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2010

2369 record(s)
 
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  • Gives catchment/delineated areas for secondary schools in Angus

  • Initial Awareness Sites submitted as part of the Local Plan Review Main Issues Report

  • Angus Council has prepared a Core Paths Plan for the Council area, to meet the requirements of the Land Reform (Scotland) Act 2003. The Plan was adopted by the Council on 23 November 2010. Core paths form the basic framework of paths, linking with other access provision. Any route across land or inland water can be a core path. The core paths network as a whole should provide access opportunities for the full range of access takers, including walkers, cyclists and horseriders, of varying abilities. Some core paths will be surfaced paths suitable for all abilities use others will be rough tracks, grass paths or routes across open land.

  • Data contents consist of information about wrecks an obstructions. The data originate from investigations of BSH.

  • The site Waki is composed of 4 3km-transects (20m wide). 5106 trees with dbh>=20cm have been recorded by Office national des forêts (ONF). Fauna have been inventoried few days after (ONCFS). 910 under-storey plants have been inventoried on 39 plots (IRD). Soils have been described using 25 samples (1.20m depth max.) and 4 soil pits. Laboratory analysis are available for one soil profiles and the four soil pits.

  • The site of EFELE (Effluents d’Elevage et Environnement) is part of the french network labeled as SOERE PRO. The objectives of EFELE are the same as QualiAgro and Colmar sites : the aim of the project is to characterize the long term effects of organic products applications on soil properties and to quantify their effects on water and air quality. The experimental site was initiated in 2012 and is located in Brittany, at Le Rheu. The soil is a loamy soil (neoluvisol à luvisol/redoxisol). The field is managed with a maize/ wheat crop rotation, and white mustard is sown after the wheat to cover the soil during the intercropping period. Two trials are studied at EFELE site : - A first trial named « PROs » is structured as a complete randomized block design with 4 replicates. The effects of 5 typical animal wastes are compared to control treatments : i) cattle farmyard manure and composted pig manure are applied every 2 years before maize sowing, and ii) layers manure, pig slurry and a digestate obtained after pig slurry digestion are applied in spring, on wheat vegetation at early spring or just before maize sowing. The rates of application range from 50 t ha-1 for cattle manure, 25 t ha-1 for composted pig manure, 20-25 t ha-1 for the slurry and the digestate and 3 t ha-1 for layers manure, - A second trial named « TS/MO » is structured as a band trial with 3 replicates. The objectives of this trial are to study the effects of cattle farmyard manure on soil properties under conventional tillage and reduced tillage. The meteorological data are monitored on the site, and 7 experimental plots are equipped with TDR probes (TRASE system), tensiometers (UMS T4e) and temperature probes placed at the depth of 13, 40, 60, 80 and 110 cm. Data are collected at a hourly time step. 10 plots are also equipped with wick lysimeters (0.25 x 0.50 m) placed at the depth of 40 and 90 cm. The monitoring of N2O and CO2 emission is done by a set of 6 automatics chambers. The soil surface layer (0-25 cm) is sampled every year before the animal wastes application, to characterize the evolution of the physical, biological and chemical properties. Soil, plant and animal wastes samples are kept in collection.

  • Tree Preservation Orders in Angus

  • Local Plan Development Boundaries of villages and towns. Also known as Settlement Boundaries.

  • Gives current catchment/delineated areas for pre-school classes attached to primary schools in Angus.

  • Guyadiv is a network of permanent forest plots installed in French Guiana. The site of Mont Itoupé is composed of 10 20x120m-plots. An incomplete inventory on the pool of trees with dbh>=10cm has been made in 2010. 104 trees by plot have been registrated (except one plot with 102 trees inventoried). 104, 103, 101, 103, 104, 96, 102, 104, 99, 103 species have been identified, respectively to each plot. 100%, 99%, 97.1%, 99%, 100%, 92.3%, 98.1%, 100%, 97.1% and 99% of the inventoried trees have been identified to the level of species, respectively to each plot. We only have the point coordinates and not the precise demarcation of the sample plots. In order to calculate the bounding box for these plots, we have expanded the point location 500 meters in each direction.