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Asbestos Fibers and Other Elongate Mineral Particles: State of the ...

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not demonstrate any clear health risks associated<br />

with exposure to <strong>the</strong> nonasbestiform EMPs covered<br />

by <strong>the</strong> NIOSH “airborne asbestos fiber” definition.<br />

Whe<strong>the</strong>r or not to include EMPs from nonasbesti<br />

form analogs <strong>of</strong> <strong>the</strong> asbestos minerals<br />

in federal regulatory asbestos policies has been<br />

<strong>the</strong> subject <strong>of</strong> long-st<strong>and</strong>ing debate. The exposure-related<br />

toxicity <strong>and</strong> health effects associated<br />

with <strong>the</strong> various morphologies (e.g., acicular,<br />

prismatic) <strong>of</strong> <strong>the</strong> nonasbestiform analogs <strong>of</strong><br />

<strong>the</strong> asbestos minerals continue to be a central<br />

point in <strong>the</strong> debate. In 1986, OSHA revised its<br />

asbestos st<strong>and</strong>ard <strong>and</strong> included nonasbestiform<br />

anthophyllite, tremolite, <strong>and</strong> actinolite (ATA)<br />

as covered minerals within <strong>the</strong> scope <strong>of</strong> <strong>the</strong> revised<br />

st<strong>and</strong>ard [OSHA 1986]. OSHA’s decision<br />

to include nonasbestiform ATA proved controversial.<br />

In a 1990 proposal to reverse this revision,<br />

OSHA [1990] noted that <strong>the</strong>re were “a<br />

number <strong>of</strong> studies which raise serious questions<br />

about <strong>the</strong> potential health hazard from occupational<br />

exposure to nonasbestiform tremolite,<br />

anthophyllite <strong>and</strong> actinolite,” but that <strong>the</strong> “current<br />

evidence is not sufficiently adequate for OSHA to<br />

conclude that <strong>the</strong>se mineral types pose a health<br />

risk similar in magnitude or type to asbestos.”<br />

In <strong>the</strong> preamble to <strong>the</strong> final rule removing<br />

nonasbestiform ATA from its asbestos st<strong>and</strong>ard,<br />

OSHA [1992] stated that:<br />

20<br />

…various uncertainties in <strong>the</strong> data** <strong>and</strong><br />

a body <strong>of</strong> data showing no carcinogenic effect,<br />

do not allow <strong>the</strong> Agency to perform<br />

qualitative or quantitative risk assessments<br />

concerning occupational exposures. Fur<strong>the</strong>r,<br />

<strong>the</strong> subpopulations <strong>of</strong> nonasbestiform<br />

** OSHA was referring to <strong>the</strong> scientific data on which<br />

NIOSH based its own carcinogenic health effect recommendation<br />

to OSHA.<br />

ATA which, based on mechanistic <strong>and</strong> toxicological<br />

data, may be associated with a<br />

carcinogenic effect, do not appear to present<br />

an occupational risk. Their presence in<br />

<strong>the</strong> workplace is not apparent from <strong>the</strong> record<br />

evidence.<br />

In its 2005 proposed rule for asbestos, MSHA<br />

stated that substantive changes to its asbestos<br />

definition were beyond <strong>the</strong> scope <strong>of</strong> <strong>the</strong> proposed<br />

rule <strong>and</strong> chose to retain its definition <strong>of</strong><br />

asbestos, which “does not include nonfibrous<br />

or nonasbestiform minerals” [MSHA 2005].<br />

These decisions are reflected in MSHA’s final<br />

rule published in 2008 [MSHA 2008]. In formal<br />

comments during <strong>the</strong> rulemaking process,<br />

NIOSH agreed with MSHA’s decision not<br />

to modify its asbestos definition in <strong>the</strong> current<br />

rulemaking, stating that “NIOSH is presently<br />

re-evaluating its definition <strong>of</strong> asbestos <strong>and</strong><br />

nonasbestiform minerals, <strong>and</strong> will work with<br />

o<strong>the</strong>r agencies to assure consistency to <strong>the</strong> extent<br />

possible” [NIOSH 2005]. In <strong>the</strong> interim,<br />

<strong>the</strong> following subsections provide more detail<br />

on <strong>the</strong> three elements comprising NIOSH’s rationale<br />

for recommending in 1990 that nonasbestiform<br />

analogs <strong>of</strong> <strong>the</strong> asbestos minerals be<br />

encompassed by <strong>the</strong> REL.<br />

2.7.1.1.1 Epidemiological Studies<br />

The first element <strong>of</strong> NIOSH’s rationale for recommending<br />

in 1990 that nonasbestiform analogs<br />

<strong>of</strong> <strong>the</strong> asbestos minerals be encompassed<br />

by <strong>the</strong> REL related to evidence from epidemiological<br />

studies.<br />

A number <strong>of</strong> epidemiological studies have been<br />

conducted to evaluate <strong>the</strong> health risk to workers<br />

reported to be exposed to EMPs. Epidemiological<br />

studies have been conducted in <strong>the</strong><br />

Governeur talc district <strong>of</strong> upstate New York in<br />

NIOSH CIB 62 • <strong>Asbestos</strong>

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