This paper by Dr Chris Evans and colleagues was stimulated originally by the detection of unexpected changes in soil pH in Moor House ECN data.


Reference

Evans, C.D., Monteith, D.T., Fowler, D., Cape, J.N., Brayshaw, S. (2011). Hydrochloric Acid: An Overlooked Driver of Environmental Change. Environ. Sci. Technol. 45(5), pp 1887–1894. DOI: 10.1021/es103574u


Why this research matters

This paper is relevant to the following issues:

  • Climate change
  • Biodiversity protection

In brief

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In more detail

Acidic pollutants derived primarily from the burning of fossil fuels by power stations and large industrial plants and deposited as “acid rain” have led to the widespread acidification of terrestrial (land) and aquatic (freshwater) ecosystems.  Most research in this area has focused on sulphur (S) and nitrogen (N) compounds. Hydrochloric acid (HCl), although also emitted by coal burning, has been largely overlooked as a driver of ecosystem change because most of it was thought to be deposited close to emission sources rather than in remote natural ecosystems.

In the UK, efforts to reduce sulphur emissions, and changes in energy supply away from coal-fired power stations, have had an additional outcome; a 95% reduction in emissions of hydrochloric acid within 20 years (this has been mirrored in other industrialised countries, including the USA and parts of Europe).

Long-term data analysed in this study suggest that the near-disappearance of HCl from deposition could account for 30−40% of chemical recovery from acidification during this time, and that it has had an effect on both near-to-source and remote areas.

In contrast to deposited sulphur and nitrogen compounds that tend to accumulate in wetland soils, HCl tends to pass through these catchments more freely and is therefore likely to have been a more important acidifying pollutant in these systems.

Although the reduction in HCl loadings has enabled natural ecosystems to recover from acidification, there is one arguably less desirable consequence. The shift towards less acidic conditions may be affecting the peatland carbon cycle, contributing to increases in the amount of dissolved organic carbon entering surface waters. This is important for two reasons.

First, dissolved organic carbon (DOC) gives water draining peaty soils its brown colour. When water containing DOC is treated with chlorine in conventional water treatment processes, potentially harmful 'disinfection bi-products' can result. It is important, therefore, that the concentration of DOC is reduced to safe levels before this treatment step. Removing DOC from drinking water is expensive so it is important to understand natural controls on DOC concentration.

Second, peatlands are important stores of carbon. 10-15% of the world's peatlands are found in the UK. Carbon released from peatland soils may eventually re-enter the atmosphere as carbon dioxide or methane, both greenhouse gases. Hence, safeguarding natural carbon stores is an important strategy in our response to climate change.

With many regions of the world increasingly reliant on coal for power generation, hydrochloric acid should be recognized as a potentially significant part of resulting emissions, with distinctive ecosystem impacts.


 

Abstract

This is the published abstract of the research paper

Research on the ecosystem impacts of acidifying pollutants, and measures to control them, has focused almost exclusively on sulfur (S) and nitrogen (N) compounds. Hydrochloric acid (HCl), although emitted by coal burning, has been overlooked as a driver of ecosystem change because most of it was considered to redeposit close to emission sources rather than in remote natural ecosystems. Despite receiving little regulatory attention, measures to reduce S emissions, and changes in energy supply, have led to a 95% reduction in United Kingdom HCl emissions within 20 years. Long-term precipitation, surface water, and soil solution data suggest that the near-disappearance of HCl from deposition could account for 30−40% of chemical recovery from acidification during this time, affecting both near-source and remote areas. Because HCl is highly mobile in reducing environments, it is a more potent acidifier of wetlands than S or N, and HCl may have been the major driver of past peatland acidification. Reduced HCl loadings could therefore have affected the peatland carbon cycle, contributing to increases in dissolved organic carbon leaching to surface waters. With many regions increasingly reliant on coal for power generation, HCl should be recognized as a potentially significant constituent of resulting emissions, with distinctive ecosystem impacts.