Impacts of Intensive Management and Landscape Structure on Timber and Energy Wood Production and net CO2 Emissions from Energy Wood Use of Norway Spruce

The aim of this study was to analyze the effects of intensive management and forest landscape structure (in terms of age class distribution) on timber and energy wood production (m3 ha−1), net present value (NPV, € ha−1) with implications on net CO2 emissions (kg CO2 MWh−1 per energy unit) from energy wood use of Norway spruce grown on medium to fertile sites. This study employed simulations using a forest ecosystem model and the Emission Calculation Tool, considering in its analyses: timber (saw logs, pulp) and energy wood (small-sized stem wood and/or logging residuals for top part of stem, branches, and needles) from the first thinning and harvesting residuals and stumps from the final felling. At the stand level, both fertilization and high pre-commercial stand density clearly increased timber production and the amount of energy wood. Short rotation length (40 and 60 years) outputted, on average, the highest annual stem wood production (most fertile and medium fertile sites), the 60 year rotation also outputted the highest average annual net present value (NPV with interest rates of 1–4%). On the other hand, even longer rotation lengths, up to 80 and 100 years, were needed to output the lowest net CO2 emissions per year in energy wood use. At the landscape level, the largest productivity (both for timber and energy wood) was obtained using rotation lengths of 60 and 80 years with an initial forest landscape structure dominated by older mature stands (a right-skewed age-class distribution). If the rotation length was 120 years, the initial forest landscape dominated by young stands (a left-skewed age-class distribution) provided the highest productivity. However, the NPV with interest rate of 2% was, on average, the highest with a right-skewed distribution regardless of the rotation length. If the rotation length was 120 years, normal age class distribution provided, on average, the highest NPV. On the other hand, the lowest emissions (kg CO2 MWh−1a−1) were obtained with the left-skewed age-class distribution using the rotation lengths of 60 and 80 years, and with the normal age-class distribution using the rotation length of 120 years. Altogether, the management regimes integrating both timber and energy wood production and using fertilization provided, on average, the lowest emissions over all management alternatives considered.

[1]  Leif Gustavsson,et al.  Primary energy and greenhouse gas implications of increasing biomass production through forest fertilization , 2010 .

[2]  H. Peltola,et al.  Impacts of thinning and fertilization on timber and energy wood production in Norway spruce and Scots pine: scenario analyses based on ecosystem model simulations , 2011 .

[3]  Jordi Garcia-Gonzalo,et al.  Carbon stocks and timber yield in two boreal forest ecosystems under current and changing climatic conditions subjected to varying management regimes , 2006 .

[4]  William Omondi Oloo Land Use, Land Use Change and Forestry , 2010 .

[5]  S. Kellomäki,et al.  Changes in wood production of Picea abies and Pinus sylvestris under a warmer climate: comparison of field measurements and results of a mathematical model. , 1996 .

[6]  J. Melillo,et al.  Indirect Emissions from Biofuels: How Important? , 2009, Science.

[7]  H. Griffiths,et al.  The carbon balance of forest biomes , 2005 .

[8]  Economics. Production,et al.  Evaluation of environmental impacts in life cycle assessment , 2003 .

[9]  Anssi Ahtikoski,et al.  Applying the MOTTI simulator to analyse the effects of alternative management schedules on timber and non-timber production , 2005 .

[10]  W. McDowell,et al.  Nitrogen Saturation in Temperate Forest Ecosystems Hypotheses revisited , 2000 .

[11]  Heikki Hänninen,et al.  Sima: a model for forest succession based on the carbon and nitrogen cycles with application to silvicultural management of the forest ecosystem , 1992 .

[12]  A. Mäkelä,et al.  Economic analysis of stand establishment for Scots pine , 2006 .

[13]  Effects of nitrogen fertilization on carbon accumulation in boreal forests : Model computations compared with the results of long-term fertilization experiments , 1998 .

[14]  J. Aber,et al.  Nitrogen saturation in northern forest ecosystems , 1989 .

[15]  E. Beuker Long‐term effects of temperature on the wood production of Pinus sylvestris L. and Picea abies (L.) Karst. In old provenance experiments , 1994 .

[16]  William H. McDowell,et al.  Nitrogen Saturation in Temperate Forest Ecosystems , 1998 .

[17]  Dale W. Johnson Effects of forest management on soil carbon storage , 1992 .

[18]  J. Stendahl,et al.  Integrated carbon analysis of forest management practices and wood substitution , 2007 .

[19]  Sampo Soimakallio,et al.  Greenhouse gas balances and new business opportunities for biomass-based transportation fuels and agrobiomass in Finland , 2009 .

[20]  K. Shine,et al.  Intergovernmental panel on Climate change (IPCC),in encyclopedia of Enviroment and society,Vol.3 , 2007 .

[21]  G. Katul,et al.  Soil fertility limits carbon sequestration by forest ecosystems in a CO2-enriched atmosphere , 2001, Nature.

[22]  M. Lindner Waldbaustrategien im Kontext möglicher Klimaänderungen , 1999, Forstwissenschaftliches Centralblatt vereinigt mit Tharandter forstliches Jahrbuch.

[23]  Timo Karjalainen,et al.  Comparison of greenhouse gas emissions from forest operations in Finland and Sweden , 2003 .

[24]  Jacinto F. Fabiosa,et al.  Use of U.S. Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land-Use Change , 2008, Science.

[25]  K. Korhonen,et al.  Adaptation of forest ecosystems, forests and forestry to climate change. FINADAPT Working Paper 4 , 2005 .

[26]  Antti Asikainen,et al.  Greenhouse gas emissions from the use of primary energy in forest operations and long-distance transportation of timber in Finland , 1996 .

[27]  Heikki Hänninen,et al.  A simulation model for the succession of the boreal forest ecosystem. , 1992 .

[28]  Hannu Hökkä,et al.  Models for predicting stand development in MELA System , 2002 .

[29]  Charles F. Cooper,et al.  Carbon storage in managed forests , 1983 .

[30]  Walter Klöpffer,et al.  Life cycle assessment , 1997, Environmental science and pollution research international.

[31]  Marja Kolström,et al.  Ecological simulation model for studying diversity of stand structure in boreal forests , 1998 .

[32]  A. Cajander,et al.  Theory of forest types , 1926 .

[33]  Rattan Lal,et al.  Land Use, Land-Use Change and Forestry , 2015 .

[34]  H. Peltola,et al.  Impacts of forest landscape structure and management on timber production and carbon stocks in the boreal forest ecosystem under changing climate , 2007 .

[35]  B. Lundgren,et al.  Decrease in soil microbial activity and biomasses owing to nitrogen amendments , 1983 .

[36]  K. Korhonen,et al.  Sensitivity of managed boreal forests in Finland to climate change, with implications for adaptive management , 2008, Philosophical Transactions of the Royal Society B: Biological Sciences.

[37]  S. Kellomäki,et al.  Computations on the yield of timber by Scots pine when subjected to varying levels of thinning under a changing climate in southern Finland , 1993 .

[38]  Eero Nikinmaa,et al.  Analyses of the growth of Scots pine: matching structure with function. , 1992 .

[39]  Seppo Kellomäki,et al.  Life cycle assessment tool for estimating net CO2 exchange of forest production , 2011 .

[40]  A. Ibrom,et al.  'Carbon forestry': managing forests to conserve carbon. , 2005, SEB experimental biology series.

[41]  Robert W. Howarth,et al.  Nitrogen limitation on land and in the sea: How can it occur? , 1991 .

[42]  Daniel B. Botkin,et al.  Predicting the effects of different harvesting regimes on forest floor dynamics in northern hardwoods , 1978 .

[43]  P. Martikainen,et al.  Mineralization of carbon and nitrogen in soil samples taken from three fertilized pine stands: Long-term effects , 1989, Plant and Soil.

[44]  IEA Bioenergy Greenhouse Gas Balances of Biomass and Bioenergy Systems , 2002 .

[45]  Kim Pingoud,et al.  Which rotation length is favourable to carbon sequestration , 2001 .

[46]  R. Tate Nitrogen in Terrestrial Ecosystems. Questions of Productivity, Vegetational Changes, and Ecosystem Stability , 1992 .

[47]  B. Reineking,et al.  Models for forest ecosystem management: a European perspective. , 2007, Annals of botany.