R. Bobbink et Jgm. Roelofs, NITROGEN CRITICAL LOADS FOR NATURAL AND SEMINATURAL ECOSYSTEMS - THE EMPIRICAL-APPROACH, Water, air and soil pollution, 85(4), 1995, pp. 2413-2418
One of the major threats to the structure and the functioning of natur
al and semi-natural ecosystems is the recent increase in air-borne nit
rogen pollution (NHy and NOx). Ecological effects of increased N suppl
y are reviewed with respect to changes in vegetation and fauna in terr
estrial and aquatic natural and semi-natural ecosystems. Observed and
validated changes using data of field surveys, experimental studies or
, of dynamic ecosystem models (the 'empirical approach'), are used as
an indication for the impacts of N deposition. Based upon these data N
critical loads are set with an indication of the reliability. Critica
l loads are given within a range per ecosystem, because of spatial dif
ferences in ecosystems. The following groups of ecosystems have been t
reated: softwater lakes, wetlands & bogs, species-rich grasslands, hea
thlands and forests. In this paper the effects of N deposition on soft
water lakes have been discussed in detail and a summary of the N criti
cal loads for all groups of ecosystems is presented. The nitrogen crit
ical load for the most sensitive ecosystems (softwater lakes, ombrotro
phic bogs) is between 5-10 kg N ha(-1) yr(-1), whereas a more avenge v
alue for the range of studied ecosystems is 15-20 kg N ha(-1) yr(-1).
Finally, major gaps in knowledge with respect to N critical loads are
identified.