70 research outputs found

    Invertebrate communities and environmental conditions in a series of urban drainage ponds in Eastern Scotland: implications for biodiversity and conservation value of SUDS.

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    Increasing use is being made of constructed wetlands to store and treat urban drainage prior to release into watercourses. Known as sustainable urban drainage systems (SUDS) in the UK these have potential to support and enhance freshwater biodiversity in urban areas, but the diversity and value of communities present in these ponds is not well-established. This study establishes the characteristics of invertebrate communities and investigates links with prevailing environmental conditions in four SUDS sites in Dunfermline, Scotland over a five-year period. The SUDS ponds supported communities of between 10 and 47 invertebrate species. Only one beetle species of conservation significance was recorded, along with an invasive species of mollusc. There were significant temporal changes in species richness and community composition, with the sites losing species and becoming more dissimilar over time. Variation in the invertebrate species composition at the sites was linked to both average environmental conditions and temporal variability, particularly soluble reactive phosphorus and dissolved oxygen levels. The biodiversity value SUDS of invertebrate communities may be limited by pollutant loads being received from drainage, but they can still potentially contribute to freshwater diversity in urban areas. In order to maximise their biodiversity potential, more research needs to be undertaken on appropriate design and management considerations

    The impact of shadow flicker or pulsating shadow effect, caused by wind turbine blades, on Atlantic salmon (Salmo salar)

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    The Impact Of Shadow Flicker Or Pulsating Shadow Effect, Caused By Wind Turbine Blades, On Atlantic Salmon (Salmo Salar): Research Summary

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    As the need for onshore wind energy expands, such climate adaptation measures may have unintended and potentially significant influences on how fish respond when situated next to rivers or streams. The aim of this project was to examine evidence of potential impacts of shadow flicker, from wind turbine blades, on Atlantic salmon in the context of species conservation management and climate mitigation strategy in Scotland. Our current understanding of the possible effects of shadow flicker on Atlantic salmon was investigated by reviewing the available literature (peer-reviewed and grey from national and international sources) for existing studies of a similar or relevant nature. Various databases and web-based search engines were used to identify these studies, relevant information was extracted and summarised, and potential impacts across the salmon’s lifecycle identified. There was no direct evidence available, either from laboratory experiments or studies of wild fish, that describe the effects of shadow flicker on Atlantic salmon or any other fish species. Based on the available literature, and our expert opinion, there is currently insufficient evidence to support or refute any biological or ecological impact of shadow flicker on Atlantic salmon. The review has highlighted a lack of basic understanding of the role light patterns may play for Atlantic salmon in rivers and further research is recommended. At present there is no evidence to support any change to related policy guidance. However, under the precautionary principle, some advice for best practice might be advised to prevent shadow flicker being cast on river surfaces. Where appropriate, potential mitigation methods were identified that could reduce any impacts on Atlantic salmon should impacts of shadow flicker on fish be demonstrated in the future

    The impact of shadow flicker or pulsating shadow effect, caused by wind turbine blades, on Atlantic salmon (Salmo salar)

    Get PDF

    The Impact Of Shadow Flicker Or Pulsating Shadow Effect, Caused By Wind Turbine Blades, On Atlantic Salmon (Salmo Salar): Research Summary

    Get PDF
    As the need for onshore wind energy expands, such climate adaptation measures may have unintended and potentially significant influences on how fish respond when situated next to rivers or streams. The aim of this project was to examine evidence of potential impacts of shadow flicker, from wind turbine blades, on Atlantic salmon in the context of species conservation management and climate mitigation strategy in Scotland. Our current understanding of the possible effects of shadow flicker on Atlantic salmon was investigated by reviewing the available literature (peer-reviewed and grey from national and international sources) for existing studies of a similar or relevant nature. Various databases and web-based search engines were used to identify these studies, relevant information was extracted and summarised, and potential impacts across the salmon’s lifecycle identified. There was no direct evidence available, either from laboratory experiments or studies of wild fish, that describe the effects of shadow flicker on Atlantic salmon or any other fish species. Based on the available literature, and our expert opinion, there is currently insufficient evidence to support or refute any biological or ecological impact of shadow flicker on Atlantic salmon. The review has highlighted a lack of basic understanding of the role light patterns may play for Atlantic salmon in rivers and further research is recommended. At present there is no evidence to support any change to related policy guidance. However, under the precautionary principle, some advice for best practice might be advised to prevent shadow flicker being cast on river surfaces. Where appropriate, potential mitigation methods were identified that could reduce any impacts on Atlantic salmon should impacts of shadow flicker on fish be demonstrated in the future

    The thin(ning) green line? Investigating changes in Kenya's seagrass coverage

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    Knowledge of seagrass distribution is limited to a few well-studied sites and poor where resourcesare scant (e.g. Africa), hence global estimates of seagrass carbon storage are inaccurate. Here, we analysed freely available Sentinel-2 and Landsat imagery to quantify contemporary coverage and change in seagrass between 1986 and 2016 on Kenya’s coast. Using field surveys and independent estimates of historical seagrass, we estimate total cover of Kenya’s seagrass to be 317.1 ± 27.2 km226 , following losses of 0.85% yr-1 since 1986. Losses increased from 0.29% yr-1 in 2000 to 1.59% yr-1 in 2016, releasing up to 2.17 Tg carbon since 1986. Anecdotal evidence suggests fishing pressure is an important cause of loss and is likely to intensify in the near future. If these results are representative for Africa, global estimates of seagrass extent and loss need reconsidering

    Optimising camera trap data quality at mammal resting places.

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    A thorough understanding of how camera traps function is essential for ensuring correct set-up and quality of data. We illustrate the challenges through a case study of camera trapping an otter Lutra lutra resting and breeding place. Appropriate survey design, such as using multiple cameras, decreasing the distance between cameraand otter holt entrance, and camera trapping for sufficient duration, is likely to reduce the propensity for false negatives and increase our ability to correctly identify and protect mammal resting places

    Component processes of detection probability in camera-trap studies: understanding the occurrence of false-negatives

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    Camera-trap studies in the wild record true-positive data, but data loss from false-negatives (i.e. an animal is present but not recorded) is likely to vary and widely impact data quality. Detection probability is defined as the probability of recording an animal if present in the study area. We propose a framework of sequential processes within detection-a pass, trigger, image registration, and images being of sufficient quality. Using Closed Circuit TV (CCTV) combined with camera-trap arrays we quantified variation in, and drivers of, these processes for three medium sized mammal species. We also compared trigger success of wet and dry otter Lutra lutra, as an example of a semi-aquatic species. Data loss from failed trigger, failed registration and poor capture quality varied between species, camera-trap model and settings, and were affected by different environmental and animal variables. Distance had a negative effect on trigger probability and a positive effect on registration probability. Faster animals had both reduced trigger and registration probabilities. Close passes (1m) frequently did not generate triggers, resulting in over 20% data loss for all species. Our results, linked to the framework describing processes, can inform study design to minimise, or account for data loss during analysis and interpretation
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