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STANDARDS FOR EXPOSURE TO AIRBORNE CONTAMINANTS

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Title: STANDARDS FOR EXPOSURE TO AIRBORNE CONTAMINANTS


1
STANDARDS FOR EXPOSURE TO
AIRBORNE CONTAMINANTS
Yves Alarie, Ph.D Professor Emeritus
University of Pittsburgh,USA
2
A. STANDARDS OR GUIDELINES A variety of standards
have been promulgated. Some are Federal
standards, while others are guidelines
promulgated by different groups. Table 18
provides a summary and the definition of the
most important. a) National Ambient Air Quality
Standards (NAAQS). Established by EPA, following
a review of the literature on a particular
substance. The review is published as an "Air
Quality Criteria Document" and readily available
in libraries. The current NAAQS are listed in
Table 19.
3
b) Threshold Limit Values (TLV) Biological
Exposure Indices (BEI). These are established by
the American Conference of Governmental
Industrial Hygienists (ACGIH) which was
established in 1938. It started issuing exposure
guidelines in 1946 for a small number of
industrial chemicals and there is a TLV for about
600 industrial chemicals. Each year it published
a booklet (1) listing those values. This booklet
is available from Executive Secretary ACGIH 6500
Glenway Avenue, Building D-7 Cincinnati, Ohio
45211-4438
4
More recently the ACGIH has introduced Biological
Exposure Indices (BEIs) as reference values
intended as guidelines for evaluation of
potential health hazards in the practice of
industrial hygiene. These, unlike TLVs which
refer to an air concentration, are for amount of
the chemical or its metabolite in blood, urine,
exhaled air, etc. There are 34 established
and/or proposed BEIs.
5

Both TLVs and BEIs are established after a
literature review, much more extensive for BEIs
than for TLVs and this review is published.66
In this publication you can find the basis for
establishing a TLV or BEI. Many TLVs have been
recently reviewed and much more extensive
documentation is now available. Also there have
been obvious changes over the years as to what
the committee members regard as an adverse
health effect and what "most workers" means.
Twenty years ago "most workers was about 85.
Now I don't know.
6
  • It should be kept in mind that these values
    are guidelines, developed initially for Normal,
    Healthy, Adult, Male, not female and certainly
    not pregnant females.
  • Before you can use these values you should
    read the "Preface" which is now 10 pages long in
    the booklet. Also you should read the
    Documentation for each substance that you are
    interested in.

7
  • c) Permissible Exposure Limit ( PEL).
  • These are established by the Occupational
    Safety and Health Administration (OSHA). They
    are THE LAW.
  • In 1970, OSHA used the TLVs values published
    in 1968 by the ACGIH and made those values PELs.

8
  • In 1989, OSHA revised its list of PEL by
    adopting the ACGIH 1987-88 TLVs with a few
    exceptions. You can obtain these from
  • "NIOSH Pocket Guide to Chemical Hazards, June
    1990"67. This publication contains a variety of
    other information for all the listed chemicals
    and is very useful to have, or as reprinted68.
    However, this revision was challenged in court
    and reversed.
  • See Table 18.

9
  • d) Recommended Exposure Level (REL).
  • The National Institute of Occupational Safety
    and Health (NIOSH) develop these for the
    workplace and transmits them to OSHA and the Mine
    Safety and Health Administration (MSHA) for use
    in promulgating legal standards i.e., PEL. For
    each chemical there is a "Criteria for a
    Recommended Standard" document. There are about
    120 of these documents available in libraries.
    They are a good source of information, not only
    on the toxicity of the chemical but also work
    practices, medical surveillance, protective
    equipment, etc. Unfortunately they are now out
    of date.

10
  • e) Air Toxics.
  • These are more recent and established by each
    State. They are ambient air criteria for the
    general population. A variety of approaches have
    been taken. A popular one is to take the PEL and
    divide it by some factor to take into account the
    fact that the general population would be exposed
    24 hrs/day and 7 days/week instead of the PEL or
    TLV which is for 8 hrs/day and 5 days/week. Then
    you can throw in some safety factors of 10 and
    another safety factor of 10 if there is any rumor
    that one rat somewhere got cancer. You end up
    with a number. Nonsense.

11
  • B. ESTABLISHING A TLV OR PEL
  • a) Types of Data.
  • There is no established protocol to develop a
    TLV or PEL. The types of data assembled to
    arrive at a decision will include the following
  • - Human exposures, laboratory
    experiments
  • - Human exposures, on the job
  • - Human exposures, accidental exposures
  • - Animal exposures

12
  • b) Types of Effect.
  • i) Health Hazard
  • Any type of toxicological effect can be
    considered to establish a TLV or PEL. A review
    of the Documentation for TLV and the Lecture
    Notes of Dr. H. F. Smyth Jr. of the University of
    Pittsburgh was undertaken by OSHA to get an idea
    of the major health hazard categories used to
    establish TLVs. These are given in the Table.
    As you can see there are large differences, from
    nauseating odor to cancer. Therefore, when you
    see that a TLV for X is 10 ppm and a TLV for Y is
    100 ppm don't conclude that X is 10 times more
    toxic than Y. This is the worst mistake you can
    make.

13
  • ii) "Good Housekeeping"
  • - No TLV above 10 mg/m3 for any aerosol,
    including "nuisance or inert dust
  • - No TLV above 1,000 ppm for gases or vapors,
    except for CO2 (TLV 5,000 ppm) or for simple
    asphyxiants which are permitted up to 3
    (reduction of O2 content to 18) at sea level
    pressure (760 mmHg) or to an equivalent partial
    pressure of O2 of 135 mmHg.
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