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Back to 1995 Reports
1995 Annual Research and Extension ReportMicrohabitat and Predator-Prey Relationships: Examination of Interactions between Anuran Larvae and Aquatic InsectsGeorge W. Tanner and Kimberly J. BabbittDepartment of Wildlife Ecology and Conservation OBJECTIVES1. To determine the spatial and temporal patterns of use of wetlands modified by drainage, by anurans and aquatic insects.2. To determine experimentally the role of habitat heterogeneity in mediating predator-prey interactions between larval anurans and aquatic insect predators. BACKGROUNDWetland loss and modification can have large impacts on anuran
populations. Loss of wetland breeding sites has obvious consequences for
species viability; however, the effect of wetland alteration is less clear
and poorly documented. Activities related to cattle ranching, such as
changes in local drainge patterns and consequent modification of wetland
hydrology can affect species composition of both plants and animals, and
can therefore lead to alteration in habitat structure as well as predator
communities. Our ongoing research at the MacArthur AgroEcology Research Center
focuses on the spatial and temporal patterns of anuran and aquatic insect
use of wetlands and their relationship to wetland hydrology. In addition,
because plant communities change along hydrologic gradients, we focus on
the relationship between physical attributes of wetlands (i.e., plant
cover, biomass, water depth) and their relationship to anuran numbers and
biomas. This field research is complimented by a series of experimental
manipulations designed to address specific questions regarding
predator-prey interactions and the importance of habitat complexity in
mediating such interactions. Twelve ephemeral wetlands are sampled every 3 weeks throughout the entire year. Sampling is conducted with a 0.5m x 0.5m x 0.67m open-ended box trap. Within each wetland, sampling is stratified such that 3 replicate, random samples are obtained from each of 3 water depth zones. Nine samples (3 per zone) are taken at each wetland, so when all wetlands contain water, 108 samples (12 wetlands x 9 samples) are collected per sampling period (i.e., 1 week period, every 3 weeks). Physichemical parameters are measured to characterize microhabitat. Dissolved oxygen, temperature (surface and bottom) and pH are measured in proximity to the trap. Water depth is measured within each trap. Hydroperiod of each wetland is monitored with a permanent marker located at the center of the wetland. Vegetation is characterized by total percent cover, relative abundance of each species, and wet-weight biomass. All anuran larvae, macroinvertebrates, crustaceans, and fish are collected from each trap using a bar seine. The box is swept (after being cleared of vegetation) for individuals until three consective sweeps yield no additional captures. The information obtained form each trap includes total number of individuals by species and species richness. Total biomass and stage of development for all anurans are dtermined to assess ontogenetic changes in microhabitat use. Experimental studies are conductd in field enclosures, wading pools adn smaller contains (i.e., aquaria or plastic dishpans). Field experiments are conducted in a totally fenced wetlands to exclude cattle and feral hogs using 28, 0.9m x 0.9m x 0.67m enclosures constructed of wooden frames and fiberglass window screening. Enclosures have tight fitting, but removable tops, and bottoms made of heavy duty plastic. The experiments are conducted as factorial designs with spatially-clumped replicated to all treatments. The enclosures are placed in areas of equal water depth in spatial blocks. An example of a field experiment is a 2x2x2 factorial design with 2
density levels (20 versus 40 individuals) crossed with high and low levels
of vegetation (based of field estimates of biomass) crossed with presence
or absence of an early-instar, odonate predator. Metamorphosing tadpoles
are collected and age, weight,and size at metamorphosis, as well as percent
survival are recorded.
Eighteen sampling trips have been conducted yielding 1600 samples. Wihth
the exception of the aquatic insects, all components of the 1600 samples
have been processed and entered into computer databases. Aquatic insect
samples are currently being processed.
A proposal was submitted to the Florida Nongame Wildlife Program.
2001 Southern DataStream |
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