Natural acidity or anthropogenic acidification in the spring flood of northern Sweden?

https://doi.org/10.1016/S0048-9697(99)00259-4Get rights and content

Abstract

Episodic pH decline associated with spring flood runoff in a typical headwater stream in the boreal forest of northern Sweden is driven almost exclusively by natural processes. Despite a drastic decline in acid neutralisation capacity (ANC), a 75-fold increase in hydrogen ion concentration and an associated increase in inorganic monomeric aluminium fractions, anthropogenic deposition (the strong acids SO42− and NO3 associated with anthropogenic deposition) made only a minor contribution (5–8%) to the ANC and pH decline during the spring flood of 1997. Instead the ANC decline from 60 μeq. l−1 during winter baseflow to −26 μeq. l−1 at peak flow, as well as the associated pH decline from approximately 6.4–4.6 was, according to an episodic acidification model, driven almost exclusively by organic acids originating from the soil and dilution by low ionic strength snowmelt water. The natural component of ANC and pH decline during spring flood, such as that reported here, has important implications for the aquatic ecology of the boreal zone in general, and for the Swedish liming program in particular, since government subsidies are used to keep pH above 6.0 throughout spring flood, in the belief that this is the natural pH level prior to the appearance of acid rain in Europe.

Introduction

Episodic pH decline during spring flood is an ubiquitous phenomena that has been reported from several regions of the world (i.e. Tranter et al., 1987, Wigington et al., 1992, Wigington et al., 1996). In many regions the large and rapid pH decline in surface waters during spring flood, which is a particularly sensitive time for the early life stages of many aquatic species, has in acidified regions of the world been mainly ascribed to anthropogenic SO42− and NO3 deposition in combination with dilution of the buffering capacity (Molot et al., 1989, Davies et al., 1992, Eshleman et al., 1995). The anthropogenic contribution to this acid shock is intensified by elevated concentrations of acidity eluted preferentially from the snow pack at the onset of snowmelt (Johannessen and Henriksen, 1978). There is, however, growing evidence that the concentration of organic acids may rise naturally during snowmelt (Kahl et al., 1991, Campbell et al., 1992, Jansson and Ivarsson, 1994, Kortelainen and Saukkonen, 1995, Laudon and Bishop, 1999).

Using an ANC dilution model outlined in Laudon and Bishop (1999) in combination with a organic dissociation model (Köhler, unpublished data) we quantified the effects of sulphate, chloride, organic acids and dilution in driving a large ANC decline and a 75-fold increase in hydrogen ion activity during the peak of spring flood in a forested boreal catchment from northern Sweden. This quantification is an important tool in understanding the role of anthropogenic acidification and for improving the liming strategy during the spring flood in northern Sweden.

Section snippets

Field site

Västrabäcken is a forested 8.6 ha, headwater catchment, typical of the boreal region in northern Sweden. The catchment is located at the Svartberget Research Station in the county of Västerbotten (64°14′ N, 10°46′ E) approximately 50 km inland from the Baltic Sea coast. The drainage area is mainly covered by pine (Pinus sylvestris) in the upper, drier areas (20% of the catchment) and Norway spruce (Picea abies) in the lower reaches (75% of the catchment). A locally derived glacial till with an

Methods

Water sampling and discharge measurements were carried out at a thin plate 90° V-notch weir at the outlet of the catchment. The sampling program was based on weekly samples of baseflow prior to the onset of the spring flood, and then daily sampling until the water flow had receded to levels close to those of baseflow. Water samples for chemical analysis were collected in acid-washed 250-ml polyethylene bottles. The samples were stored cold and in the dark until analysed.

Nine 1.5-m2 acid washed

Results

The spring flood of the Västrabäcken catchment commenced on the 1 May 1997 and reached maximum discharge 2 weeks later. During baseflow, prior to the spring flood, the pH of the stream varied between 6.2 and 6.5 for over 1 month. At the onset of the rising hydrograph, pH declined rapidly to a minimum of 4.6 at peak flow (Fig. 1a). The decline in pH was accompanied by a decline in ANC (Fig. 1b), coinciding with a decrease in base cations (BC) (Fig. 1c), SO42− (Fig. 1d) while Cl stayed at

Discussion

Paleolimnological reconstructions of pre-industrial lake acidity in 120 geographically representative head water lakes from northern Sweden showed an average decline of only 0.05 pH units in the region during the industrial era (Korsman, 1993, Korsman, in press). The paleolimnic record, however, is only believed to indicate the yearly mean pH value of the surface water, and does not provide specific insight into the anthropogenic influence on spring flood episodes in head water streams, which

Conclusion

The spring flood ANC and pH decline at Västrabäcken demonstrates that a large pH decline and Ali, increase can be a natural property of the boreal surface water ecosystems. The natural acidity of surface waters in northern Sweden is a situation which the aquatic life has adapted to over thousands of years. Headwater streams in this region also represent important habitats for fish reproduction. Liming to raise the pH of such naturally acid streams is, therefore, a threat to the natural

Acknowledgements

We thank the Swedish Environmental Protection Agency, NFR and Lilli and Oscar Lamms minnesfond for their financial support. The doctoral position for Stephan Köhler was financed by the Centre of Environmental Research in Umeå. Kevin Bishop also received research support from Umeå University, Faculty of Natural Sciences.

References (34)

  • P.G.C Campbell et al.

    Geochemistry of Quebec north shore salmon rivers during snowmelt — organic-acid pulse and aluminum mobilization

    Can J Fish Aquat Sci

    (1992)
  • N Christophersen et al.

    Linking hydrological, geochemical and soil chemical processes on the catchment scale: an interplay between modeling and field work

    Water Resour Res

    (1990)
  • N Clarke et al.

    The determination of quickly reacting aluminium in natural waters by kinetic discrimination in a flow system

    Int J Environ Anal Chem

    (1992)
  • K.N Eshleman et al.

    The role of organic acids in the acid–base status of surface waters at Bickford Watershed, Massachusetts

    Water Resour Res

    (1985)
  • K.N Eshleman et al.

    A 2-component mixing model for predicting regional episodic acidification of surface waters during spring snowmelt periods

    Water Resour Res

    (1995)
  • Forsgren, F. Comparing hydrograph separation techniques in the Svartberget catchment. (In Swedish) MSc thesis...
  • G Gran

    Determination of the equivalence point in potentiometric titrations

    Analyst London

    (1952)
  • Cited by (36)

    • Twenty-five year record of chemicals in open field precipitation and throughfall from a medium-altitude forest catchment (Strengbach - NE France): An obvious response to atmospheric pollution trends

      2019, Atmospheric Environment
      Citation Excerpt :

      This situation occurs particularly because the emissions of such contaminants and their deposition remain significant, especially regarding nitrogen (Rogora et al., 2006; Nanus et al., 2017). Therefore, it is important to have an accurate evaluation of “true” atmospheric deposition (Pascaud, 2013; Coddeville et al., 2016) and to monitor these inputs over long time periods in “supposed pristine” ecosystems taken as observatories and “sentinels” of these disturbances (i.e., Paces, 1985; Moldan and Schnoor, 1992; Matzner and Meiwes, 1994; Probst et al., 1995a; Kram et al., 1997; Laudon et al., 1999; Pierret et al., 2018). More generally, in such ecosystems, wet and dry atmospheric deposits are the only external sources of chemical elements including nutrients and pollutants for ecosystems that could affect soil quality and aquatic resources.

    • Hydrological processes behind annual and decadal-scale variations in the water quality of runoff in Finnish catchments with acid sulfate soils

      2013, Journal of Hydrology
      Citation Excerpt :

      In Europe, these soils can be found to a large extent on the coastal plains of Western Finland, and consist of fine-grained sediments originating from the Littorina- and Postlittorina Sea (7500–0 BP) (Puustinen et al., 1994; Yli-Halla et al., 1999). In normal conditions in boreal environments, peat lands and coniferous forests are a source of organic acids to rivers and lakes, which, in turn, control pH in many water courses (Kortelainen and Mannio, 1990; Kortelainen et al., 1989; Kortelainen and Saukkonen, 1995; Laudon et al., 1999; Mattsson et al., 2005, 2007). However, many water courses in Western Finland that drain a.s. soils show an opposite relationship between organic acids and pH or acidity due to the acidic and metal rich discharge from a.s. soils that overshadow any other source of acidity (Edén et al., 1999; Mattsson et al., 2007; Österholm and Åström, 2004; Palko and Weppling, 1994).

    • Forest land cover continues to exacerbate freshwater acidification despite decline in sulphate emissions

      2012, Environmental Pollution
      Citation Excerpt :

      This paper uses a reanalysis of the data of Puhr et al. (2000) as an indication of water quality status in Galloway under conditions of higher deposition; the data were collected on 12th March 1996 for 93 sites during a single storm event. High-flow events were targeted as they commonly promote acid episodes (Welsh and Burns, 1987; Puhr et al., 2000; Laudon et al., 1999; Erlandsson et al., 2010). Catchments were selected to represent a range of catchment afforestation (0–100%) and to be as uniform as possible in terms of geology.

    • Characterization of acid sulfate soils and assessing their impact on a humic boreal lake

      2011, Journal of Geochemical Exploration
      Citation Excerpt :

      Although the impacts are obviously much smaller, other human activities, e.g. dredging operations and draining for buildings and infrastructure also contribute to the forming of a.s. soils. However, many watercourses in northern Europe are also relatively acidic and poorly buffered due to granitic bedrock and soils rich in humic substances, in particularly large peat and coniferous forest areas (Laudon et al., 1999). In addition, the significant input of acid rain during previous decades has diminished the buffering capacity of the soil.

    View all citing articles on Scopus
    View full text