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Air Quality Guidelines - World Health Organization Regional Office ...

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effects of airborne nitrogen pollutants on vegetation<br />

Table 36. (contd)<br />

Ecosystem Critical load � Indication of exceedance<br />

(kg N/ha<br />

per year)<br />

Trees and forest ecosystems<br />

(contd)<br />

Deciduous trees 15–20 # Nutrient imbalance; increased<br />

shoot/root ratio<br />

Acidic coniferous forests 7–20 ## Changes in ground flora and<br />

mycorrhizas; increased leaching<br />

Acidic deciduous forests 10–20 # Changes in ground flora<br />

Calcareous forests 15–20 (#) Changes in ground flora<br />

Acidic forests (unmanaged) 7–15 (#) Changes in ground flora and<br />

leaching<br />

Forests in humid climates 5–10 (#) Decline in lichens; increase in freeliving<br />

algae<br />

249<br />

a ## Reliable: a number of published papers on various types of study show comparable results.<br />

# Fairly reliable: the results of some studies are comparable.<br />

(#) Expert judgement: no data are available for this type of ecosystem; the critical load is based on knowledge<br />

of ecosystems likely to be more or less comparable with this ecosystem.<br />

b Use low end of the range for nitrogen-limited and high end for phosphorus-limited calcareous grasslands.<br />

receptor groups according to the general relationships between abiotic factors<br />

and critical loads for nitrogen (Table 37).<br />

At this moment, the critical loads are set in values of total nitrogen inputs.<br />

More information is needed in future on the relative effects of oxidized and<br />

reduced nitrogen deposition. Critical loads for nitrogen are formulated as<br />

reliably as possible. As most research has focused on acidification in forestry,<br />

serious gaps in knowledge exist on the effects of enhanced nitrogen deposition<br />

on natural and seminatural terrestrial and aquatic ecosystems. The<br />

following gaps in knowledge are particularly important:<br />

• more research is needed in Mediterranean, tropical and subtropical vegetation<br />

zones;<br />

• quantified effects of enhanced nitrogen deposition on fauna in all types<br />

of vegetation reviewed are extremely scarce;<br />

• the critical loads for nitrogen deposition to Arctic and alpine heathlands<br />

and forests are largely speculative;

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