The relationship between nitrogen deposition, species composition and foliar nitrogen concentrations in woodland flora in the vicinity of livestock farms

Citation
Cer. Pitcairn et al., The relationship between nitrogen deposition, species composition and foliar nitrogen concentrations in woodland flora in the vicinity of livestock farms, ENVIR POLLU, 102, 1998, pp. 41-48
Citations number
18
Categorie Soggetti
Environment/Ecology
Journal title
ENVIRONMENTAL POLLUTION
ISSN journal
02697491 → ACNP
Volume
102
Year of publication
1998
Supplement
1
Pages
41 - 48
Database
ISI
SICI code
0269-7491(1998)102:<41:TRBNDS>2.0.ZU;2-P
Abstract
Measurements of atmospheric ammonia concentration along a gradient of decre asing concentration, species composition and tissue nitrogen content of a r ange of plant species were made in woodland in the vicinity of four intensi ve animal units in Scotland. Ammonia concentrations were large at woodland edges close to the livestock buildings (annual means 20-60 mu g m(-3)) and exceed critical levels for NH3 (8 mu g m(-3) annual mean). Surveys of speci es composition of ground flora along an 0.5 km transect from livestock buil dings show marked changes within 300 m downwind of the buildings. Species s uch as Deschampsia flexuosa, Holcus lanatus, Rubus idaeus and Urtica dioica were abundant close to livestock units and their percentage cover decrease d rapidly with distance from source, while the more N-sensitive species suc h as Oxalis acetosella, Galium odoratum, mosses and ferns which are found u pwind and outside the influence of the NH3 source, were scarce at all sites receiving >25 kg ha(-1) N year(-1). Visible injury to pine and spruce need les was observed immediately downwind of the buildings. Foliar nitrogen con centration of a number of species was large close to the buildings and decl ined with distance. Total nitrogen deposition at the woodland boundaries is estimated to range from 40 to 80 kg N ha(-1) year(-1) at the 4 sites and e xceeds critical loads for acidic coniferous forest, i.e. 15-20 kg N ha(-1) year(-1) to protect ground flora, and is also often in excess of that (11-5 0 kg N ha(-1) year(-1)) proposed to protect tree health. Foliar nitrogen co ntent of mosses, (L-N, % dry weight) is related to nitrogen deposition (F-N , kg N ha(-1) year(-1)) according to L-N = 3.81(1-e(-0.04FN)).