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Introduction
A central tenet of mating system theory is that habitat structure and composition affect the
distribution of individuals in time and space, which in turn affect patterns of mating within a
population (Emlen & Oring 1977, Westneat et al. 1990). For example, resource defense
polygyny occurs when males defend resources attractive to females In habitats where resources
are unevenly distributed, males that defend more of the resource may acquire more mates than
other males. If resources are evenly distributed, they are less easily monopolized, and males tend
to mate monogamously (Emlen and Oring 1977). Similarly, extra-pair paternity (EPP) may be
influenced by habitat. In areas where resources are clumped, density may be high, which can
increase encounter rates between individuals on different territories, thereby increasing EPP
(Birkhead 1978, Westneat and Sherman 1997). Habitat structure and distribution can also affect
the trade-offs with mate-guarding, thereby affecting EPP (Westneat et al. 1990, Mays and
Ritchison 2006).
Habitat structure is often greatly influenced by human activity. While the negative effects of
habitat destruction are well known, a common response to such negative impacts is to use
management techniques to restore or maintain habitat. It is becoming more apparent that these
practices can also affect the reproduction and viability of target species in more subtle, but no
less important ways. For example, the initial attempt to rescue the wood duck (ALt sponsa) was
to mount nest boxes in highly visible groups that were easily found and quickly occupied by
females. However, this arrangement significantly increased intraspecific brood parasitism and
decreased egg hatchability (Semel et al. 1988). Careful study revealed that natural tendencies to
parasitize nest sites were adapted to the natural condition of dispersed and hidden nest sites
(Semel et al. 1988). In the same way, management practices that affect abundance can also affect
the mating system and mate choice dynamics of animals in ways that can severely impact
reproductive success, sexual selection, gene flow and population dynamics. I intend to
investigate the effects of fire, as used to manage tallgrass prairie grasslands, on the mating
system of an obligate grassland breeding bird, the dickcissel (Spiza americana). Specifically, I
intend to compare the rate of polygyny, EPP, and nesting success of this bird in sites with burn
intervals of one, two, four, and twenty years.
Tallgrass prairie is an early successional ecosystem dependent on fire to prevent the incursion of
trees and other woody plants. The time between fires (fire interval) affects the structural
complexity and composition of prairie vegetation, with short intervals producing simple, grass
dominated structures and longer intervals promoting a structurally complex mix of grass, forbs,
and woody shrubs. Historically, fires are thought to have occurred every 2-10 years (Hulbert
1973, Rowe 1969, Wright and Bailey 1982). Current management practices favor annual burns
that maximize primary productivity. While it is known that annual burns decrease the abundance
of certain grassland birds, their effects on the reproduction and mating system of these birds is
unknown.
Status | Finished |
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Effective start/end date | 7/1/08 → 6/30/09 |
Funding
- Animal Behavior Society: $1,000.00
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