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Siltation<br />
Siltation principally results from soil disturbance <strong>as</strong>sociated with ground cultivation,<br />
drainage, road construction and maintenance, and harvesting operations. It is<br />
best managed at the site level and good site planning is an essential part of any<br />
forest operation. The Guidelines require a methodological approach, which involves<br />
consideration of available techniques and resources, the potential environmental<br />
impacts of the work, and early consultation with appropriate bodies to <strong>as</strong>sess the<br />
sensitivity of the area. Usually there will be a need for a detailed site <strong>as</strong>sessment and<br />
the production of a well-annotated map (site plan) showing pertinent information,<br />
particularly site constraints. Common <strong>as</strong>pects are:<br />
• the need for meticulous planning and supervision of operations;<br />
• the adoption of less disruptive practices;<br />
• the careful matching of machinery to site conditions;<br />
• varying the scale and timing of operations according to site sensitivity;<br />
• the use of a wide range of protective me<strong>as</strong>ures; and<br />
• the preparation of a contingency plan in c<strong>as</strong>e of the accidental spillage of<br />
chemicals or oils.<br />
Effectiveness of the Forests and Water Guidelines<br />
Research and monitoring have played a key role in <strong>as</strong>sessing the effectiveness of<br />
best management practices (Nisbet, 2001). The preferred approach h<strong>as</strong> been to form<br />
a partnership with the water regulatory authorities and others in undertaking this<br />
work. In general, sensitive catchments and large-scale treatments were selected to<br />
provide good test c<strong>as</strong>es. Where possible both water quality and biology are examined.<br />
Results are published, often in peer-reviewed scientific literature, for general scrutiny.<br />
Examples relevant to afforestation are Nisbet et al. (1995), Nisbet (1997) and Nisbet<br />
et al. (2002). The effects of fertiliser applications are described in Nisbet and Stonard<br />
(1995) and Lees and Tervet (1994). Road construction, harvesting and restocking<br />
impacts are written up by Pratt et al. (1996), Neal and Reynolds (1998), and Nisbet et<br />
al. (2002). These studies confirm the effectiveness of the Guidelines in controlling the<br />
threat of diffuse pollution from forestry. Demonstration studies such <strong>as</strong> the EU LIFE<br />
UK182 Project in Galloway (CVCWT, 2004) have also played a vital part in promoting<br />
and communicating the success of best practice for protecting the freshwater<br />
environment.<br />
THE USE OF WOODLANDS IN AGRICULTURAL LANDSCAPES<br />
The success of the Guidelines h<strong>as</strong> resulted in attention shifting from viewing forestry<br />
<strong>as</strong> a threat to exploring how it can be used to improve the ecological status of water<br />
bodies. In particular, opportunities exist for forestry to help tackle diffuse pollution<br />
from more intensive land uses such <strong>as</strong> agriculture. One example is the use of riparian<br />
woodland buffers to retain sediments, nutrients and pesticides in waters draining<br />
from adjacent farmland. Investigations of the use of forestry in largely agricultural<br />
catchments are beginning to demonstrate the potential value of woodlands. Work<br />
in the upper reaches of the Severn within the Pontbren catchment showed that<br />
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