L. Cheng et al., EFFECTIVE ACIDITY MODELING TO ESTABLISH ACIDIC DEPOSITION OBJECTIVES AND MANAGE EMISSIONS, Atmospheric environment, 29(3), 1995, pp. 383-392
A mesoscale deposition model has been modified to include a simple che
mical mechanism for six sulphur and nitrogen compounds for the predict
ion of the spatial distribution of effective acidity. Effective acidit
y is defined as the direct mineral acidity plus the hydrogen ions gene
rated as a result of receptor-processing of acid-producing substances
in deposition, minus the hydrogen ions lost by receptor-processing of
acid-consuming substances. This model provides the quantitative relati
onship between emissions from sources and ambient deposition levels, i
nformation required by both the objective setting process and the mana
gement of source emissions to meet the objectives. Model predictions o
f effective acidity resulting from wet deposition agree within 30% of
that calculated from observations. Model outputs indicate that a maxim
um effective acidity of 0.182 keg H+ per hectare per year (keq ha(-1)
yr(-1)) is experienced in northeastern Alberta, a region containing se
nsitive soils. This value lies within the range of 0.1-0.3 keq ha(-1)
yr(-1) which has been suggested as an acidic deposition objective for
the protection of the sensitive soils. A scenario with a 40% reduction
in emissions of SO2 and NOx from a single source in northeastern Albe
rta reduces this maximum to 0.146 and significantly shrinks the area w
ith effective acidify in excess of 0.14 keq ha(-1) yr(-1).