The Occupational Safety and Health Act of 1970 (Act) delegates
broad authority to the Secretary of Labor (Secretary) to promulgate
standards to ensure safe and healthful working conditions for the
Nation's workers (the Occupational Safety and Health Administration
(OSHA) being the agency responsible for carrying out this
authority). Section 3(8) of the Act defines an "occupational safety
and health standard" as a standard that is "reasonably necessary or
appropriate to provide safe or healthful employment." Where toxic
materials or harmful physical agents are concerned, a standard must
also comply with § 6(b)(5), which directs the Secretary to
"set the standard which most adequately assures, to the extent
feasible, on the basis of the best available evidence, that no
employee will suffer material impairment of health or functional
capacity."
When the toxic material or harmful physical agent to be
regulated is a carcinogen, the Secretary has taken the position
that no safe exposure level can be determined, and that § 6(b)(5)
requires him to set an exposure limit at the lowest technologically
feasible level that will not impair the viability of the industries
regulated. In this case, after having determined that there is a
causal connection between benzene (a toxic substance used in
manufacturing such products as motor fuels, solvents, detergents,
and pesticides) and leukemia (a cancer of the white blood cells),
the Secretary promulgated a standard reducing the permissible
exposure limit on airborne concentrations of benzene from the
consensus standard of 10 parts benzene per million parts of air (10
ppm) to 1 ppm, and prohibiting dermal contact with solutions
containing benzene. On preenforcement review, the Court of Appeals
held the standard invalid because it was based on findings
unsupported by the administrative record. The court concluded that
OSHA had exceeded its standard-setting authority because it had not
been shown that the 1 ppm exposure limit was "reasonably necessary
or appropriate to provide safe and healthful employment" as
required by § 3(8), and that
Page 448 U. S. 608
§ 6(b)(5) did not give OSHA the unbridled discretion to adopt
standards designed to create absolutely risk-free workplaces,
regardless of cost.
Held: The judgment is affirmed. Pp.
448 U. S.
630-662;
448 U. S.
667-671;
448 U. S.
672-688.
581 F.2d 493, affirmed.
MR. .JUSTICE STEVENS, joined by MR. CHIEF JUSTICE BURGER, MR.
.JUSTICE STEWART, and MR. JUSTICE POWELL, concluded that the
standard in question is invalid. Pp.
448 U. S.
630-652,
448 U. S.
658-659.
(a) The Court of Appeals was correct in refusing to enforce the
1 ppm exposure limit on the ground that it was not supported by
appropriate findings. OSHA's rationale for lowering the permissible
exposure limit from 10 ppm to 1 ppm was based not on any finding
that leukemia has ever been caused by exposure to 10 ppm of
benzene, and that it will
not be caused by exposure to 1
ppm, but, rather, on a series of assumptions indicating that some
leukemia might result from exposure to 10 ppm, and that the number
of cases might be reduced by lowering the exposure level to 1 ppm.
Pp.
448 U. S.
630-638.
(b) By empowering the Secretary to promulgate standards that are
"reasonably necessary or appropriate to provide safe or healthful
employment and places of employment" as required by § 3(8), the Act
implies that, before promulgating any standard, the Secretary must
make a finding that the workplaces in question are not safe. But
"safe" is not the equivalent of "risk-free." A workplace can hardly
be considered "unsafe" unless it threatens the workers with a
significant risk of harm. Therefore, before the Secretary can
promulgate
any permanent health or safety standard, he
must make a threshold finding that the place of employment is
unsafe in the sense that significant risks are present and can be
eliminated or lessened by a change in practices. This requirement
applies to permanent standards promulgated pursuant to § 6(b)(5),
as well as to other types of permanent standards, there being no
reason why § 3(8)'s definition of a standard should not be deemed
incorporated by reference into § 6(b)(5). Moreover, requiring the
Secretary to make a threshold finding of significant risk is
consistent with the scope of his regulatory power under § 6(b)(5)
to promulgate standards for "toxic materials" and "
harmful
physical agents." This interpretation is supported by other
provisions of the Act, such as § 6(g), which requires the
Secretary, in determining the priority for establishing standards,
to give due regard to the urgency of the need for mandatory safety
and health standards for particular industries or workplaces, and §
6(b)(8), which requires the Secretary, when he substantially alters
an
Page 448 U. S. 609
existing consensus standard, to explain how the new rule will
"better effectuate" the Act's purposes. Pp.
448 U. S.
639-646.
(c) The Act's legislative history also supports the conclusion
that Congress was concerned not with absolute safety, but with the
elimination of significant harm. Pp. 646-652.
(d) Where the Secretary relied on a special policy for
carcinogens that imposed the burden on industry of proving the
existence of a safe level of exposure, thereby avoiding his
threshold responsibility of establishing the need for more
stringent standards, he exceeded his power. Pp.
448 U. S.
658-659.
MR. JUSTICE STEVENS, joined by MR. CHIEF JUSTICE BURGER and MR.
JUSTICE STEWART, also concluded that:
1. The burden was on OSHA to show, on the basis of substantial
evidence, that it is at least more likely than not that long-term
exposure to 10 ppm of benzene presents a significant risk of
material health impairment. Here, OSHA did not even attempt to
carry such burden of proof. Imposing such a burden on OSHA will not
strip it of its ability to regulate carcinogens, nor will it
require it to wait for deaths to occur before taking any action.
The requirement that a "significant" risk be identified is not a
mathematical straitjacket; OSHA is not required to support its
finding that a significant risk exists with anything approaching
scientific certainty; and the record in this case and OSHA's own
rulings on other carcinogens indicate that there are a number of
ways in which OSHA can make a rational judgment about the relative
significance of the risks associated with exposure to a particular
carcinogen. Pp.
448 U. S.
652-658.
2. OSHA did not make the required finding with respect to the
dermal contact ban that the ban was "reasonably necessary and
appropriate" to remove a significant risk of harm from such
contact, but, rather, acted on the basis of the absolute, no-risk
policy that it applies to carcinogens under the assumptions not
only that benzene in small doses is a carcinogen but also that it
can be absorbed through the skin in sufficient amounts to present a
carcinogenic risk. These assumptions are not a proper substitute
for the findings of significant risk of harm required by the Act.
Pp.
448 U. S.
659-662.
MR. JUSTICE POWELL, agreeing that neither the airborne
concentration standard nor the dermal contact standard satisfied
the Act's requirements, would not hold that OSHA did not even
attempt to carry its burden of proof on the threshold question
whether exposure to benzene at 10 ppm presents a significant risk
to human health. He concluded that, even assuming OSHA had met such
burden, the Act also requires OSHA to determine that the economic
effects of its standard bear a
Page 448 U. S. 610
reasonable relationship to the expected benefits. A standard is
neither "reasonably necessary" nor "feasible," as required by the
Act, if it calls for expenditures wholly disproportionate to the
expected health and safety benefits. Here, although OSHA did find
that the "substantial costs" of the benzene regulations were
justified, the record contains neither adequate documentation of
this conclusion nor any evidence that OSHA weighed the relevant
considerations. The agency simply announced its finding of cost
justification without explaining the method by which it determined
that the benefits justified the costs and their economic effects.
Pp.
448 U. S.
667-671.
MR. JUSTICE REHNQUIST would invalidate, as constituting an
invalid delegation of legislative authority to the Secretary, the
relevant portion of § 6(b)(5) of the Act as it applies to any toxic
substance or harmful physical agent for which a safe level is,
according to the Secretary, unknown or otherwise "infeasible." In
the case of such substances, the language of § 6(b)(5) gives the
Secretary absolutely no indication where on the continuum of
relative safety he should set the standard. Nor is there anything
in the legislative history, the statutory context, or any other
source traditionally examined by this Court, that provides
specificity to the feasibility criterion in § 6(b)(5). Pp.
448 U. S.
672-688.
STEVENS, J., announced the judgment of the Court and delivered
an opinion, in which BURGER, C.J., and STEWART, J., joined, and in
Parts I, II, III-A, III-B, III-C, and III-E of which POWELL, J.,
joined. BURGER, C.J., filed a concurring opinion,
post, p.
448 U. S. 662.
POWELL, J., filed an opinion concurring in part and concurring in
the judgment,
post, p.
448 U. S. 664.
REHNQUIST, J., filed an opinion concurring in the judgment,
post, p.
448 U. S. 671.
MARSHALL, J., filed a dissenting opinion, in which BRENNAN, WHITE,
and BLACKMUN, JJ., joined,
post, p.
448 U. S.
688.
Page 448 U. S. 611
MR. JUSTICE STEVENS announced the judgment of the Court and
delivered an opinion, in which THE CHIEF JUSTICE and MR. JUSTICE
STEWART joined and in Parts I, II, III-A, III-B, III-C, and III-E
of which MR. JUSTICE POWELL joined.
The Occupational Safety and Health Act of 1970 (Act), 84 Stat.
1590, 29 U.S.C. § 651
et seq., was enacted for the purpose
of ensuring safe and healthful working conditions for every working
man and woman in the Nation. This litigation concerns a standard
promulgated by the Secretary of Labor to regulate occupational
exposure to benzene, a substance which has been shown to cause
cancer at high exposure levels. The principal question is whether
such a showing is a sufficient basis for a standard that places the
most stringent limitation on exposure to benzene that is
technologically and economically possible.
The Act delegates broad authority to the Secretary to promulgate
different kinds of standards. The basic definition
Page 448 U. S. 612
of an "occupational safety and health standard" is found in §
3(8), which provides:
"The term 'occupational safety and health standard' means a
standard which requires conditions, or the adoption or use of one
or more practices, means, methods, operations, or processes,
reasonably necessary or appropriate to provide safe or healthful
employment and places of employment."
84 Stat. 1591, 29 U.S.C. § 652(8).
Where toxic materials or harmful physical agents are concerned,
a standard must also comply with § 6(b)(5), which provides:
"The Secretary, in promulgating standards dealing with toxic
materials or harmful physical agents under this subsection, shall
set the standard which most adequately assures, to the extent
feasible, on the basis of the best available evidence, that no
employee will suffer material impairment of health or functional
capacity even if such employee has regular exposure to the hazard
dealt with by such standard for the period of his working life.
Development of standards under this subsection shall be based upon
research, demonstrations, experiments, and such other information
as may be appropriate. In addition to the attainment of the highest
degree of health and safety protection for the employee, other
considerations shall be the latest available scientific data in the
field, the feasibility of the standards, and experience gained
under this and other health and safety laws."
84 Stat. 1594, 29 U.S.C. § 655(b)(5). [
Footnote 1]
Page 448 U. S. 613
Wherever the toxic material to be regulated is a carcinogen, the
Secretary has taken the position that no safe exposure level can be
determined, and that § 6(b)(5)requires him to set an exposure limit
at the lowest technologically feasible level that will not impair
the viability of the industries regulated. In this case, after
having determined that there is a causal connection between benzene
and leukemia (a cancer of the white blood cells), the Secretary set
an exposure limit on airborne concentrations of benzene of one part
benzene per million parts of air (1 ppm), regulated dermal and eye
contact with solutions containing benzene, and imposed complex
monitoring and medical testing requirements on employers whose
workplaces contain 0.5 ppm or more of benzene. 29 CFR §§
1910.1028(c), (e) (1979).
On preenforcement review pursuant to 29 U.S.C. § 655(f), the
United States Court of Appeals for the Fifth Circuit held the
regulation invalid.
American Petroleum Institute v. OSHA,
581 F.2d 493 (1978). The court concluded that the Occupational
Safety and Health Administration (OSHA) [
Footnote 2] had exceeded its standard-setting authority
because it had not shown that the new benzene exposure limit was
"reasonably necessary or appropriate to provide safe or healthful
employment" as required by § 3(8), [
Footnote 3] and because § 6(b)(5)
Page 448 U. S. 614
does "not give OSHA the unbridled discretion to adopt standards
designed to create absolutely risk-free workplaces regardless of
costs." [
Footnote 4] Reading
the two provisions together, the Fifth Circuit held that the
Secretary was under a duty to determine whether the benefits
expected from the new standard bore a reasonable relationship to
the costs that it imposed.
Id. at 503. The court noted
that OSHA had made an estimate of the costs of compliance, but that
the record lacked substantial evidence of any discernible benefits.
[
Footnote 5]
We agree with the Fifth Circuit's holding that § 3(8) requires
the Secretary to find, as a threshold matter, that the
Page 448 U. S. 615
toxic substance in question poses a significant health risk in
the workplace, and that a new, lower standard is therefore
"reasonably necessary or appropriate to provide safe or healthful
employment and places of employment." Unless and until such a
finding is made, it is not necessary to address the further
question whether the Court of Appeals correctly held that there
must be a reasonable correlation between costs and benefits, or
whether, as the federal parties argue, the Secretary is then
required by § 6(b)(5) to promulgate a standard that goes as far as
technologically and economically possible to eliminate the
risk.
Because these are unusually important cases of first impression,
we have reviewed the record with special care. In this opinion, we
(1) describe the benzene standard, (2) analyze the Agency's
rationale for imposing a 1 ppm exposure limit, (3) discuss the
controlling legal issues, and (4) comment briefly on the dermal
contact limitation.
I
Benzene is a familiar and important commodity. It is a
colorless, aromatic liquid that evaporates rapidly under ordinary
atmospheric conditions. Approximately 11 billion pounds of benzene
were produced in the United States in 1976. Ninety-four percent of
that total was produced by the petroleum and petrochemical
industries, with the remainder produced by the steel industry as a
byproduct of coking operations. Benzene is used in manufacturing a
variety of products, including motor fuels (which may contain as
much as 2% benzene), solvents, detergents, pesticides, and other
organic chemicals. 43 Fed.Reg. 5918 (1978).
The entire population of the United States is exposed to small
quantities of benzene, ranging from a few parts per billion to 0.5
ppm, in the ambient air. Tr. 1029-1032. Over one million workers
are subject to additional low-level exposures as a consequence of
their employment. The majority of these employees work in gasoline
service stations, benzene
Page 448 U. S. 616
production (petroleum refineries and coking operations),
chemical processing, benzene transportation, rubber manufacturing,
and laboratory operations. [
Footnote 6]
Benzene is a toxic substance. Although it could conceivably
cause harm to a person who swallowed or touched it, the principal
risk of harm comes from inhalation of benzene vapors. When these
vapors are inhaled, the benzene diffuses through the lungs and is
quickly absorbed into the blood.
Page 448 U. S. 617
Exposure to high concentrations produces an almost immediate
effect on the central nervous system. Inhalation of concentrations
of 20,000 ppm can be fatal within minutes; exposures in the range
of 250 to 500 ppm can cause vertigo, nausea, and other symptoms of
mild poisoning. 43 Fed.Reg. 5921 (1978). Persistent exposures at
levels above 250 ppm may lead to blood deficiencies and diseases of
the blood-forming organs, including aplastic anemia, which is
generally fatal.
Industrial health experts have long been aware that exposure to
benzene may lead to various types of nonmalignant diseases. By
1948, the evidence connecting high levels of benzene to serious
blood disorders had become so strong that the Commonwealth of
Massachusetts imposed a 35 ppm limitation on workplaces within its
jurisdiction. In 1969, the American National Standards
Institute(ANSI) adopted a national consensus standard of 10 ppm
averaged over an 8-hour period, with a ceiling concentration of 25
ppm for 10-minute periods or a maximum peak concentration of 50
ppm.
Id. at 5919. In 1971, after the Occupational Safety
and Health Act was passed, the Secretary adopted this consensus
standard as the federal standard, pursuant to 29 U.S.C. § 655(a).
[
Footnote 7]
Page 448 U. S. 618
As early as 1928, some health experts theorized that there might
also be a connection between benzene in the workplace and leukemia.
[
Footnote 8] In the late 1960's
and early 1970's a number of epidemiological studies were published
indicating that workers exposed to high concentrations of benzene
were subject to a significantly increased risk of leukemia.
[
Footnote 9] In a 1974 report
recommending a permanent standard for benzene, the National
Institute for Occupational Safety and Health
Page 448 U. S. 619
(NIOSH), OSA's research arm, [
Footnote 10] noted that these studies raised the
"distinct possibility" that benzene caused leukemia. But, in light
of the fact that all known cases had occurred at very high exposure
levels, NIOSH declined to recommend a change in the 10 ppm
standard, which it considered sufficient to protect against
nonmalignant diseases. NIOSH suggested that further studies were
necessary to determine conclusively whether there was a link
between benzene and leukemia and, if so, what exposure levels were
dangerous. [
Footnote 11]
Between 1974 and 1976, additional studies were published which
tended to confirm the view that benzene can cause leukemia, at
least when exposure levels are high. [
Footnote 12] In an
Page 448 U. S. 620
August, 1976, revision of its earlier recommendation, NIOSH
stated that these studies provided "conclusive" proof of a causal
connection between benzene and leukemia. 1 Record, Ex 2-5, p. 100.
Although it acknowledged that none of the intervening studies had
provided the dose-response data it had found lacking two years
earlier,
id. at 9, NIOSH nevertheless recommended that the
exposure limit be set as low as possible. As a result of this
recommendation, OSHA contracted with a consulting firm to do a
study on the costs to industry of complying with the 10 ppm
standard then in effect, or, alternatively, with whatever standard
would be the lowest feasible. Tr. 505-506.
In October 1976, NIOSH sent another memorandum to OSHA, seeking
acceleration of the rulemaking process and "strongly" recommending
the issuance of an emergency temporary standard pursuant to § 6(c)
of the Act, 29 U.S.C. § 655(C) [
Footnote 13] for benzene and two other chemicals believed
to
Page 448 U. S. 621
be carcinogens. NIOSH recommended that a 1 ppm exposure limit be
imposed for benzene. [
Footnote
14] 1 Record, Ex. 6. Apparently because of the NIOSH
recommendation, OSHA asked its consultant to determine the cost of
complying with a 1 pm standard, instead of with the "minimum
feasible" standard. Tr. 506-507. It also issued voluntary
guidelines for benzene, recommending that exposure levels be
limited to 1 ppm on an 8-hour time-weighted average basis wherever
possible. 2 Record, Ex. 44.
In the spring of 1976, NIOSH had selected two Pliofilm plants in
St Marys and Akron, Ohio, for an epidemiological study of the link
between leukemia and benzene exposure. In April, 1977, NIOSH
forwarded an interim report to OSHA indicating at least a five-fold
increase in the expected incidence of leukemia for workers who had
been exposed to benzene
Page 448 U. S. 622
at the two plants from 1940 to 1949. [
Footnote 15] The report submitted to OSHA erroneously
suggested that exposures in the two plants had generally been
between zero and 15 ppm during the period in question. [
Footnote 16] As a result of this new
evidence
Page 448 U. S. 623
and the continued prodding of NIOSH, 1 Record, Ex. 7, OSHA did
issue an emergency standard effective May 21, 1977, reducing the
benzene exposure limit from 10 ppm to 1 ppm, the ceiling for
exposures of up to 10 minutes from 25 ppm to 5 ppm, and eliminating
the authority for peak concentrations of 50 ppm. 42 Fed.Reg. 22516
(1977). In its explanation accompanying the emergency standard,
OSHA stated that benzene had been shown to cause leukemia at
exposures below 25 ppm and that, in light of its consultant's
report, it was feasible to reduce the exposure limit to 1 ppm.
Id. at 22517, 22521.
On May 19, 1977, the Court of Appeals for the Fifth Circuit
entered a temporary restraining order preventing the emergency
standard from taking effect. Thereafter, OSHA abandoned its efforts
to make the emergency standard effective, and instead issued a
proposal for a permanent standard patterned almost entirely after
the aborted emergency standard.
Id. at 27452.
In its published statement giving notice of the proposed
permanent standard, OSHA did not ask for comments as to whether or
not benzene presented a significant health risk at exposures of 10
ppm or less. Rather, it asked for comments as to whether 1 ppm was
the minimum feasible exposure limit. [
Footnote 17]
Ibid. As OSHA's Deputy Director of
Health Standards, Grover Wrenn, testified at the hearing, this
formulation
Page 448 U. S. 624
of the issue to be considered by the Agency was consistent with
OSHA's general policy with respect to carcinogens. [
Footnote 18] Whenever a carcinogen is
involved, OSHA will presume that no safe level of exposure exists
in the absence of clear proof establishing such a level, and will
accordingly set the exposure limit at the lowest level feasible.
[
Footnote 19] The proposed 1
ppm exposure
Page 448 U. S. 625
limit in this case thus was established not on the basis of a
proven hazard at 10 ppm, but rather on the basis of "OSHA's best
judgment at the time of the proposal of the feasibility of
compliance with the proposed standard by the [a]ffected
industries." Tr. 30. Given OSHA's cancer policy, it was, in fact,
irrelevant whether there was any evidence at all of a leukemia risk
at 10 ppm. The important point was that there was no evidence that
there was
not some risk, however small, at that level. The
fact that OSHA did not ask for comments on whether there was a safe
level of exposure for benzene was indicative of its further view
that a demonstration of such absolute safety simply could not be
made. [
Footnote 20]
Public hearings were held on the proposed standard, commencing
on July 19, 1977. The final standard was issued on February 10,
1978. 29 CFR § 1910.1028 (1979). [
Footnote 21] In its final form, the benzene standard is
designed to protect workers from whatever hazards are associated
with low-level benzene
Page 448 U. S. 626
exposures by requiring employers to monitor workplaces to
determine the level of exposure, to provide medical examinations
when the level rises above 0.5 ppm, and to institute whatever
engineering or other controls are necessary to keep exposures at or
below 1 ppm.
In the standard as originally proposed by OSHA, the employer's
duty to monitor, keep records, and provide medical examinations
arose whenever
any benzene was present in a workplace
covered by the rule. [
Footnote
22] Because benzene is omnipresent in small quantities, NIOSH
and the President's Council on Wage and Price Stability recommended
the use of an "action level" to trigger monitoring and medical
examination requirements. Tr. 1030-1032; App. 121-133. OSHA
accepted this recommendation, providing under the final standard
that, if initial monitoring discloses benzene concentrations below
0.5 ppm averaged over an 8-hour work day, no further action is
required unless there is a change in the company's practices.
[
Footnote 23] If exposures
are above the action
Page 448 U. S. 627
level, but below the 1 ppm exposure limit, employers are
required to monitor exposure levels on a quarterly basis and to
provide semiannual medical examinations for their exposed
employees. Neither the concept of an action level nor the specific
level selected by OSHA is challenged in this proceeding.
Whenever initial monitoring indicates that employees are subject
to airborne concentrations of benzene above 1 ppm averaged over an
8-hour workday, with a ceiling of 5 ppm for any 15-minute period,
employers are required to modify their plants or institute work
practice controls to reduce exposures within permissible limits.
Consistent with OSHA's general policy, the regulation does not
allow respirators to be used if engineering modifications are
technologically feasible. [
Footnote 24] Employers in this category are also required
to perform monthly monitoring so long as their workplaces remain
above 1 ppm, provide semiannual medical examinations to exposed
workers, post signs in and restrict access to "regulated areas"
where the permissible exposure limit is exceeded, and conduct
employee training programs where necessary.
The standard also places strict limits on exposure to liquid
Page 448 U. S. 628
benzene. As originally framed, the standard totally prohibited
any skin or eye contact with any liquid containing any benzene.
Ultimately, after the standard was challenged, OSHA modified this
prohibition by excluding liquids containing less than 0.5% benzene.
After three years, that exclusion will be narrowed to liquids
containing less than 0.1% benzene.
The permanent standard is expressly inapplicable to the storage,
transportation, distribution, sale, or use of gasoline or other
fuels subsequent to discharge from bulk terminals. [
Footnote 25] This exception is particularly
significant in light of the fact that over 795,000 gas station
employees, who are exposed to an average of 102,700 gallons of
gasoline (containing up to 2% benzene) annually, are thus excluded
from the protection of the standard. [
Footnote 26]
As presently formulated, the benzene standard is an expensive
way of providing some additional protection for a relatively small
number of employees. According to OSHA's figures, the standard will
require capital investments in engineering controls of
approximately $266 million, first-year operating costs (for
monitoring medical testing, employee training, and respirators) of
$187 million to $205 million and
Page 448 U. S. 629
recurring annual costs of approximately $34 million. [
Footnote 27] 43 Fed.Reg. 5934
(1978). The figures outlined in OSHA's explanation of the costs of
compliance to various industries indicate that only 35,000
employees would gain any benefit from the regulation in terms of a
reduction in their exposure to benzene. [
Footnote 28] Over two-thirds of these workers (24,450)
are employed in the rubber manufacturing industry. Compliance costs
in that industry are estimated to be rather low, with no capital
costs and initial operating expenses estimated at only $34 million
($1,390 per employee); recurring annual costs would also be rather
low, totaling less than $1 million. By contrast, the segment of the
petroleum refining industry that produces benzene would be required
to incur $24 million in capital costs and $600,000 in first-year
operating expenses to provide additional protection for 300 workers
($82,000 per employee), while the petrochemical industry would be
required to incur $20.9 million in capital costs and $1 million in
initial operating expenses for the benefit of 552 employees(
$39,675 per employee). [
Footnote
29]
Id. at 5936-5938.
Page 448 U. S. 630
Although OSHA did not quantify the benefits to each category of
worker in terms of decreased exposure to benzene, it appears from
the economic impact study done at OSHA's direction that those
benefits may be relatively small. Thus, although the current
exposure limit is 10 ppm, the actual exposures outlined in that
study are often considerably lower. For example, for the period
1970-1975 the petrochemical industry reported that, out of a total
of 496 employees exposed to benzene, only 53 were exposed to levels
between 1 and 5 ppm, and only 7 (all at the same plant) were
exposed to between 5 and 10 ppm. 1 Economic Impact Statement, p.
4-6, Table 4-2, 11 Record, Ex. 5A, p. 4-6, Table 4-2.
See also
id. Tables 4.3-4.8 (indicating sample exposure levels in
various industries).
II
The critical issue at this point in the litigation is whether
the Court of Appeals was correct in refusing to enforce the 1 ppm
exposure limit on the ground that it was not supported by
appropriate findings. [
Footnote
30]
Page 448 U. S. 631
Any discussion of the 1 ppm exposure limit must, of course,
begin with the Agency's rationale for imposing that limit.
[
Footnote 31] The written
explanation of the standard fills 14 pages of the printed appendix.
Much of it is devoted to a discussion of the voluminous evidence of
the adverse effects of exposure to benzene at levels of
concentration well above 10 ppm. This discussion demonstrates that
there is ample justification for regulating occupational exposure
to benzene and that the prior limit of 10 ppm, with a ceiling of 25
ppm (or a peak of 50 ppm) was reasonable. It does not, however,
provide direct support for the Agency's conclusion that the limit
should be reduced from 10 ppm to 1 ppm.
The evidence in the administrative record of adverse effects of
benzene exposure at 10 ppm is sketchy, at best. OSHA noted that
there was "no dispute" that certain nonmalignant blood disorders,
evidenced by a reduction in the level of red or white cells or
platelets in the blood, could result from exposures of 250 ppm. It
then stated that several studies had indicated that relatively
slight changes in normal blood values could result from exposures
below 25 ppm, and perhaps below 10 ppm. OSHA did not attempt to
make any estimate based on these studies of how significant the
risk of nonmalignant disease would be at exposures of 10 ppm or
less. [
Footnote 32] Rather,
it stated that, because of the lack of data concerning the linkage
between low-level exposures and blood abnormalities, it was
impossible to construct a dose-response
Page 448 U. S. 632
curve at this time. [
Footnote
33] OSHA did conclude, however, that the studies demonstrated
that the current 10 ppm exposure limit was inadequate to ensure
that no single worker would suffer a nonmalignant blood disorder as
a result of benzene exposure. Noting that it is "customary" to set
a permissible exposure limit by applying a safety factor of 10-100
to the lowest level at which adverse effects had been observed, the
Agency stated that the evidence supported the conclusion that the
limit should be set at a point "substantially less than 10 ppm"
even if benzene's leukemic effects were not considered. 43 Fed.Reg.
5924-5925 (1978). OSHA did not state, however, that the
nonmalignant effects of benzene exposure justified a reduction in
the permissible exposure limit to 1 ppm. [
Footnote 34]
OSHA also noted some studies indicating an increase in
chromosomal aberrations in workers chronically exposed to
Page 448 U. S. 633
concentrations of benzene "probably less than 25 ppm." [
Footnote 35] However, the Agency
took no definitive position as to what these aberrations meant in
terms of demonstrable health effects, and stated that no
quantitative dose-response relationship had yet been established.
Under these circumstances, chromosomal effects were categorized by
OSHA as an
"adverse biological event of serious concern which may pose or
reflect a potential health risk and, as such, must be considered in
the larger purview of adverse health effects associated with
benzene."
Id. at 5932-5934.
With respect to leukemia, evidence of an increased risk
(
i.e., a risk greater than that borne by the general
population) due to benzene exposures at or below 10 ppm was even
sketchier. Once OSHA acknowledged that the NIOSH study it had
relied upon in promulgating the emergency standard did not support
its earlier view that benzene had been shown to cause leukemia at
concentrations below 25 ppm,
see n 12,
supra, there was only one study that
provided any evidence of such an increased risk. That study,
conducted by the Dow Chemical Co., uncovered three leukemia deaths,
versus 0.2 expected deaths, out of a population of 594 workers; it
appeared that the three workers had never been exposed to more than
2 to 9 ppm of benzene. The authors of the study, however, concluded
that it could not be viewed as proof of a relationship between
low-level benzene exposure and leukemia because all three workers
had probably been occupationally exposed to a number of other
potentially carcinogenic chemicals at other points in their careers
and because no leukemia deaths had been uncovered among workers who
had been exposed to much higher levels of benzene. In its
explanation of the permanent standard, OSHA stated that the
possibility that these three leukemias had been caused by benzene
exposure could not be
Page 448 U. S. 634
ruled out and that the study, although not evidence of an
increased risk of leukemia at 10 ppm, was therefore "consistent
with the findings of many studies that there is an excess leukemia
risk among benzene exposed employees." 43 Fed.Reg. 5928 (1978). The
Agency made no finding that the Dow study, any other empirical
evidence, or any opinion testimony demonstrated that exposure to
benzene at or below the 10 ppm level had ever, in fact, caused
leukemia.
See 581 F.2d at 503, where the Court of Appeals
noted that OSHA was "unable to point to any empirical evidence
documenting a leukemia risk at 10 ppm. . . ."
In the end, OSHA's rationale for lowering the permissible
exposure limit to 1 ppm was based not on any finding that leukemia
has ever been caused by exposure to 10 ppm of benzene and that it
will
not be caused by exposure to 1 ppm, but rather on a
series of assumptions indicating that some leukemias might result
from exposure to 10 ppm and that the number of cases might be
reduced by reducing the exposure level to 1 ppm. In reaching that
result, the Agency first unequivocally concluded that benzene is a
human carcinogen. [
Footnote
36] Second, it concluded that industry had failed to prove that
there is a safe threshold level of exposure to benzene below which
no excess leukemia cases would occur. In reaching this conclusion,
OSHA rejected industry contentions that certain epidemiological
studies indicating no excess risk of leukemia among workers exposed
at levels below 10 ppm were sufficient to establish that the
threshold level of safe exposure was at or above
Page 448 U. S. 635
10 ppm. [
Footnote 37] It
also rejected an industry witness' testimony that a dose-response
curve could be constructed on the basis of the reported
epidemiological studies, and that this curve indicated that
reducing the permissible exposure limit from 10 to 1 ppm would
prevent, at most, one leukemia and one other cancer death every six
years. [
Footnote 38]
Third, the Agency applied its standard policy with respect to
carcinogens, [
Footnote 39]
concluding that, in the absence of definitive
Page 448 U. S. 636
proof of a safe level, it must be assumed that any level above
zero presents some increased risk of cancer. [
Footnote 40] As the federal parties point out in
their brief, there are a number of scientists and public health
specialists who subscribe to this view, theorizing that a
susceptible person may contract cancer from the absorption of even
one molecule of a carcinogen like benzene. Brief for Federal
Parties 18-19. [
Footnote
41]
Page 448 U. S. 637
Fourth, the Agency reiterated its view of the Act, stating that
it was required by § 6(b)(5) to set the standard either at the
level that has been demonstrated to be safe or at the lowest level
feasible, whichever is higher. If no safe level is established, as
in this case, the Secretary's interpretation of the statute
automatically leads to the selection of an exposure limit that is
the lowest feasible. [
Footnote
42] Because of benzene's importance to the economy, no one has
ever suggested that it would be feasible to eliminate its use
entirely, or to try to limit exposures to the small amounts that
are omnipresent. Rather, the Agency selected 1 ppm as a workable
exposure level,
see n 14,
supra, and then determined that compliance
with that level was technologically feasible, and that "the
economic impact of . . . [compliance] will not be such as to
threaten the financial welfare of the affected firms or the general
economy." 43 Fed.Reg. 5939 (1978). It therefore held that 1 ppm was
the minimum feasible exposure level within the meaning of § 6(b)(5)
of the Act.
Finally, although the Agency did not refer in its discussion of
the pertinent legal authority to any duty to identify the
anticipated benefits of the new standard, it did conclude that some
benefits were likely to result from reducing the exposure limit
from 10 ppm to 1 ppm. This conclusion was based, again, not on
evidence, but rather on the assumption that the risk of leukemia
will decrease as exposure levels decrease. Although the Agency had
found it impossible to construct a dose-response curve that would
predict with any accuracy the
Page 448 U. S. 638
number of leukemias that could be expected to result from
exposures at 10 ppm, at 1 ppm, or at any intermediate level, it
nevertheless "determined that the benefits of the proposed standard
are likely to be appreciable." [
Footnote 43] 43 Fed.Reg. 5941 (1978). In light of the
Agency's disavowal of any ability to determine the numbers of
employees likely to be adversely affected by exposures of 10 ppm,
the Court of Appeals held this finding to be unsupported by the
record. 581 F.2d at 503. [
Footnote 44]
It is noteworthy that at no point in its lengthy explanation did
the Agency quote or even cite § 3(8) of the Act. It made no finding
that any of the provisions of the new standard were "reasonably
necessary or appropriate to provide safe or healthful employment
and places of employment." Nor did it allude to the possibility
that any such finding might have been appropriate.
Page 448 U. S. 639
III
Our resolution of the issues in these cases turns, to a large
extent, on the meaning of and the relationship between § 3(8),
which defines a health and safety standard as a standard that is
"reasonably necessary and appropriate to provide safe or healthful
employment," and § 6(b)(5), which directs the Secretary, in
promulgating a health and safety standard for toxic materials,
to
"set the standard which most adequately assures, to the extent
feasible, on the basis of the best available evidence, that no
employee will suffer material impairment of health or functional
capacity. . . ."
In the Government's view, § 3(8)'s definition of the term
"standard" has no legal significance, or, at best, merely requires
that a standard not be totally irrational. It takes the position
that § 6(b)(5) is controlling, and that it requires OSHA to
promulgate a standard that either gives an absolute assurance of
safety for each and every worker or reduces exposures to the lowest
level feasible. The Government interprets "feasible" as meaning
technologically achievable at a cost that would not impair the
viability of the industries subject to the regulation. The
respondent industry representatives, on the other hand, argue that
the Court of Appeals was correct in holding that the "reasonably
necessary and appropriate" language of § 3(8), along with the
feasibility requirement of § 6(b)(5), requires the Agency to
quantify both the costs and the benefits of a proposed rule and to
conclude that they are roughly commensurate.
In our view, it is not necessary to decide whether either the
Government or industry is entirely correct. For we think it is
clear that § 3(8) does apply to all permanent standards promulgated
under the Act, and that it requires the Secretary, before issuing
any standard, to determine that it is reasonably necessary and
appropriate to remedy a significant risk of material health
impairment. Only after the Secretary has made the threshold
determination that such a risk exists
Page 448 U. S. 640
with respect to a toxic substance, would it be necessary to
decide whether § 6(b)(5) requires him to select the most protective
standard he can, consistent with economic and technological
feasibility, or whether, as respondents argue, the benefits of the
regulation must be commensurate with the costs of its
implementation. Because the Secretary did not make the required
threshold finding in these cases, we have no occasion to determine
whether costs must be weighed against benefits in an appropriate
case.
A
Under the Government's view, § 3(8), if it has any substantive
content at all, [
Footnote
45] merely requires OSHA to issue standards
Page 448 U. S. 641
that are reasonably calculated to produce a safer or more
healthy work environment. Tr. of Oral Arg 18, 20. Apart from this
minimal requirement of rationality, the Government argues that §
3(8) imposes no limits on the Agency's power, and thus would not
prevent it from requiring employers to do whatever would be
"reasonably necessary" to eliminate all risks of any harm from
their workplaces. [
Footnote
46] With respect to toxic substances and harmful physical
agents, the Government takes an even more extreme position. Relying
on § 6(b)(5)'s direction to set a standard "which most adequately
assures . . . that no employee will suffer material impairment of
health or functional capacity," the Government contends that the
Secretary is required to impose standards that either guarantee
workplaces that are free from any risk of material health
impairment, however small, or that come as close as possible to
doing so without ruining entire industries.
If the purpose of the statute were to eliminate completely and
with absolute certainty any risk of serious harm, we would agree
that it would be proper for the Secretary to interpret §§ 3(8) and
6(b)(5) in this fashion. But we think it is clear that the statute
was not designed to require employers to provide absolutely
risk-free workplaces whenever it is technologically feasible to do
so, so long as the cost is not great enough to destroy an entire
industry. Rather, both the language and structure of the Act, as
well as its legislative history, indicate that it was intended to
require the elimination, as far as feasible, of significant risks
of harm.
Page 448 U. S. 642
B
By empowering the Secretary to promulgate standards that are
"reasonably necessary or appropriate to provide safe or healthful
employment and places of employment," the Act implies that, before
promulgating any standard, the Secretary must make a finding that
the workplaces in question are not safe. But "safe" is not the
equivalent of "risk-free." There are many activities that we engage
in every day -- such as driving a car or even breathing city air --
that entail some risk of accident or material health impairment;
nevertheless, few people would consider these activities "unsafe."
Similarly, a workplace can hardly be considered "unsafe" unless it
threatens the workers with a significant risk of harm.
Therefore, before he can promulgate any permanent health or
safety standard, the Secretary is required to make a threshold
finding that a place of employment is unsafe -- in the sense that
significant risks are present and can be eliminated or lessened by
a change in practices. This requirement applies to permanent
standards promulgated pursuant to § 6(b)(5), as well as to other
types of permanent standards. For there is no reason why § 3(8)'s
definition of a standard should not be deemed incorporated by
reference into § 6(b)(5). The standards promulgated pursuant to §
6(b)(5) are just one species of the genus of standards governed by
the basic requirement. That section repeatedly uses the term
"standard" without suggesting any exception from, or qualification
of, the general definition; on the contrary, it directs the
Secretary to select "the standard" -- that is to say, one of
various possible alternatives that satisfy the basic definition in
§ 3(8) -- that is most protective. [
Footnote 47] Moreover, requiring the
Page 448 U. S. 643
Secretary to make a threshold finding of significant risk is
consistent with the scope of the regulatory power granted to him by
§ 6(b)(5), which empowers the Secretary to promulgate standards not
for chemicals and physical agents generally, but for
"
toxic materials" and "
harmful physical agents."
[
Footnote 48]
This interpretation of §§ 3(8) and 6(b)(5) is supported by the
other provisions of the Act. Thus, for example, § 6(g) provides, in
part, that,
"[i]n determining the priority for establishing standards under
this section, the Secretary shall give due regard to the urgency of
the need for mandatory safety and health standards for particular
industries, trades,
Page 448 U. S. 644
crafts, occupations, businesses, workplaces or work
environments."
The Government has expressly acknowledged that this section
requires the Secretary to undertake some cost-benefit analysis
before he promulgates any standard, requiring the elimination of
the most serious hazards first. [
Footnote 49] If such an analysis must precede the
promulgation of any standard, it seems manifest that Congress
intended, at a bare minimum, that the Secretary find a significant
risk of harm, and therefore a probability of significant benefits,
before establishing a new standard
Section 6(b)(8) lends additional support to this analysis. That
subsection requires that, when the Secretary substantially alters
an existing consensus standard, he must explain how the new rule
will "better effectuate" the purposes of the Act. [
Footnote 50] If this requirement was
intended to be more than a meaningless formality, it must be read
to impose upon the Secretary the duty to find that an existing
national consensus standard is not adequate to protect workers from
a continuing and significant risk of harm. Thus, in this case, the
Secretary was required to find that exposures at the current
permissible
Page 448 U. S. 645
exposure level of 10 ppm present a significant risk of harm in
the workplace.
In the absence of a clear mandate in the Act, it is unreasonable
to assume that Congress intended to give the Secretary the
unprecedented power over American industry that would result from
the Government's view of §§ 3(8) and 6(b)(5), coupled with OSHA's
cancer policy. Expert testimony that a substance is probably a
human carcinogen -- either because it has caused cancer in animals
or because individuals have contracted cancer following extremely
high exposures -- would justify the conclusion that the substance
poses some risk of serious harm, no matter how minute the exposure
and no matter how many experts testified that they regarded the
risk as insignificant. That conclusion would, in turn, justify
pervasive regulation, limited only by the constraint of
feasibility. In light of the fact that there are literally
thousands of substances used in the workplace that have been
identified as carcinogens or suspect carcinogens, the Government's
theory would give OSHA power to impose enormous costs that might
produce little, if any, discernible benefit. [
Footnote 51]
Page 448 U. S. 646
If the Government were correct in arguing that neither § 3(8)
nor § 6(b)(5) requires that the risk from a toxic substance be
quantified sufficiently to enable the Secretary to characterize it
as significant in an understandable way, the statute would make
such a "sweeping delegation of legislative power" that it might be
unconstitutional under the Court's reasoning in
A.L.A.
Schechter Poultry Corp. v. United States, 295 U.
S. 495,
295 U. S. 539,
and
Panama Refining Co. v. Ryan, 293 U.
S. 388. A construction of the statute that avoids this
kind of open-ended grant should certainly be favored.
C
The legislative history also supports the conclusion that
Congress was concerned not with absolute safety, but with the
elimination of significant harm. The examples of industrial hazards
referred to in the Committee hearings and debates all involved
situations in which the risk was unquestionably significant. For
example, the Senate Committee on Labor and Public Welfare noted
that byssinosis, a disabling lung disease caused by breathing
cotton dust, affected as many as 30% of the workers in carding or
spinning rooms in some American cotton mills and that as many as
100,000 active or retired workers were then suffering from the
disease. It also noted that statistics indicated that 20,000 out of
50,000 workers who had performed insulation work were likely to die
of asbestosis, lung cancer, or mesothelyioma as a result of
breathing asbestos fibers. Another example given of an occupational
health hazard that would be controlled by the Act was
betanaphthylamine, a "chemical so toxic that any exposure at all is
likely to cause the development of bladder cancer over a period of
years." S.Rep. No. 91-1282, pp. 3-4 (1970); Legislative History of
the Occupational Safety and Health Act of 1970 (Committee Print
compiled for the Senate Committee on Labor and Public Welfare), pp.
143-144 (1971) (hereafter Leg.Hist.).
Moreover, Congress specifically amended § 6(b)(5) to make
Page 448 U. S. 647
it perfectly clear that it does not require the Secretary to
promulgate standards that would assure an absolutely risk-free
workplace. Section 6(b)(5) of the initial Committee bill provided
that
"[t]he Secretary, in promulgating standards under this
subsection, shall set the standard which most adequately and
feasibly assures, on the basis of the best available evidence, that
no employee will suffer
any impairment of health or
functional capacity, or diminished life expectancy, even if such
employee has regular exposure to the hazard dealt with by such
standard for the period of his working life."
(Emphasis supplied.) S. 2193, 91st Cong., 2d Sess., p. 39
(1970), Leg.Hist. 242. On the floor of the Senate, Senator Dominick
questioned the wisdom of this provision, stating:
"How in the world are we ever going to live up to that? What are
we going to do about a place in Florida where mosquitoes are
getting at the employee -- perish the thought that there may be
mosquitoes in Florida? But there are black flies in Minnesota and
Wisconsin. Are we going to say that, if employees get bitten by
those for the rest of their lives, they will not have been done any
harm at all? Probably they will not be, but do we know?"
116 Cong.Rec. 36522 (1970), Leg.Hist. 345. He then offered an
amendment deleting the entire subsection. [
Footnote 52]
Page 448 U. S. 648
After discussions with the sponsors of the Committee bill,
Senator Dominick revised his amendment. Instead of deleting the
first sentence of § 6(b)(5) entirely, his new amendment limited the
application of that subsection to toxic materials and harmful
physical agents and changed "any" impairment of health to
"material" impairment. [
Footnote
53] In discussing this change, Senator Dominick noted that the
Committee's bill read as if a standard had to "assure that, no
matter what anybody was doing, the standard would protect him for
the rest of his life against any foreseeable hazard." Such an
"unrealistic standard," he stated, had not been intended by the
sponsors of the bill. Rather, he explained that the intention of
the bill as implemented by the amendment, was to require the
Secretary
"to use his best efforts to promulgate the best available
standards, and in so doing, . . . he should take into account that
anyone working in toxic agents and physical
Page 448 U. S. 649
agents which might be harmful may be subjected to such
conditions for the rest of his working life, so that we can get at
something which might not be toxic now, if he works in it a short
time, but, if he works in it the rest of his life, might be very
dangerous; and we want to make sure that such things are taken into
consideration in establishing standards."
116 Cong.Rec. at 37622-37623, Leg.Hist. 52-503. [
Footnote 54] Senator Williams, one of the
sponsors of the Committee bill, agreed with the interpretation, and
the amendment was adopted.
In their reply brief, the federal parties argue that the
Dominick amendment simply means that the Secretary is not required
to eliminate threats of insignificant harm; they argue that §
6(b)(5) still requires the Secretary to set standards that ensure
that not even one employee will be subject to any risk of serious
harm -- no matter how small that risk may be. [
Footnote 55]
Page 448 U. S. 650
This interpretation is at odds with Congress' express
recognition of the futility of trying to make all workplaces
totally risk-free. Moreover, not even OSHA follows this
interpretation of § 6(b)(5) to its logical conclusion. Thus, if
OSHA is correct that the only no-risk level for leukemia due to
benzene exposure is zero, and if its interpretation of § 6(b)(5) is
correct, OSHA should have set the exposure limit as close to zero
as feasible. But OSHA did not go about its task in that way.
Rather, it began with a 1 ppm level, selected at least in part to
ensure that employers would not be required to eliminate benzene
concentrations that were little greater than the so-called
"background" exposures experienced by the population at large.
See n.
14
supra. T hen, despite suggestions by some labor unions
that it was feasible for at least some industries to reduce
exposures to well below 1 ppm, [
Footnote 56] OSHA decided to apply the same limit to all,
largely as a matter of administrative convenience. 43 Fed.Reg. 5947
(1978).
OSHA also deviated from its own interpretation of § 6(b)(5) in
adopting an action level of 0.5 ppm below which monitoring and
medical examinations are not required. In light of OSHA's cancer
policy, it must have assumed that some employees would be at risk
because of exposures below 0.5 ppm. These employees would thus
presumably benefit from medical examinations, which might uncover
any benzene-related problems. OSHA's consultant advised the Agency
that it was technologically and economically feasible to require
that such examinations be provided. Nevertheless, OSHA adopted an
action level, largely because the insignificant benefits
Page 448 U. S. 651
of giving such examinations and performing the necessary
monitoring did not justify the substantial cost. [
Footnote 57]
OSHA's concessions to practicality in beginning with a 1 ppm
exposure limit and using an action level concept implicitly adopt
an interpretation of the statute as not requiring regulation of
insignificant risks. [
Footnote
58] It is entirely consistent with this interpretation to hold
that the Act also requires the Agency to limit its endeavors in the
standard-setting area to eliminating significant risks of harm.
Finally, with respect to the legislative history, it is
important to note that Congress repeatedly expressed its concern
about allowing the Secretary to have too much power over American
industry. Thus, Congress refused to give the Secretary the power to
shut down plants unilaterally because of an imminent danger,
see Whirlpool Corp. v. Marshall, 445 U. S.
1, and narrowly circumscribed the Secretary's power to
issue temporary emergency standards. [
Footnote 59] This effort by
Page 448 U. S. 652
Congress to limit the Secretary's power is not consistent with a
view that the mere possibility that some employee somewhere in the
country may confront some risk of cancer is a sufficient basis for
the exercise of the Secretary's power to require the expenditure of
hundreds of millions of dollars to minimize that risk.
D
Given the conclusion that the Act empowers the Secretary to
promulgate health and safety standards only where a significant
risk of harm exists, the critical issue becomes how to define and
allocate the burden of proving the significance of the risk in a
case such as this, where scientific knowledge is imperfect and the
precise quantification of risks is therefore impossible. The
Agency's position is that there is substantial evidence in the
record to support its conclusion that there is no absolutely safe
level for a carcinogen, and that, therefore, the burden is properly
on industry to prove, apparently beyond a shadow of a doubt, that
there is a safe level for benzene exposure. The Agency argues that,
because of the uncertainties in this area, any other approach would
render it helpless, forcing it to wait for the leukemia deaths that
it believes are likely to occur [
Footnote 60] before taking any regulatory action.
Page 448 U. S. 653
We disagree. As we read the statute, the burden was on the
Agency to show, on the basis of substantial evidence, that it is at
least more likely than not that long-term exposure to 10 ppm of
benzene presents a significant risk of material health impairment.
Ordinarily, it is the proponent of a rule or order who has the
burden of proof in administrative proceedings.
See 5
U.S.C. § 556(d). In some cases involving toxic substances, Congress
has shifted the burden of proving that a particular substance is
safe onto the party opposing the proposed rule. [
Footnote 61] The fact that Congress did not
follow this course in enacting the Occupational Safety and Health
Act indicates that it intended the Agency to bear the normal burden
of establishing the need for a proposed standard.
In this case, OSHA did not even attempt to carry its burden of
proof. The closest it came to making a finding that benzene
presented a significant risk of harm in the workplace was its
statement that the benefits to be derived from lowering the
permissible exposure level from 10 to 1 ppm were "likely" to be
"appreciable." The Court of Appeals held that this finding was not
supported by substantial evidence. Of greater importance, even if
it were supported by substantial evidence, such a finding would not
be sufficient to satisfy the Agency's obligations under the
Act.
The inadequacy of the Agency's findings can perhaps be
Page 448 U. S. 654
illustrated best by its rejection of industry testimony that a
dose-response curve can be formulated on the basis of current
epidemiological evidence, and that, even under the most
conservative extrapolation theory, current exposure levels would
cause at most two deaths out of a population of about 30,000
workers every six years.
See n 38,
supra. In rejecting this testimony, OSHA
made the following statement:
"In the face of the record evidence of numerous actual deaths
attributable to benzene-induced leukemia and other fatal blood
diseases, OSHA is unwilling to rely on the hypothesis that at most
two cancers every six years would be prevented by the proposed
standard. By way of example, the Infante study disclosed seven
excess leukemia deaths in a population of about 600 people over a
25-year period. While the Infante study involved higher exposures
then those currently encountered, the incidence rates found by
Infante, together with the numerous other cases reported in the
literature of benzene leukemia and other fatal blood diseases, make
it difficult for OSHA to rely on the [witness'] hypothesis to
assure the statutorily mandated protection of employees. In any
event, due to the fact that there is no safe level of exposure to
benzene and that it is impossible to precisely quantify the
anticipated benefits, OSHA must select the level of exposure which
is most protective of exposed employees."
43 Fed.Reg. 5941 (1978). There are three possible
interpretations of OSHA's stated reason for rejecting the witness'
testimony: (1) OSHA considered it probable that a greater number of
lives would be saved by lowering the standard from 10 ppm; (2) OSHA
thought that saving two lives every six years in a workforce of
30,000 persons is a significant savings that makes it reasonable
and appropriate to adopt a new standard; or (3) even if the small
number is not significant, and even if the savings may be even
smaller, the Agency nevertheless believed it had
Page 448 U. S. 655
a statutory duty to select the level of exposure that is most
protective of the exposed employees if it is economically and
technologically feasible to do so. Even if the Secretary did not
intend to rely entirely on this third theory, his construction of
the statute would make it proper for him to do so. Moreover, he
made no express findings of fact that would support his 1 ppm
standard on any less drastic theory. Under these circumstances, we
can hardly agree with the Government that OSHA discharged its duty
under the Act.
Contrary to the Government's contentions, imposing a burden on
the Agency of demonstrating a significant risk of harm will not
strip it of its ability to regulate carcinogens, nor will it
require the Agency to wait for deaths to occur before taking any
action. First, the requirement that a "significant" risk be
identified is not a mathematical straitjacket. It is the Agency's
responsibility to determine, in the first instance, what it
considers to be a "significant" risk. Some risks are plainly
acceptable, and others are plainly unacceptable. If, for example,
the odds are one in a billion that a person will die from cancer by
taking a drink of chlorinated water, the risk clearly could not be
considered significant. On the other hand, if the odds are one in a
thousand that regular inhalation of gasoline vapors that are 2%
benzene will be fatal, a reasonable person might well consider the
risk significant and take appropriate steps to decrease or
eliminate it. Although the Agency has no duty to calculate the
exact probability of harm, it does have an obligation to find that
a significant risk is present before it can characterize a place of
employment as "unsafe." [
Footnote 62]
Page 448 U. S. 656
Second, OSHA is not required to support its finding that a
significant risk exists with anything approaching scientific
certainty. Although the Agency's findings must be supported by
substantial evidence, 29 U.S.C. § 655(f), § (b)(5) specifically
allows the Secretary to regulate on the basis of the "best
available evidence." As several Courts of Appeals have held, this
provision requires a reviewing court to give OSHA some leeway where
its findings must be made on the frontiers of scientific knowledge
.
See Industrial Union Dept., AFL-CIO v. Hodson, 162
U.S.App.D.C. 331, 340, 499 F.2d 467, 476 (1974);
Society of the
Plastics Industry, Inc. v. OSHA, 509 F.2d 1301, 130 (CA2
1975),
cert. denied, 421 U.S. 992. Thus, so long as they
are supported by a body of reputable scientific thought, the Agency
is free to use conservative assumptions in interpreting the data
with respect to carcinogens, risking error on the side of
overprotection, rather than underprotection. [
Footnote 63]
Finally, the record in this case and OSHA's own rulings on other
carcinogens indicate that there are a number of ways in which the
Agency can make a rational judgment about the
Page 448 U. S. 657
relative significance of the risks associated with exposure to a
particular carcinogen. [
Footnote
64]
It should also be noted that, in setting a permissible exposure
level in reliance on less-than-perfect methods, OSHA would have the
benefit of a backstop in the form of monitoring
Page 448 U. S. 658
and medical testing. Thus, if OSHA properly determined that the
permissible exposure limit should be set at 5 ppm, it could still
require monitoring and medical testing for employees exposed to
lower levels. [
Footnote 65]
By doing so, it could keep a constant check on the validity of the
assumptions made in developing the permissible exposure limit,
giving it a sound evidentiary basis for decreasing the limit if it
was initially set too high. [
Footnote 66] Moreover, in this way, it could ensure that
workers who were unusually susceptible to benzene could be removed
from exposure before they had suffered any permanent damage.
[
Footnote 67]
E
Because our review of these cases has involved a more detailed
examination of the record than is customary, it must
Page 448 U. S. 659
be emphasized that we have neither made any factual
determinations of our own nor have we rejected any factual findings
made by the Secretary. We express no opinion on what factual
findings this record might support, either on the basis of
empirical evidence or on the basis of expert testimony; nor do we
express any opinion on the more difficult question of what factual
determinations would warrant a conclusion that significant risks
are present which make promulgation of a new standard reasonably
necessary or appropriate. The standard must, of course, be
supported by the findings actually made by the Secretary, not
merely by findings that we believe he might have made.
In this case, the record makes it perfectly clear that the
Secretary relied squarely on a special policy for carcinogens that
imposed the burden on industry of proving the existence of a safe
level of exposure, thereby avoiding the Secretary's threshold
responsibility of establishing the need for more stringent
standards. In so interpreting his statutory authority, the
Secretary exceeded his power.
IV
Throughout the administrative proceedings, the dermal contact
issue received relatively little attention. In its proposed rule,
OSHA recommended a total ban on skin and eye contact with liquid
benzene on the basis of its policy that, "in dealing with a
carcinogen, all potential routes of exposure (
i.e.,
inhalation, ingestion, and skin absorption) [should] be limited to
the extent feasible." 43 Fed.Reg. 5948 (1978). There was little
opposition to this requirement at the hearing on the proposed rule,
apparently because the proposed rule also excluded from both the
permissible exposure level and the dermal contact ban work
operations involving liquid mixtures containing 1% (and after one
year, 0.1%) or less benzene.
In its final standard, however, OSHA eliminated the percentage
exclusion for liquid benzene on the ground that there was no
predictable correlation between the percentage of benzene
Page 448 U. S. 660
in a liquid and the airborne exposure arising from it.
See n.
22
supra. Although the extent to which liquid benzene is
absorbed through the skin is concededly unknown, OSHA also refused
to exempt any liquids, no matter how little benzene they contained,
from the ban on dermal contact. In support of this position, it
stated that there was no evidence to "suggest that the absorption
rate depends on the amount of benzene present in the liquid." 43
Fed.Reg. 948-5949 (1978).
After the permanent standard was promulgated, OSHA received a
number of requests from various industries that the percentage
exclusion for liquids containing small amounts of benzene be
reinstated. Those concerned with airborne exposures argued that
they should not be required to monitor workplaces simply because
they handled petroleum-based products in which benzene is an
unavoidable contaminant. Others concerned with the dermal contact
ban made similar arguments. In particular, tire manufacturers
argued that it was impossible for them to comply with the ban,
because gloves cannot be worn during certain tire-building
operations in which solvents are used and solvents containing
absolutely no benzene are not commercially available.
Because of these requests, OSHA held a new series of hearings
and promulgated an amendment to the rule, reinstating the
percentage exclusion but lowering it from the proposed 1% to 0.5%.
The Agency did, however, provide for a 3-year grace period before
the exclusion dropped to 0.1%, rather than the one year that had
originally been proposed. In explaining its amendment, OSHA
reiterated its policy with respect to carcinogens, stating that,
because there is no absolutely safe level for any type of exposure,
exposures by whatever route must be limited to the extent feasible.
For airborne exposures, a zero permissible exposure limit had not
been feasible. However, in most industries, a ban on any dermal
contact was feasible, since compliance could be achieved simply by
the use of protective clothing, such as impermeable
Page 448 U. S. 661
gloves. The Agency recognized that the dermal contact ban could
present a problem for tire manufacturers, but stated that the
percentage exclusion would alleviate the problem, because solvents
containing 0.5% or less benzene were available in sufficient
quantities. Although it noted that solvents containing 0.1% or less
benzene were not then available in quantity, the Agency stated that
a 3-year grace period would be sufficient to
"allow time for increased production of solvents containing
lower amounts of benzene and for development and evaluation of
alternative methods of compliance with the standard's dermal
provision."
Id. at 27968-27969.
The Court of Appeals struck down the dermal contact prohibition
on two grounds. First, it held that the record did not support a
finding that the ban would result in quantifiable benefits in terms
of a reduced leukemia risk; therefore, it was not "reasonably
necessary" within the meaning of § 3(8) of the Act. Second, the
court held that the Agency's conclusion that benzene may be
absorbed through the skin was not based on the best available
evidence, as required by § 6(b)(5). 581 F.2d at 505-506. On the
second ground, the court noted that the evidence on the issue of
absorption of benzene through the skin was equivocal, with some
studies indicating that it could be absorbed and some indicating
that it could not. All of these studies were relatively old, and
the only expert who had testified on the issue stated that a simple
test was now available to determine, with a great deal of accuracy,
whether and to what extent absorption will result. In light of §
6(b)(5), which requires the Agency to promulgate standards on the
basis of the "best available evidence" and "the latest available
scientific data in the field," the court held that, where there is
uncontradicted testimony that a simple test will resolve the issue,
the Agency is required to acquire that information before
"promulgating regulations which would require an established
industry to change long-followed work processes that are not
demonstrably unsafe." 581 F.2d at 508.
Page 448 U. S. 662
While the court below may have been correct in holding that,
under the peculiar circumstances of this case, OSHA was required to
obtain more information, there is no need for us to reach that
issue. For in order to justify a ban on dermal contact, the Agency
must find that such a ban is "reasonably necessary and appropriate"
to remove a significant risk of harm from such contact. The Agency
did not make such a finding, but rather acted on the basis of the
absolute, no-risk policy that it applies to carcinogens. Indeed, on
this issue, the Agency's position is even more untenable, inasmuch
as it was required to assume not only that benzene in small doses
is a carcinogen, but also that it can be absorbed through the skin
in sufficient amounts to present a carcinogenic risk. These
assumptions are not a proper substitute for the findings of a
significant risk of harm required by the Act.
The judgment of the Court of Appeals remanding the petition for
review to the Secretary for further proceedings is affirmed.
It is so ordered.
* Together with No. 78-1036,
Marshall, Secretary of Labor v.
American Petroleum Institute et al., also on certiorari to the
same court.
[
Footnote 1]
The second and third sentences of this section, which impose
feasibility limits on the Secretary and allow him to take into
account the best available evidence in developing standards, may
apply to all health and safety standards. This conclusion follows
if the term "subsection" used in the second sentence refers to the
entire subsection 6(b) (which sets out procedures for the adoption
of all types of health and safety standards), rather than simply to
the toxic materials subsection, § 6(b)(5). While MR. JUSTICE
MARSHALL,
post at
448 U. S. 694, and respondents agree with this position,
see Brief for Respondents American Petroleum Institute
et al. 39;
see also Currie, OSHA, 1976 Am.Bar
Found.Research J. 1107, 1137, n. 151, the Government does not,
see Brief for Federal Parties 58;
see also Berger
& Riskin, Economic and Technological Feasibility in Regulating
Toxic Substances Under the Occupational Safety and Health Act, 7
Ecology L.Q. 285, 294 (1978). There is no need for us to decide
this issue in these cases.
[
Footnote 2]
OSHA is the administrative agency within the Department of Labor
that is responsible for promulgating and enforcing standards under
the Act. In this opinion, we refer to the "Secretary," "OSHA" and
the "Agency" interchangeably.
[
Footnote 3]
"The Act imposes on OSHA the obligation to enact only standards
that are reasonably necessary or appropriate to provide safe or
healthful workplaces. If a standard does not fit in this
definition, it is not one that OSHA is authorized to enact."
581 F.2d at 502.
[
Footnote 4]
"Although 29 U.S.C.A. § 655(b)(5) requires the goal of attaining
the highest degree of health and safety protection for the
employee, it does not give OSHA the unbridled discretion to adopt
standards designed to create absolutely risk-free workplaces
regardless of cost. To the contrary, that section requires
standards to be feasible, and it contains a number of pragmatic
limitations in the form of specific kinds of information OSHA must
consider in enacting standards dealing with toxic materials. Those
include 'the best available evidence,' 'research, demonstrations,
experiments, and such other information as may be appropriate,'
'the latest available scientific data in the field,' and
'experience gained under this and other health and safety laws.'
Moreover, in standards dealing with toxic materials, just as with
all other occupational safety and health standards, the conditions
and other requirements imposed by the standard must be 'reasonably
necessary or appropriate to provide safe or healthful employment
and places of employment.' 29 U.S.C.A. § 652(8)."
Ibid.
[
Footnote 5]
"The lack of substantial evidence of discernable benefits is
highlighted when one considers that OSHA is unable to point to any
empirical evidence documenting a leukemia risk at 10 ppm even
though that has been the permissible exposure limit since 1971.
OSHA's assertion that benefits from reducing the permissible
exposure limit from 10 ppm to 1 ppm are likely to be appreciable,
an assumption based only on inferences drawn from studies involving
much higher exposure levels, rather than on studies involving these
levels or sound statistical projections from the high-level
studies, does not satisfy the reasonably necessary requirement
limiting OSHA's action.
Aqua Slide requires OSHA to
estimate the extent of expected benefits in order to determine
whether those benefits bear a reasonable relationship to the
standard's demonstrably high costs."
Id. at 503-504.
[
Footnote 6]
OSHA's figures indicate that 795,000 service station employees
have some heightened exposure to benzene as a result of their
employment.
See 2 U.S. Dept. of Labor, OSHA, Technology
Assessment and Economic Impact Study of an OSHA Regulation for
Benzene, p. D-7 (May 1977) (hereinafter Economic Impact Statement),
11 Record, Ex. 5B, p. D-7. These employees are specifically
excluded from the regulation at issue in this case.
See
infra at 628. OSHA states that another 629,000 employees who
are covered by the regulation work in the other industries
described. 43 Fed.Reg. 5935 (1978).
It is not clear from the record or its explanation of the
permanent standard how OSHA arrived at the estimate of 629,000
exposed employees. OSHA's consultant, Arthur D Little, Inc.,
estimated that there were 191,000 exposed employees, 30,000 of whom
were exposed to 1 ppm or more of benzene. 1 Economic Impact
Statement, p. 3-5, 11 Record, E. 5A, p. 3-5. In its explanation of
the permanent standard, OSHA stated that there were 1,440 exposed
employees who worked in benzene plants, 98,000 in other petroleum
refineries, 24,000 in coke ovens, 4,000 in light oil plants, 2,760
in the petrochemical industry, 52,345 who worked in bulk terminals,
23,471 drivers who loaded benzene from those terminals, 74,000 in
oil and gas production, 17,000 in pipeline work, 100 at tank-car
facilities, 200 at tank-truck facilities, 480 on barges, 11,400 in
tire-manufacturing plants, and 13,050 in other types of rubber
production. 43 Fed.Reg. 5936-5938 (1978). Although OSHA gave no
estimate for laboratory workers, the A. D. Little study indicated
that there were 25,000 exposed workers in that industry. These
figures add up to 347,246 exposed employees -- approximately
282,000 less than the overall estimate of 629,000. It is possible
that some or all of these employees work in the "other industries"
briefly described in OSHA's explanation; these are primarily small
firms that manufacture adhesives, paint and ink or that use benzene
solvents.
Id. at 5939. No estimate of the number of
exposed employees in those industries or the aggregate cost of
compliance by those industries is given either by OSHA or by A. D.
Little in its consulting report.
[
Footnote 7]
Section 6(a) of the Act, as set forth in 29 U.S.C. § 655(a),
provides:
"Without regard to chapter 5 of Title 5 or to the other
subsections of this section, the Secretary shall, as soon as
practicable during the period beginning with the effective date of
this chapter and ending two years after such date, by rule
promulgate as an occupational safety or health standard any
national consensus standard, and any established Federal standard,
unless he determines that the promulgation of such a standard would
not result in improved safety or health for specifically designated
employees. In the event of conflict among any such standards, the
Secretary shall promulgate the standard which assures the greatest
protection of the safety or health of the affected employees."
In this case, the Secretary complied with the directive to
choose the most protective standard by selecting the ANSI standard
of 10 ppm, rather than the 25 ppm standard adopted by the American
Conference of Government Industrial Hygienists. 43 Fed.Reg. 5919
(1978).
[
Footnote 8]
See Delore & Borgomano, Leucemie aigue au cours de
l'intoxication benzenique. Sur l'origine toxique de certaines
leucemies aigues et leurs relations avec les anemies graves, 9
Journal de Medecine de Lyon 227 (1928). A translation of that
document appears in the benzene administrative record. 2 Record,
Ex. 2-60.
See also Hunter, Chronic Exposure to
Benzene(Benzol). II. The Clinical Effects, 21 J.Ind.Hyg. &
Toxicol. 331 (1939), 3 Record, Ex. 2-74, which refers to "leucemia"
as a side effect of chronic exposure to benzene.
[
Footnote 9]
Dr. Muzaffer Aksoy, a Turkish physician who testified at the
hearing on the proposed benzene standard, did a number of studies
concerning the effects of benzene exposure on Turkish shoemakers.
The workers in Dr. Aksoy's studies used solvents containing large
percentages of benzene, and were constantly exposed to high
concentrations of benzene vapors (between 150 and 650 ppm) under
poorly ventilated and generally unhygienic conditions.
See
Aksoy, Acute Leukemia Due to Chronic Exposure to Benzene, 52 Am.J.
of Medicine 160 (1972), 1 Record, Ex. 2-29; Aksoy, Benzene
(Benzol): Its Toxicity and Effects on the Hematopoietic System,
Istanbul Faculty of Medicine Monograph Series No. 1 (1970), 2
Record, Ex. 2-55; Aksoy, Erdem, & DinCol, Leukemia in Shoe
Workers Exposed Chronically to Benzene, 44 Blood 837 (1974), 2
Record, Ex. 2-53 (reporting on 26 shoe workers who had contracted
leukemia from 1967 to 1973; this represented an incidence of 13 per
100,000, rather than the 6 cases per 100,000 that would normally be
expected).
Dr. Enrico Vigliani also reported an excess number of leukemia
cases among Italian shoemakers exposed to glues containing a high
percentage of benzene and workers in rotogravure plants who had
been exposed over long periods of time to inks and solvents
containing as much as 605& benzene.
See Vigliani &
Saita, Benzene and Leukemia, 271 New Eng.J. of Medicine 872-876
(1964), 1 Record, Ex. 2-27; Forni & Vigliani, Chemical
Leukemogenesis in Man, 7 Ser.Haemat. 211 (1974), 2 Record, Ex.
2-50.
[
Footnote 10]
Title 29 U.S.C. § 669(a)(3) requires the Department of Health,
Education, and Welfare(HEW) (now in part the Department of Health
and Human Services) to develop "criteria" dealing with toxic
materials and harmful physical agents that describe "exposure
levels that are safe for various periods of employment." HEW's
obligations under this section have been delegated to NIOSH, 29
U.S.C. § 671.
[
Footnote 11]
See Dept. of HEW, NIOSH, Criteria for a Recommended
Standard -- Occupational Exposure to Benzene 74-75 (Pub. No.
74-137, 1974), 1 Record, Ex. 2-3. In response to a letter from the
Director of the Office of Standards Division, NIOSH stated that its
10 ppm standard was designed to protect against leukemia, as well
as other health risks. NIOSH noted, however, that further research
was necessary in order to establish adequate dose-response data for
benzene and leukemia. 12 Record, Ex. 32A, 32B.
[
Footnote 12]
Aksoy published another study in 1976 reporting on an additional
eight leukemia cases uncovered after 1973. In that article, he also
noted that a 1969 ban on the use of benzene as a solvent had led to
a decline in the number of reported leukemia cases beginning in
1974. Aksoy, Types of Leukemia in Chronic Benzene Poisoning, 55
Acta Haematologica 65 (1976), 1 Record, Ex. 2-30. Vigliani also
noted a decline in leukemia cases in Italy after benzene was no
longer used in glues and inks.
See Vigliani & Forni,
Benzene and Leukemia, 11 Environmental Res. 122 (1976), 1 Record,
Ex. 2-15; Vigliani, Leukemia Associated with Benzene Exposure, 271
Annals N.Y. Acad. of Sciences 143 (1976), 2 Record, Ex. 2-49. In
the latter study, Vigliani noted that, in the past, 100% pure
benzene solvents had been used and workers had been exposed on a
prolonged basis to concentrations of 200-500 ppm, with peaks of up
to 1500 ppm.
A number of epidemiological studies were also done among
American rubber workers during this period. Dr. A. J. McMichael's
studies indicated a nine-fold increase in the risk of contracting
leukemia among workers who were heavily exposed in the 1940's and
1950's to pure benzene used as a solvent. McMichael, Spirtas,
Kupper, & Gamble, Solvent Exposure and Leukemia Among Rubber
Workers: An Epidemiologic Study, 17 J. of Occup.Med. 234, 238
(1975), 2 Record, Ex. 2-37.
See also Andjelkovic, Taulbee,
& Symons, Mortality Experience of a Cohort of Rubber Workers,
1964-1973, 18 J. of Occup.Med. 387 (1976), 2 Record, Ex. 2-54 (also
indicating an excess mortality rate from leukemia among rubber
workers) .
[
Footnote 13]
Section 655(c) provides:
"(1) The Secretary shall provide, without regard to the
requirements of chapter 5 of title 5, for an emergency temporary
standard to take immediate effect upon publication in the Federal
Register if he determines (A) that employees are exposed to grave
danger from exposure to substances or agents determined to be toxic
or physically harmful or from new hazards, and (b) that such
emergency standard is necessary to protect employees from such
danger."
"(2) Such standard shall be effective until superseded by a
standard promulgated in accordance with the procedures prescribed
in paragraph (3) of this subsection."
"(3) Upon publication of such standard in the Federal Register
the Secretary shall commence a proceeding in accordance with
subsection (b) of this section, and the standard as published shall
also serve as a proposed rule for the proceeding. The Secretary
shall promulgate a standard under this paragraph no later than six
months after publication of the emergency standard as provided in
paragraph (2) of this subsection."
[
Footnote 14]
At the hearing on the permanent standard, NIOSH representatives
testified that they had selected 1 ppm initially in connection with
the issuance of a proposed standard for vinyl chloride. In that
proceeding, they had discovered that 1 ppm was approximately the
lowest level detectable through the use of relatively
unsophisticated monitoring instruments. With respect to benzene,
they also thought that 1 ppm was an appropriate standard because
any lower standard might require the elimination of the small
amounts of benzene (in some places, up to 0.5 ppm) that are
normally present in the atmosphere. Tr. 1142-1143. NIOSH's
recommendation was not based on any evaluation of the feasibility,
either technological or economic, of eliminating all exposures
above 1 ppm.
Id. at 1156.
[
Footnote 15]
Seven fatalities from leukemia were discovered out of the 748
workers surveyed. However, Dr. Infante, who conducted the study,
stated that his statistical techniques had probably underestimated
the number of leukemia cases that had actually occurred.
Id. at 747. The normal expected incidence of leukemia in
such a population would be 1.4. 2 Record, Ex. 2-51, p 6.
[
Footnote 16]
The authors' statement with respect to exposure levels was based
on 1946 report by the Ohio Industrial Commission indicating that,
after some new ventilation equipment had been installed, exposures
at the St. Marys plant had been brought within "safe" limits, in
most instances ranging from zero to 10 to 15 ppm.
Id. at
3. As the authors later admitted, the level considered "safe" in
1946 was 100 ppm. Tr. 814-815. Moreover, only one of the seven
workers who died of leukemia had begun working at St. Marys after
1946. Five of the others had worked at the Akron plant, which
employed 310 of the 748 workers surveyed.
Id. at
2537-2538. A 1948 report by the Ohio Department of Health indicated
exposure levels at the Akron plant of well over 100 ppm, with
excursions in some areas up to 1,000 ppm. 17 Record, Ex. 84A, App.
A, pp. 612. Surveys taken in the intervening years, as well as
testimony by St. Marys employees at the hearing on the proposed
standard, Tr. 3432-3437, indicated that both of the plants may have
had relatively high exposures through the 1970's.
Industry representatives argued at the hearing that this
evidence indicated that the exposure levels had been very high, as
they had been in the other epidemiological studies conducted in the
past.
See Post-Hearing Brief for American Petroleum
Institute in No. H-059 (OSHRC), pp. 2337, 31 Record, Ex. 217-33,
pp. 23-37. NIOSH witnesses, however, simply stated that actual
exposure levels for the years in question could not be determined;
they did agree, however, that their study should not be taken as
proof of a five-fold increase in leukemia risk at 10-15 ppm. Tr.
814-815. In its explanation of the permanent standard, OSHA agreed
with the NIOSH witnesses that no dose-response relationship could
be inferred from the study:
"Comments at the hearing demonstrated that there were area
exposures during this study period exceeding these levels [10-15
ppm], at times reaching values of hundreds of parts per million.
Since no personal monitoring data are available, any conclusion
regarding the actual individual time-weighted average exposure is
speculative. Because of the lack of definitive exposure data, OSHA
cannot derive any conclusions linking the excess leukemia risk
observed with any specific exposure level."
43 Fed.Reg. 5927 (1978).
[
Footnote 17]
OSHA also sought public comment as to whether certain industries
should be exempt from compliance, whether the proposed compliance
procedures and labeling techniques were adequate, what the
environmental and economic consequences of the regulation would be,
and whether it was feasible to replace benzene in solvents and
other products of which it constituted more than 1%.
[
Footnote 18]
It became clear at the hearing that OSHA had not promulgated the
proposed standard in response to any new concern about the
nonmalignant effects of low-level benzene exposure.
See
Tr. 126-127:
"Is it accurate to say that the reason why the -- why OSHA has
proposed to reduce the exposure limits in the standard below the
current levels is because of a perceived risk of leukemia, and not
because of any new evidence it has received that the current
standards are inadequate to protect against acute or chronic
benzene toxicity, other than leukemia?"
"MR. WRENN: I think I will simply refer the part of my statement
you were referring to, in which it says, it is however benzene's
leukemogenicity which is of greatest concern to OSHA. That is
certainly the central issue within the ETS [emergency temporary
standard] and the proposed standard."
[
Footnote 19]
Mr. Wrenn testified:
"The proposed standard requires that employee exposure to
benzene in air be reduced to one part per million, with a five part
per million ceiling allowable over any fifteen minute period during
an eight hour work shift, and prohibits eye or prolonged skin
contact with liquid benzene."
"This airborne exposure limit is based on OSHA's established
regulatory policy that, in the absence of a demonstrated safe
level, or a no-effect level for a carcinogen, it will be assumed
that none exists, and that the agency will attempt to limit
employee exposure to the lowest level feasible."
Id. at 29-30.
See also:
"MR. WARREN: Mr. Wrenn, in promulgating the emergency temporary,
and proposed permanent, benzene standards, OSHA relies heavily, and
I am quoting from your testimony now, on the regulatory policy that
there is no safe level for carcinogens at any -- for any exposed
population, and the fact that leukemia, and a leukemogen is a
carcinogen, is that correct?"
"MR. WRENN: I believe that I stated that slightly differently in
my oral summary of the statement than it is stated in the statement
itself. I said that, in the absence of a known or demonstrated safe
level or no-effect level, our policy is to assume that none exists,
and to regulate accordingly."
Id. at 48-49.
"MR. WRENN: I would prefer to state it as I have on a couple of
occasions already this morning, and that, in the absence of a
demonstrated safe level of exposure, we will assume that none
exists for the purpose of regulatory policy."
Id. at 50.
[
Footnote 20]
In answer to the question of what demonstration would suffice to
establish a "safe level," Mr. Wrenn stated:
"I would like to draw a distinction, however, between what I
have referred to as the demonstration that a safe level exists and
speculation or elaborate theories that one may make, and I think
that the agency, in its history, and very likely its future
regulatory policy, would, in the face of evidence demonstrating
that a carcinogenic hazard does exist or did exist, in this
particular set of circumstances, would be very reluctant to accept
as the basis for its regulatory decisions a theoretical argument
that a safe level may, in fact, exist for a particular
substance."
Id. at 51-52. A NIOSH representative who testified
later put it more succinctly, stating that, ". . . if benzene
causes leukemia, and if leukemia is a cancer, then exposure really
is almost moot."
Id. at 1007.
[
Footnote 21]
An amendment to the standard was promulgated on June 27, 1978.
43 Fed.Reg. 27962.
See n 22,
infra.
[
Footnote 22]
Apart from its exclusion of gasoline storage and distribution
facilities (an exclusion retained in the final rule,
see
text, at
n 25,
infra), the proposed rule also excluded from coverage work
operations in which liquid mixtures containing 1% or less benzene
were used. After a year, this exclusion was to be narrowed to
operations where 0.1% benzene solutions were used. The rationale
for the exclusion was that airborne exposures from such liquids
would generally be within the 1 ppm limit. However, testimony at
the hearing on the proposed rule indicated that there was no
"consistent predictable relationship" between benzene content in a
liquid and the resulting airborne exposure. Therefore, OSHA
abandoned the idea of a percentage exclusion for liquid benzene in
its final standard. 43 Fed.Reg. 5942 (1978).
OSHA later reconsidered its position and, in an amendment to the
permanent standard, reinstated an exclusion for liquids, setting
the level at 0.5%, to be reduced to 0.1% after three years,
id. at 27962.
[
Footnote 23]
The exemption from the monitoring and medical testing portions
of the standard for workplaces with benzene exposure levels below
0.5 ppm was not predicated on any finding that regulation of such
workplaces was not feasible. OSHA's consultant, Arthur D. Little,
Inc., concluded that 1 ppm was a feasible exposure limit even
assuming that there was no action level (or, to put it another way,
assuming that the action level was zero). Rather, it was, as NIOSH
witnesses stated, a practical decision based on a determination
that, where benzene exposures are below 0.5 ppm, they will be
unlikely ever to rise above the permissible exposure level of 1
ppm. NIOSH was also concerned that, in the absence of an action
level, employers who used sophisticated analytical equipment might
be required to monitor and provide medical examinations simply
because of the presence of benzene in the ambient air. Tr.
1030-1032, 1133-1134.
[
Footnote 24]
Indeed, in its explanation of the standard OSHA states that an
employer is required to institute engineering controls (for
example, installing new ventilation hoods) even if those controls
are insufficient, by themselves, to achieve compliance and
respirators must therefore be used as well. 43 Fed.Reg. 5952
(1978). OSHA's preference for engineering modifications is based on
its opinion that respirators are rarely used properly (because they
are uncomfortable, are often not properly fitted, etc.), and
therefore cannot be considered adequate protective measures.
[
Footnote 25]
It is also inapplicable to work operations involving 0.5% liquid
benzene (0.1% after three years),
see n 22,
supra, and to the handling of
benzene in sealed containers or systems, except insofar as
employers are required to provide cautionary notices and
appropriate employee training.
[
Footnote 26]
Prior to the introduction of the action level concept, A. D.
Little estimated that compliance costs for the service station
industry might be as high as $4 billion. Tr. 508-509. Moreover, A.
D. Little's Economic Impact Statement indicated that service
station employees were generally exposed to very low levels of
benzene. 1 Economic Impact Statement p. 4-21, 11 Record, Ex. 5A, p.
4-21. Still, in its explanation accompanying the permanent
standard, OSHA did not rule out regulation of this industry
entirely, stating that it was in the process of studying whether
and to what extent it should regulate exposures to gasoline in
general. 43 Fed.Reg. 5943 (1978).
[
Footnote 27]
OSHA's estimate of recurring annual costs was based on the
assumption that the exposure levels it had projected would be
confirmed by initial monitoring and that, after the first year,
engineering controls would be successful in bringing most exposures
within the 1 ppm limit. Under these circumstances, the need for
monitoring, medical examinations, and respirators would, of course,
be drastically reduced.
[
Footnote 28]
Three hundred of these employees work in benzene plants, 5,000
in other petroleum refineries, 4,000 in light oil plants, 552 in
the petrochemical industry, 156 in benzene transportation, 1,250 in
laboratories, 11,400 in tire manufacturing plants, and 13,050 in
other rubber manufacturing plants. OSHA also estimated that another
16,216 workers (5,000 in petroleum refineries, 1, 104 in the
petrochemical industry, 7,300 in bulk terminals, 312 in benzene
transportation, and 2,500 in laboratories) would be exposed to 0.5
to 1 ppm of benzene, and thus would receive a benefit in terms of
more comprehensive medical examinations.
Id. at
5936-5938.
[
Footnote 29]
The high cost per employee in the latter two industries is
attributable to OSHA's policy of requiring engineering controls,
rather than allowing respirators to be used to reduce exposures to
the permissible limit. The relatively low estimated cost per
employee in the rubber industry is based on OSHA's assumption that
other solvents and adhesives can be substituted for those that
contain benzene, and that capital costs will therefore not be
required.
[
Footnote 30]
The other issue before us is whether the Court of Appeals
correctly refused to enforce the dermal contact ban. That issue is
discussed in
448 U. S.
infra.
In the court below, respondents also challenged the monitoring
and medical testing requirements, arguing that certain industries
should have been totally exempt from them and that, as to other
industries, the Agency had not demonstrated that all the
requirements were reasonably necessary to ensure worker health and
safety. They also argued that OSHA's requirement that the
permissible exposure limit be met through engineering controls,
rather than through respirators, was not reasonably necessary under
the Act. Because it invalidated the 1 ppm exposure limit, the Fifth
Circuit had no occasion to deal with these issues, and they are not
now before this Court.
[
Footnote 31]
As we have often held, the validity of an agency's determination
must be judged on the basis of the agency's stated reasons for
making that determination.
See SEC v. Chenery Corp.,
318 U. S. 80,
318 U. S. 95
("[A]n administrative order cannot be upheld unless the grounds
upon which the agency acted in exercising its powers were those
upon which its action can be sustained");
FPC v. Texaco
Inc., 417 U. S. 380,
417 U. S. 397;
FTC v. Sperry & Hutchinson Co., 405 U.
S. 233,
405 U. S.
249.
[
Footnote 32]
As OSHA itself noted, some blood abnormalities caused by benzene
exposure may not have any discernible health effects, while others
may lead to significant impairment, and even death. 43 Fed.Reg.
5921 (1978).
[
Footnote 33]
A dose-response curve shows the relationship between different
exposure levels and the risk of cancer [or any other disease]
associated with those exposure levels. Generally, exposure to
higher levels carries with it a higher risk, and exposure to lower
levels is accompanied by a reduced risk.
581 F.2d at 504, n. 24.
OSHA's comments with respect to the insufficiency of the data
were addressed primarily to the lack of data at low exposure
levels. OSHA did not discuss whether it was possible to make a
rough estimate, based on the more complete epidemiological and
animal studies done at higher exposure levels, of the significance
of the risks attributable to those levels, nor did it discuss
whether it was possible to extrapolate from such estimates to
derive a risk estimate for low-level exposures.
[
Footnote 34]
OSHA did not invoke the automatic rule of reducing exposures to
the lowest limit feasible that it applies to cancer risks. Instead,
the Secretary reasoned that prudent health policy merely required
that the permissible exposure limit be set "sufficiently below the
levels at which adverse effects have been observed to assure
adequate protection for all exposed employees." 43 Fed.Reg. 5925
(1978). While OSHA concluded that application of this rule would
lead to an exposure limit "substantially less than 10 ppm," it did
not state either what exposure level it considered to present a
significant risk of harm, or what safety factor should be applied
to that level to establish a permissible exposure limit.
[
Footnote 35]
While citing these studies, OSHA also noted that other studies
of similarly exposed workers had not indicated any increased level
of chromosome damage.
[
Footnote 36]
"The evidence in the record conclusively establishes that
benzene is a human carcinogen. The determination of benzene's
leukemogenicity is derived from the evaluation of all the evidence
in totality, and is not based on any one particular study. OSHA
recognizes, as indicated above, that individual reports vary
considerably in quality, and that some investigations have
significant methodological deficiencies. While recognizing the
strengths and weaknesses in individual studies, OSHA nevertheless
concludes that the benzene record as a whole clearly establishes a
causal relationship between benzene and leukemia."
Id. at 5931.
[
Footnote 37]
In rejecting these studies, OSHA stated that:
"Although the epidemiological method can provide strong evidence
of a causal relationship between exposure and disease in the case
of positive findings, it is, by its very nature, relatively crude,
and an insensitive measure."
After noting a number of specific ways in which such studies are
often defective, the Agency stated that it is "OSHA's policy, when
evaluating negative studies, to hold them to higher standards of
methodological accuracy."
Id. at 5931-5932. Viewing the
industry studies in this light, OSHA concluded that each of them
had sufficient methodological defects to make them unreliable
indicators of the safety of low-level exposures to benzene.
[
Footnote 38]
OSHA rejected this testimony, in part, because it believed the
exposure data in the epidemiological studies to be inadequate to
formulate a dose-response curve. It also indicated that, even if
the testimony was accepted -- indeed, as long as there was any
increase in the risk of cancer -- the Agency was under an
obligation to "select the level of exposure which is most
protective of exposed employees."
Id. at 5941.
[
Footnote 39]
In his dissenting opinion, MR. JUSTICE MARSHALL states that the
Agency did not rely "blindly on some Draconian carcinogen
policy'" in setting a permissible exposure limit for benzene.
He points to the large number of witnesses the Agency heard and the
voluminous record it compiled as evidence that it relied, instead,
on the particular facts concerning benzene. With all due respect,
we disagree with MR. JUSTICE MARSHALL's interpretation of the
Agency's rationale for its decision. After hearing the evidence,
the Agency relied on the same policy view it had stated at the
outset, see supra at 448 U. S.
623-625, namely, that, in the absence of clear evidence
to the contrary, it must be assumed that no safe level exists for
exposure to a carcinogen. The Agency also reached the entirely
predictable conclusion that industry had not carried its concededly
impossible burden, see n 41, infra, of proving that a safe level of
exposure exists for benzene. As the Agency made clear later in its
proposed generic cancer policy, see n. 51 infra, it felt compelled to
allow industry witnesses to go over the same ground in each
regulation dealing with a carcinogen, despite its policy view. The
generic policy, which has not yet gone into effect, was
specifically designed to eliminate this duplication of effort in
each case by foreclosing industry from arguing that there is a safe
level for the particular carcinogen being regulated. 42 Fed.Reg.
54154-54155 (1977).
[
Footnote 40]
"As stated above, the positive studies on benzene demonstrate
the causal relationship of benzene to the induction of leukemia.
Although these studies, for the most part, involve high exposure
levels, it is OSHA's view that, once the carcinogenicity of a
substance has been established qualitatively, any exposure must be
considered to be attended by risk when considering any given
population. OSHA therefore believes that occupational exposure to
benzene at low levels poses a carcinogenic risk to workers."
43 Fed.Reg. 5932 (1978).
[
Footnote 41]
The so-called "one hit" theory is based on laboratory studies
indicating that one molecule of a carcinogen may react in the test
tube with one molecule of DNA to produce a mutation. The theory is
that, if this occurred in the human body, the mutated molecule
could replicate over a period of years and eventually develop into
a cancerous tumor.
See OSHA's Proposed Rule on the
Identification, Classification and Regulation of Toxic Substances
Posing a Potential Carcinogenic Risk, 42 Fed.Reg. 54148,
54165-54167 (1977). Industry witnesses challenged this theory,
arguing that the presence of several different defense mechanisms
in the human body make it unlikely that a person would actually
contract cancer as a result of absorbing one carcinogenic molecule.
Thus, the molecule might be detoxified before reaching a critical
site, damage to a DNA molecule might be repaired, or a mutated DNA
molecule might be destroyed by the body's immunological defenses
before it could develop into a cancer. Tr. 2836.
In light of the improbability of a person's contracting cancer
as a result of a single hit, a number of the scientists testifying
on both sides of the issue agreed that every individual probably
does have a threshold exposure limit below which he or she will not
contract cancer.
See, e.g., id. at 1179-1181. The problem,
however, is that individual susceptibility appears to vary greatly,
and there is, at present, no way to calculate each and every
person's threshold. Thus, even industry witnesses agreed that, if
the standard must ensure with absolute certainty that every single
worker is protected from any risk of leukemia, only a zero exposure
limit would suffice.
Id. at 2492, 2830.
[
Footnote 42]
"There is no doubt that benzene is a carcinogen, and must, for
the protection and safety of workers, be regulated as such. Given
the inability to demonstrate a threshold or establish a safe level,
it is appropriate that OSHA prescribe that the permissible exposure
to benzene be reduced to the lowest level feasible."
43 Fed.Reg. 5932 (1978).
[
Footnote 43]
At an earlier point in its explanation, OSHA stated:
"There is general agreement that benzene exposure causes
leukemia as well as other fatal diseases of the blood-forming
organs. In spite of the certainty of this conclusion, there does
not exist an adequate scientific basis for establishing the
quantitative dose response relationship between exposure to benzene
and the induction of leukemia and other blood diseases. The
uncertainty in both the actual magnitude of expected deaths and in
the theory of extrapolation from existing data to the OSHA exposure
levels places the estimation of benefits on 'the frontiers of
scientific knowledge.' While the actual estimation of the number of
cancers to be prevented is highly uncertain, the evidence indicates
that the number may be appreciable. There is general agreement
that, even in the absence of the ability to establish a 'threshold'
or 'safe' level for benzene and other carcinogens, a dose response
relationship is likely to exist; that is, exposure to higher doses
carries with it a higher risk of cancer, and, conversely, exposure
to lower levels is accompanied by a reduced risk, even though a
precise quantitative relationship cannot be established."
Id. at 5940.
[
Footnote 44]
The court did, however, hold that the Agency's other conclusions
-- that there is some risk of leukemia at 10 ppm and that the risk
would decrease by decreasing the exposure limit to 1 ppm -- were
supported by substantial evidence. 581 F.2d at 503.
[
Footnote 45]
We cannot accept the argument that § 3(8) is totally
meaningless. The Act authorizes the Secretary to promulgate three
different kinds of standards -- national consensus standards,
permanent standards, and temporary emergency standards. The only
substantive criteria given for two of these -- national consensus
standards and permanent standards for safety hazards not covered by
§ 6(b)(5) -- are set forth in § 3. While it is true that § 3 is
entitled "definitions," that fact does not drain each definition of
substantive content. For otherwise there would be no purpose in
defining the critical terms of the statute. Moreover, if the
definitions were ignored, there would be no statutory criteria at
all to guide the Secretary in promulgating either national
consensus standards or permanent standards other than those dealing
with toxic materials and harmful physical agents. We may not expect
Congress to display perfect craftsmanship, but it is unrealistic to
assume that it intended to give no direction whatsoever to the
Secretary in promulgating most of his standards.
The structure of the separate subsection describing emergency
temporary standards, 29 U.S.C. § 655(c), quoted in
n 13,
supra, supports this
conclusion. It authorizes the Secretary to bypass the normal
procedures for setting permanent standards if he makes two
findings: (A) that employees are exposed to "grave danger" from
exposure to toxic substances, and (b) that an emergency standard is
"necessary" to protect the employees from that danger. Those
findings are to be compared with those that are implicitly required
by the definition of the permanent standard -- (A) that there be a
significant -- as opposed to a "grave" -- risk, and (b) that
additional regulation is "reasonably necessary or appropriate" --
as opposed to "necessary." It would be anomalous for Congress to
require specific findings for temporary standards but to give the
Secretary a
carte blanche for permanent standards.
[
Footnote 46]
The Government does not concede that the feasibility requirement
in the second sentence of § 6(b)(5) applies to health and safety
standards other than toxic substances standards.
See n. 1,
supra. However, even if it did, the Government's
interpretation of the term "feasible," when coupled with its view
of § 3(8), would still allow the Agency to require the elimination
of even insignificant risks at great cost, so long as an entire
industry's viability would not be jeopardized.
[
Footnote 47]
Section 6(b)(5) parallels § 6(a) in this respect. Section 6(a)
requires the Secretary, when faced with a choice between two
national consensus standards, to choose the more protective
standard,
see n 7,
supra. Just as § 6(a) does not suggest that this more
protective standard need not meet the definition of a national
consensus standard set forth in § 3(9), so § 6(b)(5) does not
suggest that the most protective toxic material standard need not
conform to the definition of a "standard" in § 3(8).
[
Footnote 48]
The rest of § 6(b)(5), while requiring the Secretary to
promulgate the standard that "most adequately assures . . . that no
employee will suffer material impairment of health or functional
capacity," also contains phrases implying that the Secretary should
consider differences in degrees of significance, rather than simply
a total elimination of all risks. Thus, the standard to be selected
is one that "most adequately assures, to the extent feasible, on
the basis of the best available evidence," that no such harm will
result. The Secretary is also directed to take into account
"research, demonstrations, experiments, and such other information
as may be appropriate," and to consider,
"[i]n addition to the attainment of the highest degree of health
and safety protection for the employee . . . , the latest available
scientific data in the field, the feasibility of the standards, and
experience gained under this and other health and safety laws."
MR. JUSTICE MARSHALL states that our view of § 3(8) would make
the first sentence in § 6(b)(5) superfluous. We disagree. The first
sentence of § 6(b)(5) requires the Secretary to select a highly
protective standard once he has determined that a standard should
be promulgated. The threshold finding that there is a need for such
a standard in the sense that there is a significant risk in the
workplace is not unlike the threshold finding that a chemical is
toxic, or a physical agent is harmful. Once the Secretary has made
the requisite threshold finding, § 6(b)(5) directs him to choose
the most protective standard that still meets the definition of a
standard under § 3(8), consistent with feasibility.
[
Footnote 49]
"First, 29 U.S.C. § 655(g) requires the Secretary to establish
priorities in setting occupational health and safety standards so
that the more serious hazards are addressed first. In setting such
priorities, the Secretary must, of course, consider the relative
costs, benefits and risks."
Reply Brief for Federal Parties 13. The Government argues that
the Secretary's setting of priorities under this section is not
subject to judicial review. Tr. of Oral Arg. 23. While we agree
that a court cannot tell the Secretary which of two admittedly
significant risks he should act to regulate first, this section,
along with §§ 3(8) and 6(b)(5), indicates that the Act does limit
the Secretary's power to requiring the elimination of significant
risks.
[
Footnote 50]
Section 6(b)(8), as set forth in 29 U.S.C. § 65(b)(8),
provides:
"Whenever a rule promulgated by the Secretary differs
substantially from an existing national consensus standard, the
Secretary shall, at the same time, publish in the Federal Register
a statement of the reasons why the rule as adopted will better
effectuate the purposes of this chapter than the national consensus
standard."
[
Footnote 51]
OSHA's proposed generic cancer policy, 42 Fed.Reg. 54148 (1977),
indicates that this possibility is not merely hypothetical. Under
its proposal, whenever there is a certain quantum of proof --
either from animal experiments or, less frequently, from
epidemiological studies -- that a substance causes cancer at any
exposure level, an emergency temporary standard would be
promulgated immediately, requiring employers to provide monitoring
and medical examinations and to reduce exposures to the lowest
feasible level. A proposed rule would then be issued along the same
lines, with objecting employers effectively foreclosed from
presenting evidence that there is little or no risk associated with
current exposure levels.
Id. at 54154-54155; 29 CFR, Part
1990 (1977).
The scope of the proposed regulation is indicated by the fact
that NIOSH has published a list of 2,415 potential occupational
carcinogens, NIOSH, Suspected Carcinogens: A Subfile of the
Registry of Toxic Effects of Chemical Substances (HEW Pub. No.
77-149, 2d ed.1976). OSHA has tentatively concluded that 269 of
these substances have been proved to be carcinogens, and therefore
should be subject to full regulation.
See OSHA Press
Release, USDL 78 625 (July 14, 1978).
[
Footnote 52]
In criticizing the Committee bill, Senator Dominick also made
the following observations
"It is unrealistic to attempt, as this section apparently does,
to establish a utopia free from any hazards. Absolute safety is an
impossibility, and it will only create confusion in the
administration of this act for the Congress to set clearly
unattainable goals."
116 Cong.Rec. 37614 (1970), Leg.Hist. 480.
"But I ask, Mr. President, just thinking about that language,
let us take a fellow who is a streetcar conductor or a bus
conductor at the present time. How in the world, in the process of
the pollution we have in the streets or in the process of the
automobile accidents that we have all during a working day of any
one driving a bus or trolley car, or whatever it may be, can we set
standards that will make sure he will not have any risk to his life
for the rest of his life? It is totally impossible for this to be
put in a bill; and yet it is in the committee bill."
116 Cong.Rec. at 37337, Leg.Hist. 423.
As an opponent of the legislation, Senator Dominick may have
exaggerated the significance of the problem, since the language in
§ 3(8) already was sufficient to prevent the Secretary from trying
"to establish a utopia free from any hazards." Nevertheless, the
fact that Congress amended the bill to allay Senator Dominick's
concern demonstrates that it did not intend the statute to achieve
"clearly unattainable goals."
[
Footnote 53]
Senator Dominick had also been concerned that the placement of
the word "feasibly" could be read to require the Secretary to "ban
all occupations in which there remains
some risk of
injury, impaired health, or life expectancy," since the way to most
"adequately" and "feasibly" assure absolute protection might well
be to prohibit the occupation entirely. 116 Cong.Rec. at 36530,
Leg.Hist. 366-367. In his final amendment, he attempted to cure
this problem by relocating the feasibility requirement, changing
"the standard which most adequately and feasibly assures" to "the
standard which most adequately assures, to the extent
feasible."
[
Footnote 54]
MR. JUSTICE MARSHALL argues that Congress could not have thought
§ 3(8) had any substantive meaning, inasmuch as § 6(b)(5), as
originally drafted, applied to all standards, and not simply to
standards for toxic materials and harmful physical substances.
However, as this legislative history indicates, it appears that the
omission of the words "toxic substances" and "harmful physical
agents" from the original draft of § 6(b)(5) was entirely
inadvertent. As Senator Dominick noted, the Committee had always
intended that subsection to apply only to that limited category of
substances. The reason that Congress drafted a special section for
these substances was not, as MR. JUSTICE MARSHALL suggests, because
it thought that there was a need for special protection in these
areas. Rather, it was because Congress recognized that there were
special problems in regulating health risks, as opposed to safety
risks. In the latter case, the risks are generally immediate and
obvious, while, in the former, the risks may not be evident until a
worker has been exposed for long periods of time to particular
substances. It was to ensure that the Secretary took account of
these long-term risks that Congress enacted § 6(b)(5) .
[
Footnote 55]
Reply Brief for Federal Parties 226. While it is true that some
of Senator Dominick's comments were concerned with the relative
unimportance of minor injuries (
see his "fly" example
quoted
supra at
448 U. S.
647), it is clear that he was also concerned with the
remote possibility of major injuries,
see n 52,
supra.
[
Footnote 56]
One union suggested a 0.5 ppm permissible exposure limit for oil
refineries and a 1 ppm ceiling (rather than a time-weighted
average) exposure for all other industries, with no use of an
action level, Tr. 1250, 1257. Another wanted a 1 ppm ceiling limit
for all industries,
id. at 3375-337.
[
Footnote 57]
"A need for an action level is also suggested by the record
evidence that some minimal exposure to benzene occurs naturally
from animal and plant matter (Tr. 749-750; 759-760). Naturally
occurring benzene concentrations, it appears, may range from 0.02
to 15 parts per billion (Ex. 117, p. 1). Additionally, it was
suggested by certain employers that their operations be exempted
from the requirements of the standard because these operations
involve only intermittent and low level exposures to benzene. The
use of the action level concept should accommodate these concerns
in all cases where exposures are indeed extremely low, since it
substantially reduces the monitoring of employees who are below the
action level and removes for these employees the requirements for
medical surveillance. At the same time, employees with
significant overexposure are afforded the full protection
of the standard."
(Emphasis added.) 43 Fed.Reg. 5942 (1978).
[
Footnote 58]
The Government also states that it is OSHA's policy to attempt
to quantify benefits wherever possible. While this is certainly a
reasonable position, it is not consistent with OSHA's own view of
its duty under § 6(b)(5). In light of the inconsistencies in OSHA's
position and the legislative history of the Act, we decline to
defer to the Agency's interpretation.
[
Footnote 59]
In
Florida Peach Growers Assn., Inc. v. U.S. Dept. of
Labor, 489 F.2d 120, 130, and n. 16 (CA5 1974), the court
noted that Congress intended to restrict the use of emergency
standards, which are promulgated without any notice or hearing. It
held that, in promulgating an emergency standard, OSHA must find
not only a danger of exposure or even some danger from exposure,
but also a grave danger from exposure necessitating emergency
action.
Accord, Dry Color Mfrs. Assn., Inc. v. U.S. Dept. of
Labor, 486 F.2d 98, 100 (CA3 1973) (an emergency standard must
be supported by something more than a possibility that a substance
may cause cancer in man).
Congress also carefully circumscribed the Secretary's
enforcement powers by creating a new, independent board to handle
appeals from citations issued by the Secretary for noncompliance
with health and safety standards.
See 29 U.S.C. §§
659-661.
[
Footnote 60]
As noted above, OSHA acknowledged that there was no empirical
evidence to support the conclusion that there was any risk
whatsoever of deaths due to exposures at 10 ppm. What OSHA relied
upon was a theory that, because leukemia deaths had occurred at
much higher exposures, some (although fewer) were also likely to
occur at relatively low exposures. The Court of Appeals
specifically held that its conclusion that the number was "likely"
to be appreciable was unsupported by the record.
See supra
at
448 U. S.
638.
[
Footnote 61]
See Environmental Defense Fund, Inc. v. EPA, 179
U.S.App.D.C. 43, 49, 57-63, 548 F.2d 998, 1004, 1012-1018 (1977),
cert. denied, 431 U.S. 925, where the court rejected the
argument that the EPA has the burden of proving that a pesticide is
unsafe in order to suspend its registration under the Federal
Insecticide, Fungicide, and Rodenticide Act. The court noted that
Congress had deliberately shifted the ordinary burden of proof
under the Administrative Procedure Act, requiring manufacturers to
establish the continued safety of their products.
[
Footnote 62]
In his dissenting opinion,
post at
448 U. S. 706,
MR. JUSTICE MARSHALL states:
"[W]hen the question involves determination of the acceptable
level of risk, the ultimate decision must necessarily be based on
considerations of policy as well as empirically verifiable facts.
Factual determinations can, at most, define the risk in some
statistical way; the judgment whether that risk is tolerable cannot
be based solely on a resolution of the facts."
We agree. Thus, while the Agency must support its finding that a
certain level of risk exists by substantial evidence, we recognize
that its determination that a particular level of risk is
"significant" will be based largely on policy considerations. At
this point, we have no need to reach the issue of what level of
scrutiny a reviewing court should apply to the latter type of
determination.
[
Footnote 63]
MR. JUSTICE MARSHALL states that, under our approach, the Agency
must either wait for deaths to occur or must "deceive the public"
by making a basically meaningless determination of significance
based on totally inadequate evidence. MR. JUSTICE MARSHALL's view,
however, rests on the erroneous premise that the only reason OSHA
did not attempt to quantify benefits in this case was because it
could not do so in any reasonable manner. As the discussion of the
Agency's rejection of an industry attempt at formulating a
dose-response curve demonstrates, however,
see supra at
448 U. S.
653-655, the Agency's rejection of methods such as
dose-response curves was based at least in part on its view that
nothing less than absolute safety would suffice.
[
Footnote 64]
For example, in the coke oven emissions standard, OSHA had
calculated that 21,000 exposed coke oven workers had an annual
excess mortality of over 200, and that the proposed standard might
well eliminate the risk entirely. 41 Fed.Reg. 46742, 46750 (1976),
upheld in
American Iron & Steel Inst. v. OSHA, 577
F.2d 825(CA3 1978),
cert. granted, post, p. 909. In
hearings on the coke oven emissions standard, the Council on Wage
and Price Stability estimated that 8 to 35 lives would be saved
each year, out of an estimated population of 14,000 workers, as a
result of the proposed standard. Although noting that the range of
benefits would vary depending on the assumptions used, OSHA did not
make a finding as to whether its own staff estimate or CWPS's was
correct, on the ground that it was not required to quantify the
expected benefits of the standard or to weigh those benefits
against the projected costs.
In other proceedings, the Agency has had a good deal of data
from animal experiments on which it could base a conclusion on the
significance of the risk. For example, the record on the vinyl
chloride standard indicated that a significant number of animals
had developed tumors of the liver, lung, and skin when they were
exposed to 50 ppm of vinyl chloride over a period of 11 months. One
hundred out of 200 animals died during that period. 39 Fed.Reg.
35890, 35891 (1974). Similarly, in a 1974 standard regulating 14
carcinogens, OSHA found that one of the substances had caused lung
cancer in mice or rats at 1 ppm and even 0.1 ppm, while another had
caused tumors in 80% of the animals subjected to high doses.
Id. at 3756, 3757, upheld in
Synthetic Organic
Chemical Mfrs. Assn. v. Brennan, 503 F.2d 1155(CA3 1974),
cert. denied, 420 U.S. 973, and
Synthetic Organic
Chemical Mfrs. Assn. v. Brennan, 506 F.2d 385 (CA3 1974),
cert. denied, 423 U.S. 830.
In this case, the Agency did not have the benefit of animal
studies, because scientists have been unable as yet to induce
leukemia in experimental animals as a result of benzene exposure.
It did, however, have a fair amount of epidemiological evidence,
including both positive and negative studies. Although the Agency
stated that this evidence was insufficient to construct a precise
correlation between exposure levels and cancer risks, it would at
least be helpful in determining whether it is more likely than not
that there is a significant risk at 10 ppm.
[
Footnote 65]
See GAF Corp. v. Occupational Safety and Health Review
Comm'n, 183 U.S.App.D.C. 20, 561 F.2d 913 (1977), where the
court upheld the asbestos standard insofar as it required employers
to provide medical examinations for employees exposed to any
asbestos fibers, even if they were exposed to concentrations below
the permissible exposure limit.
The respondent industry representatives have never disputed
OSHA's power to require monitoring and medical examinations in
general, although the did object to some of the specific
requirements imposed in this case.
See n 30,
supra. Because of our
disposition of the case, we have no occasion to pass on these
specific objections, or to determine what cost-benefit
considerations, if any, should govern the Agency's imposition of
such requirements.
[
Footnote 66]
This is precisely the type of information-gathering function
that Congress had in mind when it enacted § 6(b)(7), which empowers
the Secretary to require medical examinations to be furnished to
employees exposed to certain hazards and potential hazards "in
order to most effectively determine whether the health of such
employees is adversely affected by such exposure."
See
S.Rep. No. 91-1282, p. 7 (1970), Leg.Hist. 147.
[
Footnote 67]
In its explanation of the final standard, OSHA noted that there
was some testimony that blood abnormalities would disappear after
exposure had ceased. 43 Fed.Reg. 5946 (1978). Again, however, OSHA
refused to rely on the hypothesis that this would always occur.
Yet, in requiring medical examinations of employees exposed to
between 0.5 ppm and 1 ppm, OSHA was essentially providing itself
with the same kind of backstop.
MR. CHIEF JUSTICE BURGER, concurring.
These cases press upon the Court difficult unanswered questions
on the frontiers of science and medicine. The statute and the
legislative history give ambiguous signals as to how the Secretary
is directed to operate in this area. The opinion by MR. JUSTICE
STEVENS takes on a difficult task to decode the message of the
statute as to guidelines for administrative action.
To comply with statutory requirements, the Secretary must bear
the burden of "finding" that a proposed health and safety standard
is "reasonably necessary or appropriate to provide safe or
healthful employment and places of employment." This policy
judgment entails the subsidiary finding that the preexisting
standard presents a "significant risk" of material health
impairment for a worker who spends his entire employment life in a
working environment where exposure
Page 448 U. S. 663
remains at maximum permissible levels. The Secretary's factual
finding of "risk" must be "quantified sufficiently to enable the
Secretary to characterize it as significant in an understandable
way."
Ante at
448 U. S. 646.
Precisely what this means is difficult to say. But because these
mandated findings were not made by the Secretary, I agree that the
1 ppm benzene standard must be invalidated. However, I would stress
the differing functions of the courts and the administrative agency
with respect to such health and safety regulation.
The Congress is the ultimate regulator, and the narrow function
of the courts is to discern the meaning of the statute and the
implementing regulations with the objective of ensuring that, in
promulgating health and safety standards, the Secretary "has given
reasoned consideration to each of the pertinent factors," and has
complied with statutory commands.
Permian Basin Area Rate
Cases, 390 U. S. 747,
390 U. S. 792
(1968). Our holding that the Secretary must retrace his steps with
greater care and consideration is not to be taken in derogation of
the scope of legitimate agency discretion. When the facts and
arguments have been presented and duly considered, the Secretary
must make a policy judgment as to whether a specific risk of health
impairment is significant in terms of the policy objectives of the
statute. When he acts in this capacity, pursuant to the legislative
authority delegated by Congress, he exercises the prerogatives of
the legislature -- to focus on only one aspect of a larger problem,
or to promulgate regulations that, to some, may appear as imprudent
policy or inefficient allocation of resources. The judicial
function does not extend to substantive revision of regulatory
policy. That function lies elsewhere -- in Congressional and
Executive oversight or amendatory legislation -- although, to be
sure, the boundaries are often ill-defined and indistinct.
Nevertheless, when discharging his duties under the statute, the
Secretary is well admonished to remember that a heavy
responsibility burdens his authority. Inherent in this statutory
scheme is authority to refrain from regulation of
Page 448 U. S. 664
insignificant or
de minimis risks.
See Alabama
Power Co. v. Costle, 204 U.S.App. D.C. 51, 88-89. 636 F.2d
323, 360-361 (1979) (opinion of Leventhal, J.). When the
administrative record reveals only scant or minimal risk of
material health impairment, responsible administration calls for
avoidance of extravagant, comprehensive regulation. Perfect safety
is a chimera; regulation must not strangle human activity in the
search for the impossible.
MR. JUSTICE POWELL, concurring in part and concurring in the
judgment.
I join Parts I, II, III-A, III-B, III-C, and III-E of the
plurality opinion. [
Footnote 2/1]
The Occupational Safety and Health Administration relied in large
part on its "carcinogen policy" -- which had not been adopted
formally -- in promulgating the benzene exposure and dermal contact
regulation at issue in these cases. [
Footnote 2/2] For the reasons stated by the plurality, I
agree that §§ 6(b)(5) and 3(8) of the Occupational Safety and
Health Act of 1970, 29 U.S.C. §§ 655(b)(5) and 652(8), must be read
together. They require OSHA to make a threshold finding that
proposed occupational health standards are reasonably necessary to
provide safe workplaces. When OSHA acts to reduce existing national
consensus standards,
Page 448 U. S. 665
therefore. it must find that (i) currently permissible exposure
levels create a significant risk of material health impairment; and
(ii) a reduction of those levels would significantly reduce the
hazard.
Although I would not rule out the possibility that the necessary
findings could rest in part on generic policies properly adopted by
OSHA,
see McGarity, Substantive and Procedural Discretion
in Administrative Resolution of Science Policy Questions:
Regulating Carcinogens in EPA and OSHA, 67 Geo.L.J. 729, 754-759
(1979), no properly supported agency policies are before us in
these cases. [
Footnote 2/3] I
therefore agree with the plurality that the regulation is invalid
to the extent it rests upon the assumption that exposure to known
carcinogens always should be reduced to a level proved to be safe
or, if no such level is found, to the lowest level that the
affected industry can achieve with available technology.
I
If the disputed regulation were based exclusively on this
"carcinogen policy," I also would agree that we need not consider
whether the Act requires OSHA to determine that the benefits of a
proposed standard are reasonably related to the costs of
compliance.
Ante at
448 U. S. 615.
As the Court of Appeals for the Fifth Circuit recognized, however,
OSHA takes the "fall-back position" that its regulation is
justified by specific findings based upon the voluminous
evidentiary record compiled in this case.
American Petroleum
Institute v. OSHA, 581 F.2d 493, 503. OSHA found, for example,
that the number
Page 448 U. S. 666
of cancers prevented by reducing permissible exposure levels
from 10 ppm to 1 ppm "may be appreciable," that "the benefits of
the proposed standard are likely to be appreciable," and that the
"substantial costs [of the new standard] are justified in light of
the hazards." 43 Fed.Reg. 5940-5941 (1978). Thus, OSHA found -- at
least generally -- that the hazards of benzene exposure at
currently permissible levels are serious enough to justify an
expenditure of hundreds of millions of dollars. For me, that
finding necessarily subsumes the conclusion that the health risk is
"significant." If OSHA's conclusion is supported by substantial
evidence, the threshold requirement discussed in the plurality
opinion would be satisfied.
As I read its opinion, the plurality does not consider whether
the agency's findings are supported by substantial evidence. The
Court of Appeals found them insufficient because OSHA failed "to
estimate the extent of expected benefits. . . ." 581 F.2d at 504.
That court apparently would have required OSHA to supply a specific
numerical estimate of benefits derived through mathematical
techniques for "risk quantification" or "cost effectiveness
analysis."
Id. at 504, n. 23;
see id. at 504-505.
I do not agree with the Court of Appeals' conclusion that the
statute requires quantification of risk in every case.
The statutory preference for the "best available evidence," 29
U.S.C. § 655(b)(5), implies that OSHA must use the best known
techniques for the accurate estimation of risks and benefits when
such techniques are available. But neither the statute nor the
legislative history suggests that OSHA's hands are tied when
reasonable quantification cannot be accomplished by any known
methods.
See post at
448 U. S. 693
(MARSHALL, J., dissenting). In this litigation, OSHA found that "it
is impossible to precisely quantify the anticipated benefits. . .
." 43 Fed.Reg. 5941 (1978). If this finding is supported by
substantial evidence, the statute does not prevent the Secretary
from finding a significant health hazard on the
Page 448 U. S. 667
basis of the weight of expert testimony and opinion. I do not
understand the plurality to hold otherwise.
See ante at
448 U. S.
662.
For the foregoing reasons, I would not hold that "OSHA did not
even attempt to carry its burden of proof" on the threshold
question whether exposure to benzene at 10 ppm presents a
significant risk to human health
Ante at
448 U. S. 653.
In my view, the question is whether OSHA successfully carried its
burden on the basis of record evidence. That question, in turn,
reduces to two principal issues. First, is there substantial
evidence supporting OSHA's determination that available
quantification techniques are too imprecise to permit a reasonable
numerical estimate of risks? If not, then OSHA has failed to show
that its regulation rests on the "best available evidence." Second,
is OSHA's finding of significant risks at current exposure levels
supported by substantial evidence? If not, then OSHA has failed to
show that the new regulation is reasonably necessary to provide
safe and healthful workplaces.
II
Although I regard the question as close, I do not disagree with
the plurality's view that OSHA has failed, on this record, to carry
its burden of proof on the threshold issues summarized above. But
even if one assumes that OSHA properly met this burden,
see
post at
448 U. S.
697-701,
448 U. S.
713-714 (MARSHALL, J., dissenting), I conclude that the
statute also requires the agency to determine that the economic
effects of its standard bear a reasonable relationship to the
expected benefits. An occupational health standard is neither
"reasonably necessary" nor "feasible," as required by statute, if
it calls for expenditures wholly disproportionate to the expected
health and safety benefits.
OSHA contends that § 6(b)(5) not only permits, but actually
requires, it to promulgate standards that reduce health risks
without regard to economic effects, unless those effects
Page 448 U. S. 668
would cause widespread dislocation throughout an entire
industry. [
Footnote 2/4] Under the
threshold test adopted by the plurality today, this authority will
exist only with respect to "significant" risks. But the plurality
does not reject OSHA's claim that it must reduce such risks without
considering economic consequences less serious than massive
dislocation. In my view, that claim is untenable.
Although one might wish that Congress had spoken with greater
clarity, the legislative history and purposes of the statute do not
support OSHA's interpretation of the Act. [
Footnote 2/5]
Page 448 U. S. 669
It is simply unreasonable to believe that Congress intended OSHA
to pursue the desirable goal of risk-free workplaces to the extent
that the economic viability of particular industries -- or
significant segments thereof -- is threatened. As the plurality
observes, OSHA itself has not chosen to carry out such a
self-defeating policy in all instances.
Ante at
448 U. S. 650.
If it did, OSHA regulations would impair the ability of American
industries to compete effectively with foreign businesses and to
provide employment for American workers. [
Footnote 2/6]
I therefore would not lightly assume that Congress intended OSHA
to require reduction of health risks found to be significant
whenever it also finds that the affected industry
Page 448 U. S. 670
can bear the costs.
See 448
U.S. 607fn2/4|>n. 4,
supra. Perhaps more
significantly, however, OSHA's interpretation of § 6(b)(5) would
force it to regulate in a manner inconsistent with the important
health and safety purposes of the legislation we construe today.
Thousands of toxic substances present risks that fairly could be
characterized as "significant."
Cf. ante at
448 U. S. 645,
n. 51. Even if OSHA succeeded in selecting the gravest risks for
earliest regulation, a standard-setting process that ignored
economic considerations would result in a serious misallocation of
resources and a lower effective level of safety than could be
achieved under standards set with reference to the comparative
benefits available at a lower cost. [
Footnote 2/7] I would not attribute such an irrational
intention to Congress.
In these cases, OSHA did find that the "substantial costs" of
the benzene regulations are justified.
See supra at
448 U. S.
665-666. But the record before us contains neither
adequate documentation of this conclusion nor any evidence that
OSHA weighed the relevant considerations. The agency simply
announced its finding of cost-justification without explaining the
method by which it determines that the benefits justify the costs
and their economic effects. No rational system of regulation can
permit its administrators to make policy judgments without
explaining how their decisions effectuate the purposes of the
governing law, and nothing in the statute authorizes such laxity in
these cases. [
Footnote 2/8] Since
neither the airborne
Page 448 U. S. 671
concentration standard nor the dermal contact standard for
exposure to benzene satisfies the requirements of the governing
statute, I join the Court's judgment affirming the judgment of the
Court of Appeals.
[
Footnote 2/1]
These portions of the plurality opinion primarily address OSHA's
special carcinogen policy, rather than OSHA's argument that it also
made evidentiary findings. I do not necessarily agree with every
observation in the plurality opinion concerning the presence or
absence of such findings. I also express no view on the question
whether a different interpretation of the statute would violate the
nondelegation doctrine of
A.L.A. Schechter Poultry Corp. v.
United States, 295 U. S. 495
(1935), and
Panama Refining Co. v. Ryan, 293 U.
S. 388 (1935).
See post at
448 U. S.
672-687 (REHNQUIST, J., concurring in judgment).
[
Footnote 2/2]
The Secretary of Labor promulgated the relevant standard
pursuant to his statutory authority. Since OSHA is the agency
responsible for developing such regulations under the Secretary's
direction, this opinion refers to "OSHA" or "the agency" as the
decisionmaker most directly concerned.
[
Footnote 2/3]
OSHA has adopted a formal policy for regulating carcinogens
effective April 21, 1980. 45 Fed.Reg. 5282 (1980) (to be codified
at 29 CFR, Part 1990). But no such policy was in effect when the
agency promulgated its benzene regulation. Moreover, neither the
factual determinations nor the administrative judgments upon which
the policy rests are supported adequately on this record alone.
Accordingly, we have no occasion to consider the extent to which
valid agency policies may supply a basis for a finding that health
risks exist in particular cases.
[
Footnote 2/4]
OSHA argues that § 6(b)(5) requires it to promulgate standards
that are "feasible" only in the sense that they are "capable of
achievement"; that is, achievable "at bearable cost with available
technology." Brief for Federal Parties 57. The lower courts have
indicated that a standard is not "infeasible" under OSHA's test
unless it would precipitate "massive economic dislocation" in the
affected industry.
See, e.g., American Federation of Labor v.
Brennan, 530 F.2d 109, 123 (CA3 1975). In this case, OSHA
simply asked a consulting firm to ascertain the costs of complying
with a 1 ppm standard.
See ante at
448 U. S. 621.
OSHA then concluded that "the economic impact of [compliance] will
not . . . threaten the financial welfare of the affected firms or
the general economy." 43 Fed.Reg. 5939 (1978). The cost of
complying with a standard may be "bearable" and still not
reasonably related to the benefits expected. A manufacturing
company, for example, may have financial resources that enable it
to pay the OSHA-ordered costs. But expenditures for unproductive
purposes may limit seriously its financial ability to remain
competitive and provide jobs.
[
Footnote 2/5]
I will not repeat the detailed summary of the legislative
history contained in the plurality opinion.
Ante at
448 U. S.
646-652. Many of the considerations that the plurality
relies upon to show Congress' concern with significant harms
persuade me that Congress did not intend OSHA to reduce each
significant hazard without regard to economic consequences. Senator
Williams, a sponsor of the legislation, stated:
"Our bill is fair and reasonable. It is a good faith effort to
balance the need of workers to have a sa[f]e and healthy work
environment against the requirement of industry to function without
undue interference."
116 Cong.Rec. 37342 (1970), Legislative History of the
Occupational Safety and Health Act of 1970 (Committee Print
compiled for the Senate Committee on Labor and Public Welfare), p.
435 (1971). There could be no such "balance" if OSHA were
authorized to impose standards without regard to economic
consequences short of serious dislocation.
Senator Dominick described a preliminary version of § 6(b)(5) as
follows:
"What we were trying to do in the bill . . . was to say that,
when we are dealing with toxic agents or physical agents, we ought
to take such steps as are
feasible and
practical
to provide an atmosphere within which a person's health or safety
would not be affected. Unfortunately, we had language providing
that anyone [
sic] would be assured that no one would have
a hazard. . . ."
"It was an unrealistic standard. . . ."
116 Cong.Rec. 37622 (170), Legislative History,
supra
at 502 (emphasis added). Senator Dominick's objection to the
"unrealistic" standard of the forerunner of § 6(b)(5) does not
imply that he thought § 3(8) of the Act lacked substantive content.
See post at
448 U. S.
710-711 (MARSHALL, J., dissenting). The Senator hardly
would have proposed that § 6(b)(5) be deleted entirely,
see
ante at
448 U. S. 647,
if he had not thought that other sections of the Act required
health regulations that were reasonable and practical.
[
Footnote 2/6]
Congress has assigned OSHA an extremely difficult and complex
task, and the guidance afforded OSHA is considerably less than
clear. The agency's primary responsibility, reflected in its title,
is to minimize health and safety risks in the workplace. Yet the
economic health of our highly industrialized society requires a
high rate of employment and an adequate response to increasingly
vigorous foreign competition. There can be little doubt that
Congress intended OSHA to balance reasonably the societal interest
in health and safety with the often conflicting goal of maintaining
a strong national economy.
[
Footnote 2/7]
For example, OSHA's reading of § 6(b)(5) could force the
depletion of an industry's resources in an effort to reduce a
single risk by some speculative amount, even though other
significant risks remain unregulated.
[
Footnote 2/8]
The decision that costs justify benefits is largely a policy
judgment delegated to OSHA by Congress. When a court reviews such
judgments under the "substantial evidence" standard mandated by 29
U.S.C. § 655(f), the court must determine whether the responsible
agency has "careful[ly] identifi[ed] . . . the reasons why [it]
chooses to follow one course, rather than another" as the most
reasonable method of effectuating the purposes of the applicable
law.
Industrial Union Dept. v. Hodgson, 162 U.S.App.D.C.
331, 339-340, 499 F.2d 467, 475-476 (1974). Since OSHA failed to
identify its reasons in these cases, I express no opinion as to the
standard of review that may be appropriate in other situations.
MR JUSTICE REHNQUIST, concurring in the judgment.
The statutory provision at the center of the present
controversy, § 6(b)(5) of the Occupational Safety and Health Act of
1970, states, in relevant part, that the Secretary of Labor,
". . . in promulgating standards dealing with toxic materials or
harmful physical agents . . . shall set the standard which most
adequately assures,
to the extent feasible, on the basis
of the best available evidence, that no employee will suffer
material impairment of health or functional capacity even if such
employee has regular exposure to the hazard dealt with by such
standard for the period of his working life."
84 Stat. 1594, 29 U.S.C. § 655(b)(5) (emphasis added). According
to the Secretary, who is one of the petitioners herein, § 6(b)(5)
imposes upon him an absolute duty, in regulating harmful substances
like benzene for which no safe level is known, to set the standard
for permissible exposure at the lowest level that "can be achieved
at bearable cost with available technology." Brief for Federal
Parties 57. While the Secretary does not attempt to refine the
concept of "bearable cost," he apparently believes that a proposed
standard is economically feasible so long as its impact "will not
be such as to threaten the financial welfare of the affected firms
or the general economy." 43 Fed.Reg. 5939 (1978).
Respondents reply, and the lower court agreed, that § 6(b)(5)
must be read in light of another provision in the
Page 448 U. S. 672
same Act, § 3(8), which defines an "occupational health and
safety standard" as
". . . a. standard which requires conditions, or the adoption or
use of one or more practices, means, methods, operations, or
processes, reasonably necessary or appropriate to provide safe or
healthful employment and places of employment."
84 Stat. 1591, 29 U.S.C. § 652(8). According to respondents, §
6(b)(5), as tempered by § 3(8), requires the Secretary to
demonstrate that any particular health standard is justifiable on
the basis of a rough balancing of costs and benefits.
In considering these alternative interpretations, my colleagues
manifest a good deal of uncertainty, and ultimately divide over
whether the Secretary produced sufficient evidence that the
proposed standard for benzene will result in any appreciable
benefits at all. This uncertainty, I would suggest, is eminently
justified, since I believe that this litigation presents the Court
with what has to be one of the most difficult issues that could
confront a decisionmaker: whether the statistical possibility of
future deaths should ever be disregarded in light of the economic
costs of preventing those deaths. I would also suggest that the
widely varying positions advanced in the briefs of the parties and
in the opinions of MR. JUSTICE STEVENS, THE CHIEF JUSTICE, MR.
JUSTICE POWELL, and MR. JUSTICE MARSHALL demonstrate, perhaps
better than any other fact, that Congress, the governmental body
best suited and most obligated to make the choice confronting us in
this litigation, has improperly delegated that choice to the
Secretary of Labor and, derivatively, to this Court.
I
In his Second Treatise of Civil Government, published in 1690,
John Locke wrote that
"[t]he power of the legislative, being derived from the people
by a positive voluntary grant and institution, can be no other than
what that positive
Page 448 U. S. 673
grant conveyed, which being only to make laws, and not to make
legislators, the legislative can have no power to transfer their
authority of making laws and place it in other hands. [
Footnote 3/1] Two hundred years later, this
Court expressly recognized the existence of and the necessity for
limits on Congress' ability to delegate its authority to
representatives of the Executive Branch:"
"That Congress cannot delegate legislative power to the
President is a principle universally recognized as vital to the
integrity and maintenance of the system of government ordained by
the Constitution."
Field v. Clark, 143 U. S. 649,
143 U. S. 692
(1892). [
Footnote 3/2]
The rule against delegation of legislative power is not,
however, so cardinal a principle as to allow for no exception. The
Framers of the Constitution were practical statesmen, who saw that
the doctrine of separation of powers was a two-sided coin. James
Madison, in Federalist Paper No. 48, for example, recognized that,
while the division of authority among the various branches of
government was a useful principle, "the degree of separation which
the maxim requires as essential to a free government can never, in
practice, be duly maintained." The Federalist No. 48, p. 308 (H.
Lodge ed. 1888).
This Court also has recognized that a hermetic sealing-off of
the three branches of government from one another could easily
frustrate the establishment of a National Government
Page 448 U. S. 674
capable of effectively exercising the substantive powers granted
to the various branches by the Constitution. Mr. Chief Justice
Taft, writing for the Court in
J. W. Hampton & Co. v.
United States, 276 U. S. 394
(1928), noted the practicalities of the balance that has to be
struck:
"[T]he rule is that, in the actual administration of the
government, Congress or the Legislature should exercise the
legislative power, the President or the State executive, the
Governor, the executive power, and the Courts or the judiciary the
judicial power, and, in carrying out that constitutional division
into three branches, it is a breach of the National fundamental law
if Congress gives up its legislative power and transfers it to the
President, or to the Judicial branch, or if by law it attempts to
invest itself or its members with either executive power or
judicial power. This is not to say that the three branches are not
coordinate parts of one government, and that each, in the field of
its duties, may not invoke the action of the two other branches
insofar as the action invoked shall not be an assumption of the
constitutional field of action of another branch. In determining
what it may do in seeking assistance from another branch, the
extent and character of that assistance must be fixed according to
common sense, and the inherent necessities of the governmental
co-ordination."
Id. at
276 U. S.
406.
During the third and fourth decades of this century, this Court,
within a relatively short period of time, struck down several Acts
of Congress on the grounds that they exceeded the authority of
Congress under the Commerce Clause or under the nondelegation
principle of separation of powers, and, at the same time, struck
down state statutes because they violated "substantive" due process
or interfered with interstate commerce.
See generally R.
Jackson, The Struggle for Judicial Supremacy 48-123(1949). When
many of these decisions were later overruled, the principle that
Congress
Page 448 U. S. 675
could not simply transfer its legislative authority to the
Executive fell under a cloud. Yet, in my opinion, decisions such as
Panama Refining Co. v. Ryan, 293 U.
S. 388 (1935), suffer from none of the excesses of
judicial policymaking that plagued some of the other decisions of
that era. The many later decisions that have upheld congressional
delegations of authority to the Executive Branch have done so
largely on the theory that Congress may wish to exercise its
authority in a particular field, but, because the field is
sufficiently technical, the ground to be covered sufficiently
large, and the Members of Congress themselves not necessarily
expert in the area in which they choose to legislate, the most that
may be asked under the separation of powers doctrine is that
Congress lay down the general policy and standards that animate the
law, leaving the agency to refine those standards, "fill in the
blanks," or apply the standards to particular cases. These
decisions, to my mind, simply illustrate the above-quoted
principle, stated more than 50 years ago by Mr. Chief Justice Taft,
that delegations of legislative authority must be judged "according
to common sense and the inherent necessities of the governmental
coordination."
Viewing the legislation at issue here in light of these
principles, I believe that it fails to pass muster. Read literally,
the relevant portion of § 6(b)(5) is completely precatory,
admonishing the Secretary to adopt the most protective standard if
he can, but excusing him from that duty if he cannot. In the case
of a hazardous substance for which a "safe" level is either unknown
or impractical, the language of § 6(b)(5) gives the Secretary
absolutely no indication where on the continuum of relative safety
he should draw his line. Especially in light of the importance of
the interests at stake, I have no doubt that the provision at
issue, standing alone, would violate the doctrine against
uncanalized delegations of legislative power. For me, the remaining
question, then, is whether additional standards are ascertainable
from the legislative history or statutory context of §6(b)(5) or,
if not, whether
Page 448 U. S. 676
such a standardless delegation was justifiable in light of the
"inherent necessities" of the situation.
II
One of the primary sources looked to by this Court in adding
gloss to an otherwise broad grant of legislative authority is the
legislative history of the statute in question. The opinions of MR.
JUSTICE STEVENS and MR. JUSTICE MARSHALL, however, give little more
than a tip of the hat to the legislative origins of § 6(b)(5). Such
treatment is perhaps understandable, since the legislative history
of that section, far from shedding light on what important policy
choices Congress was making in the statute, gives one the feeling
of viewing the congressional purpose "by the dawn's early
light."
The precursor of § 6(b)(5) was placed in the Occupational Safety
and Health Act of 1970 while that bill was pending in the House
Committee on Education and Labor. At that time, the section
read:
"The Secretary, in promulgating standards under this subsection,
shall set the standard which most adequately assures, on the basis
of the best available professional evidence, that no employee will
suffer any impairment of health, or functional capacity, or
diminished life expectancy even if such employee has regular
exposure to the hazard dealt with by such standard for the period
of his working life."
§ 7(a)(4), H.R. 16785, 91st Cong., 2d Sess., 49 (1970),
Legislative History of the Occupational Safety and Health Act of
1970 (Committee Print compiled for the Senate Committee on Labor
and Public Welfare), p. 943(1971) (hereinafter Leg.Hist.). Three
aspects of this original proposal are particularly significant.
First, and perhaps most importantly, as originally introduced, the
provision contained no feasibility limitation, providing instead
that the Secretary "shall set the standard which most adequately
assures" that no employee will suffer
Page 448 U. S. 677
harm. Second, it would have required the Secretary to protect
employees from "any" impairment of health or functional capacity.
Third, on its face, although perhaps not in its intent, the
provision applied to both health and safety standards promulgated
under the Act. [
Footnote 3/3]
There can be little doubt that, at this point in its journey
through Congress, § 6(b)(5) would have required the Secretary, in
regulating toxic substances, to set the permissible level of
exposure at a safe level or, if no safe level was known, at zero.
When the Senate Committee on Labor and Public Welfare considered a
provision identical in almost all respects to the House version,
however, Senator Javits objected that the provision in question
"might be interpreted to require absolute health and safety in all
cases, regardless of feasibility. . . ." S.Rep. No. 91-1282, p. 58
(1970), Leg.Hist.197.
See also 116 Cong.Rec. 37327 (1970),
Leg.Hist. 418. The Committee therefore amended the bill to provide
that the Secretary "shall set the standard which most adequately
and feasibly" assured that no employee would suffer any
impairment of health. S. 2193, 91st Cong., 2d Sess., p. 39 (1970),
Leg.Hist. 242 (emphasis added). The only additional explanation for
this change appeared in the Senate Report accompanying the bill to
the Senate floor. There, the Committee explained:
"[S]tandards promulgated under section 6(b) shall represent
feasible requirements which, where appropriate, shall be
based on research, experiments, demonstrations, past experience,
and the latest available scientific
Page 448 U. S. 678
data. Such standards should be directed at assuring,
so far
as possible, that no employee will suffer impaired health or
functional capacity or diminished life expectancy by reason of
exposure to the hazard involved, even though such exposure may be
over the period of his entire working life."
S.Rep. No. 91-1282, p. 7 (1970), Leg.Hist. 147 (emphasis
added).
Despite Senator Javits' inclusion of the words "and feasibly" in
the provision, participants in the floor debate immediately
characterized § 6(b)(5) as requiring the Secretary "to establish a
utopia free from any hazards," and to "assure that there will not
be any risk at all." 116 Cong.Rec. 37614 (1970), Leg.Hist. 480-481
(remarks of Sen. Dominick). Senator Saxbe stated:
"When we come to saying that an employer must guarantee that
such an employee is protected from any possible harm, I think it
will be one of the most difficult areas we are going to have to
ascertain. . . ."
"I believe the terms that we are passing back and forth are
going to have to be identified."
116 Cong.Rec. at 26522, Leg.Hist. 345. In response to these
concerns, Senator Dominick introduced a substitute for the proposed
provision, deleting the sentence at issue here entirely. He
explained that his amendment would delete
"the requirement in section 6(b)(5) that the Secretary will
establish occupational safety and health standards which most
adequately and feasibly assure to the extent possible that
no employee will suffer any impairment of health or
functional capacity, or diminished life expectancy even if the
employee has regular exposure to the hazard dealt with by the
standard for the period of his working life."
"This requirement is inherently confusing and unrealistic. It
could be read to require the Secretary to ban all
Page 448 U. S. 679
occupations in which there remains
some risk of injury,
impaired health, or life expectancy. In the case of all
occupations, it will be impossible to eliminate all risks to safety
and health. Thus, the present criteria could, if literally applied,
close every business in this nation. In addition, in many cases,
the standard which might most 'adequately' and 'feasibly' assure
the elimination of the danger would be the prohibition of the
occupation itself."
"If the provision is intended as no more than an admonition to
the Secretary to do his duty, it seems unnecessary, and could, if
deemed advisable, be included in the legislative history."
(Emphasis in original.) 116 Cong.Rec. at 36530, Leg.Hist.
367.
Eventually, Senator Dominick and his supporters settled for the
present language of § 6(b)(5). This agreement resulted in three
changes from the original version of the provision as amended by
Senator Javits. First, the provision was altered to state
explicitly that it applied only to standards for "toxic materials
or harmful physical agents," in apparent contrast with safety
standards. Second, the Secretary was no longer admonished to
protect employees from "any" impairment of their health, but rather
only from "material" impairments. Third, and most importantly for
our purposes, the phrase "most adequately and feasibly assures" was
revamped to read "most adequately assures, to the extent
feasible."
We have been presented with a number of different
interpretations of this shift. According to the Secretary, Senator
Dominick recognized that he could not delete the seemingly absolute
requirements of § 6(b)(5) entirely, and instead agreed to limit its
application to toxic materials or harmful physical agents, and to
specify that the Secretary was only to protect employees from
material impairment of their health. Significantly, the Secretary
asserts that his mandate to set such standards at the safest level
technologically and economically
Page 448 U. S. 680
achievable remained unchanged by the Dominick amendment.
According to the Secretary, the change in language from "most
adequately and feasibly assures" to "most adequately assures, to
the extent feasible," represented only a slight shift in emphasis,
perhaps suggesting "a preference for health protection over cost."
App. to Brief for Federal Parties 7a, n. 2.
See also Brief
for Federal Parties 59.
MR. JUSTICE MARSHALL reads this history quite differently. In
his view, the version of § 6(b)(5) that reached the Senate floor
did not "clearly embod[y] the feasibility requirement," and thus
was soundly criticized as being unrealistic.
See post at
448 U. S. 693.
It was only as a result of the floor amendments, which replaced
"most adequately and feasibly assures" with "most adequately
assures, to the extent feasible," that the Secretary clearly was
authorized to reject a standard if it proved technologically or
economically infeasible.
See also post at
448 U. S. 710,
and
448 U. S.
720-721, n. 34.
Respondents cast yet a third light on these events, focusing
upon a few places in the legislative history where the words
"feasible" and "reasonable" were used more or less interchangeably.
See S.Rep. No. 91-2193, pp. 8-10 (1969), Leg.Hist. 380;
115 Cong.Rec. 22517 (1969) (Sen. Javits). It is their contention
that, when Congress said "feasible," it meant cost-justified.
According to respondents, who agree in this regard with the
Secretary, the meaning of the feasibility requirement did not
change substantially between the version that left the Senate
Committee on Labor and Public Welfare and the version that was
ultimately adopted as part of the Act.
To my mind, there are several lessons to be gleaned from this
somewhat cryptic legislative history. First, as pointed out by MR.
JUSTICE MARSHALL, to the extent that Senator Javits, Senator
Dominick and other Members were worried about imposing upon the
Secretary the impossible burden of assuring absolute safety, they
did not view § 3(8) of the Act
Page 448 U. S. 681
as a limitation on that duty. I therefore find it difficult to
accept the conclusion of the lower court, as embellished by
respondents, that § 3(8) acts as a general check upon the
Secretary's duty under § 6(b)(5) to adopt the most protective
standard feasible.
Second, and more importantly, I believe that the legislative
history demonstrates that the feasibility requirement, as employed
in § 6(b)(5), is a legislative mirage, appearing to some Members
but not to others, and assuming any form desired by the beholder. I
am unable to accept MR. JUSTICE MARSHALL's argument that, by
changing the phrasing of § 6(b)(5) from "most adequately and
feasibly assures" to "most adequately assures, to the extent
feasible," the Senate injected into that section something that was
not already there. [
Footnote 3/4]
If I am correct in this regard, then the amendment introduced by
Senator Javits to relieve the Secretary of the duty to create a
risk-free workplace left Senator Dominick free to object to the
amended provision on the same grounds. Perhaps Senator Dominick
himself offered the aptest description of the feasibility
requirement as "no more than an admonition to the Secretary to do
his duty. . . ." 116 Cong.Rec. 36530 (1970); Leg.Hist. 367.
In sum, the legislative history contains nothing to indicate
that the language "to the extent feasible" does anything other
Page 448 U. S. 682
than render what had been a clear, if somewhat unrealistic,
standard largely, if not entirely, precatory. There is certainly
nothing to indicate that these words, as used in § 6(b)(5), are
limited to technological and economic feasibility. When Congress
has wanted to limit the concept of feasibility in this fashion, it
has said so, as is evidenced in a statute enacted the same week as
the provision at issue here. [
Footnote
3/5] I also question whether the Secretary wants to assume the
duties such an interpretation would impose upon him. In these
cases, for example, the Secretary actually declined to adopt a
standard lower than 1 ppm for some industries, not because it was
economically or technologically infeasible, but rather because
"different levels for different industries would result in serious
administrative difficulties." 43 Fed.Reg. 5947 (1978).
See also
ante at
448 U. S. 650
(plurality opinion). If § 6(b)(5) authorizes the Secretary to
reject a more protective standard in the interest of administrative
feasibility, I have little doubt that he could reject such
standards for any reason whatsoever, including even political
feasibility.
III
In prior cases, this Court has looked to sources other than the
legislative history to breathe life into otherwise vague
delegations of legislative power. In
American Power & Light
Co. v. SEC, 329 U. S. 90,
329 U. S. 104
(1946), for example, this Court concluded that certain seemingly
vague delegations "derive[d] much meaningful content from the
purpose of the Act, its factual background and the statutory
context in which they appear." Here, however, there is little or
nothing in the
Page 448 U. S. 683
remaining provisions of the Occupational Safety and Health Act
to provide specificity to the feasibility criterion in § 6(b)(5).
It may be true, as suggested by MR. JUSTICE MARSHALL, that the Act
as a whole expresses a distinct preference for safety over dollars.
But that expression of preference, as I read it, falls far short of
the proposition that the Secretary must eliminate marginal or
insignificant risks of material harm right down to an industry's
breaking point.
Nor are these cases like
Lichter v. United States,
334 U. S. 742,
334 U. S.
783(1948), where this Court upheld delegation of
authority to recapture "excessive profits" in light of a
preexisting administrative practice. Here, the Secretary's approach
to toxic substances like benzene could not have predated the
enactment of § 6(b)(5) itself. Moreover, there are indications that
the post-enactment administrative practice has been less than
uniform. For example, the Occupational Safety and Health Review
Commission (OSHRC), the body charged with adjudicating citations
issued by the Secretary under the Act, apparently does not agree
with the definition of "feasibility," advanced in these cases by
the Secretary. In
Continental Can Co., 4 OSHC 1541,
1976-1977 OSHD � 21,009 (1976), the Commission reasoned:
"Clearly, employers have finite resources available for use to
abate health hazards. And, just as clearly, if they are to be made
to spend without limit for abatement of this hazard, their
financial ability to abate other hazards, including life
threatening hazards, is reduced."
Id. at 1547, 1976-1977 OSHD, p. 25,256. Furthermore,
the record in these cases contains at least one indication that the
Secretary himself was, at one time, quite uncertain what limits §
6(b)(5) placed upon him. In announcing the proposed 1 ppm standard
and discussing its economic ramifications, the Secretary explained
that,
"[w]hile the precise meaning of feasibility is not clear from
the Act, it is
Page 448 U. S. 684
OSHA's view that the term may include the economic ramifications
of requirements imposed by standards."
43 Fed.Reg. 5934 (1978). This candid and tentative statement
falls far short of the Secretary's present position that economic
and technological considerations set the only limits on his duty to
adopt the most protective standard. Finally, as noted earlier, the
Secretary has failed to apply his present stringent view uniformly,
rejecting in these cases a lower standard for some industries on
the grounds of administrative convenience.
In some cases where broad delegations of power have been
examined, this Court has upheld those delegations because of the
delegatee's residual authority over particular subjects of
regulation. In
United States v. Curtiss-Wright Export
Corp., 299 U. S. 304
(1936), this Court upheld a statute authorizing the President to
prohibit the sale of arms to certain countries if he found that
such a prohibition would "contribute to the reestablishment of
peace." This Court reasoned that, in the area of foreign affairs,
Congress
"must often accord to the President a degree of discretion and
freedom from statutory restriction which would not be admissible
were domestic affairs alone involved."
Id. at
299 U. S. 320.
Similarly,
United States v. Mazurie, 419 U.
S. 544 (1975), upheld a broad delegation of authority to
various Indian tribes to regulate the introduction of liquor into
Indian country. According to
Mazurie, limitations on
Congress' authority to delegate legislative power are "less
stringent in cases where the entity exercising the delegated
authority itself possesses independent authority over the subject
matter."
Id. at
419 U. S.
556-557. In the present cases, however, neither the
Executive Branch in general nor the Secretary in particular enjoys
any independent authority over the subject matter at issue.
Finally, as indicated earlier, in some cases, this Court has
abided by a rule of necessity, upholding broad delegations of
authority where it would be "unreasonable and impracticable
Page 448 U. S. 685
to compel Congress to prescribe detailed rules" regarding a
particular policy or situation.
American Power & Light Co.
v. SEC, 329 U.S. at
329 U. S. 105.
See also Buttfield v. Stranahan, 192 U.
S. 470,
192 U. S. 496
(1904). But no need for such an evasive standard as "feasibility"
is apparent in the present cases. In drafting § 6(b)(5), Congress
was faced with a clear, if difficult, choice between balancing
statistical lives and industrial resources or authorizing the
Secretary to elevate human life above all concerns save massive
dislocation in an affected industry. That Congress recognized the
difficulty of this choice is clear from the previously noted remark
of Senator Saxbe, who stated that,
"[w]hen we come to saying that an employer must guarantee that
such an employee is protected from any possible harm, I think it
will be one of the most difficult areas we are going to have to
ascertain."
116 Cong.Rec. 36522 (1970), Leg.Hist. 345. That Congress chose,
intentionally or unintentionally, to pass this difficult choice on
to the Secretary is evident from the spectral quality of the
standard it selected, and is capsulized in Senator Saxbe's
unfulfilled promise that "the terms that we are passing back and
forth are going to have to be identified."
Ibid.
IV
As formulated and enforced by this Court, the nondelegation
doctrine serves three important functions. First, and most
abstractly, it ensures to the extent consistent with orderly
governmental administration that important choices of social policy
are made by Congress, the branch of our Government most responsive
to the popular will.
See Arizona v. California,
373 U. S. 546,
373 U. S. 626
(1963) (Harlan, J., dissenting in part);
United States v.
Robel, 389 U. S. 258,
389 U. S. 276
(1967) (BRENNAN, J., concurring in result). Second, the doctrine
guarantees that, to the extent Congress finds it necessary to
delegate authority, it provides the recipient of that authority
with an
Page 448 U. S. 686
"intelligible principle" to guide the exercise of the delegated
discretion.
See J. W. Hampton & Co. v. United States,
276 U.S. at
276 U. S. 409;
Panama Refining Co. v. Ryan, 293 U.S. at
293 U. S. 430.
Third, and derivative of the second, the doctrine ensures that
courts charged with reviewing the exercise of delegated legislative
discretion will be able to test that exercise against ascertainable
standards.
See Arizona v. California, supra at
373 U. S. 626
(Harlan, J., dissenting in part);
American Power & Light
Co. v. SEC, supra at
329 U. S.
106.
I believe the legislation at issue here fails on all three
counts. The decision whether the law of diminishing returns should
have any place in the regulation of toxic substances is
quintessentially one of legislative policy. For Congress to pass
that decision on to the Secretary in the manner it did violates, in
my mind, John Locke's caveat -- reflected in the cases cited
earlier in this opinion -- that legislatures are to make laws, not
legislators. Nor, as I think the prior discussion amply
demonstrates, do the provisions at issue or their legislative
history provide the Secretary with any guidance that might lead him
to his somewhat tentative conclusion that he must eliminate
exposure to benzene as far as technologically and economically
possible. Finally, I would suggest that the standard of
"feasibility" renders meaningful judicial review impossible.
We ought not to shy away from our judicial duty to invalidate
unconstitutional delegations of legislative authority solely out of
concern that we should thereby reinvigorate discredited
constitutional doctrines of the pre-New Deal era. If the
nondelegation doctrine has fallen into the same desuetude as have
substantive due process and restrictive interpretations of the
Commerce Clause, it is, as one writer has phrased it, "a case of
death by association." J. Ely, Democracy and Distrust, A Theory of
Judicial Review 133 (1980). Indeed, a number of observers have
suggested that this Court should once more take up its burden of
ensuring that Congress does not unnecessarily delegate important
choices of social policy to politically
Page 448 U. S. 687
unresponsive administrators. [
Footnote 3/6] Other observers, as might be imagined have
disagreed. [
Footnote 3/7]
If we are ever to reshoulder the burden of ensuring that
Congress itself make the critical policy decisions, these are
surely the cases in which to do it. It is difficult to imagine a
more obvious example of Congress simply avoiding a choice which was
both fundamental for purposes of the statute and yet politically so
divisive that the necessary decision or compromise was difficult,
if not impossible, to hammer out in the legislative forge. Far from
detracting from the substantive authority of Congress, a
declaration that the first sentence of § 6(b)(5) of the
Occupational Safety and Health Act constitutes an invalid
delegation to the Secretary of Labor would preserve the authority
of Congress. If Congress wishes to legislate in an area which it
has not previously sought to enter, it will, in today's political
world, undoubtedly run into opposition no matter how the
legislation is formulated. But that is the very essence of
legislative authority under our system. It is the hard choices, and
not the filling in of the blanks, which must be made by the elected
representatives of the people. When fundamental policy decisions
underlying important legislation about to be enacted are to be
made, the buck stops with Congress and the President insofar as he
exercises his constitutional role in the legislative process.
I would invalidate the first sentence of § 6(b)(5) of the
Occupational Safety and Health Act of 1970 as it applies to
Page 448 U. S. 688
any toxic substance or harmful physical agent for which a safe
level, that is, a level at which "no employee will suffer material
impairment of health or functional capacity even if such employee
has regular exposure to [that. hazard] for the period of his
working life," is, according to the Secretary, unknown or otherwise
"infeasible." Absent further congressional action, the Secretary
would then have to choose, when acting pursuant to § 6(b)(5),
between setting a safe standard or setting no standard at all.
[
Footnote 3/8] Accordingly, for the
reasons stated above, I concur in the judgment of the Court
affirming the judgment of the Court of Appeals.
[
Footnote 3/1]
J. Locke, Second Treatise of Civil Government, in the Tradition
of Freedom, 1141, p. 244 (M. Mayer ed. 17). In the same treatise,
Locke also wrote that
"[t]he legislative cannot transfer the power of making laws to
any other hands; for it being but a delegated power from the
people, they who have it cannot pass it over to others."
Ibid.
[
Footnote 3/2]
As early as 1812, this Court had considered and rejected an
argument that a statute authorizing the President to terminate a
trade embargo on Britain and France if those two nations ceased
violating "the neutral commerce of the United States" delegated too
much discretion to the Executive Branch.
See The Brig
Aurora v. United States, 7 Cranch 382,
11 U. S. 383,
386 [argument of counsel -- omitted],
11 U. S.
388.
[
Footnote 3/3]
Respondents argue that, despite its seemingly general
application, the original version of § 6(b)(5) actually referred
only to health hazards, as opposed to safety hazards.
See
Addendum B to Brief for Respondents American Petroleum Institute
et al. 5b-6b. In support of this proposition, they cite a
portion of the legislative history where the House Committee on
Education and Labor stated that the proposed version of § 6(b)(5)
would apply when the Secretary set an "occupational health
standard." H.R.Rep. No. 91-1291, p. 18 (1970), Leg.Hist. 848.
[
Footnote 3/4]
The legislative history indicates strongly that Senator Dominick
himself saw little, if any, difference between the phrases "most
adequately and feasibly assures" and "most adequately assures, to
the extent feasible." In the course of his earlier attempt to
delete the first sentence of § 6(b)(5) entirely, he paraphrased the
unamended version of that section as requiring the Secretary to
promulgate standards that "most adequately and feasibly assure,
to the extent possible," that no employee would suffer
harm.
See 116 Cong.Rec. 36530 (1970), Leg.Hist. 367
(emphasis added). Unless Senator Dominick found a significant
difference between the words "possible" and "feasible," it is clear
that there is little difference between Senator Dominick's
perception of what the unamended section required in the way of
feasibility and what that section required after his amendment.
[
Footnote 3/5]
Sections 211(c)(2)(A) and (B) of the Clean Air Act, as amended
on Dec. 31, 1970, 84 Stat. 169, authorize the Environmental
Protection Agency to regulate, control, or prohibit automotive fuel
additives after "consideration of other
technologically or
economically feasible means of achieving emission standards. .
. ." 42 U.S.C. § 7545(c)(2)(A) (1976 ed., Supp. II) (emphasis
added).
[
Footnote 3/6]
See J. Ely, Democracy and Distrust, A Theory of
Judicial Review 131-134 (1980); J. Freedman, Crisis and Legitimacy,
The Administrative Process and American Government 78-94 (1978); T.
Lowi, The End of Liberalism: Ideology, Policy, and the Crisis of
Public Authority 129-146, 297-299 (1969); Wright, Beyond
Discretionary Justice, 81 Yale L.J. 575, 582-587 (1972); Waist-Deep
in Regulation, Washington Post, Nov. 3, 1979, p. A10, col. 1.
Cf. W. Douglas, Go East, Young Man 217 (1974).
[
Footnote 3/7]
See K. Davis, Discretionary Justice: A Preliminary
Inquiry 49-51 (1969); Stewart, The Reformation of American
Administrative Law, 88 Harv.L.Rev. 1669, 1693-1697 (1975).
Cf. Jaffe, The Illusion of the Ideal Administration, 86
Harv.L.Rev. 1183, 1190, n. 37 (1973).
[
Footnote 3/8]
This ruling would not have any effect upon standards governing
toxic substances or harmful physical agents for which safe levels
are feasible upon extant standards promulgated as "national
consensus standards" under § 6(a), nor upon the Secretary's
authority to promulgate "emergency temporary standards" under §
6(c).
MR. JUSTICE MARSHALL, with whom MR. JUSTICE BRENNAN, MR. JUSTICE
WHITE, and MR. JUSTICE BLACKMUN join, dissenting.
In cases of statutory construction, this Court's authority is
limited. If the statutory language and legislative intent are
plain, the judicial inquiry is at an end. Under our jurisprudence,
it is presumed that ill-considered or unwise legislation will be
corrected through the democratic process; a court is not permitted
to distort a statute's meaning in order to make it conform with the
Justices' own views of sound social policy.
See TVA v.
Hill, 437 U. S. 153
(1978).
Today's decision flagrantly disregards these restrictions on
judicial authority. The plurality ignores the plain meaning of the
Occupational Safety and Health Act of 1970 in order to bring the
authority of the Secretary of Labor in line with the plurality's
own views of proper regulatory policy. The unfortunate consequence
is that the Federal Government's efforts to protect American
workers from cancer and other crippling diseases may be
substantially impaired.
Page 448 U. S. 689
The first sentence of § 6(b)(5) of the Act provides:
"The Secretary, in promulgating standards dealing with toxic
materials or harmful physical agents under this subsection, shall
set the standard which most adequately assures, to the extent
feasible, on the basis of the best available evidence, that no
employee will suffer material impairment of health or functional
capacity even if such employee has regular exposure to the hazard
dealt with by such standard for the period of his working
life."
29 U.S.C. § 655(b)(5). In this case, the Secretary of Labor
found, on the basis of substantial evidence, that (1) exposure to
benzene creates a risk of cancer, chromosomal damage, and a variety
of nonmalignant but potentially fatal blood disorders, even at the
level of 1 ppm; (2) no safe level of exposure has been shown; (3)
benefits in the form of saved lives would be derived from the
permanent standard; (4) the number of lives that would be saved
could turn out to be either substantial or relatively small; (5)
under the present state of scientific knowledge, it is impossible
to calculate even in a rough way the number of lives that would be
saved, at least without making assumptions that would appear absurd
to much of the medical community; and (6) the standard would not
materially harm the financial condition of the covered industries.
The Court does not set aside any of these findings. Thus, it could
not be plainer that the Secretary's decision was fully in accord
with his statutory mandate "most adequately [to] assur[e] . . .
that no employee will suffer material impairment of health or
functional capacity. . . ."
The plurality's conclusion to the contrary is based on its
interpretation of 29 U.S.C. § 652(8), which defines an occupational
safety and health standard as one "which requires conditions . . .
reasonably necessary or appropriate to provide safe or healthful
employment. . . ." According to the plurality, a standard is not
"reasonably necessary or appropriate"
Page 448 U. S. 690
unless the Secretary is able to show that it is "at least more
likely than not,"
ante at
448 U. S. 653,
that the risk he seeks to regulate is a "significant" one.
Ibid. Nothing in the statute's language or legislative
history, however, indicates that the "reasonably necessary or
appropriate" language should be given this meaning. Indeed, both
demonstrate that the plurality's standard bears no connection with
the acts or intentions of Congress, and is based only on the
plurality's solicitude for the welfare of regulated industries. And
the plurality uses this standard to evaluate not the agency's
decision in this case, but a strawman of its own creation.
Unlike the plurality, I do not purport to know whether the
actions taken by Congress and its delegates to ensure occupational
safety represent sound or unsound regulatory policy. The critical
problem in cases like the ones at bar is scientific uncertainty.
While science has determined that exposure to benzene at levels
above 1 ppm creates a definite risk of health impairment, the
magnitude of the risk cannot be quantified at the present time. The
risk at issue has hardly been shown to be insignificant; indeed
future research may reveal that the risk is, in fact, considerable.
But the existing evidence may frequently be inadequate to enable
the Secretary to make the threshold finding of "significance" that
the Court requires today. If so, the consequence of the plurality's
approach would be to subject American workers to a continuing risk
of cancer and other fatal diseases, and to render the Federal
Government powerless to take protective action on their behalf.
Such an approach would place the burden of medical uncertainty
squarely on the shoulders of the American worker, the intended
beneficiary of the occupational Safety and Health Act. It is
fortunate indeed that at least a majority of the Justices reject
the view that the Secretary is prevented from taking regulatory
action when the magnitude of a health risk cannot be quantified on
the basis of current techniques.
See ante at
448 U. S. 666
(POWELL, J., concurring in part
Page 448 U. S. 691
and concurring in judgment);
see also ante at
448 U. S. 656,
and n. 63 (plurality opinion).
Because today's holding has no basis in the Act, and because the
Court has no authority to impose its own regulatory policies on the
Nation, I dissent.
I
Congress enacted the Occupational Safety and Health Act as a
response to what was characterized as "the grim history of our
failure to heed the occupational health needs of our workers."
[
Footnote 4/1] The failure of
voluntary action and legislation at the state level,
see
S.Rep. No. 91-1282, p. 4 (1970), Leg.Hist. 144, had resulted in a
"bleak" and "worsening" [
Footnote
4/2] situation in which 14,500 persons had died annually as a
result of conditions in the workplace. In the four years preceding
the Act's passage, more Americans were killed in the workplace than
in the contemporaneous Vietnam War, S.Rep. No. 91-1283, at 2
Leg.Hist. 142. The Act was designed as "a safety bill of rights for
close to 60 million workers." [
Footnote
4/3] Its stated purpose is
"to assure so far as possible every working man and woman in the
Nation safe and healthful working conditions, and to preserve our
human resources."
29 U.S.C. § 651(b).
See Atlas Roofing Co. v. Occupational
Safety and Health Review Comm'n, 430 U.
S. 442,
430 U. S.
444-445 (1977)
The Act is enforced primarily through two provisions. First, a
"general duty" is imposed upon employers to furnish employment and
places of employment "free from recognized hazards that are causing
or are likely to cause death or serious physical harm. . . ." 29 U.
S C. § 654(a)(1). Second the Secretary of Labor is authorized to
set "occupational safety
Page 448 U. S. 692
and health standards," defined as standards requiring
"conditions, or the adoption or use of one or more practices,
means, methods, operations, or processes, reasonably necessary or
appropriate to provide safe or healthful employment and places of
employment."
29 U.S.C. § 652(8).
The legislative history of the Act reveals Congress' particular
concern for health hazards of "unprecedented complexity" that had
resulted from chemicals whose toxic effects "are only now being
discovered." S.Rep. No. 91-1282,
supra, at 2, Leg.Hist.
142.
"Recent scientific knowledge points to hitherto unsuspected
cause-and-effect relationships between occupational exposures and
many of the so-called chronic diseases -- cancer, respiratory
ailments, allergies, heart disease, and others."
Ibid. Members of Congress made repeated references to
the dangers posed by carcinogens and to the defects in our
knowledge of their operation and effect. [
Footnote 4/4] One of the primary purposes of the Act was
to ensure regulation of these "insidious
silent' killers."
[Footnote 4/5]
This special concern led to the enactment of the first sentence
of 29 U.S.C. § 655(b)(5), which, as noted above, provides:
"The Secretary, in promulgating standards dealing with toxic
materials or harmful physical agents under this subsection, shall
set the standard which most adequately assures, to the extent
feasible, on the basis of the best available evidence, that no
employee will suffer material impairment of health or functional
capacity even if such employee has regular exposure to the hazard
dealt with by such standard for the period of his working
life."
This directive is designed to implement three legislative
purposes.
Page 448 U. S. 693
First, Congress recognized that there may be substances that
become dangerous only upon repeated or frequent exposure. [
Footnote 4/6] The Secretary was therefore
required to provide protection even from substances that would
cause material impairment only upon exposure occurring throughout
an employee's working life. Second, the requirement that the
Secretary act on the basis of "the best available evidence" was
intended to ensure that the standard-setting process would not be
destroyed by the uncertainty of scientific views. Recognizing that
existing knowledge may be inadequate, Congress did not require the
Secretary to wait until definitive information could be obtained.
Thus, "it is not intended that the Secretary be paralyzed by debate
surrounding diverse medical opinions." H.R. Rep. No. 91-1291, p. 18
(1970), Leg.Hist. 848. Third, Congress' special concern for the
"silent killers" was felt to justify an especially strong directive
to the Secretary in the standard-setting process. 116 Cong.Rec.
37622 (1970), Leg.Hist. 502 (Sen. Dominick).
The authority conferred by § 655(b)(5), however, is not
absolute. The subsection itself contains two primary limitations.
The requirement of "material" impairment was designed to prohibit
the Secretary from regulating substances that create a trivial
hazard to affected employees. [
Footnote
4/7] Moreover, all standards promulgated under the subsection
must be "feasible." During the floor debates, Congress expressed
concern that a prior version of the bill, not clearly embodying the
feasibility requirement, would require the Secretary to close down
whole industries in order to eliminate risks of impairment. This
standard was criticized as unrealistic. [
Footnote 4/8]
Page 448 U. S. 694
The feasibility requirement was imposed as an affirmative limit
on the standard-setting power.
The remainder of § 655(b)(5), applicable to all safety and
health standards, requires the Secretary to base his standards
"upon research, demonstrations, experiments, and such other
information as may be appropriate." In setting standards, the
Secretary is directed to consider "the attainment of the highest
degree of health and safety protection for the employee," and
also
"the latest available scientific data in the field, the
feasibility of the standards, and experience gained under this and
other health and safety laws."
The Act makes provision for judicial review of occupational
safety and health standards promulgated pursuant to § 655(b)(5).
The reviewing court must uphold the Secretary's
Page 448 U. S. 695
determinations if they are supported by "substantial evidence in
the record considered as a whole." 29 U.S.C. § 655(f). It is to
that evidence that I now turn.
II
The plurality's discussion of the record in this case is both
extraordinarily arrogant and extraordinarily unfair. It is arrogant
because the plurality presumes to make its own factual findings
with respect to a variety of disputed issues relating to carcinogen
regulation.
See, e.g., ante at
448 U. S.
656-657, and n. 64. It should not be necessary to remind
the Members of this Court that they were not appointed to undertake
independent review of adequately supported scientific findings made
by a technically expert agency. [
Footnote 4/9] And the plurality's discussion is unfair
because its characterization of the Secretary's report bears
practically no resemblance to what the Secretary actually did in
this case. Contrary to the plurality's suggestion, the Secretary
did not rely blindly on some Draconian carcinogen "policy."
See
ante at
448 U. S.
624-625,
448 U. S.
635-636. If he had, it would have been sufficient for
him to have observed that
Page 448 U. S. 696
benzene is a carcinogen, a proposition that respondents do not
dispute. Instead, the Secretary gathered over 50 volumes of
exhibits and testimony and offered a detailed and evenhanded
discussion of the relationship between exposure to benzene at all
recorded exposure levels and chromosomal damage, aplastic anemia,
and leukemia. In that discussion he evaluated, and took seriously,
respondents' evidence of a safe exposure level.
See also
ante at
448 U. S. 666
(POWELL, J., concurring in pa.rt and in judgment).
The hearings on the proposed standard were extensive,
encompassing 17 days from July 19 through August 10, 1977. The 95
witnesses included epidemiologists, toxicologists, physicians,
political economists, industry representatives, and members of the
affected workforce. Witnesses were subjected to exhaustive
questioning by representatives from a variety of interested groups
and organizations.
Three basic positions were presented at the hearings. The first
position was that the proposed 1 ppm standard was necessary,
because exposure to benzene would cause material impairment of the
health of workers no matter how low the exposure level. Some direct
evidence indicated that exposure to benzene had caused chromosomal
damage, blood disorders, and leukemia at or below the 10 ppm level
itself. More important, it was suggested that the recorded effects
of benzene at higher levels required an inference that leukemia and
other disorders would result at levels of 1 ppm and lower,
especially after the prolonged exposure typical in industrial
settings. Therefore, the standard should be set at the lowest
feasible level, which was 1 ppm.
The second position was that a 1 ppm exposure level would itself
pose an unwarranted threat to employee health and safety, and that
the available evidence necessitated a significantly lower level. An
exposure limit below 1 ppm, it was argued, would be feasible. There
were suggestions that benzene was gradually being replaced in many
of the affected
Page 448 U. S. 697
industries, and that most companies were already operating at or
below the 1 ppm level.
The third position was that the 1971 standard should be
retained. Proponents of this position suggested that evidence
linking low levels of benzene exposure to leukemia was uncertain,
that the current exposure limit was sufficiently safe, and that the
benefits of the proposed standard would be insufficient to justify
the standard's costs. In addition, there was testimony that the
expenses required by the proposed standard would be
prohibitive.
The regulations announcing the permanent standard for benzene
are accompanied by an extensive statement of reasons summarizing
and evaluating the results of the hearings. The Secretary found
that the evidence showed that exposure to benzene causes
chromosomal damage, a variety of nonmalignant blood disorders, and
leukemia. 43 Fed.Reg. 5921 (1978). He concluded that low
concentrations imposed a hazard that was sufficiently grave to call
for regulatory action under the Act.
Evidence of deleterious effects. The Secretary referred
to studies which conclusively demonstrated that benzene could
damage chromosomes in blood-forming cells.
Id. at 5932.
There was testimony suggesting a causal relationship between
chromosomal damage and leukemia, although it could not be
determined whether and to what extent such damage would impair
health.
Id. at 5933. [
Footnote 4/10] Some studies had suggested chromosomal
damage at exposure levels of 10-25 ppm and lower. [
Footnote 4/11] No quantitative dose-response
curve, showing the relationship between exposure levels and
incidence of chromosomal damage, could yet be established.
Id. at 5933-5934. The evidence of chromosomal damage was,
in the Secretary's view, a cause for "serious concern."
Id. at 5933.
The most common effect of benzene exposure was a decrease
Page 448 U. S. 698
in the levels of blood platelets and red and white blood cells.
If sufficiently severe, the result could be pancytopenia or
aplastic anemia, noncancerous but potentially fatal diseases. There
was testimony that some of the nonmalignant blood disorders caused
by benzene exposure could progress to, or represented, a
preleukemic stage which might eventually evolve into a frank
leukemia.
Id. at 5922. [
Footnote 4/12]
Considerable evidence showed an association between benzene and
nonmalignant blood disorders at low exposure levels. Such an
association had been established in one study in which the levels
frequently ranged from zero to 25 ppm with some concentrations
above 100 ppm,
ibid.; in another, they ranged from 5 to 30
ppm,
id. at 5923. Because of the absence of adequate data,
a dose-response curve showing the relationship between benzene
exposure and blood disorders could not be constructed. There was
considerable testimony, however, that such disorders had resulted
from exposure to benzene at or near the current level of 10 ppm and
lower. [
Footnote 4/13] The
Secretary concluded that the current standard did not provide
adequate protection. He observed that a "safety factor" of 10 to
100 was generally used to discount the level at which a causal
connection had been found in existing studies. [
Footnote 4/14] Under this approach, he concluded
that, quite apart from any leukemia risk, the permissible exposure
limit should be set at a level considerably lower than 10 ppm.
Finally, there was substantial evidence that exposure to benzene
caused leukemia. The Secretary concluded that the evidence
established that benzene was a carcinogen. A causal relationship
between benzene and leukemia was first reported in France in 1897,
and since that time, similar results had been found in a number of
countries, including Italy, Turkey, Japan, Switzerland, the Soviet
Union, and the United
Page 448 U. S. 699
States. The latest study, undertaken by the National Institute
for Occupational Safety and Health (NIOSH) in the 1970's, reported
a five-fold excess over the normal incidence of leukemia among
workers exposed to benzene at industrial plants in Ohio. There was
testimony that this study seriously understated the risk. [
Footnote 4/15]
The Secretary reviewed certain studies suggesting that low
exposure levels of 10 ppm and more did not cause any excess
incidence of leukemia. Those studies, he suggested, suffered from
severe methodological defects, as their authors frankly
acknowledged. [
Footnote 4/16]
Finally, the Secretary discussed a study suggesting a statistically
significant excess in leukemia at levels of 2 to 9 ppm.
Ibid. [
Footnote 4/17] He
found that, despite certain deficiencies in the study, it should be
considered as consistent with other studies demonstrating an excess
leukemia risk among employees exposed to benzene.
Id. at
5928.
Areas of uncertainty. The Secretary examined three
areas
Page 448 U. S. 700
of uncertainty that had particular relevance to his decision.
First, he pointed to evidence that the latency period for
benzene-induced leukemia could range from 2 to over 20 years.
Id. at 5930. Since lower exposure levels lead to an
increase in the latency period, it would be extremely difficult to
obtain evidence showing the dose-response relationship between
leukemia and exposure to low levels of benzene. Because there has
been no adequate monitoring in the past, it would be practically
impossible to determine what the exposure levels were at a time
sufficiently distant so that the latency period would have elapsed.
The problem was compounded by the difficulty of conducting a
suitable study. Because exposure levels approaching 10 ppm had been
required only recently, direct evidence showing the relationship
between leukemia and exposure levels between 1 and 10 ppm would be
unavailable in the foreseeable future.
Second, the Secretary observed that individuals have differences
in their susceptibility to leukemia.
Ibid. Among those
exposed to benzene was a group of unknown but possibly substantial
size having various "predisposing factors" whose members were
especially vulnerable to the disease.
Id. at 5930, 5946.
The permanent standard was designed to minimize the effects of
exposure for these susceptible individuals as well as for the
relatively insensitive,
id. at 5946, and also to
facilitate early diagnosis and treatment.
Id. at 5930.
The Secretary discussed the contention that a safe level of
exposure to benzene had been demonstrated. From the testimony of
numerous scientists, he concluded that it had not.
Id. at
5932. [
Footnote 4/18] He also
found that, although no dose-response curve could be plotted,
id. at 5946, [
Footnote
4/19] the extent of the risk
Page 448 U. S. 701
would decline with the exposure level.
Ibid. [
Footnote 4/20] Exposure at a level of 1
ppm would therefore be less dangerous than exposure at one of 10
ppm. The Secretary found that the existing evidence justified the
conclusion that he should not "wait for answers" while employees
continued to be exposed to benzene at hazardous levels.
Finally, the Secretary responded to the argument that the
permissible exposure level should be zero or lower than 1 ppm.
Id. at 5947. [
Footnote
4/21] Even though many industries had already achieved the 1
ppm level, he found that a lower level would not be feasible.
Ibid.
Costs and benefits. The Secretary offered a detailed
discussion of the role that economic considerations should play in
his determination. He observed that standards must be "feasible,"
both economically and technologically. In his view, the permanent
standard for benzene was feasible under both tests. The economic
impact would fall primarily on the more stable industries, such as
petroleum refining and petrochemical production.
Id. at
5934. These industries would be able readily to absorb the costs or
to pass them on to consumers. None of the 20 affected industries,
involving 157,000 facilities and 629,000 exposed employees,
id. at 5935, would be unable to bear the required
expenditures,
id. at 5934. He concluded that the
compliance costs were "well within the financial capability of the
covered industries."
Id. at 5941. An extensive survey of
the national economic impact of the standard, undertaken by a
private contractor, found first-year operating costs of between
$187 and $205 million, recurring annual costs of $34 million, and
investment in engineering controls of about $266 million. [
Footnote 4/22] Since respondents have not
attacked
Page 448 U. S. 702
the Secretary's basic conclusions as to cost, the Secretary's
extensive discussion need not be summarized here.
Finally, the Secretary discussed the benefits to be derived from
the permanent standard. During the hearings, it had been argued
that the Secretary should estimate the health benefits of the
proposed regulation. To do this, he would be required to construct
a dose-response curve showing, at least in a rough way, the number
of lives that would be saved at each possible exposure level.
Without some estimate of benefits, it was argued, the Secretary's
decisionmaking would be defective. During the hearings, an industry
witness attempted to construct such a dose-response curve.
Restricting himself to carcinogenic effects, he estimated that the
proposed standard would save two lives every six years, and
suggested that this relatively minor benefit would not justify the
regulation's costs.
The Secretary rejected the hypothesis that the standard would
save only two lives in six years. This estimate, he concluded, was
impossible to reconcile with the evidence in the record.
Ibid. [
Footnote 4/23] He
determined that, because of numerous
Page 448 U. S. 703
uncertainties in the existing data, it was impossible to
construct a dose-response curve by extrapolating from those data to
lower exposure levels. [
Footnote
4/24] More generally, the Secretary
Page 448 U. S. 704
observed that it had not been established that there was a safe
level of exposure for benzene. Since there was considerable
testimony that the risk would decline with the exposure level,
id. at 5940, the new standard would save lives. The number
of lives saved "may be appreciable," but there was no way to make a
more precise determination. [
Footnote
4/25] The question was "on the frontiers of scientific
knowledge."
Ibid.
The Secretary concluded that, in light of the scientific
uncertainty, he was not required to calculate benefits more
precisely.
Id. at 5941. In any event, he gave "careful
consideration" to the question of whether the admittedly
substantial costs were justified in light of the hazards of benzene
exposure. He concluded that those costs were "necessary" in order
to promote the purposes of the Act.
III
A
This is not a case in which the Secretary found, or respondents
established, that no benefits would be derived from a permanent
standard, or that the likelihood of benefits was insignificant. Nor
was it shown that a quantitative estimate of benefits could be made
on the basis of "the best available evidence." Instead, the
Secretary concluded that benefits will result, that those benefits
"may" be appreciable, but that the dose-response relationship of
low levels of benzene
Page 448 U. S. 705
exposure and leukemia, nonmalignant blood disorders, and
chromosomal damage was impossible to determine. The question
presented is whether, in these circumstances, the Act permits the
Secretary to take regulatory action, or whether he must allow
continued exposure until more definitive information becomes
available.
As noted above, the Secretary's determinations must be upheld if
supported by "substantial evidence in the record considered as a
whole." 29 U.S.C. § 655(f). This standard represents a legislative
judgment that regulatory action should be subject to review more
stringent than the traditional "arbitrary and capricious" standard
for informal rulemaking. We have observed that the arbitrary and
capricious standard itself contemplates a searching "inquiry into
the facts" in order to determine "whether the decision was based on
a consideration of the relevant factors and whether there has been
a clear error of judgment."
Citizens to Preserve Overton Park
v. Volpe, 401 U. S. 402,
401 U. S. 416
(1971). Careful performance of this task is especially important
when Congress has imposed the comparatively more rigorous
"substantial evidence" requirement. As we have emphasized, however,
judicial review under the substantial evidence test is ultimately
deferential.
See, e.g., Richardson v. Perales,
402 U. S. 389,
402 U. S. 401
(1971);
Consolo v. Federal Maritime Comm'n, 383 U.
S. 607,
383 U. S.
618-621 (1966). The agency's decision is entitled to the
traditional presumption of validity, and the court is not
authorized to substitute its judgment for that of the Secretary. If
the Secretary has considered the decisional factors and acted in
conformance with the statute, his ultimate decision must be given a
large measure of respect.
Id. 383 U.
S.
The plurality is insensitive to three factors which, in my view,
make judicial review of occupational safety and health standards
under the substantial evidence test particularly difficult. First,
the issues often reach a high level of technical complexity. In
such circumstances, the courts are required to immerse themselves
in matters to which they are unaccustomed
Page 448 U. S. 706
by training or experience. Second, the factual issues with which
the Secretary must deal are frequently not subject to any
definitive resolution. Often "the factual finger points, it does
not conclude."
Society of Plastics Industry, Inc. v. OSHA,
509 F.2d 1301, 1308 (CA2) (Clark, J.),
cert. denied, 421
U.S. 992 (1975). Causal connections and theoretical extrapolations
may be uncertain. Third, when the question involves determination
of the acceptable level of risk, the ultimate decision must
necessarily be based on considerations of policy, as well as
empirically verifiable facts. Factual determinations can, at most,
define the risk in some statistical way; the judgment whether that
risk is tolerable cannot be based solely on a resolution of the
facts.
The decision to take action in conditions of uncertainty bears
little resemblance to the sort of empirically verifiable factual
conclusions to which the substantial evidence test is normally
applied. Such decisions were not intended to be unreviewable; they
too must be scrutinized to ensure that the Secretary has acted
reasonably and within the boundaries set by Congress. But a
reviewing court must be mindful of the limited nature of its role.
See Vermont Yankee Nuclear Power Corp. v. NRDC,
435 U. S. 519
(1978). It must recognize that the ultimate decision cannot be
based solely on determinations of fact, and that those factual
conclusions that have been reached are ones which the courts are
ill-equipped to resolve on their own.
Under this standard of review, the decision to reduce the
permissible exposure level to 1 ppm was well within the Secretary's
authority. The Court of Appeals upheld the Secretary's conclusions
that benzene causes leukemia, blood disorders, and chromosomal
damage even at low levels, that an exposure level of 10 ppm is more
dangerous than one of 1 ppm, and that benefits will result from the
proposed standard. It did not set aside his finding that the number
of lives that would be saved was not subject to quantification.
Page 448 U. S. 707
Nor did it question his conclusion that the reduction was
"feasible."
In these circumstances, the Secretary's decision was reasonable,
and in full conformance with the statutory language requiring that
he
"set the standard which most adequately assures, to the extent
feasible, on the basis of the best available evidence, that no
employee will suffer material impairment of health or functional
capacity even if such employee has regular exposure to the hazard
dealt with by such standard for the period of his working
life."
29 U.S.C. § 655(b)(5). On this record, the Secretary could
conclude that regular exposure above the 1 ppm level would pose a
definite risk resulting in material impairment to some
indeterminate but possibly substantial number of employees. Studies
revealed hundreds of deaths attributable to benzene exposure.
Expert after expert testified that no safe level of exposure had
been shown, and that the extent of the risk declined with the
exposure level. There was some direct evidence of incidence of
leukemia, nonmalignant blood disorders, and chromosomal damage at
exposure levels of 10 ppm and below. Moreover, numerous experts
testified that existing evidence required an inference that an
exposure level above 1 ppm was hazardous. We have stated that
"well-reasoned expert testimony -- based on what is known and
uncontradicted by empirical evidence -- may. in and of itself, be
'substantial evidence' when first-hand evidence on the question . .
. is unavailable."
FPC v. Florida Power & Light Co., 404 U.
S. 453,
404 U. S. 461
65 (1972). Nothing in the Act purports to prevent the Secretary
from acting when definitive information as to the quantity of a
standard's benefits is unavailable. [
Footnote 4/26] Where, as here, the deficiency in
Page 448 U. S. 708
knowledge relates to the extent of the benefits, rather than
their existence, I see no reason to hold that the Secretary has
exceeded his statutory authority.
B
The plurality avoids this conclusion through reasoning that may
charitably be described as obscure. According to the plurality, the
definition of occupational safety and health standards as those
"reasonably necessary or appropriate to provide safe or healthful .
. . working conditions" requires the Secretary to show that it is
"more likely than not" that the risk he seeks to regulate is a
"significant" one.
Ante at
448 U. S. 653.
The plurality does not show how this requirement can be plausibly
derived from the "reasonably necessary or appropriate" clause.
Indeed, the plurality's reasoning is refuted by the Act's language,
structure, and legislative history, and it is foreclosed by every
applicable guide to statutory construction. In short, the
plurality's standard is a fabrication bearing no connection with
the acts or intentions of Congress.
At the outset, it is important to observe that "reasonably
necessary or appropriate" clauses are routinely inserted in
regulatory legislation, and in the past, such clauses have
uniformly been interpreted as general provisos that regulatory
actions must bear a reasonable relation to those statutory purposes
set forth in the statute's substantive provisions.
See, e.g.,
FCC v. National Citizens Committee for Broadcasting,
436 U. S. 775,
436 U. S.
796-797 (1978);
Mourning v. Family Publications
Service, Inc., 411 U. S. 356,
411 U. S. 369
(1973);
Thorpe
Page 448 U. S. 709
v. Housing Authority of City of Durham, 393 U.
S. 268,
393 U. S.
280-281 (1969). The Court has never -- until today --
interpreted a "reasonably necessary or appropriate" clause as
having a substantive content that supersedes a specific
congressional directive embodied in a provision that is focused
more particularly on an agency's authority. This principle, of
course, reflects the common understanding that the determination of
whether regulations are "reasonably necessary" may be made only by
reference to the legislative judgment reflected in the statute; it
must not be based on a court's own, inevitably subjective, view of
what steps should be taken to promote perceived statutory
goals.
The plurality suggests that, under the "reasonably necessary"
clause, a workplace is not "unsafe" unless the Secretary is able to
convince a reviewing court that a "significant" risk is at issue.
Ante at
448 U. S. 642.
That approach is particularly embarrassing in this case, for it is
contradicted by the plain language of the Act. The plurality's
interpretation renders utterly superfluous the first sentence of §
655(b)(5), which, as noted above, requires the Secretary to set the
standard "which most adequately assures . . . that no employee will
suffer material impairment of health." Indeed, the plurality's
interpretation reads that sentence out of the Act. By so doing, the
plurality makes the test for standards regulating toxic substances
and harmful physical agents substantially identical to the test for
standards generally -- plainly the opposite of what Congress
intended. And it is an odd canon of construction that would insert
in a vague and general definitional clause a threshold requirement
that overcomes the specific language placed in a standard-setting
provision. The most elementary principles of statutory construction
demonstrate that precisely the opposite interpretation is
appropriate.
See, e.g., FPC v. Texaco Inc., 417 U.
S. 380,
417 U. S.
394-395 (1974);
Clark v. Uebersee Finanz-Korp.,
332 U. S. 480,
332 U. S.
488-489 (1947). In short, Congress could have provided
that the Secretary may not take regulatory action until the
existing
Page 448 U. S. 710
scientific evidence proves the risk at issue to be
"significant," [
Footnote 4/27]
but it chose not to do so.
The plurality's interpretation of the "reasonably necessary or
appropriate" clause is also conclusively refuted by the legislative
history. While the standard-setting provision that the plurality
ignores received extensive legislative attention, the definitional
clause received none at all. An earlier version of the Act,
see 448
U.S. 607fn4/8|>n. 8,
supra, did not embody a clear
feasibility constraint and was not restricted to toxic substances
or to "material" impairments. The "reasonably necessary or
appropriate" clause was contained in this prior version of the
bill, as it was at all relevant times. In debating this version,
Members of Congress repeatedly expressed concern that it would
require a risk-free universe.
See, e.g., ante at
448 U. S.
646-649. The definitional clause was not mentioned at
all, an omission that would be incomprehensible if Congress
intended
Page 448 U. S. 711
by that clause to require the Secretary to quantify the risk he
sought to regulate in order to demonstrate that it was
"significant."
The only portions of the legislative history on which the
plurality relies,
see ibid., have nothing to do with the
"reasonably necessary or appropriate" clause from which the
"threshold finding" requirement is derived. Those portions
consisted of criticisms directed toward the earlier version of the
statute
which already contained the definitional clause.
These criticisms, in turn, were met by subsequent amendments that
limited application of the strict "no employee will suffer" clause
to toxic substances, inserted an explicit feasibility constraint,
and modified the word "impairment" by the adjective "material." It
is disingenuous, at best, for the plurality to suggest that
isolated statements in the legislative history, expressing concerns
that were met by subsequent amendments not requiring any
"threshold" finding, can justify reading such a requirement into a
"reasonably necessary" clause that was in the Act all along.
[
Footnote 4/28]
Page 448 U. S. 712
The plurality's various structural arguments are also
unconvincing. The fact that a finding of "grave danger" is required
for temporary standards,
see ante at
448 U. S. 40, n.
45, hardly implies that the Secretary must show for permanent
standards that it is more probable than not that the substance to
be regulated poses a "significant" risk. Nor is the reference to
"toxic materials,"
ante at
448 U. S. 643,
in any way informative. And the priority-setting provision,
ante at
448 U. S.
643-644, cannot plausibly be read to condition the
Secretary's standard-setting authority on an ability to meet the
Court's "threshold" requirement.
The plurality ignores applicable canons of construction,
apparently because it finds their existence inconvenient. But as we
stated quite recently, the inquiry into statutory purposes should
be
"informed by an awareness that the regulation is entitled to
deference unless it can be said not to be a reasoned and
supportable interpretation of the Act."
Whirlpool Corp. v. Marshall, 445 U. S.
1,
445 U. S. 11
(1980). Can it honestly be said that the Secretary's interpretation
of the Act is "unreasoned" or "unsupportable"? And as we stated in
the same case, "safety legislation is to be liberally construed to
effectuate the congressional purpose."
Id. at
445 U. S. 13. The
plurality's disregard of these principles gives credence to the
frequently voiced criticism that they are honored only when the
Court finds itself in substantive agreement with the agency action
at issue.
In short, today's decision represents a usurpation of
decisionmaking authority that has been exercised by and properly
belongs with Congress and its authorized representatives.
Page 448 U. S. 713
The plurality's construction has no support in the statute's
language, structure, or legislative history. The threshold finding
that the plurality requires is the plurality's own invention. It
bears no relationship to the acts or intentions of Congress, and it
can be understood only as reflecting the personal views of the
plurality as to the proper allocation of resources for safety in
the American workplace.
C
The plurality is obviously more interested in the consequences
of its decision than in discerning the intention of Congress. But
since the language and legislative history of the Act are plain,
there is no need for conjecture about the effects of today's
decision.
"It is not for us to speculate, much less act, on whether
Congress would have altered its stance had the specific events of
this case been anticipated."
TVA v. Hill, 437 U.S. at
438 U. S. 18. I
do not pretend to know whether the test the plurality erects today
is, as a matter of policy, preferable to that created by Congress
and its delegates: the area is too fraught with scientific
uncertainty, and too dependent on considerations of policy, for a
court to be able to determine whether it is desirable to require
identification of a "significant" risk before allowing an
administrative agency to take regulatory action. But in light of
the tenor of the plurality opinion, it is necessary to point out
that the question is not one-sided, and that Congress' decision to
authorize the Secretary to promulgate the regulation at issue here
was a reasonable one.
In this case, the Secretary found that exposure to benzene at
levels above 1 ppm posed a definite, albeit unquantifiable, risk of
chromosomal damage, nonmalignant blood disorders, and leukemia. The
existing evidence was sufficient to justify the conclusion that
such a risk was presented, but it did not permit even rough
quantification of that risk. Discounting for the various scientific
uncertainties, the Secretary gave
Page 448 U. S. 714
"careful consideration to the question of whether th[e]
substantial costs" of the standard "are justified in light of the
hazards of exposure to benzene," and concluded that
"these costs are necessary in order to effectuate the statutory
purpose . . . and to adequately protect employees from the hazards
of exposure to benzene."
43 Fed.Reg. 5941 (1978).
In these circumstances, it seems clear that the Secretary found
a risk that is "significant" in the sense that the word is normally
used. There was some direct evidence of chromosomal damage,
nonmalignant blood disorders, and leukemia at exposures at or near
10 ppm and below. In addition, expert after expert testified that
the recorded effects of benzene exposure at higher levels justified
an inference that an exposure level above 1 ppm was dangerous. The
plurality's extraordinarily searching scrutiny of this factual
record reveals no basis for a conclusion that quantification is, on
the basis of "the best available evidence," possible at the present
time. If the Secretary decided to wait until definitive information
was available, American workers would be subjected for the
indefinite future to a possibly substantial risk of benzene-induced
leukemia and other illnesses. It is unsurprising, at least to me,
that he concluded that the statute authorized him to take
regulatory action now.
Under these circumstances, the plurality's requirement of
identification of a "significant" risk will have one of two
consequences. If the plurality means to require the Secretary
realistically to "quantify" the risk in order to satisfy a court
that it is "significant," the record shows that the plurality means
to require him to do the impossible. But regulatory inaction has
very significant costs of its own. The adoption of such a test
would subject American workers to a continuing risk of cancer and
other serious diseases; it would disable the Secretary from
regulating a wide variety of carcinogens for which quantification
simply cannot be undertaken at the present time.
Page 448 U. S. 715
There are encouraging signs that today's decision does not
extend that far. [
Footnote 4/29]
My Brother POWELL concludes that the Secretary is not prevented
from taking regulatory action "when reasonable quantification
cannot be accomplished by any known methods."
See ante at
448 U. S. 666.
The plurality also indicates that it would not prohibit the
Secretary from promulgating safety standards when quantification of
the benefits is impossible.
See ante at
448 U. S.
656-657, and n. 63. The Court might thus allow the
Secretary to attempt to make a very rough quantification of the
risk imposed by a carcinogenic substance, and give considerable
deference to his finding that the risk was significant. If so, the
Court would permit the Secretary to promulgate precisely the same
regulation involved in these cases if he had not relied on a
carcinogen "policy," but undertaken a review of the evidence and
the
Page 448 U. S. 716
expert testimony and concluded, on the basis of conservative
assumptions, that the risk addressed is a significant one. Any
other interpretation of the plurality's approach would allow a
court to displace the agency's judgment with its own subjective
conception of "significance," a duty to be performed without
statutory guidance.
The consequences of this second approach would hardly be
disastrous; indeed, it differs from my own principally in its
assessment of the basis for the Secretary's decision in these
cases. It is objectionable, however, for three reasons. First, the
requirement of identification of a "significant" risk simply has no
relationship to the statute that the Court today purports to
construe. Second, if the "threshold finding" requirement means only
that the Secretary must find "that there is a need for such a
standard,"
ante at
448 U. S. 643,
n. 48, the requirement was plainly satisfied by the Secretary's
express statement that the standard's costs
"are necessary in order to effectuate the statutory purpose . .
. and to adequately protect employees from the hazards of exposure
to benzene."
43 Fed.Reg. 5941 (1978). Third, the record amply demonstrates
that, in light of existing scientific knowledge, no purpose would
be served by requiring the Secretary to take steps to quantify the
risk of exposure to benzene at low levels. Any such quantification
would be based not on scientific "knowledge" as that term is
normally understood, but on considerations of policy. For
carcinogens like benzene, the assumptions on which a dose-response
curve must be based are necessarily arbitrary. To require a
quantitative showing of a "significant" risk, therefore, would
either paralyze the Secretary into inaction or force him to deceive
the public by acting on the basis of assumptions that must be
considered too speculative to support any realistic assessment of
the relevant risk.
See McGarity, Substantive and
Procedural Discretion in Administrative Resolution of Science
Policy Questions: Regulating Carcinogens in EPA and OSHA, 67
Geo.L.J. 729, 806 (1979). It is encouraging that the Court appears
willing
Page 448 U. S. 717
not to require quantification when it is not fairly possible.
See ante at
448 U. S.
656-657, and n. 63.
Though it is difficult to see how a future Congress could be any
more explicit on the matter than was the Congress that passed the
Act in 1970, it is important to remember that today's decision is
subject to legislative reversal. Congress may continue to believe
that the Secretary should not be prevented from protecting American
workers from cancer and other fatal diseases until scientific
evidence has progressed to a point where he can convince a federal
court that the risk is "significant." Today's decision is
objectionable not because it is final, but because it places the
burden of legislative inertia on the beneficiaries of the safety
and health legislation in question in these cases. By allocating
the burden in this fashion, the Court requires the American worker
to return to the political arena and to win a victory that he won
once before in 1970. I am unable to discern any justification for
that result.
D
Since the plurality's construction of the "reasonably necessary
or appropriate" clause is unsupportable, I turn to a brief
discussion of the other arguments that respondents offer in support
of the judgment below.
First, respondents characterize the Act as a pragmatic statute
designed to balance the benefits of a safety and health regulation
against its costs. Respondents observe that the statute speaks in
terms of relative protection by providing that safety must be
assured "so far as possible," 29 U.S.C. § 651(b), and by stating
that the "no material impairment" requirement is to be imposed only
"to the extent feasible." [
Footnote
4/30]
Page 448 U. S. 718
Respondents contend that the term "feasible" should be read to
require consideration of the economic burden of a standard not
merely its technological achievability. I do not understand the
Secretary to disagree. But respondents present no argument that the
expenditure required by the benzene standard is not feasible in
that respect. The Secretary concluded on the basis of substantial
evidence that the costs of the standard would be readily absorbed
by the 20 affected industries. One need not define the feasibility
requirement with precision in order to conclude that the benzene
standard is "feasible" in the sense that it will not materially
harm the financial condition of the regulated industries.
Respondents suggest that the feasibility requirement should be
understood not merely to refer to a standard's expense, but also to
mandate a finding that the benefits of an occupational safety and
health standard bear a reasonable relation
Page 448 U. S. 719
to its costs. I believe that the statute's language, structure,
and legislative history foreclose respondents' position. In its
ordinary meaning, an activity is "feasible" if it is capable of
achievement, not if its benefits outweigh its costs.
See
Webster's Third New International Dictionary 831 (1976). Moreover,
respondents' interpretation would render § 655(b)(5) internally
inconsistent by reading into the term "feasible" a requirement
irreconcilable with the express language authorizing the Secretary
to set standards assuring that "no employee will suffer material
impairment. . . ." Respondents' position would render that language
merely hortatory. As noted above, no cost-benefit analysis is
referred to at any point in the statute or its legislative history,
an omission which cannot be deemed inadvertent in light of the
explicit cost-benefit requirements inserted into other regulatory
legislation. [
Footnote 4/31]
Finally, the legislative history of the feasibility requirement,
see 448
U.S. 607fn4/8|>n. 8,
supra, demonstrates that
Congress' sole concern was that standards be economically and
technologically achievable. The legislative intent was to prevent
the Secretary from materially harming the financial condition of
regulated industries in order to eliminate risks of impairment.
Congress did not intend to preclude the Secretary from taking
regulatory action where, as here, no such threat to industry is
posed. [
Footnote 4/32]
Page 448 U. S. 720
In order to decide these cases, however, it is not necessary to
resolve the question whether the term "feasible" may contemplate
some balancing of the costs and benefits of regulatory action.
[
Footnote 4/33] Taking into
account the uncertainties in existing knowledge, the Secretary made
an express finding that the hazards of benzene exposure were
sufficient to justify the regulation's costs. 43 Fed.Reg. 5941
(1978). Any requirement to balance costs and benefits cannot be
read to invalidate this wholly rational conclusion. A contrary
result, forcing the Secretary to wait for quantitative data that
may not be available in the foreseeable future, would run directly
counter to the protective purposes of the Act. [
Footnote 4/34]
Page 448 U. S. 721
Finally, respondents suggest broadly that the Secretary did not
fulfill his statutory responsibility to act on the basis of
"research, demonstrations, experiments," and to consider
"the latest available scientific data in the field, the
feasibility of the standards, and experience gained under this and
other health and safety laws."
29 U.S.C. § 655(b)(5). Here, they contend, the Secretary based
his decision solely on "views and arguments." Brief for Respondents
American Petroleum Institute
et al. 52. I disagree. The
Secretary compiled an extensive record composed of over 50 volumes
of exhibits. Most of those exhibits are the reported results of
research and demonstrations representing "the latest available
scientific data." The Secretary offered a careful discussion of
these data in the statement accompanying the permanent standard.
His ultimate conclusions were grounded in extensive findings of
fact. Where, as here, there are gaps in existing knowledge, the
Secretary's decision must necessarily be based on considerations of
policy, as well as on empirically verifiable facts.
In passing the Occupational Safety and Health Act of 1970,
Congress was aware that it was authorizing the Secretary to
regulate in areas of scientific uncertainty. But it intended to
require stringent regulation even when definitive information was
unavailable. In reducing the permissible level of exposure to
benzene, the Secretary applied proper legal standards. His
determinations are supported by substantial evidence.
Page 448 U. S. 722
The Secretary's decision was one, then, which the governing
legislation authorized him to make. [
Footnote 4/35]
IV
In recent years, there has been increasing recognition that the
products of technological development may have harmful effects
whose incidence and severity cannot be predicted with certainty.
The responsibility to regulate such products has fallen to
administrative agencies. Their task is not an enviable one.
Frequently no clear causal link can be established between the
regulated substance and the harm to be averted. Risks of harm are
often uncertain, but inaction has considerable costs of its own.
The agency must decide whether to take regulatory action against
possibly substantial risks or to wait until more definitive
information becomes available -- a judgment
Page 448 U. S. 723
which, by its very nature, cannot be based solely on
determinations of fact. [
Footnote
4/36]
Those delegations, in turn, have been made on the understanding
that .judicial review would be available to ensure that the
agency's determinations are supported by substantial evidence, and
that its actions do not exceed the limits set by Congress. In the
Occupational Safety and Health Act, Congress expressed confidence
that the courts would carry out this important responsibility. But
in these cases, the plurality has far exceeded its authority. The
plurality's "threshold finding" requirement is nowhere to be found
in the Act, and is antithetical to its basic purposes.
"The fundamental policy questions appropriately resolved in
Congress . . . are
not subject to reexamination in the
federal courts under the guise of judicial review of agency
action."
Vermont Yankee Nuclear Power Corp. v. NRDC, 435 U.S. at
435 U. S. 558
(emphasis in original). Surely this is no less true of the decision
to ensure safety for the American worker than the decision to
proceed with nuclear power.
See ibid.
Because the approach taken by the plurality is so plainly
irreconcilable with the Court's proper institutional role, I am
certain that it will not stand the test of time. In all likelihood,
today's decision will come to be regarded as an extreme reaction to
a regulatory scheme that, as the Members of the plurality perceived
it, imposed an unduly harsh burden on regulated industries. But as
the Constitution "does not enact Mr. Herbert Spencer's Social
Statics,"
Lochner v. New York, 198 U. S.
45,
198 U. S. 75
(1905) (Holmes, J., dissenting), so the responsibility to
scrutinize federal administrative action does not authorize this
Court to strike its own balance between the
Page 448 U. S. 724
costs and benefits of occupational safety standards. I am
confident that the approach taken by the plurality today, like that
in
Lochner itself, will eventually be abandoned, and that
the representative branches of government will once again be
allowed to determine the level of safety and health protection to
be accorded to the American worker.
[
Footnote 4/1]
Legislative History of the Occupational Safety and Health Act of
1970 (Committee Print compiled for the Senate Committee on Labor
and Public Welfare), p. iii (1971) (Foreword by Sen. Williams)
(hereinafter Leg.Hist.) .
[
Footnote 4/2]
S.Rep. No. 91-1282, p. 2 (1970), Leg.Hist. 142.
[
Footnote 4/3]
Leg.Hist. iii.
[
Footnote 4/4]
S.Rep. No. 91-1282, P. 2 (1970), Leg.Hist. 142; 116 Cong.Rec.
37326 (1970), Leg.Hist. 415 (Sen. Williams); H.R.Rep. No. 91-1291,
p. 19 (1970), Leg.Hist. 849; 116 Cong.Rec. 38392-38393 (1970),
Leg.Hist. 1049 (Rep. Karth).
[
Footnote 4/5]
116 Cong.Rec. 38375 (1970), Leg.Hist. 1003 (Sen. Daniels).
[
Footnote 4/6]
116 Cong.Rec. at 37623, Leg.Hist. 503 (Sen. Dominick); H.R. No.
91-1291, p. 28 (1970), Leg.Hist. 858.
[
Footnote 4/7]
See 448
U.S. 607fn4/34|>n. 34,
infra.
[
Footnote 4/8]
An earlier version of the bill had provided:
"The Secretary, in promulgating standards under this subsection,
shall set the standard which most adequately and feasibly assures,
on the basis of the best available evidence, that no employee will
suffer any impairment of health or functional capacity, or
diminished life expectancy even if such employee has regular
exposure to the hazard dealt with by such standard for the period
of his working life."
S. 2193, 91st Cong., 2d Sess., 39 (1970), Leg.Hist. 242.
This standard, it was feared,
"could be read to require the Secretary to ban all occupations
in which there remains some risk of injury, impaired health, or
life expectancy. In the case of all occupations, it will be
impossible to eliminate all risks to safety and health. Thus, the
present criteria could, if literally applied, close every business
in this nation. In addition, in many cases, the standard which
might most 'adequately' and 'feasibly' assure the elimination of
the danger would be the prohibition of the occupation itself."
116 Cong.Rec. 36530 (1970), Leg.Hist. 367 (Statement on
Amendment of Sen. Dominick). In explaining the present language,
Senator Dominick stated:
"What we were trying to do in the bill -- unfortunately, we did
not have the proper wording or the proper drafting -- was to say
that, when we are dealing with toxic agents or physical agents, we
ought to take such steps as are feasible and practical to provide
an atmosphere within which a person's health or safety would not be
affected. Unfortunately, we had language providing that anyone
would be assured that no one would have a hazard . . . , so that no
one would have any problem for the rest of his working life."
"It was an unrealistic standard. As modified, we would be
approaching the problem by looking at the problem and setting a
standard or criterion which would not result in harm."
116 Cong.Rec. at 37622, Leg.Hist. 502.
[
Footnote 4/9]
I do not, of course, suggest that it is appropriate for a
federal court reviewing agency action blindly to defer to the
agency's findings of fact and determinations of policy. Under
Citizens to Preserve Overton Park, Inc. v. Volpe,
401 U. S. 402,
401 U. S. 416
(1971), courts must undertake a "searching and careful" judicial
inquiry into those factors. Such an inquiry is designed to require
the agency to take a "hard look,"
Kleppe v. Sierra Club,
427 U. S. 390,
427 U. S. 410,
n. 21 (1976) (citation omitted), by considering the proper factors
and weighing them in a reasonable manner. There is also room for
especially rigorous judicial scrutiny of agency decisions under a
rationale akin to that offered in
United States v. Carolene
Products Co., 304 U. S. 144,
304 U. S. 152,
n. 4 (1938).
See Environmental Defense Fund v.
Ruckelshaus, 142 U.S.App.D.C. 74, 439 F.2d 584 (1971).
I see no basis, however, for the approach taken by the plurality
today, which amounts to nearly
de novo review of questions
of fact and of regulatory policy on behalf of institutions that are
by no means unable to protect themselves in the political process.
Such review is especially inappropriate when the factual questions
at issue are ones about which the Court cannot reasonably be
expected to have expertise.
[
Footnote 4/10]
Tr. 258-259, 1039.
[
Footnote 4/11]
Id. at 148, 200-201, 258
[
Footnote 4/12]
Id. at 145, 173-174, 352, 1227, 1928, 3206; 15 Record,
Ex. 43B, p. 166.
[
Footnote 4/13]
Id. at 149, 360-361, 997, 1023, 2543, 2689, 3203; 11
Record, Ex. 3.
[
Footnote 4/14]
Tr 149, 1218, 2692, 2847.
[
Footnote 4/15]
Id. at 308, 314, 747, 768, 769-770, 874, 2445. As the
Secretary observed, the issue of the exposure level in the NIOSH
study was extensively debated during the hearings. A report from
the Industrial Commission of Ohio suggested that concentrations
generally ranged from zero to 10 or 15 ppm. But the Secretary
concluded that evidence at the hearings showed that area exposures
during the study period had sometimes substantially exceeded that
level. Because of the conflicting evidence and the absence of
monitoring data, he found that the excess leukemia risk observed in
the NIOS study could not be linked to any particular exposure
level.
[
Footnote 4/16]
As to the study on which industry relied most heavily, for
example, the Secretary, largely repeating the author's own
admissions, observed that (1) a number of employees included in the
sample may not have been exposed to benzene at any time; (2) there
was inadequate followup of numerous employees, so that persons who
may have contracted leukemia were not included in the data; (3) the
diagnoses were subject to serious question, and cases of leukemia
may have gone unnoticed; (4) no determination of exposure levels
had been made; and (5) the occupational histories of the workers
were admittedly incomplete. 43 Fed.Reg. 5928 (1978).
[
Footnote 4/17]
Tr. 1023-1024, 1227; 22A Record, Ex. 154.
[
Footnote 4/18]
The testimony of Dr. Aksoy, one of the world's leading experts,
was typical: "[E]ven one ppm . . . causes leukemia." Tr. 204.
See also id. at 30, 150, 262, 328, 351-352, 363-364, 394,
745-746, 1057, 1210, 2420; 9 Record, Ex. 2.8-272, p. 1.
[
Footnote 4/19]
Tr. 130, 360, 414-415, 416-417, 760-761, 781-782, 925, 1055-1056
; 17 Record, Ex. 75, p. 2; 1 Record, Ex. 2-4, p. 11.
[
Footnote 4/20]
Tr. 382, 401, 405, 1372, 2846, 2842-2843.
[
Footnote 4/21]
Id. at 148-149 ("the permissible exposure limit for
benzene should be zero") (testimony of Dr. Aksoy).
See also
id. at 1251
et seq., 3506
et seq.
[
Footnote 4/22]
The plurality's estimate of the amount of expenditure per
employee,
see ante at
448 U. S. 629,
is highly misleading. Most of the costs of the benzene standard
would be incurred only once, and would thus protect an
unascertainable number of employees in the future; that number will
be much higher than the number of employees currently employed
[
Footnote 4/23]
The projection, designed as an extrapolation from an
amalgamation of existing studies, was dependent on a number of
assumptions which the Secretary could reasonably view as
questionable. Indeed, the witness himself stated that his estimate
was based on "a lousy set of data," was "slightly better than a
guess," Tr. 2772, and that there was "no real basis,"
id.
at 2719, for a dose-response curve on which the estimate was wholly
dependent.
The witness' assumptions were severely tested during the
hearings,
see id. at 2795
et seq., and the
Secretary could reasonably reject them on the basis of the evidence
in the record. For example: (1) The witness appeared to assume
that, in previous tests, leukemia had been contracted after a
lifetime of exposure; the evidence afforded no basis for that
assumption, and the duration of exposure may have been quite short
for particular employees. If the duration period was short, the
witness' estimate would have been much too low. (2) The witness
assumed that exposure levels in the NIOSH study were around 100
ppm. The Secretary found, however, that no such assumption could be
made, and there was evidence that exposure levels had generally
been between zero and 10-15 ppm. (3) The witness assumed that the
dose-response curve was linear at all levels, but there was no
basis for that assumption. In the case of vinyl chloride (another
carcinogen for which the Secretary has promulgated exposure
standards), recent evidence suggested that the dose-response curve
rises steeply at low doses and becomes less steep as the levels are
increased. (4) Twenty-five percent of the workers in the NIOSH
study had not been found, and the witness assumed that they were
still alive and would not contract leukemia. Six hundred additional
workers exposed in that study were still alive; the witness assumed
they too would not contract leukemia. There was considerable
testimony that, for these and other reasons, the NIOSH study
significantly underestimated the risk. The witness assumes that it
had not. (5) The NIOSH study found a five-fold excess risk from
benzene exposure; the witness assumed that the excess was much
lower, despite the NIOSH finding and the testimony that that
finding was a significant understatement of the risk. In light of
these uncertainties, the Secretary could conclude that the witness'
estimate was unsupportable.
[
Footnote 4/24]
Witnesses testifying to the inability to construct a
dose-response curve referred primarily to the impossibility of
correlating the incidence of leukemia, blood disorders, and
chromosomal damage with the levels and duration of exposure in past
studies. Thus, Dr. Herman Kraybill of the National Cancer Institute
testified:
"[W]e like to estimate risk factors. This has been done, as many
of you recall, with vinyl chloride several years ago."
". . . [T]o estimate the risk factors on [the basis of]
experimental data, this presupposes if you have good toxicity data.
When I say toxicity data, I mean good dose-response data on vinyl
chloride, which, indeed, we did have that."
"But with benzene, it appeared that we didn't have this
situation, so therefore, most of us gave up. . . ."
"
* * * *"
". . . With benzene, we sort of struck out."
Id. at 760-761. Because of the enormous uncertainties
in levels and duration of exposure in prior studies, any
assumptions would necessarily be arbitrary. The possible range of
assumptions was so great that the ultimate conclusion would be
entirely uninformative.
See id. at 360, 415,
1055-1056.
[
Footnote 4/25]
At one point, the Secretary did indicate that appreciable
benefits were "likely" to result. The Court of Appeals held that
this conclusion was unsupported by substantial evidence. The
Secretary's suggestion, however, was made in the context of a
lengthy discussion intended to show that appreciable benefits "may"
be predicted, but that their likelihood could not be quantified.
The suggestion should not be taken as a definitive statement that
appreciable benefits were more probable than not.
For reasons stated
infra, there is nothing in the Act
to prohibit the Secretary from acting when he is unable to conclude
that appreciable benefits are more probable than not.
[
Footnote 4/26]
This is not to say that the Secretary is prohibited from
examining relative costs and benefits in the process of setting
priorities among hazardous substances, or that systematic
consideration of costs and benefits is not to be attempted in the
standard-setting process. Efforts to quantify costs and benefits,
like statements of reasons generally, may help to promote informed
consideration of decisional factors and facilitate judicial review.
See Dunlop v. Bachowski, 421 U. S. 560,
421 U. S.
571-574 (1975). The Secretary indicates that he has
attempted to quantify costs and benefits in the past.
See
43 Fed.Reg. 54354, 54427-54431 (1978) (lead);
id. at
27350, 27378-27379 (cotton dust).
It is not necessary in the present litigation to say whether the
Secretary must show a reasonable relation between costs and
benefits. Discounting for the scientific uncertainty, the Secretary
expressly -- and reasonably -- found such a relation here.
[
Footnote 4/27]
It is useful to compare the Act with other regulatory statutes
in which Congress has required a showing of a relationship between
costs and benefits or of an "unreasonable risk." In some statutes,
Congress has expressly required cost-benefit analysis or a
demonstration of some reasonable relation between costs and
benefits.
See 33 U.S.C. § 701a (Flood Control Act of
1936); 42 U.S.C. § 7545(c)(2)(b) (1976 ed., Supp. II) (Clean Air
Act); 33 U.S.C. §1314(b)(4)(b) (1976 ed., Supp. II) (Clean Water
Act). In others, Congress has imposed two independent requirements:
that administrative action be "feasible" and justified by a
balancing of costs and benefits,
e.g., 43 U.S.C. §1347(b)
(1976 ed., Supp. II) (Outer Continental Shelf Lands Act); 42 U.S.C.
§ 6295(a)(2)(D) (1976 ed., Supp. II) (Energy Policy and
Conservation Act). This approach demonstrates a legislative
awareness of the difference between a feasibility constraint and a
constraint based on weighing costs and benefits.
See infra
at
448 U. S.
719-720. In still others, Congress has authorized
regulation of "unreasonable risk," a term which has been read by
some courts to require a balancing of costs and benefits.
See,
e.g., Aqua Slide 'N' Dive Corp. v. Consumer Product Safety
Comm'n, 569 F.2d 831 (CA5 1978) (construing 15 U.S.C. §
2058(c)(2)(A) (Consumer Product Safety Act));
Forester v.
Consumer Product Safety Comm'n, 182 U.S.App.D.C. 153, 559 F.2d
774 (1977) (construing 15 U.S.C. §1261(s) (Child Protection and Toy
Safety Act)).
[
Footnote 4/28]
The plurality also relies on its perception that, if the
"reasonably necessary" clause were not given the meaning it
ascribes to it, there would be no guidance for "standards other
than those dealing with toxic materials and harmful physical
agents."
Ante at
448 U. S. 640,
n. 45. For two reasons, this argument is without force. First, even
if the "reasonably necessary" clause does have independent content,
and even if that content is as the plurality describes it, it
cannot, under any fair-minded reading, supersede the express
language of § 655(b)(5) for toxic substances and harmful physical
agents.
Second, as noted above, an earlier version of the bill applied
the "no employee will suffer" language to all substances. At that
time, there was no "gap," and accordingly it could not be argued
that the "reasonably necessary or appropriate" clause had the
content the plurality ascribes to it. In this light, the
plurality's reasoning must be that, when Congress amended the bill
to apply the strict § 655(b)(5) requirements only to toxic
substances, the definitional clause gained an independent meaning
that in turn comprehended all standards. But surely this argument
turns congressional purposes on their head. It reasons that, when
Congress singled out toxic substances for special regulation, it
simultaneously created a more lenient ("reasonably necessary") test
for standards generally, and that, once that more lenient test was
applicable, it somehow superseded the strict requirements for toxic
substances. That reasoning is both illogical and circular. Nor is
there any basis for the plurality's suggestion,
see ante
at
448 U. S. 649,
n. 54, that the original bill's application to all standards was
"entirely inadvertent."
[
Footnote 4/29]
The plurality suggests that it is for the agency "to determine,
in the first instance, what it considers to be a
significant'
risk," and that the agency "is free to use conservative assumptions
in interpreting the data. . . ." Ante at 448 U. S. 655,
448 U. S. 656.
Moreover, my Brother POWELL would not require "quantification of
risk in every case." Ante at 448 U. S. 666
(opinion concurring in part and concurring in judgment). As I read
his opinion, MR. JUSTICE POWELL would have permitted the Secretary
to promulgate the standard at issue here if the Secretary had
provided a more carefully reasoned explanation of his conclusion
that the risk at issue justified the admittedly significant costs
of the benzene standard. MR. JUSTICE POWELL also suggests that such
a conclusion would be subject to relatively deferential review.
Ante at 448 U. S.
670-671, n. 8.
In this respect, the differences between my approach and that of
MR. JUSTICE POWELL may be comparatively narrow. We are agreed on
two propositions that I regard as critical to a fair-minded
interpretation of the Act: (1) the Secretary may regulate risks
that are not subject to quantification on the basis of the "best
available evidence"; and (2) the Secretary's judgment that a
particular health risk merits regulatory action is subject to
limited judicial scrutiny. It is encouraging that at least five
Members of the Court accept these basic propositions.
For reasons stated in the text, however, I disagree with my
Brother POWELL's conclusion that it is appropriate to hold in these
cases that the Act requires the Secretary to show a reasonable
relationship between costs and benefits.
[
Footnote 4/30]
Finding obscurity in the w ord "feasible," my Brother REHNQUIST
invokes the nondelegation doctrine, which was last used to
invalidate an Act of Congress in 1935.
A.L.A. Schecter Poultry
Corp. v. United States, 295 U. S. 495
(1935). While my Brother REHNQUIST eloquently argues that there
remains a place for such a doctrine in our jurisprudence, I am
frankly puzzled as to why the issue is thought to be of any
relevance here. The nondelegation doctrine is designed to assure
that the most fundamental decisions will be made by Congress, the
elected representatives of the people, rather than by
administrators. Some minimal definiteness is therefore required in
order for Congress to delegate its authority to administrative
agencies.
Congress has been sufficiently definite here. The word
"feasible" has a reasonably plain meaning, and its interpretation
can be informed by other contexts in which Congress has used it.
See n.
448
U.S. 607fn4/27|>27,
supra. Since the term is placed
in the same sentence with the "no employee will suffer" language,
it is clear that "feasible" means technologically and economically
achievable. Under the Act, the Secretary is afforded considerably
more guidance than are other administrators acting under different
regulatory statutes. In short, Congress has made "the critical
policy decisions" in these cases,
see ante at
448 U. S. 687
(REHNQUIST, J., concurring in judgment) .
The plurality's apparent suggestion,
see ante at
448 U. S. 646,
that the nondelegation doctrine might be violated if the Secretary
were permitted to regulate definite but nonquantifiable risks is
plainly wrong. Such a statute would be quite definite, and would
thus raise no constitutional question under
Schechter
Poultry. Moreover, Congress could rationally decide that it
would be better to require industry to bear "feasible" costs than
to subject American workers to an indeterminate risk of cancer and
other fatal diseases.
[
Footnote 4/31]
See 448
U.S. 607fn4/27|>n. 27,
supra.
[
Footnote 4/32]
Congress' antipathy toward cost-benefit balancing is evident
throughout the legislative history of the Act. For example:
"The costs that will be incurred by employers in meeting the
standards of health and safety to be established under this bill
are, in my view, reasonable and necessary costs of doing business.
Whether we, as individuals, are motivated by simple humanity or by
simple economics, we can no longer permit profits to be dependent
upon an unsafe or unhealthy worksite."
116 Cong.Rec. 41766 (1970), Leg.Hist. 1150-1151 (Sen. Eagleton).
Similarly, Senator Yarborough stated:
"We are talking about people's lives, not the indifference of
some cost accountants. We are talking about assuring the men and
women who work in our plants and factories that they will go home
after a day's work with their bodies intact. We are talking about
assuring our American workers who work with deadly chemicals that,
when they have accumulated a few year's seniority, they will not
have accumulated lung congestion and poison in their bodies, or
something that will strike them down before they reach retirement
age."
116 Cong.Rec. at 37625, Leg.Hist. 510.
[
Footnote 4/33]
Nor need I discuss the possibility, raised by counsel for the
federal parties in oral argument, that a decision to regulate a
substance posing a negligible threat to health and safety could
itself be challenged as arbitrary and capricious under the
Administrative Procedure Act.
See Tr. of Oral Arg. 23.
[
Footnote 4/34]
Respondents also rely on the statutory requirement that the
Secretary may act only to prevent "material" impairment. They
contend that the standard promulgated here does not fall within
that category, because the risk is so low. This interpretation
derives no support from the statute or its legislative history. The
statute itself states that standards should ensure that no employee
will suffer "material impairment," not material
risk of
impairment.
The language is consistent with the legislative history. In an
early version of the Act, the word "impairment" was modified by
"any," rather than "material."
See 448
U.S. 607fn4/8|>n. 8,
supra. The feasibility and
materiality requirements were added simultaneously as part of an
effort to qualify the original language authorizing the Secretary
to ensure that "no employee will suffer any impairment of health or
functional capacity, or diminished life expectancy." Senator
Dominick was concerned that the phrase "any" impairment would
require the Secretary to prevent insect bites. 116 Cong.Rec. 36522
(1970), Leg.Hist. 345.
The respondents' construction would pose an enormous obstacle to
efforts to regulate toxic substances under § 655(b)(5). The
probability of contracting cancer will, in most contexts, be quite
small with respect to any particular employee. If the statute were
read to authorize the Secretary to act only to assure that "no
employee will suffer material risk of impairment," the Secretary
would be disabled from regulating substances which poses a small
risk with respect to any particular employee, but which will
nonetheless result in the death of numerous members of the employee
pool.
[
Footnote 4/35]
Although the Court of Appeals accepted the Secretary's finding
that dermal contact with benzene could cause leukemia, it set aside
the dermal contact standard because of the Secretary's failure to
perform an experiment recommended by an industry witness. The
failure to conduct this test, according to the court, violated the
statutory requirement that the Secretary act on the basis of "the
best available evidence" and "the latest available scientific data
in the field."
In the hearings before the agency, respondents presented no
substantial challenge to the position that benzene could be
absorbed through the skin, and there was evidence in the record to
support that position. Both animal and human studies had found such
absorption. In these circumstances, the Secretary was not obligated
to undertake additional studies simply because a witness testified
that such studies would be informative. The imposition of such a
requirement would paralyze the standard-setting process. The
Secretary's mandate is to act on the basis of "available" evidence,
not evidence which may become available in the future.
In setting aside the dermal contact standard, the Court of
Appeals also relied on its conclusion that the Secretary had not
shown that quantifiable benefits would result from the standard. As
the discussion above indicates, the court applied incorrect legal
standards in so holding.
[
Footnote 4/36]
See W. Lowrance, Of Acceptable Risk: Science and the
Determination of Safety (1976); Stewart, Paradoxes of Liberty,
Integrity and Fraternity: The Collective Nature of Environmental
Quality and Judicial Review of Administrative Action, 7 Environ.L.
463, 469-472 (1977).