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Metapopulation dynamics of crustaceans and results of habitat fragmentation simulation. Each graph can be visualized as a topographic map, with contour lines depicting average state at the steady-state asymptote for each parameter: ( a ) metapopulation size ( N ) at varying rates of habitat loss and dispersal; ( b ) percentage of sites inhabited at varying rates of habitat loss and dispersal; ( c ) time to asymptote at varying rates of habitat loss and dispersal.

Metapopulation dynamics of crustaceans and results of habitat fragmentation simulation. Each graph can be visualized as a topographic map, with contour lines depicting average state at the steady-state asymptote for each parameter: ( a ) metapopulation size ( N ) at varying rates of habitat loss and dispersal; ( b ) percentage of sites inhabited at varying rates of habitat loss and dispersal; ( c ) time to asymptote at varying rates of habitat loss and dispersal.

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Much of Illinois was once wet prairie, dotted with ancient (ca. 10,000-year-old) ephemeral wetlands. Most wetland habitat (85%) was converted to agriculture over a span of about 100 years (ca. 1850-1950). The consequences of this severe habitat fragmentation on wetland communities and metapopulations are unknown. We studied crustacean communities (...

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... little or no habitat loss occurred, a broad range of dispersal genotypes maintained similar large metapopu- lations (Fig. 4a). This result suggests that polymorphism of genetically determined dispersal rate would exist when prairie wetland habitat was intact, as was presum- ably the case in predrainage Illinois. However, modeled genotypes with greater dispersal rates were increasingly selected against as greater habitat fragmentation oc- curred. As habitat ...
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... modeled proportion of habitats occupied was much more sensitive to habitat fragmentation than to dispersal effects: 20% of sites were occupied when habitat loss occurred at 0.5% per year, regardless of dis- persal genotype (Fig. 4b). Less than 5% of sites were in- habited by a low-dispersing genotype (10.0% of eggs dis- persed per year) when habitat loss was 1.0% per year, yet that metapopulation experienced only a modest de- cline in size. Given habitat fragmentation and the conse- quent selection for low dispersal rates, sites tended to be either occupied by ...
Context 3
... in- habited by a low-dispersing genotype (10.0% of eggs dis- persed per year) when habitat loss was 1.0% per year, yet that metapopulation experienced only a modest de- cline in size. Given habitat fragmentation and the conse- quent selection for low dispersal rates, sites tended to be either occupied by large populations or unoccu- pied (cf. Figs. 4a & 4b). Low-dispersing genotypes main- tained large populations in extant sites, and as habitat loss progressed, those extant sites became more ...
Context 4
... were most dynamic (required more time to approach steady state) for genotypes with intermedi- ate dispersal rates and moderate habitat-loss rates, as evi- denced by the average time to reach the asymptotic stop point (Fig. 4c). At one extreme-very low habitat-loss rates-metapopulations for most dispersal genotypes quickly stabilized at large sizes and were distributed among many sites. At the other extreme-high dispersal rates across most habitat-loss rates-metapopulations rapidly declined to ...
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... loss of the corn belt habitat, consistent with the effects of habitat fragmentation on some insects ( Van Dyck & Matthysen 1999). Given that 85% of Illinois wet- lands have been lost (Dahl 1990) and that this loss oc- curred in about 100 years (approximately 1850-1950), habitat loss occurred at an average rate of about 0.85% per year. Examining Fig. 4 at that value shows that the remaining metapopulation of our model crustacean in- habits 10% of original habitat and is primarily composed of low-dispersing genotypes. Passive dispersal that occurs at high rates dilutes the few relict crustacean populations existing amid a drained landscape, consistent with the modeling results of ...

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Full-text available
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