|
|
HomePOLICY & USER's CORNER |
|
In this section users (policy makers, land managers, NGOs, etc.) will find information, tools and recommendations derived from results of the SCALES project, as well as useful contacts.
SCALES has three main application areas: Monitoring, Regional connectivity, and Network of protected areas. Within these areas the project studies mainly the impact of climate change, fragmentation, and disturbance and explores the potential of various policy instruments to address these issues.
Monitoring
Short description |
Deliverable Title ↓ ↑ |
Author ↓ ↑ |
Size ↓ ↑ |
Species richness declines and biotic homogenisation have slowed down for NW-European pollinators and plants
Concern about biodiversity loss has led to increased public investment in conservation. Whereas there is a widespread perception that such initiatives have been unsuccessful, there are few quantitative tests of this perception. Here, we evaluate whether rates of biodiversity change have altered in recent decades in three European countries (Great Britain, Netherlands and Belgium) for plants and flower visiting insects. We compared four 20-year periods, comparing periods of rapid land-use intensification and natural habitat loss (1930-1990) with a period of increased conservation investment (post-1990). We found that extensive species richness loss and biotic homogenisation occurred before 1990, whereas these negative trends became substantially less accentuated during recent decades, being partially reversed for certain taxa (e.g. bees in Great Britain and Netherlands). These results highlight the potential to maintain or even restore current species assemblages (which despite past extinctions are still of great conservation value), at least in regions where large-scale land-use intensification and natural habitat loss has ceased
download |
Species richness declines and biotic homogenisation have slowed down for NW-European pollinators and plants |
Carvalheiro LG, Kunin WE, Keil P, Aguirre-Gutiérrez J, Ellis WN, Fox R, Groom Q, Hennekens S, Van Landuyt W, Maes D, Van de Meutter F, Michez D, Rasmont P, Ode B, Potts SG, Reemer M, Roberts SP, Schaminée J, Wallisdevries MF, Biesmeijer JC |
990.41KB |
+ more
Derived from: Publication # 10.1111/ele.12121
Contact person(s): Carvalheiro LG, Kunin WE, Keil P, Aguirre-Gutiérrez J, Ellis WN, Fox R, Groom Q, Hennekens S, Van Landuyt W, Maes D, Van de Meutter F, Michez D, Rasmont P, Ode B, Potts SG, Reemer M, Roberts SP, Schaminée J, Wallisdevries MF, Biesmeijer JC
Related documents: Species richness declines and biotic homogenisation have slowed down ...
Date of upload: 14.12.2013
Uploaded by:
|
Methods for cross-scale species distribution modelling
Knowledge of how to combine information about environmental factors that determine species distributions across spatial scales is indispensable for effective conservation and management. Researchers have tested three methodological approaches to combine distributional and environmental data for Finnish butterflies. They found that using the best information available at each spatial scale for the development of species distribution models and combining the results by simple multiplication significantly increases the predictive ability. This study highlights the notable potential of multi-scale approaches and demonstrates that the search for environmental correlates with species’ distributions must not only be addressed at an appropriate spatial scale, but also should be combined across the spatial scales due to the inherent hierarchy of processes where the higher levels constrain the lower levels.
download |
Methods for cross-scale species distribution modelling |
Oliver Schweiger, Risto Heikkinen, Mikko Kuussaari, Juha
Pöyry |
4.46MB |
+ more
Derived from: Publication #
Contact person(s): Oliver Schweiger, Risto Heikkinen, Mikko Kuussaari, Juha
Pöyry
Related documents:
Date of upload: 17.08.2012
Uploaded by: Pavel Stoev
|
Habitat mapping method could help restore biodiversity
Driven by increased demand for food and growing populations, major changes in rural landscapes during the second half of the 20th century, particularly in Western Europe, have had damaging effects on biodiversity. Intensive agriculture, afforestation for timber production and urbanisation have been shown to not only reduce available habitat for wildlife, but to also cut the links between habitats - the ‘ecological connectivity’ that allows species to spread and move around. Without these connections, there is a greater risk of extinction. There is increasing interest in restoring habitats at a landscape and regional scale. This study, conducted under the EU SCALES project, presents a new method of mapping habitat change to assist these efforts. The researchers argue that mapping is an important first step in conservation planning, with implications for the EU’s Natura 2000 initiative, and that their approach is unique in that it can cover a large area of land, show small details and assess changes over a long period of time.
They demonstrated its use by applying it to Dorset, a county in the UK of over 2500 sq.km. The researchers combined historic maps and soil data from the 1930s, before the onset of intensive agriculture, and developed appropriate habitat classifications, such as ‘heathland’ and ‘managed grassland’. Referring to habitat types, instead of land use functions, makes it easier to compare maps produced at different times or using different methods. The information was used to produce a digital map of Dorset in the 1930s, with a fine-scaled resolution of 25 x 25 metres. The map illustrated the range of habitat types across the district at the time, and presents what could be considered an ‘ideal’ situation for semi-natural habitats. These maps were then compared to a land cover map of Dorset, produced from satellite data, for the year 2000.
The maps revealed that the total area of semi-natural vegetation in Dorset fell by 74% over the 70 year period, considerably reducing the amount of quality habitat for wildlife. This was mainly the result of conversion to land for intensive agriculture, but afforestation also played a role by introducing conifer plantations for timber. Furthermore, the connectivity between the remaining fragments of habitat had fallen considerably. Most grasslands in 2000 had almost zero connectivity with other habitats more than a few hundred metres away, when ‘connectivity’ is considered as the ability of seeds from one habitat patch to disperse and end up at another habitat patch of the same type. The case study demonstrates the capacity of this mapping method, although its accuracy could be improved with better data; the researchers suggest that actual losses in habitat are likely to be even greater than the maps indicate. They propose a quantitative framework for conservation planning that uses high resolution maps, such as these, to help identify habitats for preservation and a target level of connectivity.
Source: Hooftman, D.A.P., Bullock, J.M. (2012) Mapping to inform conservation: A case study of changes in semi-natural habitats and their connectivity over 70 years. Biological Conservation. 145(1):30-38. DOI: 10.1016/j.biocon.2011.09.015.
download |
Habitat mapping method could help restore biodiversity |
Science for Environmental Policy |
103.63KB |
+ more
Derived from: Publication #
Contact person(s): Science for Environmental Policy
Related documents:
Date of upload: 10.07.2012
Uploaded by: Pavel Stoev
|
Why monitor biodiversity?
For the long-term, multi-purpose surveillance can be advantageous to address general questions, such as the status and trend of distribution and abundance of a set of species, and the causes for their changes. This brief provides key recommendations for designing monitoring schemes.
download |
A primer for biodiversity monitoring across SCALES |
Henle, K. et al.
|
6.32MB |
+ more
Derived from: Deliverable #
Contact person(s): Henle, K. et al.
Related documents:
Date of upload: 28.03.2011
Uploaded by: Pavel Stoev
|
|
|
|
|