Elsevier

Atmospheric Environment

Volume 44, Issue 6, February 2010, Pages 824-833
Atmospheric Environment

Canopy influence on trace metal atmospheric inputs on forest ecosystems: Speciation in throughfall

https://doi.org/10.1016/j.atmosenv.2009.11.028Get rights and content

Abstract

Atmospheric inputs of selected Trace Metals (TM: Cd, Cu, Ni, Pb, Sb, Zn, as well as Al, Fe and Mn) were studied on six forested sites in France. In order to evaluate canopy interaction with atmospheric inputs, TM were measured in both Open Field Bulk Deposition (BD) and Throughfall (TF). Anthropogenic contribution to BD composition is high for Zn, Cd and Sb, reflecting actual TM emissions trends. Canopy greatly influences precipitation composition, through different processes, including assimilation and leaching by canopy, complexation as well as accumulation/dissolution of dry deposition. TM and Dissolved Organic Carbon (DOC) physical fractionation between colloidal and truly dissolved phases was performed with ultrafiltration. Al, Fe, Pb and Cu are found in the colloidal fraction whereas Cd, Ni, Zn and Sb are mostly in the truly dissolved fraction. Chemical speciation predicted with WHAM-VI shows that in throughfall, Al, Fe, Pb and Cu are almost entirely complexed by DOC, whereas Ni, Cd and Zn are present in average 30% in the free metal ion form. TM present in labile forms (Cd, Ni, Zn) interact with the canopy, are cycled in the ecosystem, and their concentration is either slightly increased or even decreased in throughfall. Sb, Pb and Cu concentration are increased through canopy, as a consequence of dry deposition accumulation.

Introduction

Atmosphere plays a key role in global metal cycles as it receives inputs from many sources and leads to metal dispersion at the Earth scale (Rauch and Pacyna, 2009). Trace Metal (TM: Cd, Cu, Ni, Pb, Sb and Zn) spreading in the atmosphere is induced by natural processes (Nriagu, 1989), as well as anthropogenic activity (Pacyna and Pacyna, 2001). They can be conveyed to long distances (Steinnes and Friedland, 2005) and impact remote ecosystems (Shotyk et al., 1996). Forest ecosystems are particularly sensitive to atmospheric inputs since forest canopy has a large interaction surface with the atmosphere (Leaf Area Index, LAI = 3 to 10 m2 m−2, Ulrich et al., 1995). Interactions between canopy and TM atmospheric inputs include accumulation of dry deposition, direct assimilation or release of elements by canopy (Lovett and Lindberg, 1984, Balestrini et al., 2007). Throughfall (TF) chemical composition thus results from all processes occurring in the phyllosphere. In order to study canopy influence on atmospheric inputs, a study of open field Bulk Deposition (BD) and TF is usually performed (Lindberg et al., 1986, Probst et al., 1992, Balestrini et al., 1998, Neal, 2002, Rodrigo et al., 2003, Hou et al., 2005b). TM dynamics in throughfall has also been considered in a few studies (Petty and Lindberg, 1990, Nieminen et al., 1999, Rodrigo et al., 2003, Hou et al., 2005b, Itoh et al., 2006). A high influence of forest canopy is generally observed with element specific dynamics since they are not all enriched through forest cover. Indeed, TM environmental pathways, availability and transport or immobilization in the ecosystem compartments, are directly linked to their speciation (Cheng et al., 1994) and to their potential role for the biosphere. While some of the studied trace elements are micronutrients (Zn, Cu, Ni), others (Cd, Sb, Pb) have no known biological role (Peralta-Videa et al., 2009). Only few studies (Hou et al., 2005a, Casartelli et al., 2006) have dealt with TM speciation in throughfall, although it provides useful information on canopy processes. Complexing capacity of DOC to Cu and some other TM (Bi, Sn, Ag) was proved, highlighting the conveying role of DOC for some metals below canopy. However, no study of throughfall speciation (including modeling and physical partitioning approaches) in temperate climate forest ecosystems has already been performed for the elements we propose to study (Cd, Cu, Ni, Pb, Sb and Zn).

The objectives of the study are to:

  • (i)

    determine TM concentrations in open field Bulk Deposition and Throughfall in six French forest sites,

  • (ii)

    determine TM and DOC physical fractionation between colloidal and truly dissolved phase in throughfall,

  • (iii)

    model TM speciation in all physical fractions,

  • (iv)

    evaluate the main processes controlling metal behavior after interaction with forest canopy.

Section snippets

Studied sites

The study sites (Table 1, Fig. 1) belong to the French RENECOFOR network (Réseau National de suivi à long terme des Ecosystèmes Forestiers, i.e. National Network for the long term Monitoring of Forest Ecosystem), managed by the ONF (Office National des Forêts, i.e. National Forest Board). These sites are part of the European network ICP Forest (level II). They have been chosen because they are representative of a large variety of French forest ecosystems: four main types of soils (podzol,

TM concentrations in bulk open field precipitation and throughfall

Summary information on rainfall amount, as well as pH, DOC, major (Al, Mn and Fe) and trace elements' concentrations is presented in Table 2.

Rainfall amount was modified through the canopy (Viville et al., 1993). Interception represented 20–50% of the rainfall amount for the studied sites, which corresponds to the average value for temperate French forests (Ulrich et al., 1995). BD was slightly acidic (mean pH is 4.3 ± 0.5) and through the canopy, mean precipitation pH slightly increased (mean pH

DOC origin and composition in throughfall

DOC concentration measured in TF is always higher than DOC concentration in BD (Fillion-Guigues et al., 1999, Peichl et al., 2007). Organic carbon in throughfall comes from foliar leaching (Qualls et al., 2000), microbiological as well as herbivore activity in the phyllosphere (Michalzik and Stadler, 2005). In throughfall, DOC concentration is mainly related to rainfall amount and phytophagous insect activity (Kindlmann and Stadler, 2004).

In this study, no influence of tree species on DOC

Conclusion

This study of trace metal deposition in open field bulk deposition and its interaction with forest cover provides new results on present-day trace metal atmospheric pollution in forest ecosystems. French forest ecosystems undergo anthropogenic inputs of TM. Throughfall composition is highly influenced by forest cover. TM concentrations and fluxes are modified in relation to their chemical properties and role for the biosphere. In throughfall, Mn, Sb, Cd, Zn and Ni are mainly found in the truly

Acknowledgements

This project benefited from a financial support by ADEME (French Agency for Environment) and received logistic support from the ONF (French Forest board). The authors warmly thank the ONF staff (Vincent Borthelle, Jean-Pierre Chassagne, Joël Clamart, Gilles Fournel, Jean-Luc Fiol, René Gregoire, Alain Jacquemard, François Mouchot, Florence Pertile, Pierre Trithardt, Jérôme Vany) for great help during field work, Marc Lanier (ONF), Gaël Durbe and Alain Alric (EcoLab, Université de Toulouse,

References (49)

  • B. Michalzik et al.

    Importance of canopy herbivores to dissolved and particulate organic matter fluxes to the forest floor

    Geoderma

    (2005)
  • C. Neal

    Interception and attenuation of atmospheric pollution in a lowland ash forested site, Old Pond Close, Northamptonshire, UK

    The Science of the Total Environment

    (2002)
  • M. Pédrot et al.

    Insights into colloid-mediated trace element release at the soil/water interface

    Journal of Colloid and Interface Science

    (2008)
  • J.R. Peralta-Videa et al.

    The biochemistry of environmental heavy metal uptake by plants: implications for the food chain

    The International Journal of Biochemistry & Cell Biology

    (2009)
  • L. Poissant et al.

    Trace inorganic elements in rainfall in the Montreal Island

    Atmospheric Environment

    (1994)
  • O. Pokrovsky et al.

    Trace element fractionation and transport in boreal rivers and soil porewaters of permafrost-dominated basaltic terrain in Central Siberia

    Geochimica et Cosmochimica Acta

    (2006)
  • O. Pourret et al.

    Competition between humic acid and carbonates for rare earth elements complexation

    Journal of Colloid and Interface Science

    (2007)
  • A. Rodrigo et al.

    The chemistry of precipitation, throughfall and stemflow in two holm oak (Quercus ilex L.) forests under a contrasted pollution environment in NE Spain

    The Science of the Total Environment

    (2003)
  • W. Shotyk et al.

    Two thousand years of atmospheric arsenic, antimony, and lead deposition recorded in an ombrotrophic peat bog profile, Jura Mountains, Switzerland

    Earth and Planetary Science Letters

    (1996)
  • E. Tipping et al.

    The solid-solution partitioning of heavy metals (Cu, Zn, Cd, Pb) in upland soils of England and Wales

    Environmental Pollution

    (2003)
  • D. Viville et al.

    Interception in a mountainous declining spruce stand in the Strengbach catchment (Vosges, France)

    Journal of Hydrology

    (1993)
  • M.R. Casartelli et al.

    Study of metal-complexed organic matter in throughfall by gel filtration and atomic absorption spectrometry

    Fresenius Environmental Bulletin

    (2006)
  • H.J.W. De Baar et al.

    Trace metals in the oceans: evolution, biology and global change

    Marine Science Frontiers for Europe

    (2003)
  • R. Duce et al.

    Atmospheric trace metal at remote northern and southern hemisphere sites – pollution or natural?

    Science

    (1975)
  • Cited by (66)

    • Coupling of redundancy analysis with geochemistry and mineralogy to assess the behavior of dust arsenic as a base of risk estimation in Dhaka, Bangladesh

      2022, Chemosphere
      Citation Excerpt :

      Therefore, As would have short residence time and tend to mobilize with increasing pH. The increase of As mobility at pH greater than 8.0 has been reported in a previous study (Xu et al., 2013). Organic matter is also an important factor in regulating the mobility of As in soil and dust environments (Gandois et al., 2010). The complexation of oxyanions with organic ligands may enhance their sorption and coprecipitation with solid inorganic phases (Adriano, 2001; Tang et al., 2014).

    • Groundwater controls on colloidal transport in forest stream waters

      2020, Science of the Total Environment
      Citation Excerpt :

      They assigned an important role to local atmospheric emissions for the composition of rainwater particles, whereas dry deposition and canopy leaching modified the chemical composition of particles carried by throughfall. Gandois et al. (2010) additionally reported that complexation with organic matter promoted formation and dissolution of colloids in throughfall; specifically Al, Fe and Pb were found associated to org C. Yet, Gandois et al. (2010) restricted their analysis to bulk deposition and throughfall samples collected weekly over one year and, therefore, could not compare their data to soil, stream or groundwater of the same catchment. In contrast to precipitation waters, NNP and colloids dispersed or leached from soil are usually substantially higher concentrated and likely exhibit a more diverse elemental composition.

    View all citing articles on Scopus
    View full text