Effects and implications
- Potential increase in graminoid (grass) biomass, with adverse effects on forbs.
- Loss of sensitive lichen species
Overview: evidence, processes and main impacts
This habitat represents a range of different systems for which there is no known experimental information on the impacts of nitrogen deposition.
The habitats vary with climate, degree of exposure to salt, geology and soil type, level of grazing and seabird activity. These factors would imply a range of sensitivities to N deposition. Habitats dominated by N sensitive lichens e.g. rocky cliffs would be expected to be the most impacted by N.
Drought is often an issue for vegetation on shallow soils, so N deposition could exacerbate drought problems. Likewise inappropriate grazing management will exacerbate N eutrophication effects and N deposition may well exacerbate consequences of non native and invasive species.
Many cliff habitats support large bird colonies which will substantially increase N deposition in the locality form of NH3 and P and K (guano) inputs in these environments.
Pollutant type and risk
Type of N deposition |
Form of N |
Risk areas |
Dry deposition Gaseous |
NH3 |
Cliffs supporting breeding seabird colonies
|
|
NOx |
Unlikely to be a problem |
Wet deposition precipitation and occult (cloud, mist) |
Ammonium, (NH4+) Nitrate, (NO3-) in varying proportions |
High wet N deposition areas |
Indicators of N enrichment
- None available
Example evidence of species specific responses
- None available
Habitat/ Ecosystem Type | Eunis Code | Critical Load/ Level | Status | Reliability | Indication of exceedance | Reference |
---|---|---|---|---|---|---|
Low and medium altitude hay meadows | E2.2 |
20-30 kg N ha-1 year-1 |
UNECE 2010 - Noordwijkerhout workshop | expert judgement |
Increase in tall grasses, decrease in diversity. |
472 |