Rc. Helliwell et al., A two-layer application of the MAGIC model to predict the effects of land use scenarios and reductions in deposition on acid sensitive soils in the UK, HYDROL E S, 2(4), 1998, pp. 497-507
A two-layer application of the catchment-based soil and surface water acidi
fication model, MAGIC, was applied to 21 sites in the UK Acid Waters Monito
ring Network (AWMN), and the results were compared with those from a one-la
yer application of the model. The two-layer model represented typical soil
properties more accurately by segregating the organic and mineral horizons
into two separate soil compartments. Reductions in sulphur (S) emissions as
sociated with the Second S Protocol and different forestry (land use) scena
rios were modelled, and their effects on soil acidification evaluated. Soil
acidification was assessed in terms of base saturation and critical loads
for the molar ratio of base cations (Ca2+ + Mg2+ + K+) to aluminium (Al) in
soil solution. The results of the two-layer application indicate that base
saturation of the organic compartment was very responsive to changes in la
nd use and deposition compared with the mineral soil. With the two-layer mo
del, the organic soil compartment was particularly sensitive to acid deposi
tion, which resulted in the critical load being predicted to be exceeded at
eight sites in 1997 and two sites in 2010. These results indicate that fur
ther reductions in S deposition are necessary to raise the base cation (BC)
:Al ratio above the threshold which is harmful to tree roots. At forested s
ites BC:AI ratios were generally well below the threshold designated for so
il critical loads in Europe and forecasts indicate that forest replanting c
an adversely affect the acid status of sensitive organic soils. This illust
rates the importance of proactive and responsible forestry management polic
ies consistent with the longer term objectives of protecting and sustaining
soil and water quality. Policy formulation must seek to protect the most s
ensitive environmental receptor, in this case organic soils. It is clear, t
herefore, that simply securing protection of surface waters, via the critic
al loads approach, may not ensure adequate protection of low base status or
ganic soils from the effects of acidification.