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determination of OSP as it can. Its proposed definition is as follows:

"Optimum sustainable population" is
a range of population sizes between
that population at which a given
stock or species realizes its max-
imum net productivity and that pop-
ulation which is the largest sup-
portable on the average within the
ecosystem. Net productivity is the
difference between reproduction and
natural mortality. Maximum net pro-
ductivity occurs at that population
level at which the given stock or
species adds the maximum number of
animals to the population on a sus-
tainable basis.56/

The outer limits of the range described in this definition thus appear to be the familiar MSY level and a hypothetical unexploited population level. While such a definition would clearly permit the maintenance of marine mammal populations at levels above MSY, it would also allow their maintenance at MSY levels. In light of the ample legislative history that Congress thought it was directing the abandonment of the MSY management standard, the proposed definition seems subject to question.57/

The skirmishes over how the administering agencies choose to define OSP will probably be less important in

56/

571

41 Fed. Reg. 44049 (Oct. 6, 1976).

The best explication of the legislative history of the development of the OSP standard can be found in Gaines & Schmidt, supra note 9 at 50103-08. The Marine Mammal Commission apparently endorses the proposed definition of the National Marine Fisheries Service as an interim definition pending the development of further information which would permit the narrowing of the range. See Marine Mammal Commission, supra note 53 at 7. However, the Commission emphasizes the difficulty of establishing precisely both actual existing population levels and MSY levels, and therefore suggests that a safety factor be included in estimates of such levels. Id. at 8-9.

the long run than the question of how much justification the courts will require to support its application in any particular instance. To date, it is at least clear from Committee for Humane Legislation, Inc. v. Richardson that the courts will not permit such agencies to ignore the requirement to determine OSP for particular species or stocks.58/ Moreover, District Judge Charles Richey's emphasis in that case that "[t]he interests of the marine mammals come first" suggests that when determinations of OSP are in fact made, they should be supported by reliable and clearly demonstrable evidence.59/

b. Depletion

No less puzzling than the Act's standard of optimum sustainable population is its provision for the determination of certain species or population stocks as "depleted." Nevertheless, such a determination has significant operational consequences. For example, public display permits may not be issued for any marine mammal determined to be depleted. Otherwise exempt

taking by Alaskan natives may be regulated when a determination of depletion is made. Most significantly,

58/

59/

540 F.2d 1141 (D.C. Cir.), aff'g 414 F. Supp. 297 (D.D.C.
1976).

The point made here is illustrated by Judge Richey's deci-
sion under the Wild Free-Roaming Horses and Burros Act in
American Horse Protection Association, Inc. v. Kleppe,
403 F. Supp. 1206 (D.D.C. 1976), in which he refused to
permit a government roundup of wild horses where the pop-
ulation figures on which it relied were merely extrapola-
tions based on estimates of prior years' populations rather
than an actual physical inventory. Judge Richey insisted
that such figures were "unreliable" and "meaningless" when
used to support an action which, on its face, was contrary
to the statutory directive that all management activities
be conducted at "minimal feasible levels." For a fuller
discussion of the case, see Chapter Six supra at text ac-
companying notes 178-83.

for reasons to be discussed, the moratorium against taking cannot be waived while any marine mammal is depleted.

Under the terms of the Act, a determination of

depletion may be made if:

the number of individuals within
a species or population stock
(A) has declined to a signif-
icant degree over a period of
years;

(B) has otherwise declined and
that if such decline continues, or
is likely to resume, such species
would be subject to the provisions
of the Endangered Species Act of
1973; or

(C) is below the optimum carrying capacity for the species or stock within its environment.60/

The ambiguity in the foregoing derives from the fact that the various criteria are stated in the disjunctive. That is, a species or population stock can be determined to be depleted if it meets any one of the three stated criteria. Thus, under criterion (C), a determination of depletion may be made if the number of individuals within a species or population stock is below the optimum carrying capacity of its environment. This criterion would be less ambiguous if its reference to optimum carrying capacity read "optimum sustainable population" instead. However, for the reasons previously described, it is submitted that the two terms mean the same thing, and therefore that a species or population must be determined to be depleted if its numbers are found to be below its OSP level.61/

60/ 16 U.S.C. $1362 (1) (Supp. IV 1974).

61/

See text accompanying notes 46-51 supra. The criterion for depletion under discussion here was added by the Conference Committee without any explanation in its report.

Even more vaguely worded is criterion (A), because the Act nowhere defines what constitutes a "significant" decline or over what period of years it is to be measured. Moreover, since each of the criteria for depletion is apparently independent of the others, it is possible to construe this criterion so as to allow a species to be declared depleted even if is numbers are above the optimum carrying capacity of its environment, so long as those numbers had declined significantly over a period of years. 62/ That interpretation, however, would be difficult to reconcile with the rest of the Act. Accordingly, a more plausible interpretation of this criterion would make it applicable where it is known that a given species or population stock has declined in numbers over a period of years, but the optimum carrying capacity of its habitat is not known.

Criterion (B) likewise engenders major interpretational difficulties. When the Marine Mammal Protection Act was passed, the Endangered Species Act of 1973 did not yet exist. Accordingly, the original reference in criterion (B) was to the Endangered Species Conservation Act of 1969. That Act, however, provided protection only for those species that were "threatened with worldwide extinction."63/ Thus, what the Marine Mammal Protection Act did in 1972 was to create a category of species or populations which, though not yet in danger of extinction, might become so in the future. That was precisely the function of the category of

62/ There is no inherent contradiction in this hypothetical situation if one assumes that the relevant environment has deteriorated over time.

63/

See Chapter Twelve infra at text accompanying notes 19-23.

"threatened" wildlife created a year later in the 1973 Act.64/

When the Endangered Species Act of 1973 was passed, its provision for protection of "threatened" species as well as "endangered" species would seem to have eliminated any need for retaining criterion (B). However, rather than eliminating that criterion, the 1973 Act merely replaced its reference to the 1969 Act with a reference to the 1973 Act. By virtue of that amendment, the Marine Mammal Protection Act now regards as "depleted" those species or population stocks which are neither endangered or threatened, but which might become so in the future. The anomaly of this scheme is that the protections afforded to "depleted" marine mammals are in certain respects even more stringent than the protections afforded to endangered species by the Endangered Species Act.65/ For example, whereas the latter Act authorizes the issuance of permits for taking endangered wildlife both for sci

64/

65/

Id. at text accompanying notes 62-64. The legislative
history of the Marine Mammal Protection Act is clear that
the object of this criterion, which was common to both
the House and Senate-passed bills, was to create a status
analogous to the "threatened" status then under consider-
ation in proposed amendments to the Endangered Species
Act of 1969. See H. Rep. No. 92-1488, 92d Cong., 2d Sess.
22 (1972).

Where a species is determined to be both depleted and endan-
gered, the Endangered Species Act of 1973 is clear that the
more restricting provisions of the Marine Mammal Protection
Act take precedence over any conflicting provisions of the
1973 Act. See 16 U.S.C. $1543 (Supp. IV 1974). Thus far,
only the Hawaiian monk seal has been declared to be both de-
pleted and endangered. See 41 Fed. Reg. 30120 (July 22,
1976) and 41 Fed. Reg. 51611 (Nov. 23, 1976). Several other
species of marine mammals are officially listed as endan-
gered, though no formal action has ever been taken to de-
clare them depleted. It is questionable whether any formal
action need be taken, however, since any endangered species
of marine mammal must of necessity also be depleted.
note 72 infra.

See

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