Abundancia De Macroalgas

On the abundance of epiphytic green algae in relation to the

nitrogen concentrations of biomonitors and nitrogen deposition

in Finland

J. Poikolainena*, H. Lippo”, M. Hongistob, E. Kubin”, K. Mikkola’, M. Lindgrend

‘Muhos Research Station, Finnish Forest Research Institute, FIN-91500 Muhos, Finkmd

bFinnish Meteorological Institute, FIN-00101 Helsinki, Finland

CRovaniemi Research Station, Finnhh Forest Research Institute, FIN-96301 Rovaniemi, Finland

*Vantaa Research Centre, Finnish Forest Research Institute, FIN-013OI Vantaa, Finland

Received 27 March 1998; accepted 10 September 1998

Abstract

Green algae have become considerably more abundant in the years 19851995 in Finland and their distribution area has expanded

northwards. Green algae on conifers were most abundant in southern Finland where the nitrogen deposition is highest. Correlations

were observed between the abundance of green algae and a modelled nitrogen and sulphur deposition as well as the nitrogen

concentration of the biomonitors. The increased abundance of green algae in Finland may be caused by several concurrent changes

which have taken place in the environment and which have all promoted the occurrence of green algae. A slight rise in mean annual

temperature, the long-term stability of nitrogen deposition, and the clear fall in the amount of sulphur deposition have probably all

increased the growth and abundance of green algae. At a local level, the differences in microclimate have also effect on the

abundance of green algae and the microclimate varies, inter alia, by the nutrient-richness of the habitat, the predominant tree

species, stand age and stand density.

Keywords: Green algae; moss; lichen; pine bark; nitrogen deposition

Introduction

The deposition of nitrogen has increased in a large

part of Europe during the past few decades while at the

same time, that of sulphur has considerably diminished

(Barrett et al., 1995; Mylona, 1996). The emissions of

oxides of nitrogen in Finland have remained approximately

at the same annual level, 250 000 tonnes, and

those of ammonium, 50 000 tonnes, in the years 19&G

1995 (Ymptiristtikatsaus, 1995). Emissions of sulphur

dioxide have diminished during the same period from

about 300 000 tonnes to 100 000 tonnes. The total deposi-

* Corresponding author. Tel.: +358-B-531-2200, fax: +358-8-531-

2211; e-mail: jarmo.poikolainen@metla.fi

tion of oxidized nitrogen exceeds 3-4 kg (N) ha-’ year-’

and of the total reduced nitrogen 2-3 kg (N) ha-’ year-’ in

southern Finland (YmptiriWkatsaus, 1995; Hongisto,

1998). Both the oxidized and the reduced nitrogen deposition

decrease to the north and they are in northern

Finland correspondingly only l-l.5 kg (N) and 0.5-l kg

(N). Dry deposition varies 20-50% of total with the

seasons.

Atmospheric nitrogen in wet deposition is in nitrate

and ammonium form (NO,, NH,-) while in dry deposition

it is mainly in the form of gaseous nitric acid

(HNO,), ammonium (NH,) or nitrogen dioxide (NO,)

(Pitcairn et al., 1995; Hongisto, 1998). Nitrogen deposition

has a twofold ecological impact. On the one hand,

nitrogen causes acidification of the soil due to leaching of

base cations. On the other hand, it is a vital plant

86 J. Poikolainen et al. I Environmental Pollution 102, Sl (1998) 85-92

nutrient, which, when in excess, causes eutrophication. It

has been observed that increased deposition has caused

changes in vegetation, especially in areas of high

deposition in Central Europe, to the extent that

eutrophic plant species have increased at the expense of

oligotrophic species (e.g. Bobbink et al., 1992; Sutton et

al., 1993). If the vegetation is not able to bind free

nitrogen in the biological cycle, leaching will increase. In

areas where nitrogen deposition exceeds about lo-15 kg

N ha-* forested catchments show increased leaching of

nitrate (Grennfelt and Hultberg, 1986).

Research on nitrogen deposition and its impacts on

forest ecosystems has been relatively modest with respect

to the use of bioindicators when compared to the

research done on sulphur deposition. Part of the reason

probably lies in the fact that, due to it being an important

plant nutrient, it is more difficult to separate its effects

on vegetation than when dealing with sulphur. Green

algae have been used a little during the past few years as

bioindicators when examining nitrogen deposition

because

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