Abstract

This research aimed to: estimate the inputs of litterfall; model the decomposition process and assess the rates of litter decay and turnover; study the litter decomposition process and dynamics of nutrients in old chestnut high forests. This study aimed to fill a gap in the knowledge of chestnut decomposition process as this type of ecosystems have never been modeled and studied from this point of view in Portugal. The study sites are located in the mountains of Marão, Padrela and Bornes in a west-to-east transect, across northern Portugal, from a more-Atlantic-to-lessmaritime influence. This research was developed on old chestnut high forests for quality timber production submitted to a silviculture management close-to-nature. We collected litterfall using littertraps and studied decomposition of leaf and bur litter by the nylon net bag technique. Simple and double exponential models were used to describe the decomposition of chestnut litterfall incubated in situ during 559 days. The results of the decomposition are discussed in relation to the initial litter quality (C, N, P, K, Ca, Mg) and the decomposition rates. Annually, the mature chestnut high-forest stands (density 360-1,260 tree ha–1, age 55-73 years old) restore 4.9 Mg DM ha–1 of litter and 2.6 Mg ha–1 yr–1 of carbon to the soil. The two-component litter decay model proved to be more biologically realistic, providing a decay rate for the fast initial stage (46-58 yr–1for the leaves and 38-42 yr–1for the burs) and a decay rate related to the recalcitrant pool (0.45-0.60 yr–1for the leaves and 0.22-0.36 yr–1for the burs). This study pointed to some decay patterns and release of bioelements by the litterfall which can be useful for calibrating existing models and indicators of sustainability to improve both silvicultural and environmental approaches for the management of chestnut forests.

Highlights

  • The sweet chestnut constitutes an important species in Europe occupying 2.53 million hectares

  • The double exponential decay model for the leaves and burs litter fitted better than the single exponential model based on the biological meaning of the regression coefficients and the goodness of fit of the model, given by the fit index (FI) equivalent to the coefficient of determination in linear regression (R2) (Table 5 and 6)

  • The results obtained in this study for total litterfall of high forest chestnut (4.9 Mg DM ha–1 yr–1) are similar to the values reported by Santa-Regina (2000) for chestnut coppice

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Summary

Introduction

The sweet chestnut constitutes an important species in Europe occupying 2.53 million hectares. In Portugal, the species is located essentially in the North from 400-1,100 m above sea level and there are three major management systems: groves, coppices and high forest for quality timber production. The coppices and high forest are relevant, especially in deep forest soils. These chestnut areas are natural ecosystems and constitute discontinuities between conifer forests and are important for forest fire prevention, biodiversity and environmental protection. The sustainable management of these areas is crucial and depends on the knowledge of the inputs and outputs of the system

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