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Abstract

Agricultural landscapes are linked to many functions that benefit human well-being, with a focus on food production. These functions are intrinsically linked with the management choices made by farmers, which are reflected in different farming systems (FS) and their shares in the landscape. However, there is a mismatch between the level where these decisions are taken-farm level-and the landscape level, where many ecosystem processes and interactions take place. The FS approach is one way to bridge the gap between both levels since it enables the joint assessment of multiple management decisions from adjacent farmers using farmlevel data and combining them at the landscape level through clustering techniques. The result is a spatial composition of different FS that enables us to capture landscape gradients and spatially relate them with biodiversity and ecosystem services, thus helping to inform and design policies to affect farming system choice. In Europe, the use of the Integrated Administration and Control System (IACS) database, coupled with the Land Parcel Information System (LPIS), a high-resolution spatially-explicit identification system for agricultural plots, provides a potentially rich source of information on agricultural management (e.g., type of crop, livestock stocking, land use). In this study, we investigated the spatial associations between ecosystem condition and ecosystem services indicators; and explored relationships between landscape gradients and these indicators using a FS approach based on IACS and LPIS data. Agroforestry systems were shown to be linked to a greater ecosystem condition and ecosystem services delivery. In contrast, LG dominated by very intensive and specialized FS revealed the most pronounced negative effects on ecosystems.

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Scientists and policy-makers globally are calling for alternative approaches to conventional intensification of agriculture that enhance ecosystem services provided by biodiversity. The evidence reviewed here suggests that alternative approaches can achieve high crop yields and profits, but the performance of other socioeconomic indicators (as well as long-term trends) is surprisingly poorly documented. Consequently, the implementation of conventional intensification and the discussion of alternative approaches are not based on quantitative evidence of their simultaneous ecological and socioeconomic impacts across the globe. To close this knowledge gap, we propose a participatory assessment framework. Given the impacts of conventional intensification on biodiversity loss and greenhouse gas emissions, such evidence is urgently needed to direct science-policy initiatives, such as the United Nations (UN) 2030 Agenda for Sustainable Development.
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Scientific planning for soil and water conservation requires knowledge of the relations between those factors that cause loss of soil and water and those that help to reduce such losses. The soil loss prediction procedure presented in this handbook provides specific guidelines which are needed for selecting the control practices best suited to the particular needs of each site. The procedure is founded on an empirical soil loss equation that is believed to be applicable wherever numerical values of it factors are available. KEYWORDS: TROPAG textbar Miscellaneous subjects textbar Climatology textbar Land Conservation and Management textbar USA (Mainland).
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Successful regeneration of holm oaks is the key to the conservation of the outstanding biodiversity levels in Spanish dehesa parklands. However, low densities of regeneration were measured in this study. The threshold for livestock stocking levels supporting regeneration was below all figures presently found in the dehesas. In the analysis of stand structure, a positive relationship between tree age and the age of agro-silvo-pastoral use of the dehesas was detected. This suggests that the forest cycle has been disrupted, and stands may dissolve gradually. Regeneration failure is an implicit component of this agroforestry system. An analysis of long-term abandoned dehesas situated at roadsides showed that holm oak stands are able to recover if grazing and cultivation are set aside. In a mail survey, managers of private large landholdings highly appreciated having holm oaks on their land, both for income- and non-income-related motivations, e.g. for the preservation of real estate value or family tradition. Land managers identified over-maturity of stands and regeneration failure among the top five problems of dehesas. Conservation policy should be directed towards incentive schemes, environmental education, and technical assistance.
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European Union (EU) member states set aside between 5 and 15% of arable land during the last two decades, but abolition of the set-aside scheme in 2008 caused a sudden loss in habitat availability and biodiversity in agricultural landscapes. Management of set-aside has many facets and in this perspective paper we focus on the biodiversity effects of successional age, sowing strategies and landscape context. Young, 1–2-year-old set-asides have been initially considered to be too ephemeral to have any conservation value. However, when a rich seed and bud bank is available, a species-rich natural (secondary) succession can be observed. Arable (annual) weed communities in the first two years of succession can even include endangered plant species with associated rare insect consumers. Furthermore, many bird species benefit from early-successional habitats, whereas small mammal communities are richer in older habitats. If the local plant species pool is poor, sowings of diverse mixtures from regional seed collections can be recommended. Set-aside managers using species-rich sowings often experience that dominant weeds suppress the less competitive annual species. This trend to species-poor communities can be avoided by intraspecific aggregation of competitively weak species. Broadening the spatial scale from the plot to the landscape, efficiency of set-aside is highest in simple landscapes, where set-aside exhibits greatest effect in enhancement of biodiversity and associated services such as pollination and biological control. In complex landscapes, however, additional set-aside does not add much to the high level of biodiversity and ecological processes already present. Twenty percent of semi-natural, non-crop habitat appears to be a rough threshold for enhancing biodiversity and sustaining services such as pollination and biological control, but improved set-aside management should have the potential to reduce the percentage of semi-natural non-crop habitat needed. EU policy should tailor set-aside schemes for the maintenance of biodiversity and also consider that management efficiency is higher in simple than complex landscapes.
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Electronic computers facilitate greatly carrying out factor analysis. Computers will help in solving the communality problem and the question of the number of factors as well as the question of arbitrary factoring and the problem of rotation. "Cloacal short-cuts will not be necessary and the powerful methods of Guttman will be feasible." A library of programs essential for factor analysis is described, and the use of medium sized computers as the IBM 650 deprecated for factor analysis. (PsycINFO Database Record (c) 2012 APA, all rights reserved)