Measurements and modelling of cloudwater deposition to moorland and forests

Inputs of trace gases, particles and cloud droplets to terrestrial surfaces

The deposition of reactive gases on terrestrial surfaces is one of the primary mechanisms by which pollutant gases are removed from the atmosphere. The chemical properties of the gases (SO2, NO2, HNO3, HCl) and of the absorbing surfaces lead to differing rates of exchange and controlling processes. The most reactive gases, HNO3, HCl (and for many surfaces NH3) exhibit negligible surface resistances; deposition velocities (Vg) appropriate for short vegetation ranging from 2 to 5 cm s−1, for forests Vg may approach 10 cm s−1. The large rates of deposition for NH3 on moorland and forests lead to annual inputs, in areas with large atmospheric concentrations of NH3 (≥ 5 μg NH3 m−3), ranging from 20 to 60 kg N ha−1. The net exchange of NH3 over cropland, attributable to deposition during vegetative growth and emission of NH3 during senescence, is less well known but believed to be small.

The co-deposition of NH3 and SO2 on external surfaces of plant canopies is believed to enhance SO2deposition with reported deposition velocities over short vegetation of 2.0 cm s−1.

Rates of cloud droplet deposition to vegetation have been shown to be very similar to rates of momentum deposition (i.e. Vt ≈ ram−1). These findings provide the basis for estimates of cloud deposition inputs of major ions to upland Britain where they may contribute up to 30% of the wet deposited sulphur and nitrogen.

An investigation of the impact of afforestation on stream-water chemistry in the Loch Dee catchment, SW Scotland

The impact of conifer afforestation on stream-water chemistry was investigated in the acidified catchment of Loch Dee, SW Scotland. Long-term trends in stream-water chemistry were evaluated during a period of forest growth from age 6 to 17 years. A significant increase was observed for pH (0.2 units) and a significant decline for aluminium (0.05 mg litre(-1)), sulphate (1.2 mg litre(-1)) and nitrate (0.02 mg litre(-1)) concentrations. The long-term decrease in stream-water acidity was ascribed to the marked reductions in sulphur depositions during the 1970s and early 1980s. There was no evidence that this response had been attenuated by afforestation, the improvements in stream-water chemistry being of a similar magnitude to those recorded in nearby moorland lochs and exceeding that in an adjacent moorland-catchment stream. The lack of a clear forest acidification effect is consistent with deposition-model estimates which show the increased scavenging of occult and dry deposition by the growing forest to be small at this site (</=10%). Critical load calculations suggest that planned emission reductions will be sufficient to protect the catchment stream from further acidification by 2003. The additional deposition capture by the continued growth of the forest is predicted to delay this response by approximately 2 years.