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Although nitrate leaching can be reduced by whole-tree harvesting, a much larger,<br />

longer-term threat of soil and water acidification is presented by the greater removal<br />

of b<strong>as</strong>e cations in harvested produce. Consequently, whole-tree harvesting is not<br />

recommended in critical load exceedance or adjacent squares, except on steep<br />

sites where whole trees have to be extracted to roadside.<br />

Biological recovery of streams showing chemical improvement in response to emission<br />

reductions may benefit from the opening-out of stream sides. Where practicable,<br />

these are<strong>as</strong> should be targeted for earlier clearance of stands c<strong>as</strong>ting heavy shade<br />

and cleared zones linked to aid upstream migration of fish and invertebrates.<br />

Nutrient enrichment<br />

There is concern that the nutrient, and hence the ecological, status of fresh waters,<br />

particularly standing waters, may be significantly changed following the aerial<br />

application of phosphate fertilisers in their catchments. Fertilisers may be accidentally<br />

sprayed or blown into watercourses, or may be transported indirectly via subsequent<br />

leaching or run-off. Waters vary in their sensitivity to nutrient enrichment from forestry,<br />

with nutrient-poor (oligotrophic) waters most at risk of nutrient pollution.<br />

Aerial phosphate fertiliser must be carefully planned to ensure that phosphate losses<br />

from consecutive applications in a given catchment do not exceed environmental<br />

quality standards in receiving lakes or reservoirs. Applications exceeding a total<br />

area of 50 ha in any 3-year period may pose a problem; the effect will depend on the<br />

soil properties, timing of application, size of the catchment and the characteristics of<br />

the water body. Early consultation with the water regulatory authority will establish<br />

whether a more detailed site <strong>as</strong>sessment is required. Assessments need to include<br />

phosphate rele<strong>as</strong>es from large-scale felling operations, which can be significant on<br />

some soil types.<br />

Fertiliser usage is declining in forestry in line with the reduction in new planting and<br />

a shift to more fertile soils. A move to more hand applications and better targeting<br />

of aerial treatments through the use of granulated fertiliser and improved helicopter<br />

guidance systems, are also reducing the risk of nutrient pollution.<br />

The generally higher nutrient status of lowland soils means that lowland woodlands<br />

rarely require fertiliser applications. Thus woodland planting on ex-agricultural land<br />

may help to reduce leaching losses and tackle nutrient pollution within sensitive<br />

are<strong>as</strong> such <strong>as</strong> Nitrate Vulnerable Zones (NVZs). Opportunities exist for maximising<br />

this benefit through the targeted planting of riparian and downslope buffer are<strong>as</strong>.<br />

Forest type is an important factor, with conifer forests less able to reduce nutrient<br />

concentrations in drainage waters. This is because of their ability to capture nitrogen<br />

pollutants from the atmosphere and concentrate nitrate levels in groundwater,<br />

particularly in are<strong>as</strong> of low rainfall. High nitrogen inputs can result where forests are<br />

downwind of local pollutant sources, such <strong>as</strong> intensive pig- and poultry-rearing units.<br />

This is likely to be an incre<strong>as</strong>ingly important consideration with the expansion of<br />

NVZs. The main are<strong>as</strong> at risk are those receiving low rainfall where the concentrating<br />

effect of evaporation is disproportionately large. Consideration should be given to<br />

avoiding large-scale conifer planting within NVZs receiving < 650 mm annual<br />

rainfall.<br />

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