Monitoring Nature Conservation in Cultural Habitats: A by Clive Hurford (auth.), Clive Hurford, Michael Schneider

By Clive Hurford (auth.), Clive Hurford, Michael Schneider (eds.)

Monitoring Nature Conservation in Cultural Habitats provides tracking as an vital element of in charge conservation administration and as a catalyst for determination making. The early sections of the e-book hide key components within the improvement of a tracking undertaking, including:

- the jobs of survey and surveillance

- Incorporating wisdom from present study

- deciding upon the conservation precedence on websites

- Minimising observer mistakes

- picking out site-specific signs for habitats

- accumulating tracking facts

The later sections of the e-book contain a sequence of case reviews protecting a variety of habitats and species. those case experiences concentration normally, even though now not solely, on websites that shape a part of the Natura 2000 sequence in Europe.

Written in a transparent and concise type, and illustrated in color all through, this sensible advisor is a useful reference for conservationists and ecologists liable for dealing with and tracking land for nature conservation, for enterprises chargeable for enforcing agri-environment schemes, and for researchers operating within the box of utilized ecology.

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Extra resources for Monitoring Nature Conservation in Cultural Habitats: A Practical Guide and Case Studies

Sample text

Bulletin of the Ecological Society of America 78: 126-139. D. (1978) Botanical composition of the Park Grass plots at Rothamsted: 1856-1976. RES, Harpenden. uk 1. 1 The need for sampling Sampling is one of the most important aspects of any practical monitoring project. Only rarely can we make a complete record of a habitat or species population at a protected site. Unless it is conspicuous, small and confined within a small area, we must draw some conclusion about the condition of the whole feature from measurements made in a carefully chosen sample of habitat units or individuals.

Thomas & Krebs 1997). Surveillance 41 x And once we’ve decided upon sample locations, exactly what are we going to record, and at what time of the year? Some of the more difficult questions here relate to sampling, which is covered elsewhere in this book (see Chapter 5), and which is an issue of equal relevance to both monitoring and surveillance. Also as relevant to surveillance as to monitoring are the issues of measurability and repeatability (see Chapters 10 and 11). The reader is referred to those chapters for more specific advice on these issues.

The effect that imprecise definitions can have on area estimates is demonstrated in Table 3-1. This table lists area estimates for Great Britain that have appeared in various ‘well respected’ publications since 1950. g. whether one or more of inland waters, the Isle of Man, Northern Ireland and the Channel Islands were included in the area measurements (Maling, 1989). e. that we have not provided unambiguous definitions for the habitats that we want to map (Cherrill & McClean, 1999). g. at what point does heathland stop being heathland and become either grassland or woodland?

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