<br />26
<br />
<br />RethJnking the Stock Concept
<br />
<br />TWO VIEWS OF INTRA-SPECIFIC STRUCTURE
<br />
<br />@_w@
<br />
<br />
<br />SPECIES 1 ~ SPECIES 2
<br />
<br />
<br />~ SPECIES'
<br />
<br />@_w@)
<br />
<br />
<br />, ,
<br />SPECIES 1 ~ SPECIES 2
<br />
<br />
<br />~ SPECIES'
<br />
<br />Figure 1. Two views of intraspecific structure, a "ty-
<br />pological" and a "biological" conception of popula-
<br />tions within species. The circles, labeled with lower-
<br />case leUers, are individual populations wbose
<br />geograpbical habitat is represented by its size and
<br />position witbin the species space. Wbere circles inter-
<br />sect, babitat is shared Tbe arrows represent exchange
<br />rates: infinitesimal between species, variable between
<br />populations within species.
<br />In the first view, individual populations within a
<br />species are perceived as isolated, allopatric entities
<br />that can be uniquely described Interchange between
<br />the populations, while greater than between species,
<br />is still very low, on tbe order of a few genomes per
<br />generation
<br />In the second view, tbe complexity and wide range
<br />of potential intraspecific structures are recognized
<br />Habitats range from completely separate to situa-
<br />tions where one is completely witbin another. Ex-
<br />change rates vary between various populations, in
<br />some cases with great temporal variability due to
<br />environmental and population density changes.
<br />
<br />ies-management questions (see Sinclair 1988; Gauldie
<br />1991). Independently, Leopold (1933) recommended
<br />managing populationS of wildlife based on their "radius
<br />of mobility," "rate of spread into unoccupied range,"
<br />and "minimum units of range and population." This ba-
<br />sic approach of managing a species at some subspecific
<br />level has therefore been a tenet in resource manage-
<br />ment for almost 100, years. In general, stock status is
<br />
<br />ConscrvadOD Biology
<br />Volume 6, No, I, Marcb 1992
<br />
<br />Dizon et aI,
<br />
<br />conferred using a variety of proxies that imply repro-
<br />ductive isolation. With isolation com~genetic diver-
<br />gence through drift and through local adaptation via
<br />processes such as differential selection ~r character dis-
<br />placement. But because reproductiv~ barriers within
<br />species are fragile or incomplete, especially in the ma-
<br />rine environment, the degree of isolation of one popu-
<br />lation relative to others can be complex, varying both in
<br />space and time.
<br />A variety of other terms in the literature all refer to
<br />organizational levels below the species: subspecies,
<br />race, deme, stock, and management unit. The use of
<br />such terms in resource management literature is highly
<br />inconsistent. Only the term "subspecies" is recognized
<br />by the International Code of Zoological Nomenclature;
<br />it is applied to populations that have received a trino-
<br />mial name. The other terms, lacking such accepted us-
<br />age, are frequently used to describe a variety of popu-
<br />lations for analytical convenience or to provide status to
<br />a group because that is the most conservative approach
<br />when data are lacking and conservation issues predom-
<br />inate. Many so-called stocks are mere "ecological ab-
<br />stractions" (Sinclair 1988),.and a perusal of the manage-
<br />ment literature indicates that when a term such as
<br />"stock" is used, it is used in the simplest and least re-
<br />strictive sense. little qualification is made or assumed
<br />about its genetic, evolutionary, or ecological implica-
<br />tions, Misconceptions occur later when such stocks are
<br />expected to behave as if they were biological popula-
<br />tions,
<br />In 1980, an ambitious attempt to formalize the stock
<br />concept was made with an international symposium
<br />(Stock Concept International Symposium convened at
<br />Alliston, Ontario, September 29-Qctober 9, 1980; see
<br />Booke [1981] for proceedings citation). Although many
<br />speakers emphasized the importance of management by
<br />stock, in that very large symposium only one author
<br />ventured any formal definitions. Booke ( 1981 ) defined a
<br />"phenotypic stock" as any population that maintains
<br />characteristics that are expressed depending on the en-
<br />vironment, and a "genotypic stock" as a population
<br />maintaining Hardy-Weinberg equilibrium, that is, con-
<br />stant gene frequencies for a particular character in each
<br />generation, The definition of phenotypic stock is similar
<br />to a later definition by Brown et aI. ( 1987): a population
<br />whose average life history parameters are meaningful
<br />from the standpoint of management. The definition of
<br />genotypic stock is similar to the definition of Larkin
<br />( 1972), who described a stock as a population having a
<br />degree of genetic uniqueness: "a population of organ-
<br />isms which, sharing a common environment and partic-
<br />ipating in a common gene pool, is sufficiently discrete to
<br />warrant consideration as a self-perpetuating system
<br />which can be managed" (p. 11). Hoelzel and Dover
<br />(1989) defined a genetic stock as one that is genetically
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