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From this detailed work an N sustainability tool for any site, which presents the relationship between drainage class, drainage design (if present), completeness of denitrification, rate of denitrification and NH4-N attenuation was developed.
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Additionally, a global dataset with 432 profiles with various soil classes, drainage types, land use, and altitude was also used to test the generality of the new model.
Fig. 2 The response of growth, mortality, and net biomass change of western boreal forests of Canada to calendar year in relation to drainage class.
In order to derive overall temporal trends, we fit a similar model to eq. 1 but omitted the drainage class year interaction (β6).
The responses of relative growth rate and net biomass change to calendar year differed significantly among drainage classes, while calendar year trends related to mortality did not differ significantly (Table 2).
Furthermore, as drainage classes form an ordered series rather than unrelated classes, differential costs for misclassification were tested in combination with each technique.
Trends in a) absolute and b) relative growth, mortality, and net biomass change associated with forest age after accounting for the effects of drainage class and calendar year.
Trends in a) absolute and b) relative growth, mortality, and net biomass change associated with calendar year after accounting for the effects of drainage class and forest age. Figure S4.
The maps predicted the same drainage class in 81% of the study area.
Similarity criteria included drainage class, taxonomic great group, parent material and slope.
Total soil C was influenced by soil depth, land use, soil type, soil drainage class, and geologic unit.
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