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Federal Register / Vol. 51, No. 119. / Friday, June 20, 1986 / Rules and Regulations
22675
result of the rule, there will be a
decrease in the amount of ambient
emissions to the environment. Although
any captured fibers could take the form
of solid waste of wastewater runoff,
sludge, or slurry, this is not anticipated
to result in a significant environmental
impact.
In achieving compliance with the
standard, industry will in some
instances need to install engineering
controls, implement work practices,
provide personal protective equipment,
and training. These measures are not
expected to have any significant
adverse environmental effects, and
could be of potential benefit to the
environment in terms of air and water
quality and solid waste disposal.
The Use of local controls, filters,
collection devices and wet methods
would reduce levels of airborne
emissions in the workplace. The
placement of proper controls and
filtering devices may mean that filtered
air is vented to baghouses or other
capture/retention devices, thereby
lessening the potential release of
airborne emissions to the external
environment. The use of air-tight
enclosures will prevent the release of
emissions to the general environment.
This is also true where devices such as
portable saws with local exhaust
ventilation and capture devices.are used
for cutting asbestos products. Although
such collection devices will increase the
amount of disposable waste where they . are implemented, it is difficult to
quantify the degree to which this will
occur. No significant adverse effect on
air quality is expected to occur as a
result of the final rule;
The use of wet methods and processes
' will also reduce the level of ambient
emissions. The use of. vacuums and
other recommended work practices for
cleanup and removal of fibers will
reduce the likelihoodof any
reentrainment of fibers into the
atmosphere, Potential wastewater
effluents resulting from these methods
and processes will also be alleviated
depending on the control method (e.g.,
HEPA vacuums, recirculation and reuse
of water) and disposal technique used -
(e.g., leak-tight containers).
The training of workers should
provide an incentive for the proper use
and handling of asbestos and asbestos-
containing products. Training also has
the potential to impact on the discharge
and disposal of asbestos materials into
the environment.
Finally, the revised rule, as well as the
EPA proposed ban on asbestos, is likely
to encourage the research, development
anduse of suitable substitutes.
..
IX. Standards Recommended to OSHA by Interested Parties
In the course of this rulemaking,, several interested parties have developed and submitted to OSHA recommended standards for controlling occupational exposures to asbestos in various workplace settings. Among the organizations and entities submitting such standards were OSHA'b Advisory Committee on Construction Safety and Health (hereafter called CACOSH or the Advisory Committee), which provided a number of relevant documents for the record, the Organization of Resource Counselors, Inc. (ORC), the Building and Construction Trades Department (BCTD) of the American Federation of Labor-Congress of Industrial Organizations (AFL-CIO), and the Asbestos Information Association of North America (AIA/NA).
OSHA has benefltted greatly from the recommendations and regulatory suggestions of these groups, and has incorporated many of their recommended approaches into the requirements of the revised standards for general industry and construction. Specific regulatory requirements recommended by these commenters are discussed in the Summary arid Explanation sections of the preamble, as appropriate. Specific recommendations. made to OSHA by CAdOSH. the AIA/ NA, and the BCTD are described in Section XI of this preamble (the Summary and Explanation for the revised rule for the construction industry), while specific requirements recommended by the ORC are described in Section X, the Summary and Explanation for maritime and general industry.
The paragraphs below briefly describe the standards recommended by these groups, concentrating on the general approach adopted by each organization in developing its . recommended standard. In addition, OSHA's response to these recommendations and the Agency's rationale for accepting, modifying, or rejecting the approaches recommended are discussed.
RecommendedStandardfor General Industry
the ORC developed a standard that it recommended to OSHA to control occupational exposures to asbestos in the industry sectors predominantly represented by its members (i.e., general industry and maritime). The standanl recommended by the ORC (Ex. 91-10) is. generally similar to the revised standard being promulgated by OSHA for general industry. For example, the ORC
recommended requirements for monitoring; medical surveillance, recordkeeping, protective clothing, employee training, and signs and labels that are nearly identical to those of OSHA's revised general industry rule. However, the ORC's recommended standard differs substantially from the revised rule in one major respect: the ORC recommends that OSHA adopt two permissible concentrations for exposure to-asbestoB, a permissible airborne concentration (PAC) and a permissible exposure limit (PEL) that governs actual in-lung employee exposure. The ORC recommended a PAC of 0.5 f/cc or less, and a PEL of 0.2 f/cc. ORC defines a PAC as the "ambient worksite concentration" or maximum 8-houf timeweighted average concentration in "which any employee may work;" ORC assumes that, if engineering controls and work practices are not sufficient to reduce the ambient concentration to this level, employees would be required to wear respiratory protection having a protection factor adequate to do so. Thus, ORC's definition of a PAC is consistent with OSHA's traditional definition of a permissible exposure limit (PEL). The ORC's definition of PEL, however, differs markedly from OSHA's. ORC states that:
The eight hour time weighted average airborne concentration of asbestos fibers, to which any employee may be exposed shall not exceed 0.2 fibers (inhaled into the lungs) per cubic centimeter of air (Ex. 93-10). `
OSHA has not adopted ORC's twopronged approach to exposure limits, for several reasons. First, OSHA has traditionally defined PELs andemployee exposures as the airborne concentration of a contaminant measured without regard to. the use ofrespirators. The . Agency has consistently used this definition of exposure because airborne concentrations, in contrast to in-lung concentrations, are easy to control and measure, and limits based on such concentrations are comparatively easy' to enforce. In addition, employers are able to determine, by means of established industrial hygiene procedures and controls such as employee monitoring, leak detection systems, continuous alarms, and the use of engineering controls and work practices, what the actual exposures of their employees are. OSHA does not believe that the cause of occupational safety and health would be well served by basing an exposure limit on ah endpoint' that is as subject to individual variability, as dependent on individual and group behavior, and as difficult to enforce and administer as the in-lung
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