Effects of administrative land-use and technical land-form constraints on timber production at the landscape level

2010 ◽  
Vol 26 (2) ◽  
pp. 120-127 ◽  
Author(s):  
Leena Kärkkäinen ◽  
Tuula Nuutinen ◽  
Hannu Hirvelä ◽  
Helena Mäkelä
2021 ◽  
Vol 12 (1) ◽  
Author(s):  
Gaëtane Le Provost ◽  
Jan Thiele ◽  
Catrin Westphal ◽  
Caterina Penone ◽  
Eric Allan ◽  
...  

AbstractLand-use intensification is a major driver of biodiversity loss. However, understanding how different components of land use drive biodiversity loss requires the investigation of multiple trophic levels across spatial scales. Using data from 150 agricultural grasslands in central Europe, we assess the influence of multiple components of local- and landscape-level land use on more than 4,000 above- and belowground taxa, spanning 20 trophic groups. Plot-level land-use intensity is strongly and negatively associated with aboveground trophic groups, but positively or not associated with belowground trophic groups. Meanwhile, both above- and belowground trophic groups respond to landscape-level land use, but to different drivers: aboveground diversity of grasslands is promoted by diverse surrounding land-cover, while belowground diversity is positively related to a high permanent forest cover in the surrounding landscape. These results highlight a role of landscape-level land use in shaping belowground communities, and suggest that revised agroecosystem management strategies are needed to conserve whole-ecosystem biodiversity.


Author(s):  
Peter H. Verburg ◽  
A. Veldkamp ◽  
Louise Willemen ◽  
Koen P. Overmars ◽  
Jean-Christophe Castella

1978 ◽  
Vol 7 (2) ◽  
pp. 67-74
Author(s):  
Douglas E. Morris ◽  
Albert E. Luloff

Joad said, “You're bound to get idears if you go thinkin’ about stuff.”John Steinbeck, The Grapes of WrathPast agricultural programs encouraged the withdrawal of cropland from agricultural production. With the removal of crop acreage restrictions and despite the favorable relationships of the 1972–1974 period, all of this land has not been immediately activated into crop production. Some programs encouraged shifts of cropland to pasture, timber production, or to soil improvement uses. Land converted to these alternatives is potentially available for crop production, but whether or at what rate it will be reemployed remains problematic.


Author(s):  
Maria A. Cunha-e-Sá ◽  
Sofia F. Franco

Although forests located near urban areas are a small fraction of the forest cover, a good understanding of the extent to which —wildland-urban interface (WUI) forest conversion affects local economies and environmental services can help policy-makers harmonize urban development and environmental preservation at this interface, with positive impact on the welfare of local communities. A growing part of the forest resource worldwide has come under urban influence, both directly (i.e., becoming incorporated into the interface or located at the interface with urban areas) and indirectly (as urban uses and values have come to dominate more remote forest areas). Yet forestry has been rather hesitant to recognize its urban mandate. Even if the decision to convert land at the WUI (agriculture, fruit, timber, or rural use) into an alternative use (residential and commercial development) is conditional on the relative magnitude and timing of the returns of alternative land uses, urban forestry is still firmly rooted in the same basic concepts of traditional forestry. This in turn neglects features characterizing this type of forestland, such as the urban influences from increasingly land-consumptive development patterns. Moreover, interface timber production-allocated land provides public goods that otherwise would be permanently lost if land were converted to an irreversible use. Any framework discussing WUI optimal rotation periods and conversion dates should then incorporate the urban dimension in the forester problem. It must reflect the factors that influence both urban and forestry uses and account for the fact that some types of land use conversion are irreversible. The goal is to present a framework that serves as a first step in explaining the trends in the use and management of private land for timber production in an urbanizing environment. Our framework integrates different land uses to understand two questions: given that most of the WUI land use change is irreversible and forestry at this interface differs from classic forestry, how does urban forestry build upon and benefit from traditional forestry concepts and approaches? In particular, what are the implications for the Faustmann harvesting strategy when conversion to an irreversible land use occurs at some point in the future? The article begins with a short background on the worldwide trend of forestland conversion at the WUI, focusing mostly on the case of developed countries. This provides a context for the theoretical framework used in the subsequent analysis of how urban factors affect regeneration and conversion dates. The article further reviews theoretical models of forest management practices that have considered either land sale following clear-cutting or a switch to a more profitable alternative land use without selling the land. A brief discussion on the studies with a generalization of the classic Faustmann formula for land expectation value is also included. For completeness, comparative statics results and a numerical illustration of the main findings from the private landowner framework are included.


2005 ◽  
Vol 60 (2) ◽  
pp. 140-146 ◽  
Author(s):  
Michael Probst ◽  
Norbert Berenzen ◽  
Annette Lentzen-Godding ◽  
Ralf Schulz ◽  
Matthias Liess

2021 ◽  
Vol 14 (10) ◽  
pp. 6467-6494
Author(s):  
Abhijeet Mishra ◽  
Florian Humpenöder ◽  
Jan Philipp Dietrich ◽  
Benjamin Leon Bodirsky ◽  
Brent Sohngen ◽  
...  

Abstract. Out of 1150 Mha (million hectares) of forest designated primarily for production purposes in 2020, plantations accounted for 11 % (131 Mha) of this area and fulfilled more than 33 % of the global industrial roundwood demand. However, adding additional timber plantations to meet increasing timber demand intensifies competition for scarce land resources between different land uses such as food, feed, livestock and timber production. Despite the significance of plantations with respect to roundwood production, their importance in meeting the long-term timber demand and the implications of plantation expansion for overall land-use dynamics have not been studied in detail, in particular regarding the competition for land between agriculture and forestry in existing land-use models. This paper describes the extension of the modular, open-source land system Model of Agricultural Production and its Impact on the Environment (MAgPIE) using a detailed representation of forest land, timber production and timber demand dynamics. These extensions allow for a better understanding of the land-use dynamics (including competition for land) and the associated land-use change emissions of timber production. We show that the spatial cropland patterns differ when timber production is accounted for, indicating that timber plantations compete with cropland for the same scarce land resources. When plantations are established on cropland, it causes cropland expansion and deforestation elsewhere. Using the exogenous extrapolation of historical roundwood production from plantations, future timber demand and plantation rotation lengths, we model the future spatial expansion of forest plantations. As a result of increasing timber demand, we show a 177 % increase in plantation area by the end of the century (+171 Mha in 1995–2100). We also observe (in our model results) that the increasing demand for timber amplifies the scarcity of land, which is indicated by shifting agricultural land-use patterns and increasing yields from cropland compared with a case without forestry. Through the inclusion of new forest plantation and natural forest dynamics, our estimates of land-related CO2 emissions better match with observed data, in particular the gross land-use change emissions and carbon uptake (via regrowth), reflecting higher deforestation with the expansion of managed land and timber production as well as higher regrowth in natural forests and plantations.


1962 ◽  
Vol 38 (1) ◽  
pp. 121-125
Author(s):  
A. B. Wheatley

1. The public right to use and enjoy its forest- and lakeland must be protected.2. Specially developed areas to provide for wild-land recreational use is necessary to enable people to participate in outdoor experiences. An expanding provincial parks system is fundamental to this.3. Multiple-use of public lands, including parks, is fundamental to a full land use concept. A waste of a resource is contrary to the public interest.4. There should always be a practice of reserving public lands for park purposes, incorporating the multiple-use concept, in order to avoid a possible development that is not compatible with the main potentials of the land.5. The recreational resource in forest areas is very real and must be part of a land use plan in which timber production and recreation, being renewable resources, should be reconciled and each developed to provide the maximum public value.


In common with those of other regions, the major wastes of the European Community (EC) that may be regarded as potential sources of lignocellulose are animal manures, crop and forestry residues, domestic and industrial solid wastes and waste paper. The availability reflects the agricultural policy under the Common Agricultural Policy (CAP) as well as the shortfall in timber production within the EC. Significant regional differences exist due to variations in climate and both agricultural and industrial practices. Of particular importance in future will be policy in respect of land use and/or steps taken to reduce agricultural surpluses.


2003 ◽  
Vol 32 (1) ◽  
pp. 103-115 ◽  
Author(s):  
Jeffrey D. Kline

Economists increasingly face opportunities to collaborate with ecologists on landscape-level analyses of socioeconomic and ecological processes. This often calls for developing empirical models to project land use change as input into ecological models. Providing ecologists with the land use information they desire can present many challenges regarding data, modeling, and econometrics. This paper provides an overview of the relatively recent adaptation of economics-based land use modeling methods toward greater spatial specificity desired in integrated research with ecologists. Practical issues presented by data, modeling, and econometrics are highlighted, followed by an example based on a multidisciplinary landscape-level analysis in Oregon's Coast Range mountains.


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