Mind map
Spatial Ecology
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Spatial Ecology
What is spatial ecology?
- Spatial patterns and distribution of plants and animals
- In relation to their environment: climate, resources, geography
Spatial data
- Detecting spatial patterns and distribution
- distribution data; presence-absence data; presence only data; movement data
- Methods
- GPS collars; transects; habitat mapping; remote sensing
- Detecting spatial patterns and distribution
Spatial ecology in conservation
- Overall threats to biodiversity
- Habitat loss and land use change; hunting; climate change
- Movement and space use
- Loss of seasonal ranges; habitat fragmentation; fencing; poaching; loss of resources
- Overall threats to biodiversity
Species distribution models - case study: moose in Scandinavia
- 1.1 Spatial autocorrelation
- We want to find out moose distribution during winter
- Count moose droppings - the more droppings, the longer they spent there; food: scots pine and field layer
- 1.2 Results
- Count data are clumped
- Non-spatial analysis - 20% explained; large scale - 29% explained; small scale - 64% explained
- 1.3 Spatial autocorrelation
- Habitat availability over- and under-estimated presence of moose in the landscape
- The distance to the nearest good and poor patch affects the probability of presence of moose
- The scale of the distance depends on the species and the environment
- 1.1 Spatial autocorrelation
Point processes and distribution - case study: saiga antelopes in Central Asia and Russia
- 2.1 Drivers of migration
- Resources (food, water); predation; parasites; competition; climate; people
- 2.2 Data and methods
- Aerial and ground surveys - spring, summer and winter; precipitation; NDVI (normalised difference vegetation index) at 16 day intervals
- Near-infrared radiation minus visible radiation divided by near-infrared radiation plus visible radiation
- Aerial and ground surveys - spring, summer and winter; precipitation; NDVI (normalised difference vegetation index) at 16 day intervals
- 2.3 Results
- Saiga antelopes follow NDVI (vegetation) south in winter; don't follow NDVI in summer to the north as this is where the people are
- 2.4 Conclusion
- A single proxy for resources (NDVI) explains the distribution of saiga antelopes
- NDVI is spatially and temporally explicit; NDVI is linked to rainfall and seasonal climate
- The effect of humans remains to be studied
- A single proxy for resources (NDVI) explains the distribution of saiga antelopes
- 2.1 Drivers of migration
Protected areas and movement - case study: wildebeest in the Serengeti, Tanzania
- Migration of wildebeest in the Serengeti (1.6 million); large scale movements throughout the year; human population increase - land use change (agriculture), poaching
- 3.1 Data and methods
- GPS collars on wildebeest
- Mapping of protected areas and their protection status - Serengeti National Park: tourism; conservation areas: tourism, settlement, livestock (hunting); gave reserves: tourism and hunting
- 3.2 Results
- Wildebeest spend considerable time outside protected areas
- 3.3 Discussion
- New Serengeti highway will cut through the migration route
From point processes to movement
- So far: locations at specific points in times - new technology (GPS) decrease time between locations (down to 2 mins)
- 4.1 Movement concept and scale
- Scale of data collection depends on the question and aim of the research
- 4.2 Too many dimensions
- Movement data consists of three dimensions: longitude, latitude & time; from 2 location dimensions to 1; net squared displacement (NSD)
- Movement analysis: NSD can be entered in general statistics, e.g. regression; NSD = intercept + slope * variable; variable - time, NDVI, predation risk, hunting
- 4.3 From 2 dimensions to 1
- Net squared displacement: distance from first point to subsequent point; routed in Brownian motion theory (physics)
- Increases linearly with time for nomadic; asymptotic for home range
- 4.4 Moose in Scandinavia
- More than 300 moose collared; 76 moose for at least one year; one location per hour or more -> 5 million locations
- 4.5 The challenge
- Distance, timing, and duration of migration; proportion of population migrating
- 4.7 All good but how to quantify this in biological terms
- Advantages of non-linear mixed effects models
- Model parameters have a biological meaning (asymptot, timing and duration of migration); fewer parameters than linear modelss thus more persimonious; provide more reliable predictions than linear models outside the parameter range
- Advantages of non-linear mixed effects models
- 4.8 Non-linear mixed effects models
- Account for individual variation; objective and repeatable way to quantify migration; no arbitrarily chosen cut off points
- 4.9 Results
- Males move further than females; timing, duration and distances vary between years and individuals
- 4.10 Conclusion
- Yearly variation in distance, timing and duration; A unified framework for migration, no cut-off points, no splitting in time or space
- Remaining questions: what is due to variation in the environment and what due to individual characteristics? What is the genetic basis of migration behaviour and what is learned from the mother?
- Yearly variation in distance, timing and duration; A unified framework for migration, no cut-off points, no splitting in time or space
- 4.1 Movement concept and scale
- So far: locations at specific points in times - new technology (GPS) decrease time between locations (down to 2 mins)
Understanding resource use and conservation: an example from Amazonian Ecuador
- 5.1 Why map resource use?
- Measure sustainability of extraction; develop appropriate no-take areas or reserves; define land ownership
- 5.2 Past approaches for mapping use
- Interviews; accompanied trips; drawn maps
- 5.3 Alternate approach
- Purchase inexpensive Personal Digital Assistants with GPS capacity; design interface and load cybertracker; train community members in GPS use; can be used in conjunction with interviews
- 5,4 Potential issues for data analysis
- Spatio-temporal autocorrelation; central place foragers
- 5.5 Three steps
- Net Squared Displacement (NSD)
- Calculate mean speed, duration and distance travelled for each type of trip
- Biased random bridge (BRB)
- Calculate size of each area used by each individual; calculate overlap between individuals
- Resource utilisation function (RUF)
- Identify habitat features associated with increased use; build predictive habitat model
- Net Squared Displacement (NSD)
- 5.6 Study rational
- Do hunters use the forest differently to non-hunters?
- 5.7 Net Squared Displacement
- 5.8Biased Random Bridge
- 5.9 Research benefits
- GPS allow accurate assessment of resource us areas; inexpensive
- Benefits of analysis method: can be applied to GPS data of any collection frequency and spatial scale; can be applied when locations are missing; journeys and resource extraction can be separated; movement between locations in incorporated; all analyses can be complete in the statistical program R, which is free to download
- 5.10 Community benefits
- Development of skills within the community - computing, understanding of GPS, giving training; greater ownership of investigation
- 5.11 Limitations
- Willingness of community to participate; methods require large numbers of locations; NSD needs all parts of the curve to have enough data; analyses can be computationally time consuming
- 5.1 Why map resource use?
General conclusion
- Spatial data are challenging
- New technologies - GPS; remote sensing (NDVI)
- New methods - reduce dimensions; allow uniform, scale-independent analyses
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- university Environmental Geography Mind Map on Spatial Ecology, created by Calli Dougall on 06/12/2015.
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- Calli Dougall
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