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farming

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  • The BOREAS TGB-07 team measured the concentration and flux of several agricultural pesticides in air, rainwater, and dry deposition samples in order to determine the associated yearly deposition rates. This data set contains information on the ambient air concentration of seven herbicides [2,4-dichlorophenoxyacidic_acid (2,4-D), bromoxynil, dicamb, 2-methyl-4-chlorophenoxyacetic acid (MCPA), triallate, trifluralin, and diclop-methyl] known to appear in the atmosphere of the Canadian prairies. Also, the concentration of three herbicides (atrazine, alaclor and metolachlor), two groups of insecticides (lindane and breakdown products and dichlro-diphenyl-trichloroethane (DDT) and breakdown products), and several polychlorinated biphenyls commonly used in the central United States were measured. All of these chemicals are reported, in the literature, to be transported in the atmosphere. Many have been reported to occur in boreal and arctic food chains. The sampling was carried out from June 16 to August 13, 1993 and May 4 to July 20, 1994 at the BOREAS site in the Prince Albert National Park (Waskesiu). [ This document was provided by NASA's Global Change Master Directory. For more information on the source of this metadata please visit http://gcmd.nasa.gov/r/geoss/[GCMD]BOREAS_TGB7AAHO ]

  • The BOREAS TGB-07 team measured the concentration and flux of several agricultural pesticides in air, rainwater, and dry deposition samples in order to determine the associated yearly deposition rates. This data set contains information on the dry deposition flux of seven herbicides [2,4-dichlorophenoxyacidic_acid (2,4-D), bromoxynil, dicamb, 2-methyl-4-chlorophenoxyacetic acid (MCPA), triallate, trifluralin, and diclop-methyl] known to appear in the atmosphere of the Canadian prairies. Also, the concentration of three herbicides (atrazine, alaclor and metolachlor), two groups of insecticides (lindane and breakdown products and dichlro-diphenyl-trichloroethane (DDT) and breakdown products), and several polychlorinated biphenyls commonly used in the central United States were measured. All of these chemicals are reported, in the literature, to be transported in the atmosphere. Many have been reported to occur in boreal and arctic food chains. The sampling was carried out from June 16 to August 13, 1993 and May 4 to July 20, 1994 at the BOREAS site in the Prince Albert National Park (Waskesiu). [ This document was provided by NASA's Global Change Master Directory. For more information on the source of this metadata please visit http://gcmd.nasa.gov/r/geoss/[GCMD]BOREAS_TGB7DDHO ]

  • The Muencheberg Soil Quality Rating (SQR) was developed by the Leibniz Centre for Agricultural Landscape Research (ZALF). SQR describes the suitability of sites under agricultural land use and helps to estimate the yield potential of sites at a global scale. This method was especially adapted for application with soil maps by the Federal Institute of Geosciences and Resources BGR and is published in the documentation of Ad-hoc-AG Boden (representing the soil experts of the geological services of the German federal states). The map shows the SQR for cropland in Germany based on the landuse stratified soilmap of Germany at scale 1:1,000,000. Climate (DWD), Relief (BKG) and landuse data (CLC2006) are used as input data in addition to the soil map. SQR consists of a series of pedotransfer rules. First, eight basic soil properties are weighted and combined to describe the soil (substrate, rooting depth, etc.). Next, hazard indicators are derived (drought risk, soil depth above solid rock). These indicators are critical for farming and limit the overall soil quality. Only those hazard indicators were selected for SQR which have the greatest effect on potential grain yield. The final SQR-score ranges from about 0 to 102 points.

  • Geoinformationssystem (GIS) zu - laufenden Bodenordnungen nach Flurbereinigungs-, Gemeinheitsteilungs- und Gemeinschaftswaldgesetz, - LEADER-Regionen (2014-2020 und 2007-2013), - VITAL-Regionen (2014-2020), - Dorfinnenentwicklungskonzepte, - Integrierte kommunale Entwicklungskonzepte, - Wegenetzkonzepte, - Dorfentwicklungsplanungen, Dorfentwicklung, - Förderkulisse Ländlicher Raum (2014-2020), - Förderkulisse NGA, - Förderkulisse NGA-Breitband.

  • Einzellayer zur Topographischen Karte 1:50000 (Waldflächen) (enthält alle auf der TK50 in grün dargestellten Merkmale)

  • Agrarstruturelle Entwicklungsplanung für das Saarland (AEP) "Vorschlagsflächen vorbehaltsgebiete Landwirtschaft". Auftraggeber: Landwirtschaftskammer für das Saarland. Fördergeber: Saarländisches Ministerium für Umwelt. Erarbeitet durch: Dipl. Ing. agr. Jens Thös Büro für landwirtschaftliche Fachplanungen Saarbrücken

  • Gebietskulisse Benachteiligen Gebiete: Es handelt sich um die „aus naturbedingten Gründen benachteiligen Gebiete“ (gemeint sind landwirtschaftliche Flächen). Es handelt sich um die Flächen folgender Gemeinden: Beckingen, Bexbach, Blieskastel, Bous, Eppelborn, Freisen, Gersheim, Großrosseln, Heusweiler, Homburg, Illingen, Kirkel, Kleinblittersdorf, Lebach, Losheim am See, Mandelbachtal, Marpingen, Merchweiler, Merzig, Namborn, Neunkirchen, Nohfelden, Nonnweiler, Oberthal, Ottweiler, Perl, Püttlingen, Quierschied, Rehlingen-Siersburg, Riegelsberg, Saarbrücken, Saarwellingen, Schmelz, Schwalbach, Spiesen-Elversberg, St. Ingbert, St. Wendel, Sulzbach, Tholey, Überherrn, Wadern, Wadgassen, Wallerfangen und Weiskirchen.

  • Rahmendaten zum Agrarstrukturelle Entwicklungsplanung für das Saarland (AEP) "Vn_Region"

  • Gebietskulisse Benachteiligen Gebiete: Gebietskulisse spezifisch benachteiligen Gebiete: Es handelt sich um Gebiete, die aus anderen spezifischen Gründen benachteiligt sind (kleine Gebiete). Betroffen davon ist die Gemeinde Mettlach

  • Rahmendaten zum Agrarstrukturelle Entwicklungsplanung für das Saarland (AEP) "Wald" Mit einer bewaldeten Fläche von 89.600 ha sind ca. 35 % des Saarlandes waldbestanden. Gemessen an einem Bundesdurchschnitt von 29 % Waldanteil gehört das Saarland zu den waldreicheren Bundesländern. Große zusammenhängende Waldbestände finden sich vor allem im Bereich des Saarkohlenwaldes, des Warndts und entlang der nördlichen Landesgrenze (Ministerium für Umwelt - 2000).

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