Laserfiche WebLink
<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 <br />