transport makeup air to spray booths or surrounding areas shall be constructed of noncombustible materials.
If negative pressure exists within inlet ductwork, all seams and joints shall be sealed if there is a possibility of infiltration of harmful quantities of noxious gases, fumes, or mists from areas through which ductwork passes.
Inlet ductwork shall be sized in accordance with volume flow requirements and provide design air requirements at the spray booth.
Inlet ductwork shall be adequately supported throughout its length to sustain at least its own weight plus any negative pressure which is exerted upon it under normal operating conditions.
Except where a spray booth has an adequate air replacement system, the velocity of air into all openings of a spray booth shall be not less than that specified in Table G-10 for the operating conditions specified. An adequate air replacement system is one which introduces replacement air upstream or above the object being sprayed and is so designed that the velocity of air in the booth cross section is not less than that specified in Table G-10 when measured upstream or above the object being sprayed.

TABLE G-10 - MINIMUM MAINTAINED VELOCITIES INTO SPRAY BOOTHS
Operating conditions for
objects completely
inside booth
Crossdraft,
f.p.m.
Airflow velocities, f.p.m.
Design Range
Electrostatic and
automatic air-less
operation contained in
booth without operator.
Negligible. 50 Large booth 50-75
Air-operated guns,
manual or automatic
Up to 50 100 small booth
100 large booth
75-125
75-125
Air-operated guns,
manual or automatic
Up to 100 150 small booth
150 large booth
125-175
125-175
200 small booth 150-250
NOTES:
  1. Attention is invited to the fact that the effectiveness of the spray booth is dependent upon the relationship of the depth of the booth to its height and width.
  2. Crossdrafts can be eliminated through proper design and such design should be sought. Crossdrafts in excess of 100 fpm (feet per minute) should not be permitted.
  3. Excessive air pressures result in loss of both efficiency and material waste in addition to creating a backlash that may carry overspray and fumes into adjacent work areas.
  4. Booths should be designed with velocities shown in the column headed "Design. However, booths operating with velocities shown in the column headed "Range" are in compliance with this standard.
When an operator is in a booth downstream of the object being sprayed, an air supplied respirator or other type of respirator must be used by employees that has been approved by the NIOSH under 42 CFR part 84 for the material being sprayed.
Where downdraft booths are provided with doors, such doors shall be closed when spray painting.
In addition to the requirements in paragraph (c)(6)(i) of this section, the total air volume exhausted through a spray booth shall be such as to dilute solvent vapor to at least 25 percent of the lower explosive limit of the solvent being sprayed. An example of the method of calculating this volume is given below.

Example: To determine the lower explosive limits of the most common solvents used in spray finishing, see Table G-11. Column 1 gives the number of cubic feet of vapor per gallon of solvent and column 2 gives the lower explosive limit (LEL) in percentage by volume of air. Note that the quantity of solvent will be diminished by the quantity of solids and nonflammables contained in the finish.

To determine the volume of air in cubic feet necessary to dilute the vapor from 1 gallon of solvent to 25 percent of the lower explosive limit, apply the following formula:

Dilution volume required per gallon of solvent = 4 (100 - LEL) (cubic feet of vapor per gallon) divided by LEL

Using toluene as the solvent.
  1. LEL of toluene from Table G-11, column 2, is 1.4 percent.
  2. Cubic feet of vapor per gallon from Table G-11, column 1, is 30.4 cubic feet per gallon.
  3. Dilution volume required =

    4 (100 - 1.4) 30.4 divided by 1.4 = 8,564 cubic feet.
  4. To convert to cubic feet per minute of required ventilation, multiply the dilution volume required per gallon of solvent by the number of gallons of solvent evaporated per minute.
TABLE G-11 - LOWER EXPLOSIVE LIMIT OF SOME COMMONLY USED SOLVENTS

Solvent
Cubic feet
per gallon
of vapor of
liquid at
70 deg. F.
Lower
explosive
limit in
percent by
volume of air
at 70 deg. F.
Column 1 Column 2
Acetone 44.0 2.6
Amyl Acetate (iso) 21.6 (1) 1.0
Amyl Alcohol (n) 29.6 1.2
Amyl Alcohol (iso) 29.6 1.2
Benzene 36.8 (1) 1.4
Butyl Acetate (n) 24.8 1.7
Butyl Alcohol (n) 35.2 1.4
Butyl Cellosolve 24.8 1.1
Cellosolve 33.6 1.8
Cellosolve Acetate 23.2 1.7
Cyclohexanone 31.2 (1) 1.1
1,1 Dichloroethylene 42.4 5.9
1,2 Dichloroethylene 42.4 9.7
Ethyl Acetate 32.8 2.5
Ethyl Alcohol 55.2 4.3
Ethyl Lactate 28.0 (1) 1.5
Methyl Acetate 40.0 3.1
Methyl Acetate 80.8 7.3
Methyl Cellosolve 40.8 2.5
Methyl Ethyl Ketone 36.0 1.8
Methyl n-Propyl Ketone 30.4 1.5
Naphtha (VM&P) (76 deg. Naphtha) 22.4 0.9
Naphtha (100 deg. Flash) Safety
    Solvent - Stoddard Solvent
23.2 1.0
Propyl Acetate (n) 27.2 2.8
Propyl Acetate (iso) 28.0 1.1
Propyl Alcohol (n) 44.8 2.1
Propyl Alcohol (iso) 44.0 2.0
Toluene 30.4 1.4
Turpentine 20.8 0.8
Xylene (o) 26.4 1.0
Footnote(1) At 212 deg. F.
Clean fresh air, free of contamination from adjacent industrial exhaust systems, chimneys, stacks, or vents, shall be supplied to a spray booth or room in quantities equal to the volume of air exhausted through the spray booth.
Where the air supply to a spray booth or room is filtered, the fan static pressure shall be calculated on the assumption that the filters are dirty to the extent that they require cleaning or replacement.
The rating of filters shall be governed by test data supplied by the manufacturer of the filter. A pressure gage shall be installed to show the pressure drop across the filters. This gage shall be marked to show the pressure drop at which the filters require cleaning or replacement. Filters shall be replaced or cleaned whenever the pressure drop across them becomes excessive or whenever the air flow through the face of the booth falls below that specified in Table G-10.
Means for heating make-up air to any spray booth or room, before or at the time spraying is normally performed, shall be provided in all places where the outdoor temperature may be expected to remain below 55 deg. F. for appreciable periods of time during the operation of the booth except where adequate and safe means of radiant heating for all operating personnel affected is provided. The replacement air during the heating seasons shall be maintained at not less than 65 deg. F. at the point of entry into the spray booth or spray room. When otherwise unheated make-up air would be at a temperature of more than 10 deg. F. below room temperature, its temperature shall be regulated as provided in section 3.6.3 of ANSI Z9.2-1960.
As an alternative to an air replacement system complying with the preceding section, general heating of the building in which the spray room or booth is located may be employed provided that all occupied parts of the building are maintained at not less than 65 deg. F. when the exhaust system is in operation or the general heating system supplemented by other sources of heat may be employed to meet this requirement.
No means of heating make-up air shall be located in a spray booth.
Where make-up air is heated by coal or oil, the products of combustion shall not be allowed to mix with the make-up air, and the products of combustion shall be conducted outside the building through a flue terminating at a point remote from all points where make-up air enters the building.
Where make-up air is heated by gas, and the products of combustion are not mixed with the make-up air but are conducted through an independent flue to a point outside the building remote from all points where make-up air enters the building, it is not necessary to comply with paragraph (c)(7)(iv)(f) of this section.
Where make-up air to any manually operated spray booth or room is heated by gas and the products of combustion are allowed to mix with the supply air, the following precautions must be taken:
The gas must have a distinctive and strong enough odor to warn workmen in a spray booth or room of its presence if in an unburned state in the make-up air.
The maximum rate of gas supply to the make-up air heater burners must not exceed that which would yield in excess of 200 p.p.m. (parts per million) of carbon monoxide or 2,000 p.p.m. of total combustible gases in the mixture if the unburned gas upon the occurrence of flame failure were mixed with all of the make-up air supplied.
A fan must be provided to deliver the mixture of heated air and products of combustion from the plenum chamber housing the gas burners to the spray booth or room.
Where a spray booth or room receives make-up air through self-closing doors, dampers, or louvers, they shall be fully open at all times when the booth or room is in use for spraying. The velocity of air through such doors, dampers, or louvers shall not exceed 200 feet per minute. If the fan characteristics are such that the required air flow through the booth will be provided, higher velocities through the doors, dampers, or louvers may be used.
Spray booths or spray rooms are to be used to enclose or confine all spray finishing operations covered by this paragraph (c). This paragraph does not apply to the spraying of the exteriors of buildings, fixed tanks, or similar structures, nor to small portable spraying apparatus not used repeatedly in the same location.
[39 FR 23502, June 27, 1974, as amended at 40 FR 23073, May 28, 1975; 40 FR 24522, June 9, 1975; 43 FR 49746, Oct. 24, 1978; 49 FR 5322, Feb. 10, 1984; 55 FR 32015, Aug. 6, 1990; 58 FR 35308, June 30, 1993; 61 FR 9227, March 7, 1996; 63 FR 1152, Jan. 8, 1998; 64 FR 13909, March 23, 1999; 72 FR 71069, Dec. 14, 2007; 74 FR 46356, Sept. 9, 2009]
Protection against the effects of noise exposure shall be provided when the sound levels exceed those shown in Table G-16 when measured on the A scale of a standard sound level meter at slow response. When noise levels are determined by octave band analysis, the equivalent A-weighted sound level may be determined as follows:

FIGURE G-9


Equivalent sound level contours. Octave band sound pressure levels may be converted to the equivalent A-weighted sound level by plotting them on this graph and noting the A-weighted sound level corresponding to the point of highest penetration into the sound level contours. This equivalent A-weighted sound level, which may differ from the actual A-weighted sound level of the noise, is used to determine exposure limits from Table 1.G-16.

TABLE G-16 - PERMISSIBLE NOISE EXPOSURES (1)
Duration per day, hours Sound level dBA slow response
8 90
6 92
4 95
3 97
2 100
11/2 102
1 105
1/2 110
1/4 or less 115
Footnote(1) When the daily noise exposure is composed of two or more periods of noise exposure of different levels, their combined effect should be considered, rather than the individual effect of each. If the sum of the following fractions: C(1)/T(1) + C(2)/T(2) C(n)/T(n) exceeds unity, then, the mixed exposure should be considered to exceed the limit value. Cn indicates the total time of exposure at a specified noise level, and Tn indicates the total time of exposure permitted at that level. Exposure to impulsive or impact noise should not exceed 140 dB peak sound pressure level.
When employees are subjected to sound exceeding those listed in Table G-16, feasible administrative or engineering controls shall be utilized. If such controls fail to reduce sound levels within the levels of Table G-16, personal protective equipment shall be provided and used to reduce sound levels within the levels of the table.
If the variations in noise level involve maxima at intervals of 1 second or less, it is to be considered continuous.
The employer shall administer a continuing, effective hearing conservation program, as described in paragraphs (c) through (o) of this section, whenever employee noise exposures equal or exceed an 8-hour time-weighted average sound level (TWA) of 85 decibels measured on the A scale (slow response) or, equivalently, a dose of fifty percent. For purposes of the hearing conservation program, employee noise exposures shall be computed in accordance with appendix A and Table G-16a, and without regard to any attenuation provided by the use of personal protective equipment.
For purposes of paragraphs (c) through (n) of this section, an 8-hour time-weighted average of 85 decibels or a dose of fifty percent shall also be referred to as the action level.
When information indicates that any employee's exposure may equal or exceed an 8-hour time-weighted average of 85 decibels, the employer shall develop and implement a monitoring program.
The sampling strategy shall be designed to identify employees for inclusion in the hearing conservation program and to enable the proper selection of hearing protectors.
Where circumstances such as high worker mobility, significant variations in sound level, or a significant component of impulse noise make area monitoring generally inappropriate, the employer shall use representative personal sampling to comply with the monitoring requirements of this paragraph unless the employer can show that area sampling produces equivalent results.
All continuous, intermittent and impulsive sound levels from 80 decibels to 130 decibels shall be integrated into the noise measurements.
Instruments used to measure employee noise exposure shall be calibrated to ensure measurement accuracy.
Monitoring shall be repeated whenever a change in production, process, equipment or controls increases noise exposures to the extent that:
Additional employees may be exposed at or above the action level; or
The attenuation provided by hearing protectors being used by employees may be rendered inadequate to meet the requirements of paragraph (j) of this section.
The employer shall notify each employee exposed at or above an 8-hour time-weighted average of 85 decibels of the results of the monitoring.
The employer shall provide affected employees or their representatives with an opportunity to observe any noise measurements conducted pursuant to this section.
The employer shall establish and maintain an audiometric testing program as provided in this paragraph by making audiometric testing available to all employees whose exposures equal or exceed an 8-hour time-weighted average of 85 decibels.
The program shall be provided at no cost to employees.
Audiometric tests shall be performed by a licensed or certified audiologist, otolaryngologist, or other physician, or by a technician who is certified by the Council of Accreditation in Occupational Hearing Conservation, or who has satisfactorily demonstrated competence in administering audiometric examinations, obtaining valid audiograms, and properly using, maintaining and checking calibration and proper functioning of the audiometers being used. A technician who operates microprocessor audiometers does not need to be certified. A technician who performs audiometric tests must be responsible to an audiologist, otolaryngologist or physician.
All audiograms obtained pursuant to this section shall meet the requirements of Appendix C: "Audiometric Measuring Instruments."
Within 6 months of an employee's first exposure at or above the action level, the employer shall establish a valid baseline audiogram against which subsequent audiograms can be compared.
Testing to establish a baseline audiogram shall be preceded by at least 14 hours without exposure to workplace noise. Hearing protectors may be used as a substitute for the requirement that baseline audiograms be preceded by 14 hours without exposure to workplace noise.
The employer shall notify employees of the need to avoid high levels of non-occupational noise exposure during the 14-hour period immediately preceding the audiometric examination.
Where mobile test vans are used to meet the audiometric testing obligation, the employer shall obtain a valid baseline audiogram within 1 year of an employee's first exposure at or above the action level. Where baseline audiograms are obtained more than 6 months after the employee's first exposure at or above the action level, employees shall wear hearing protectors for any period exceeding six months after first exposure until the baseline audiogram is obtained.
At least annually after obtaining the baseline audiogram, the employer shall obtain a new audiogram for each employee exposed at or above an 8-hour time-weighted average of 85 decibels.
Each employee's annual audiogram shall be compared to that employee's baseline audiogram to determine if the audiogram is valid and if a standard threshold shift as defined in paragraph (g)(10) of this section has occurred. This comparison may be done by a technician.
The audiologist, otolaryngologist, or physician shall review problem audiograms and shall determine whether there is a need for further evaluation. The employer shall provide to the person performing this evaluation the following information:
A copy of the requirements for hearing conservation as set forth in paragraphs (c) through (n) of this section;
The baseline audiogram and most recent audiogram of the employee to be evaluated;
Measurements of background sound pressure levels in the audiometric test room as required in Appendix D: Audiometric Test Rooms.
Records of audiometer calibrations required by paragraph (h)(5) of this section.
If the annual audiogram shows that an employee has suffered a standard threshold shift, the employer may obtain a retest within 30 days and consider the results of the retest as the annual audiogram.
If a comparison of the annual audiogram to the baseline audiogram indicates a standard threshold shift as defined in paragraph (g)(10) of this section has occurred, the employee shall be informed of this fact in writing, within 21 days of the determination.
If subsequent audiometric testing of an employee whose exposure to noise is less than an 8-hour TWA of 90 decibels indicates that a standard threshold shift is not persistent, the employer:
Shall inform the employee of the new audiometric interpretation; and
May discontinue the required use of hearing protectors for that employee.
Unless a physician determines that the standard threshold shift is not work related or aggravated by occupational noise exposure, the employer shall ensure that the following steps are taken when a standard threshold shift occurs:
Employees not using hearing protectors shall be fitted with hearing protectors, trained in their use and care, and required to use them.
Employees already using hearing protectors shall be refitted and retrained in the use of hearing protectors and provided with hearing protectors offering greater attenuation if necessary.
The employee shall be referred for a clinical audiological evaluation or an otological examination, as appropriate, if additional testing is necessary or if the employer suspects that a medical pathology of the ear is caused or aggravated by the wearing of hearing protectors.
The employee is informed of the need for an otological examination if a medical pathology of the ear that is unrelated to the use of hearing protectors is suspected.
An annual audiogram may be substituted for the baseline audiogram when, in the judgment of the audiologist, otolaryngologist or physician who is evaluating the audiogram:
The standard threshold shift revealed by the audiogram is persistent; or
The hearing threshold shown in the annual audiogram indicates significant improvement over the baseline audiogram.
As used in this section, a standard threshold shift is a change in hearing threshold relative to the baseline audiogram of an average of 10 dB or more at 2000, 3000, and 4000 Hz in either ear.
In determining whether a standard threshold shift has occurred, allowance may be made for the contribution of aging (presbycusis) to the change in hearing level by correcting the annual audiogram according to the procedure described in Appendix F: "Calculation and Application of Age Correction to Audiograms."
Audiometric tests shall be pure tone, air conduction, hearing threshold examinations, with test frequencies including as a minimum 500, 1000, 2000, 3000, 4000, and 6000 Hz. Tests at each frequency shall be taken separately for each ear.
Audiometric tests shall be conducted with audiometers (including microprocessor audiometers) that meet the specifications of, and are maintained and used in accordance with, American National Standard Specification for Audiometers, S3.6-1969, which is incorporated by reference as specified in Sec. 1910.6.
Pulsed-tone and self-recording audiometers, if used, shall meet the requirements specified in Appendix C: "Audiometric Measuring Instruments."
Audiometric examinations shall be administered in a room meeting the requirements listed in Appendix D: "Audiometric Test Rooms."
The functional operation of the audiometer shall be checked before each day's use by testing a person with known, stable hearing thresholds, and by listening to the audiometer's output to make sure that the output is free from distorted or unwanted sounds. Deviations of 10 decibels or greater require an acoustic calibration.
An exhaustive calibration shall be performed at least every two years in accordance with sections 4.1.2; 4.1.3.; 4.1.4.3; 4.2; 4.4.1; 4.4.2; 4.4.3; and 4.5 of the American National Standard Specification for Audiometers, S3.6-1969. Test frequencies below 500 Hz and above 6000 Hz may be omitted from this calibration.
Audiometer calibration shall be checked acoustically at least annually in accordance with Appendix E: "Acoustic Calibration of Audiometers." Test frequencies below 500 Hz and above 6000 Hz may be omitted from this check. Deviations of 15 decibels or greater require an exhaustive calibration.
Employers shall make hearing protectors available to all employees exposed to an 8-hour time-weighted average of 85 decibels or greater at no cost to the employees. Hearing protectors shall be replaced as necessary.
Employers shall ensure that hearing protectors are worn:
By an employee who is required by paragraph (b)(1) of this section to wear personal protective equipment; and
By any employee who is exposed to an 8-hour time-weighted average of 85 decibels or greater, and who:
Has not yet had a baseline audiogram established pursuant to paragraph (g)(5)(ii); or
Has experienced a standard threshold shift.
Employees shall be given the opportunity to select their hearing protectors from a variety of suitable hearing protectors provided by the employer.
The employer shall provide training in the use and care of all hearing protectors provided to employees.
The employer shall ensure proper initial fitting and supervise the correct use of all hearing protectors.
The employer shall evaluate hearing protector attenuation for the specific noise environments in which the protector will be used. The employer shall use one of the evaluation methods described in Appendix B: "Methods for Estimating the Adequacy of Hearing Protection Attenuation."
Hearing protectors must attenuate employee exposure at least to an 8-hour time-weighted average of 90 decibels as required by paragraph (b) of this section.
For employees who have experienced a standard threshold shift, hearing protectors must attenuate employee exposure to an 8-hour time-weighted average of 85 decibels or below.
The adequacy of hearing protector attenuation shall be re-evaluated whenever employee noise exposures increase to the extent that the hearing protectors provided may no longer provide adequate attenuation. The employer shall provide more effective hearing protectors where necessary.
The employer shall train each employee who is exposed to noise at or above an 8-hour time weighted average of 85 decibels in accordance with the requirements of this section. The employer shall institute a training program and ensure employee participation in the program.
The training program shall be repeated annually for each employee included in the hearing conservation program. Information provided in the training program shall be updated to be consistent with changes in protective equipment and work processes.
The employer shall ensure that each employee is informed of the following:
The effects of noise on hearing;
The purpose of audiometric testing, and an explanation of the test procedures.
The purpose of hearing protectors, the advantages, disadvantages, and attenuation of various types, and instructions on selection, fitting, use, and care; and
The employer shall make available to affected employees or their representatives copies of this standard and shall also post a copy in the workplace.
The employer shall provide to affected employees any informational materials pertaining to the standard that are supplied to the employer by the Assistant Secretary.
The employer shall provide, upon request, all materials related to the employer's training and education program pertaining to this standard to the Assistant Secretary and the Director.
The employer shall maintain an accurate record of all employee exposure measurements required by paragraph (d) of this section.
The employer shall retain all employee audiometric test records obtained pursuant to paragraph (g) of this section:
This record shall include:
Name and job classification of the employee;
Date of the audiogram;
The examiner's name;
Date of the last acoustic or exhaustive calibration of the audiometer; and
Employee's most recent noise exposure assessment.
The employer shall maintain accurate records of the measurements of the background sound pressure levels in audiometric test rooms.
The employer shall retain records required in this paragraph (m) for at least the following periods.
Noise exposure measurement records shall be retained for two years.
Audiometric test records shall be retained for the duration of the affected employee's employment.
All records required by this section shall be provided upon request to employees, former employees, representatives designated by the individual employee, and the Assistant Secretary. The provisions of 29 CFR 1910.1020 (a)-(e) and (g)-(i) apply to access to records under this section.
If the employer ceases to do business, the employer shall transfer to the successor employer all records required to be maintained by this section, and the successor employer shall retain them for the remainder of the period prescribed in paragraph (m)(3) of this section.
Appendices A, B, C, D, and E to this section are incorporated as part of this section and the contents of these appendices are mandatory.
Appendices F and G to this section are informational and are not intended to create any additional obligations not otherwise imposed or to detract from any existing obligations.
Paragraphs (c) through (n) of this section shall not apply to employers engaged in oil and gas well drilling and servicing operations.

[39 FR 23502, June 27, 1974, as amended at 46 FR 4161, Jan. 16, 1981; 46 FR 62845, Dec. 29, 1981; 48 FR 9776, Mar. 8, 1983; 48 FR 29687, June 28, 1983; 54 FR 24333, June 7, 1989; 61 FR 5507, Feb. 13, 1996; 61 FR 9227, March 7, 1996; 71 FR 16672, April, 3, 2006; 73 FR 75584, Dec. 12, 2008]
This Appendix is Mandatory
  1. Computation of Employee Noise Exposure
    1. Noise dose is computed using Table G-16a as follows:
      1. When the sound level, L, is constant over the entire work shift, the noise dose, D, in percent, is given by: D=100 C/T where C is the total length of the work day, in hours, and T is the reference duration corresponding to the measured sound level, L, as given in Table G-16a or by the formula shown as a footnote to that table
      2. When the workshift noise exposure is composed of two or more periods of noise at different levels, the total noise dose over the work day is given by:

        D = 100 (C(1)/T(1) + C(2)/T(2) + ... + C(n)/T(n)),

        where C(n) indicates the total time of exposure at a specific noise level, and T(n) indicates the reference duration for that level as given by Table G-16a
    2. The eight-hour time-weighted average sound level (TWA), in decibels, may be computed from the dose, in percent, by means of the formula: TWA = 16.61 log(10) (D/100) + 90. For an eight-hour workshift with the noise level constant over the entire shift, the TWA is equal to the measured sound level
    3. A table relating dose and TWA is given in Section II.

      TABLE G-16A
      A-weighted sound level, L (decibel) Reference
      duration,
      T (hour)
      80 32
      81 27.9
      82 24.3
      83 21.1
      84 18.4
      85 16
      86 13.9
      87 12.1
      88 10.6
      89 9.2
      90 8
      91 7.0
      92 6.1
      93 5.3
      94 4.6
      95 4
      96 3.5
      97 3.0
      98 2.6
      99 2.3
      100 2
      101 1.7
      102 1.5
      103 1.3
      104 1.1
      105 1
      106 0.87
      107 0.76
      108 0.66
      109 0.57
      110 0.5
      111 0.44
      112 0.38
      113 0.33
      114 0.29
      115 0.25
      116 0.22
      117 0.19
      118 0.16
      119 0.14
      120 0.125
      121 0.11
      122 0.095
      123 0.082
      124 0.072
      125 0.063
      126 0.054
      127 0.047
      128 0.041
      129 0.036
      130 0.031

      In the above table the reference duration, T, is computed by
      where L is the measured A-weighted sound level.
  2. Conversion Between "Dose" and "8-Hour Time-Weighted Average"

    Sound Level

    Compliance with paragraphs (c)-(r) of this regulation is determined by the amount of exposure to noise in the workplace. The amount of such exposure is usually measured with an audiodosimeter which gives a readout in terms of "dose." In order to better understand the requirements of the amendment, dosimeter readings can be converted to an "8-hour time-weighted average sound level." (TWA).

    In order to convert the reading of a dosimeter into TWA, see Table A-1, below. This table applies to dosimeters that are set by the manufacturer to calculate dose or percent exposure according to the relationships in Table G-16a. So, for example, a dose of 91 percent over an eight hour day results in a TWA of 89.3 dB, and, a dose of 50 percent corresponds to a TWA of 85 dB

    If the dose as read on the dosimeter is less than or greater than the values found in Table A-1, the TWA may be calculated by using the formula: TWA = 16.61 log(10) (D/100) + 90 where TWA=8-hour time-weighted average sound level and D = accumulated dose in percent exposure.
    TABLE A-1 - CONVERSION FROM "PERCENT NOISE EXPOSURE"
    OR "DOSE" TO "8-HOUR TIME-WEIGHTED
    AVERAGE SOUND LEVEL" (TWA)
    Dose or percent noise exposure TWA
    10 73.4
    15 76.3
    20 78.4
    25 80.0
    30 81.3
    35 82.4
    40 83.4
    45 84.2
    50 85.0
    55 85.7
    60 86.3
    65 86.9
    70 87.4
    75 87.9
    80 88.4
    81 88.5
    82 88.6
    83 88.7
    84 88.7
    85 88.8
    86 88.9
    87 89.0
    88 89.1
    89 89.2
    90 89.2
    91 89.3
    92 89.4
    93 89.5
    94 89.6
    95 89.6
    96 89.7
    97 89.8
    98 89.9
    99 89.9
    100 90.0
    101 90.1
    102 90.1
    103 90.2
    104 90.3
    105 90.4
    106 90.4
    107 90.5
    108 90.6
    109 90.6
    110 90.7
    111 90.8
    112 90.8
    113 90.9
    114 90.9
    115 91.1
    116 91.1
    117 91.1
    118 91.2
    119 91.3
    120 91.3
    125 91.6
    130 91.9
    135 92.2
    140 92.4
    145 92.7
    150 92.9
    155 93.2
    160 93.4
    165 93.6
    170 93.8
    175 94.0
    180 94.2
    185 94.4
    190 94.6
    195 94.8
    200 95.0
    210 95.4
    220 95.7
    230 96.0
    240 96.3
    250 96.6
    260 96.9
    270 97.2
    280 97.4
    290 97.7
    300 97.9
    310 98.2
    320 98.4
    330 98.6
    340 98.8
    350 99.0
    360 99.2
    370 99.4
    380 99.6
    390 99.8
    400 100.0
    410 100.2
    420 100.4
    430 100.5
    440 100.7
    450 100.8
    460 101.0
    470 101.2
    480 101.3
    490 101.5
    500 101.6
    510 101.8
    520 101.9
    530 102.0
    540 102.2
    550 102.3
    560 102.4
    570 102.6
    580 102.7
    590 102.8
    600 102.9
    610 103.0
    620 103.2
    630 103.3
    640 103.4
    650 103.5
    660 103.6
    670 103.7
    680 103.8
    690 103.9
    700 104.0
    710 104.1
    720 104.2
    730 104.3
    740 104.4
    750 104.5
    760 104.6
    770 104.7
    780 104.8
    790 104.9
    800 105.0
    810 105.1
    820 105.2
    830 105.3
    840 105.4
    850 105.4
    860 105.5
    870 105.6
    880 105.7
    890 105.8
    900 105.8
    910 105.9
    920 106.0
    930 106.1
    940 106.2
    950 106.2
    960 106.3
    970 106.4
    980 106.5
    990 106.5
    999 106.6
This Appendix is Mandatory

For employees who have experienced a significant threshold shift, hearing protector attenuation must be sufficient to reduce employee exposure to a TWA of 85 dB. Employers must select one of the following methods by which to estimate the adequacy of hearing protector attenuation.

The most convenient method is the Noise Reduction Rating (NRR) developed by the Environmental Protection Agency (EPA). According to EPA regulation, the NRR must be shown on the hearing protector package. The NRR is then related to an individual worker's noise environment in order to assess the adequacy of the attenuation of a given hearing protector. This appendix describes four methods of using the NRR to determine whether a particular hearing protector provides adequate protection within a given exposure environment. Selection among the four procedures is dependent upon the employer's noise measuring instruments.

Instead of using the NRR, employers may evaluate the adequacy of hearing protector attenuation by using one of the three methods developed by the National Institute for Occupational Safety and Health (NIOSH), which are described in the "List of Personal Hearing Protectors and Attenuation Data," HEW Publication No. 76-120, 1975, pages 21-37. These methods are known as NIOSH methods No. 1, No. 2 and No. 3. The NRR described below is a simplification of NIOSH method No. 2. The most complex method is NIOSH method No. 1, which is probably the most accurate method since it uses the largest amount of spectral information from the individual employee's noise environment. As in the case of the NRR method described below, if one of the NIOSH methods is used, the selected method must be applied to an individual's noise environment to assess the adequacy of the attenuation. Employers should be careful to take a sufficient number of measurements in order to achieve a representative sample for each time segment.

NOTE: The employer must remember that calculated attenuation values reflect realistic values only to the extent that the protectors are properly fitted and worn.

When using the NRR to assess hearing protector adequacy, one of the following methods must be used:
  1. When using a dosimeter that is capable of C-weighted measurements:
    1. Obtain the employee's C-weighted dose for the entire workshift, and convert to TWA (see appendix A, II).
    2. Subtract the NRR from the C-weighted TWA to obtain the estimated A-weighted TWA under the ear protector.
  2. When using a dosimeter that is not capable of C-weighted measurements, the following method may be used:
    1. Convert the A-weighted dose to TWA (see appendix A).
    2. Subtract 7 dB from the NRR.
    3. Subtract the remainder from the A-weighted TWA to obtain the estimated A-weighted TWA under the ear protector.
  3. When using a sound level meter set to the A-weighting network:
    1. Obtain the employee's A-weighted TWA.
    2. Subtract 7 dB from the NRR, and subtract the remainder from the A-weighted TWA to obtain the estimated A-weighted TWA under the ear protector.
  4. When using a sound level meter set on the C-weighting network:
    1. Obtain a representative sample of the C-weighted sound levels in the employee's environment.
    2. Subtract the NRR from the C-weighted average sound level to obtain the estimated A-weighted TWA under the ear protector.
  5. When using area monitoring procedures and a sound level meter set to the A-weighing network.
    1. Obtain a representative sound level for the area in question.
    2. Subtract 7 dB from the NRR and subtract the remainder from the A-weighted sound level for that area.
  6. When using area monitoring procedures and a sound level meter set to the C-weighting network:
    1. Obtain a representative sound level for the area in question.
    2. Subtract the NRR from the C-weighted sound level for that area.
This Appendix is Mandatory

  1. In the event that pulsed-tone audiometers are used, they shall have a tone on-time of at least 200 milliseconds.
  2. Self-recording audiometers shall comply with the following requirements:
    1. The chart upon which the audiogram is traced shall have lines at positions corresponding to all multiples of 10 dB hearing level within the intensity range spanned by the audiometer. The lines shall be equally spaced and shall be separated by at least 1/4 inch. Additional increments are optional. The audiogram pen tracings shall not exceed 2 dB in width.
    2. It shall be possible to set the stylus manually at the 10-dB increment lines for calibration purposes.
    3. The slewing rate for the audiometer attenuator shall not be more than 6 dB/sec except that an initial slewing rate greater than 6 dB/sec is permitted at the beginning of each new test frequency, but only until the second subject response.
    4. The audiometer shall remain at each required test frequency for 30 seconds (+ or - 3 seconds). The audiogram shall be clearly marked at each change of frequency and the actual frequency change of the audiometer shall not deviate from the frequency boundaries marked on the audiogram by more than + or - 3 seconds.
    5. It must be possible at each test frequency to place a horizontal line segment parallel to the time axis on the audiogram, such that the audiometric tracing crosses the line segment at least six times at that test frequency. At each test frequency the threshold shall be the average of the midpoints of the tracing excursions.
This Appendix is Mandatory

Rooms used for audiometric testing shall not have background sound pressure levels exceeding those in Table D-1 when measured by equipment conforming at least to the Type 2 requirements of American National Standard Specification for Sound Level Meters, S1.4-1971 (R1976), and to the Class II requirements of American National Standard Specification for Octave, Half-Octave, and Third-Octave Band Filter Sets, S1.11-1971 (R1976).

TABLE D-1 - MAXIMUM ALLOWABLE OCTAVE-BAND SOUND PRESSURE LEVELS
FOR AUDIOMETRIC TEST ROOMS
Octave-band center frequency (Hz) 500 1000 2000 4000 8000
Sound pressure level (dB) 40 40 47 57 62
This Appendix is Mandatory

Audiometer calibration shall be checked acoustically, at least annually, according to the procedures described in this appendix. The equipment necessary to perform these measurements is a sound level meter, octave-band filter set, and a National Bureau of Standards 9A coupler. In making these measurements, the accuracy of the calibrating equipment shall be sufficient to determine that the audiometer is within the tolerances permitted by American Standard Specification for Audiometers, S3.6-1969.

  1. "Sound Pressure Output Check"
    1. Place the earphone coupler over the microphone of the sound level meter and place the earphone on the coupler.
    2. Set the audiometer's hearing threshold level (HTL) dial to 70 dB.
    3. Measure the sound pressure level of the tones at each test frequency from 500 Hz through 6000 Hz for each earphone.
    4. At each frequency the readout on the sound level meter should correspond to the levels in Table E-1 or Table E-2, as appropriate, for the type of earphone, in the column entitled "sound level meter reading."
  2. "Linearity Check"
    1. With the earphone in place, set the frequency to 1000 Hz and the HTL dial on the audiometer to 70 dB.
    2. Measure the sound levels in the coupler at each 10-dB decrement from 70 dB to 10 dB, noting the sound level meter reading at each setting.
    3. For each 10-dB decrement on the audiometer the sound level meter should indicate a corresponding 10 dB decrease.
    4. This measurement may be made electrically with a voltmeter connected to the earphone terminals.
  3. "Tolerances"

    When any of the measured sound levels deviate from the levels in Table E-1 or Table E-2 by + or - 3 dB at any test frequency between 500 and 3000 Hz, 4 dB at 4000 Hz, or 5 dB at 6000 Hz, an exhaustive calibration is advised. An exhaustive calibration is required if the deviations are greater than 15 dB or greater at any test frequency.

    TABLE E-1 - REFERENCE THRESHOLD LEVELS FOR TELEPHONICS - TDH-39 EARPHONES
    Frequency, Hz Reference,
    threshold
    level for
    TDH-39
    earphones,
    dB
    Sound
    level
    meter
    reading,
    dB
    500 11.5 81.5
    1000 7   77   
    2000 9 79
    3000 10 80
    4000 9.5 79.5
    6000 15.5 85.5


    TABLE E-2 - REFERENCE THRESHOLD LEVELS FOR TELEPHONICS - TDH-49 EARPHONES
    Frequency, Hz Reference,
    threshold
    level for
    TDH-39
    earphones,
    dB
    Sound
    level
    meter
    reading,
    dB
    500 13.5 83.5
    1000 7.5 77.5
    2000 11 81.0
    3000 9.5 79.5
    4000 10.5 80.5
    6000 13.5 83.5
This Appendix Is Non-Mandatory

In determining whether a standard threshold shift has occurred, allowance may be made for the contribution of aging to the change in hearing level by adjusting the most recent audiogram. If the employer chooses to adjust the audiogram, the employer shall follow the procedure described below. This procedure and the age correction tables were developed by the National Institute for Occupational Safety and Health in the criteria document entitled "Criteria for a Recommended Standard . . .
Occupational Exposure to Noise," ((HSM)-11001)

For each audiometric test frequency;

  1. Determine from Tables F-1 or F-2 the age correction values for the employee by:
    1. Finding the age at which the most recent audiogram was taken and recording the corresponding values of age corrections at 1000 Hz through 6000 Hz;
    2. Finding the age at which the baseline audiogram was taken and recording the corresponding values of age corrections at 1000 Hz through 6000 Hz
  2. Subtract the values found in step (i)(B) from the value found in step (i)(A)
  3. The differences calculated in step (ii) represented that portion of the change in hearing that may be due to aging.

    EXAMPLE: Employee is a 32-year-old male. The audiometric history for his right ear is shown in decibels below.

    Employee's age Audiometric test frequency (Hz)
    1000 2000 3000 4000 6000
    26 10 5 5 10 5
    *27 0 0 0 5 5
    28 0 0 0 10 5
    29 5 0 5 15 5
    30 0 5 10 20 10
    31 5 10 20 15 15
    *32 5 10 10 25 20


    The audiogram at age 27 is considered the baseline since it shows the best hearing threshold levels. Asterisks have been used to identify the baseline and most recent audiogram. A threshold shift of 20 dB exists at 4000 Hz between the audiograms taken at ages 27 and 32.

    (The threshold shift is computed by subtracting the hearing threshold at age 27, which was 5, from the hearing threshold at age 32, which is 25). A retest audiogram has confirmed this shift. The contribution of aging to this change in hearing may be estimated in the following manner:

    Go to Table F-1 and find the age correction values (in dB) for 4000 Hz at age 27 and age 32

    Frequency (Hz)
    1000 2000 3000 4000 6000
    Age 32 6 5 7 10 14
    Age 27 5 4 6 7 11
    Difference 1 1 1 3 3


    The difference represents the amount of hearing loss that may be attributed to aging in the time period between the baseline audiogram and the most recent audiogram. In this example, the difference at 4000 Hz is 3 dB. This value is subtracted from the hearing level at 4000 Hz, which in the most recent audiogram is 25, yielding 22 after adjustment. Then the hearing threshold in the baseline audiogram at 4000 Hz (5) is subtracted from the adjusted annual audiogram hearing threshold at 4000 Hz (22). Thus the age-corrected threshold shift would be 17 dB (as opposed to a threshold shift of 20 dB without age correction)

    TABLE F-1 - AGE CORRECTION VALUES IN DECIBELS FOR MALES
    Years Audiometric Test Frequency (Hz)
    1000 2000 3000 4000 6000
    20 or younger 5 3 4 5 8
    21 5 3 4 5 8
    22 5 3 4 5 8
    23 5 3 4 6 9
    24 5 3 5 6 9
    25 5 3 5 7 10
    26 5 4 5 7 10
    27 5 4 6 7 11
    28 6 4 6 8 11
    29 6 4 6 8 12
    30 6 4 6 9 12
    31 6 4 7 9 13
    32 6 5 7 10 14
    33 6 5 7 10 14
    34 6 5 8 11 15
    35 7 5 8 11 15
    36 7 5 9 12 16
    37 7 6 9 12 17
    38 7 6 9 13 17
    39 7 6 10 14 18
    40 7 6 10 14 19
    41 7 6 10 14 20
    42 8 7 11 16 20
    43 8 7 12 16 21
    44 8 7 12 17 22
    45 8 7 13 18 23
    46 8 8 13 19 24
    47 8 8 14 19 24
    48 9 8 14 20 25
    49 9 9 15 21 26
    50 9 9 16 22 27
    51 9 9 16 23 28
    52 9 10 17 24 29
    53 9 10 18 25 30
    54 10 10 18 26 31
    55 10 11 19 27 32
    56 10 11 20 28 34
    57 10 11 21 29 35
    58 10 12 22 31 36
    59 11 12 22 32 37
    60 or older 11 13 23 33 38


    TABLE F-2 - AGE CORRECTION VALUES IN DECIBELS FOR FEMALES
    Years Audiometric Test Frequency (Hz)
    1000 2000 3000 4000 6000
    20 or younger 7 4 3 3 6
    21 7 4 4 3 6
    22 7 4 4 4 6
    23 7 5 4 4 7
    24 7 5 4 4 7
    25 8 5 4 4 7
    26 8 5 5 4 8
    27 8 5 5 5 8
    28 8 5 5 5 8
    29 8 5 5 5 9
    30 8 6 5 5 9
    31 8 6 6 5 9
    32 9 6 6 6 10
    33 9 6 6 6 10
    34 9 6 6 6 10
    35 9 6 7 7 11
    36 9 7 7 7 11
    37 9 7 7 7 12
    38 10 7 7 7 12
    39 10 7 8 8 12
    40 10 7 8 8 13
    41 10 8 8 8 13
    42 10 8 9 9 13
    43 11 8 9 9 14
    44 11 8 9 9 14
    45 11 8 10 10 15
    46 11 9 10 10 15
    47 11 9 10 11 16
    48 12 9 11 11 16
    49 12 9 11 11 16
    50 12 10 11 12 17
    51 12 10 12 12 17
    52 12 10 12 13 18
    53 13 10 13 13 18
    54 13 11 13 14 19
    55 13 11 14 14 19
    56 13 11 14 15 20
    57 13 11 15 15 20
    58 14 12 15 16 21
    59 14 12 16 16 21
    60 or older 14 12 16 17 22
This appendix provides information to help employers comply with the noise monitoring obligations that are part of the hearing conservation amendment.

WHAT IS THE PURPOSE OF NOISE MONITORING?

This revised amendment requires that employees be placed in a hearing conservation program if they are exposed to average noise levels of 85 dB or greater during an 8 hour workday. In order to determine if exposures are at or above this level, it may be necessary to measure or monitor the actual noise levels in the workplace and to estimate the noise exposure or "dose" received by employees during the workday.

WHEN IS IT NECESSARY TO IMPLEMENT A NOISE MONITORING PROGRAM?

It is not necessary for every employer to measure workplace noise. Noise monitoring or measuring must be conducted only when exposures are at or above 85 dB. Factors which suggest that noise exposures in the workplace may be at this level include employee complaints about the loudness of noise, indications that employees are losing their hearing, or noisy conditions which make normal conversation difficult. The employer should also consider any information available regarding noise emitted from specific machines. In addition, actual workplace noise measurements can suggest whether or not a monitoring program should be initiated.

HOW IS NOISE MEASURED?

Basically, there are two different instruments to measure noise exposures: the sound level meter and the dosimeter. A sound level meter is a device that measures the intensity of sound at a given moment. Since sound level meters provide a measure of sound intensity at only one point in time, it is generally necessary to take a number of measurements at different times during the day to estimate noise exposure over a workday. If noise levels fluctuate, the amount of time noise remains at each of the various measured levels must be determined.

To estimate employee noise exposures with a sound level meter it is also generally necessary to take several measurements at different locations within the workplace. After appropriate sound level meter readings are obtained, people sometimes draw "maps" of the sound levels within different areas of the workplace. By using a sound level "map" and information on employee locations throughout the day, estimates of individual exposure levels can be developed. This measurement method is generally referred to as "area" noise monitoring.

A dosimeter is like a sound level meter except that it stores sound level measurements and integrates these measurements over time, providing an average noise exposure reading for a given period of time, such as an 8-hour workday. With a dosimeter, a microphone is attached to the employee's clothing and the exposure measurement is simply read at the end of the desired time period. A reader may be used to read-out the dosimeter's measurements. Since the dosimeter is worn by the employee, it measures noise levels in those locations in which the employee travels. A sound level meter can also be positioned within the immediate vicinity of the exposed worker to obtain an individual exposure estimate. Such procedures are generally referred to as "personal" noise monitoring.

Area monitoring can be used to estimate noise exposure when the noise levels are relatively constant and employees are not mobile. In workplaces where employees move about in different areas or where the noise intensity tends to fluctuate over time, noise exposure is generally more accurately estimated by the personal monitoring approach.

In situations where personal monitoring is appropriate, proper positioning of the microphone is necessary to obtain accurate measurements. With a dosimeter, the microphone is generally located on the shoulder and remains in that position for the entire workday. With a sound level meter, the microphone is stationed near the employee's head, and the instrument is usually held by an individual who follows the employee as he or she moves about.

Manufacturer's instructions, contained in dosimeter and sound level meter operating manuals, should be followed for calibration and maintenance. To ensure accurate results, it is considered good professional practice to calibrate instruments before and after each use.

HOW OFTEN IS IT NECESSARY TO MONITOR NOISE LEVELS?

The amendment requires that when there are significant changes in machinery or production processes that may result in increased noise levels, remonitoring must be conducted to determine whether additional employees need to be included in the hearing conservation program. Many companies choose to remonitor periodically (once every year or two) to ensure that all exposed employees are included in their hearing conservation programs.

WHERE CAN EQUIPMENT AND TECHNICAL ADVICE BE OBTAINED?

Noise monitoring equipment may be either purchased or rented. Sound level meters cost about $500 to $1,000, while dosimeters range in price from about $750 to $1,500. Smaller companies may find it more economical to rent equipment rather than to purchase it. Names of equipment suppliers may be found in the telephone book (Yellow Pages) under headings such as: "Safety Equipment," "Industrial Hygiene," or "Engineers-Acoustical." In addition to providing information on obtaining noise monitoring equipment, many companies and individuals included under such listings can provide professional advice on how to conduct a valid noise monitoring program. Some audiological testing firms and industrial hygiene firms also provide noise monitoring services. Universities with audiology, industrial hygiene, or acoustical engineering departments may also provide information or may be able to help employers meet their obligations under this amendment.

Free, on-site assistance may be obtained from OSHA-supported state and private consultation organizations. These safety and health consultative entities generally give priority to the needs of small businesses.

[61 FR 9227, March 7, 1996]
Paragraphs (c) through (o) of 29 CFR 1910.95 and the accompanying appendices contain provisions which incorporate publications by reference. Generally, the publications provide criteria for instruments to be used in monitoring and audiometric testing. These criteria are intended to be mandatory when so indicated in the applicable paragraphs of 1910.95 and appendices.

It should be noted that OSHA does not require that employers purchase a copy of the referenced publications. Employers, however, may desire to obtain a copy of the referenced publications for their own information.

The designation of the paragraph of the standard in which the referenced publications appear, the titles of the publications, and the availability of the publications are as follows:

Paragraph
designation
Referenced
publication
Available
from --
Appendix B "List of Personal Hearing
Protectors and
Attenuation Data,"
HEW Pub. No. 76-120,
1975. NTIS-PB267461.
National Technical
Information
Service,
Port Royal Road,
Springfield, VA
22161.
Appendix D "Specification for Sound
Level Meters,"
S1.4-1971 (R1976).
American National
Standards
Institute, Inc.,
1430 Broadway,
New York, NY
10018.
1910.95(k)(2), Appendix E "Specifications for
Audiometers,"
S3.6-1969.
American National
Standards
Institute, Inc.,
1430 Broadway,
New York, NY
10018.
Appendix D "Specification for Octave,
Half-Octave and
Third-Octave Band
Filter Sets,"
S1.11-1971 (R1976).
Back Numbers
Department,
Dept. STD,
American
Institute of
Physics,
333 E. 45th St.,,
New York, NY
10017;
American National
Standards
Institute, Inc.,
1430 Broadway,
New York, NY
10018.


The referenced publications (or a microfiche of the publications) are available for review at many universities and public libraries throughout the country. These publications may also be examined at the OSHA Technical Data Center, Room N2439, United States Department of Labor, 200 Constitution Avenue, NW., Washington, DC 20210, (202) 219-7500 or at any OSHA Regional Office (see telephone directories under United States Government - Labor Department).

[61 FR 9227, March 7, 1996]
These definitions apply to the following terms as used in paragraphs (c) through (n) of 29 CFR 1910.95.

Action level - An 8-hour time-weighted average of 85 decibels
measured on the A-scale, slow response, or equivalently, a dose of
fifty percent.
Audiogram - A chart, graph, or table resulting from an audiometric
test showing an individual's hearing threshold levels as a
function of frequency.
Audiologist - A professional, specializing in the study and
rehabilitation of hearing, who is certified by the American
Speech-Language-Hearing Association or licensed by a state board
of examiners.
Baseline audiogram - The audiogram against which future audiograms
are compared.
Criterion sound level - A sound level of 90 decibels.
Decibel (dB) - Unit of measurement of sound level.
Hertz (Hz) - Unit of measurement of frequency, numerically equal to
cycles per second.
Medical pathology - A disorder or disease. For purposes of this
regulation, a condition or disease affecting the ear, which should
be treated by a physician specialist.
Noise dose - The ratio, expressed as a percentage, of (1) the time
integral, over a stated time or event, of the 0.6 power of the
measured SLOW exponential time-averaged, squared A-weighted sound
pressure and (2) the product of the criterion duration (8 hours)
and the 0.6 power of the squared sound pressure corresponding to
the criterion sound level (90 dB).
Noise dosimeter - An instrument that integrates a function of sound
pressure over a period of time in such a manner that it directly
indicates a noise dose.
Otolaryngologist - A physician specializing in diagnosis and
treatment of disorders of the ear, nose and throat.
Representative exposure - Measurements of an employee's noise dose
or 8-hour time-weighted average sound level that the employers
deem to be representative of the exposures of other employees in
the workplace.
Sound level - Ten times the common logarithm of the ratio of the
square of the measured A-weighted sound pressure to the square of
the standard reference pressure of 20 micropascals. Unit: decibels
(dB). For use with this regulation, SLOW time response, in
accordance with ANSI S1.4-1971 (R1976), is required.
Sound level meter - An instrument for the measurement of sound
level.
Time-weighted average sound level - That sound level, which if
constant over an 8-hour exposure, would result in the same noise
dose as is measured.

[39 FR 23502, June 27, 1974, as amended at 46 FR 4161, Jan. 16, 1981; 46 FR 62845, Dec. 29, 1981; 48 FR 9776, Mar. 8, 1983; 48 FR 29687, June 28, 1983; 54 FR 24333, June 7, 1989; 61 FR 5507, Feb. 13, 1996; 61 FR 9227, March 7, 1996]
The term "electromagnetic radiation" is restricted to that portion of the spectrum commonly defined as the radio frequency region, which for the purpose of this specification shall include the microwave frequency region.
Radiation level which should not be exceeded without careful consideration of the reasons for doing so.
The word "symbol" as used in this specification refers to the overall design, shape, and coloring of the rf radiation sign shown in figure G-11.

  1. Place handling and mounting instructions on reverse side.
  2. D=Scaling unit.
  3. Lettering: Ratio of letter height to thickness of letter lines.
    upper triangle: 5 to 1 large
    6 to 1 medium
    Lower triangle 4 to 1 Small
    6 to 1 Medium
  4. Symbol is square, triangle are right-angle isoseles.
FIGURE G-11
RADIO-FREQUENCY RADIATION HAZARD WARNING SYMBOL
Pertains to the case in which the entire body is exposed to the incident electromagnetic energy or in which the cross section of the body is smaller than the cross section of the incident radiation beam.
Pertains to the case in which part of the body is exposed to the incident electromagnetic energy.
For normal environmental conditions and for incident electromagnetic energy of frequencies from 10 MHz to 100 GHz, the radiation protection guide is 10 mW/cm.(2) (milliwatt per square centimeter) as averaged over any possible 0.1-hour period. This means the following:

Power density: 10 mW./cm.2 for periods of 0.1-hour or more.

Energy density: 1 mW.-hr./cm.2 (milliwatt hour per square centimeter) during any 0.1-hour period.

This guide applies whether the radiation is continuous or intermittent.
These formulated recommendations pertain to both whole body irradiation and partial body irradiation. Partial body irradiation must be included since it has been shown that some parts of the human body (e.g., eyes, testicles) may be harmed if exposed to incident radiation levels significantly in excess of the recommended levels.
The warning symbol for radio frequency radiation hazards shall consist of a red isosceles triangle above an inverted black isosceles triangle, separated and outlined by an aluminum color border. The words "Warning - Radio-Frequency Radiation Hazard" shall appear in the upper triangle. See figure G-11.
The inclusion and choice of warning information or precautionary instructions is at the discretion of the user. If such information is included it shall appear in the lower triangle of the warning symbol.
ANSI Z53.1-1967 or ANSI Z535.1-2006(R2011), incorporated by reference in § 1910.6, is for use for color specification. All lettering and the border shall be of aluminum color.
This section applies to all radiations originating from radio stations, radar equipment, and other possible sources of electromagnetic radiation such as used for communication, radio navigation, and industrial and scientific purposes. This section does not apply to the deliberate exposure of patients by, or under the direction of, practitioners of the healing arts.

[61 FR 9227, March 7, 1996; 78 FR 35566, June 13, 2013]
The provisions of this Subpart G shall become effective on August 27,1971, except as provided in the remaining paragraphs of this section.
The following provisions shall become effective on February 15, 1972:

1910.94 (a)(2)(iii), (a)(3), (a)(4), (b), (c)(2), (c)(3), (c)(4), (c)(5), (c)(6)(i), (c)(6)(ii), (d)(1)(ii), (d)(3), (d)(4), (d)(5), and (d)(7).
Notwithstanding anything in paragraph (a), (b) or (d) of this section, any provision in any other section of this subpart which contains in itself a specific effective date or time limitation shall become effective on such date or shall apply in accordance with such limitation.
Notwithstanding anything in paragraph (a) of this section, if any standard in 41 CFR part 50-204, other than a national consensus standard incorporated by reference in 50-204.2(a)(1), is or becomes applicable at any time to any employment and place of employment, by virtue of the Walsh-Healey Public Contracts Act, or the Service Contract Act of 1965, or the National Foundation on Arts and Humanities Act of 1965, any corresponding established Federal standard in this Subpart G which is derived from 41 CFR part 50-204 shall also become effective, and shall be applicable to such employment and place of employment, on the same date.
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