Reptile and frog responses to different farm management practices in grazing landscapes
Abstract
Managing agricultural landscapes for biodiversity conservation is
increasingly difficult as land use is intensified for
agricultural production. Finding ways to mitigate the often
negative effects of agriculture on biodiversity is therefore
critical: Using reptiles and frogs as focal taxa, my broad aim
was to examine the effect of different human-modified land cover
types on biodiversity in a grazing landscape. I present my thesis
as a series of five conceptually linked journal papers that
together address this applied ecological problem.
I surveyed reptiles and frogs at 12 sites Box Gum Grassy Woodland
grazing landscapes in south-eastern Australia. Each site
contained remnant woodland patches and four adjacent paddock
types: a) grazed pastures, b) linear plantings, c) coarse woody
debris added to grazed pastures, and d) fences between grazed
pastures. Each site was either continuously or rotationally
grazed.
In my first paper, I compared the habitat preferences of reptile
and frog species to predictions developed from five conceptual
landscape models. Importantly, no one model fully captured the
range of species responses to the different land uses, but four
of the models provided useful concepts to aid our understanding
of faunal responses to human-modified landscapes. It is important
that relevant conceptual models are used by researchers as the
different models can result in very different outcomes. These
types of models can help inform management, but all models have
limitations and often cannot provide useful management
recommendations.
In my second paper, I recorded higher reptile abundance and
species richness in areas with more tree cover and leaf litter,
and greater abundance and diversity of rare reptiles in sites
with high tree cover in the surrounding 3kms. Management
recommendations include: protecting existing remnant vegetation,
regardless of amount, and promoting key habitat features of
trees, leaf litter and shrubs. Establishing plantings and fences
in paddocks can also provide habitat in grazing landscapes.
In my third paper, I found that frogs were influenced by both
land use and the environmental conditions, and often responded to
interactions between these variables. Frog abundance decreased
with distance to water more strongly in remnants than paddocks,
and rare frog richness and the abundance of Limnodynastes
tasmaniensis increased with taller ground cover in remnants but
not adjacent paddocks. Retaining remnant vegetation, maintaining
water bodies such as farm dams, and maintaining taller ground
cover within remnant vegetation may therefore benefit frog
assemblages. Environmental context and current management must be
considered in planning future management actions.
In my fourth paper, I found that reptiles and frogs displayed
contrasting movement behaviours. For example, recaptured reptiles
exhibited greater movement within and out of paddocks than
remnants. However, the smooth toadlet (Uperoleia laevigata) moved
within remnants more than within paddocks, while the spotted
marsh frog (Limnodynastes tasmaniensis) moved out of pasture
transects more than other transects. Reptiles and frogs appear to
use the whole landscape as habitat and but perceive different
land management types as different qualities of habitat.
My fifth paper synthesised the state of knowledge of reptiles in
woodland agricultural landscapes in south-eastern Australia. I
highlight the key factors influencing these reptiles, synthesise
the management implications, and outline future research needs.
My research has provided new insights into how reptiles and frogs
are influenced by land use in grazing landscapes. Importantly, I
found that commonly discussed ecological concepts applied to
human-modified landscapes did not provide a useful framework for
understanding/predicting biodiversity responses to land cover
types.
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