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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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