The Landscape and Biodiversity Research Group

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The Landscape and Biodiversity Research Group (LBRG)[ when? ] in the School of Science and Technology at The University of Northampton carries out fundamental and applied research in the area of landscape ecology and its relationship to biodiversity and the ecology of species interactions. Research is mainly focussed on the effects of habitat modification and fragmentation on species' autecologies, seed dispersal, pollinator behaviour and plant reproductive success, and species richness. Research involves species- and community-level studies of ecology and conservation.

The LBRG currently consists of three permanent academic staff (Dr Jeff Ollerton, Dr Janet Jackson and Dr Duncan McCollin), postdoctoral researchers who are affiliated to the group either directly or as alumni (including Dr Jolyon Alderman, Visiting Research Fellow), and postgraduate research students. In addition, the group has ongoing research collaborations with colleagues at a number of UK and international universities and research centres.

The main research themes of the LBRG are:

Research has been funded by a range of organisations, including: NERC, BBSRC, The Royal Society, The Leverhulme Trust, The British Ecological Society, The Biodiversity Trust, The Royal Entomological Society, South Northamptonshire Council, Friends of the Upper Nene (FUN), The University of Northampton, English Partnerships, SITA Environmental Trust (in collaboration with the SITA Centre for Sustainable Wastes Management) and the Finnis Scott Foundation.

Related Research Articles

Mutualism (biology) Mutually beneficial interaction between species

Mutualism describes the ecological interaction between two or more species where each species has a net benefit. Mutualism is a common type of ecological interaction. Prominent examples include most vascular plants engaged in mutualistic interactions with mycorrhizae, flowering plants being pollinated by animals, vascular plants being dispersed by animals, and corals with zooxanthellae, among many others. Mutualism can be contrasted with interspecific competition, in which each species experiences reduced fitness, and exploitation, or parasitism, in which one species benefits at the "expense" of the other.

This is an index of conservation topics. It is an alphabetical index of articles relating to conservation biology and conservation of the natural environment.

The following outline is provided as an overview of and topical guide to sustainable agriculture:

Conservation biology Study of threats to biological diversity

Conservation biology is the study of the conservation of nature and of Earth's biodiversity with the aim of protecting species, their habitats, and ecosystems from excessive rates of extinction and the erosion of biotic interactions. It is an interdisciplinary subject drawing on natural and social sciences, and the practice of natural resource management.

Urban ecology Scientific study of living organisms

Urban ecology is the scientific study of the relation of living organisms with each other and their surroundings in the context of an urban environment. The urban environment refers to the environments dominated by high-density residential and commercial buildings, paved surfaces, and other urban-related factors that create a unique landscape dissimilar to most previously studied environments in the field of ecology. The goal of urban ecology is to achieve a balance between human culture and the natural environment.

Habitat conservation Management practice for protecting types of environments

Habitat conservation is a management practice that seeks to conserve, protect and restore habitats and prevent species extinction, fragmentation or reduction in range. It is a priority of many groups that cannot be easily characterized in terms of any one ideology.

Agricultural biodiversity

Agricultural biodiversity or agrobiodiversity is a subset of general biodiversity pertaining to agriculture. It can be defined as "the variety and variability of animals, plants and micro-organisms at the genetic, species and ecosystem levels that sustain the ecosystem structures, functions and processes in and around production systems, and that provide food and non-food agricultural products.” It is managed by farmers, pastoralists, fishers and forest dwellers, agrobiodiversity provides stability, adaptability and resilience and constitutes a key element of the livelihood strategies of rural communities throughout the world. Agrobiodiversity is central to sustainable food systems and sustainable diets. The use of agricultural biodiversity can contribute to food security, nutrition security, and livelihood security, and it is critical for climate adaptation and climate mitigation.

Habitat fragmentation Discontinuities in an organisms environment causing population fragmentation.

Habitat fragmentation describes the emergence of discontinuities (fragmentation) in an organism's preferred environment (habitat), causing population fragmentation and ecosystem decay. Causes of habitat fragmentation include geological processes that slowly alter the layout of the physical environment, and human activity such as land conversion, which can alter the environment much faster and causes the extinction of many species. More specifically, habitat fragmentation is a process by which large and contiguous habitats get divided into smaller, isolated patches of habitats.

Habitat destruction is the process by which a natural habitat becomes incapable of supporting its native species. The organisms that previously inhabited the site are displaced or dead, thereby reducing biodiversity and species abundance. Habitat destruction is the leading cause of biodiversity loss. Fragmentation and loss of habitat have become one of the most important topics of research in ecology as they are major threats to the survival of endangered species.

Reconciliation ecology Study of maintaining biodiversity in human-dominated ecosystems

Reconciliation ecology is the branch of ecology which studies ways to encourage biodiversity in the human-dominated ecosystems of the anthropocene era. Michael Rosenzweig first articulated the concept in his book Win-Win Ecology, based on the theory that there is not enough area for all of earth's biodiversity to be saved within designated nature preserves. Therefore, humans should increase biodiversity in human-dominated landscapes. By managing for biodiversity in ways that do not decrease human utility of the system, it is a "win-win" situation for both human use and native biodiversity. The science is based in the ecological foundation of human land-use trends and species-area relationships. It has many benefits beyond protection of biodiversity, and there are numerous examples of it around the globe. Aspects of reconciliation ecology can already be found in management legislation, but there are challenges in both public acceptance and ecological success of reconciliation attempts.

In landscape ecology, landscape connectivity is, broadly, "the degree to which the landscape facilitates or impedes movement among resource patches". Alternatively, connectivity may be a continuous property of the landscape and independent of patches and paths. Connectivity includes both structural connectivity and functional connectivity. Functional connectivity includes actual connectivity and potential connectivity in which movement paths are estimated using the life-history data.

Cross-boundary subsidy

Cross-boundary subsidies are caused by organisms or materials that cross or traverse habitat patch boundaries, subsidizing the resident populations. The transferred organisms and materials may provide additional predators, prey, or nutrients to resident species, which can affect community and food web structure. Cross-boundary subsidies of materials and organisms occur in landscapes composed of different habitat patch types, and so depend on characteristics of those patches and on the boundaries in between them. Human alteration of the landscape, primarily through fragmentation, has the potential to alter important cross-boundary subsidies to increasingly isolated habitat patches. Understanding how processes that occur outside of habitat patches can affect populations within them may be important to habitat management.

The Wild Farm Alliance (WFA) is a non-profit organization dedicated to increasing biodiversity by expanding the idea and practice of wild farming.

Wildlife corridor Habitat pathway for animals connecting wild territories

A wildlife corridor, habitat corridor, or green corridor is an area of habitat connecting wildlife populations separated by human activities or structures. This allows an exchange of individuals between populations, which may help prevent the negative effects of inbreeding and reduced genetic diversity that often occur within isolated populations. Corridors may also help facilitate the re-establishment of populations that have been reduced or eliminated due to random events. This may potentially moderate some of the worst effects of habitat fragmentation, wherein urbanization can split up habitat areas, causing animals to lose both their natural habitat and the ability to move between regions to use all of the resources they need to survive. Habitat fragmentation due to human development is an ever-increasing threat to biodiversity, and habitat corridors are a possible mitigation.

Increasing biodiversity in agriculture may increase the sustainability of the farm.

Defaunation is the global, local or functional extinction of animal populations or species from ecological communities. The growth of the human population, combined with advances in harvesting technologies, has led to more intense and efficient exploitation of the environment. This has resulted in the depletion of large vertebrates from ecological communities, creating what has been termed "empty forest". Defaunation differs from extinction; it includes both the disappearance of species and declines in abundance. Defaunation effects were first implied at the Symposium of Plant-Animal Interactions at the University of Campinas, Brazil in 1988 in the context of Neotropical forests. Since then, the term has gained broader usage in conservation biology as a global phenomenon.

Forest restoration

Forest restoration is defined as “actions to re-instate ecological processes, which accelerate recovery of forest structure, ecological functioning and biodiversity levels towards those typical of climax forest” i.e. the end-stage of natural forest succession. Climax forests are relatively stable ecosystems that have developed the maximum biomass, structural complexity and species diversity that are possible within the limits imposed by climate and soil and without continued disturbance from humans. Climax forest is therefore the target ecosystem, which defines the ultimate aim of forest restoration. Since climate is a major factor that determines climax forest composition, global climate change may result in changing restoration aims.

Irthlingborough Lakes and Meadows

Irthlingborough Lakes and Meadows is a 117-hectare (290-acre) nature reserve in Northamptonshire, owned and managed by the Wildlife Trust for Bedfordshire, Cambridgeshire and Northamptonshire. The character of the reserve is defined by flooded gravel pits and wet grassland, providing an excellent habitat for large variety of wetland flora and fauna.

Pedro Diego Jordano Barbudo is an ecologist, conservationist, researcher, focused on evolutionary ecology and ecological interactions. He is an honorary professor and associate professor at University of Sevilla, Spain. Most of his fieldwork is done in Parque Natural de las Sierras de Cazorla, Segura y Las Villas, in the eastern side of Andalucia, and in Doñana National Park, where he holds the title of Research Professor for the Estacion Biologica Doñana, Spanish Council for Scientific Research (CSIC).

Landfill restoration refers to the process of covering a landfill once it has reached its maximum capacity and transforming it into usable land. This process usually consists of covering it with a top layer of soil and impermeable materials, also called capping, to ensure that vegetation could grow. Studies have shown that capping landfills promotes vegetation growth, which provides additional benefits such as reducing rainfall infiltration, decreasing and mitigating soil erosion, improving ecological diversity, and improves the visual appearance of the landfill site. Restoring landfill sites is considered essential to recuperate ecosystems, to minimize any negative impacts the site had on the environment, and to ensure that the site is safe for any future use.

References

  1. McCollin, D. (2000) Editorial. Hedgerow policy and protection - changing paradigms and the conservation ethic. Journal of Environmental Management 60(1): 3-6
  2. McCollin D, Jackson J, Barr, C. J., Bunce, R. G. H. and Stuart, R. (2000) Hedgerows as habitat for woodland plants. Journal of Environmental Management 60(1): 77-90
  3. Jackson, J.I. & McCollin, D. (1997) Hedgerow diversity: dynamics of dispersal, colonization and establishment of woody plant species. In: Proceedings of the 6 th Annual Conference of the International Association of Landscape Ecology: Species dispersal and land use processes . Eds: Copper, A. & Power, J. (309-312).
  4. Alderman, J, McCollin, D. Hinsley, S.A., Bellamy, P.E., Picton, P., & Crockett, R. (2005) Modelling the effects of dispersal and landscape configuration on population distribution in fragmented habitat. Landscape Ecology 20: 857-870.
  5. McCollin, D., Moore, L. & Sparks, T. (2000) The flora of a cultural landscape: environmental determinants of change revealed using archival sources. Biological Conservation 92(2): 249-263.
  6. Ollerton, J.,Grace, J., & Smith, K. (2007). Pollinator Behaviour and Adaptive Floral Colour Change in Anthopora alluadii (Hymenoptera: Apidae) and Erysimum scoparium (Brassicaceae) on Tenerife. Entomologia Generalis 29: 253-268.
  7. Ollerton, J., Stott, A., Allnutt, E., Shove, S., Taylor, C. and Lamborn, E. (2007) Pollination niche overlap between a parasitic plant and its host. Oecologia 151: 473-485.
  8. Waser, N.M & Ollerton, J. (2006) Plant-pollinator interactions: from specialization to generalization. University of Chicago Press, USA.
  9. Cant,E. T. , Smith,A. D., Reynolds,D. R., and Osborne, J. L. (2005). Tracking butterfly flight paths across the landscape with harmonic radar. Proceedings of the Royal Society.
  10. Cranmer, L., Ollerton, J. and McCollin, D. (in prep.) Landscape structure directly affects bumblebee movements and plant reproductive success.
  11. Jackson, J.I. and A Kwolek (2003) Habitat Survey of the Upper Nene Valley 1999-2002 . South Northamptonshire District Council, Friends of the Upper Nene (FUN), Northamptonshire County Council.
  12. Kwolek, A. & Jackson, J. (2001) Floodplains and Agenda 21: The Upper Nene Valley Project. Sustainable Development 9(3): 165-174.
  13. Jackson, J. I. and Boutle, R. (2008) Ecological functions within Sustainable Urban Drainage Systems. Proceedings of the 11th International Conference on Urban Drainage, Edinburgh, Scotland , UK , September 2008, 730-740.