Effects of stand conversion by thinning and underplanting on water and element fluxes of a pine ecosystem (P. sylvestris L.) on lignite mine spoil
Introduction
Over decades, mine spoils in the Lusatian Lignite District were mainly afforested with Scots pine (Pinus sylvestris L.), which shows a good initial survival (Preußner and Kilias, 1992). Upgrowing stands are quite productive, but in the long term, this choice of pioneer species undervalues the site potential in most cases. Moreover, it leads to unstable stands, due to the high stress-susceptibility of overstocked monocultures (Knoche, 2001). That is why, today afforestations are carried out mainly with suitable deciduous species like sessile oak or lime being in good agreement with the natural vegetation of the region. To accelerate vegetation change, mixed forests are also established by strong thinning of 40–80-year-old pine stands, and subsequent, underplanting with hardwood trees.
However, thinning and underplanting triggers multiple ecological effects. Especially its impact on water and element turnover is poorly understood. Likely, the reduction of stand biomass increases deep percolation, reinforcing element leaching from the soil (Satterlund and Adams, 1992). Furthermore, opening up of the canopy can induce decoupling of nutrient cycling (Prescott, 2002). For example, elevated N mineralization rates have been reported after thinning by Parsons et al. (1994) and Bäumler and Zech (1998) due to stimulation of humus decomposition. This interference may be crucial for ecosystem stability, since the accumulation of growth-limiting nutrients like nitrogen and phosphorous is a key process for successfull afforestations of mine spoils (Knoche et al., 2002).
The purpose of the present study was to find out, whether thinning and underplanting have an effect on the water and element fluxes. Is stand conversion acceptable from the point of ecosystem stability or will it lead to a destabilization of the stands? This will go against the major target of forest reclamation, which is establishing long-term stable and productive mixed forests (Preußner, 1998).
Section snippets
Site, stand and methods
The water and element fluxes of a quite typical strip mine planting were investigated during the initial stage of stand conversion. Monitoring site Drochow is a 66-year-old Pinus sylvestris (L.) stand without understorey on Quaternary mine sand (reference plot). As Table 1 points out, stocking is characterized by high stem number (780 stem ha−1) and stand biomass (330 m3 ha−1 compact wood). After lowering basal area by single-tree thinning from 38 m2 ha−1 to 27 m2 ha−1 in 1997, a so-called conversion
Water fluxes
Although half of the trees were taken out by thinning, which means a reduction of stand density of 40%, interception decreased only from 38 to 31% of annual bulk precipitation (Table 2). Apparently, opening of the canopy facilitates the moistening of the crowns and allows a more rapid evaporation of the intercepted water. At the same time, the strong reduction of leaf area index increased evapotranspiration of the ecosystem by 4%. Obviously, transpiration of the ground vegetation and
Conclusions
Investigations in a 66-year-old mine spoil planting (P. sylvestris L.) characterize the ecological situation 5 years after initiating stand conversion. In the early stage of stand transformation, deep percolation increased at a consequence of reduced interception from 17 to 23% of annual bulk precipitation. However, it is likely, that with establishing of the underplantings soil water fluxes will decrease again, especially in periods of low precipitation which are quite typical for the region.
Acknowledgements
The present work is part of an integrated study to evaluate conversion of forests in the Lusatian Lignite mining District. The author likes to thank the Federal Ministry for Education and Research (BMBF, Grant No. 0339770) and the Lausitzer und Mitteldeutsche Bergbau-Verwaltungsgesellschaft mbH (LMBV) for financial support. I am very grateful to D. Klem, K. Klem, E. Weber and the reviewers for critical contributions and suggestions.
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2022, Forest Ecology and ManagementCitation Excerpt :Forest stands of the revised studies significantly varied, but all tested the effects of thinning intensities between 10% and 50% of stand density removed. Most of the identified studies were done in conifer stands, either natural (such as the ones in central Europe; Hubbard and Lowrance, 1997; Bäumler and Zech, 1997, 1999; Knoche, 2005; Chu et al., 2019) or planted, mostly from Japan (Chiwa et al., 2020; Fukuyama et al., 2010; Hotta et al., 2007; Shinomiya et al., 2020; Oanh et al., 2021) but also from Europe (Shah et al., 2021) and South America (Perrando et al., 2021). Research studies in broadleaf stands were also identified (Fernández et al., 2011; Serengil et al., 2007; Gökbulak et al., 2008).
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2018, Science of the Total EnvironmentCitation Excerpt :The same negative trend was recorded for the content of zinc (Zn). The low contents of all these nutrients was probably due to leaching (Knoche, 2005). The decreased content of alkaline cations concomitant with the lowest THB indirectly indicated a low pool of available nitrogen in soil under the P. sylvestris.