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On the 31st July – 6th August 2005 in Lublin surroundings, high and intensive rainfalls appeared (Table 1). The highest one took place at night of 3rd–4th August and its level exceeded 100 mm in two stations (Fig. 1). It was the rain of changeable intensity to 1 mm·min–1, lasting 4–5 hours. In the area of 400 square kilometers enclosed with 100 mm isohyet, an intensive runoff with erosional effects appeared. Its size in rural area was conditioned by land use, crop structure, fi eld pattern and road network. Majority of corn fi elds determined the predominance of dispersed runoff and little rainwash. Concentration of runoff and linear erosion took place only on small area of: roads, fi elds with root plants and fi elds of aerated soil (Fig. 3). The maximum of erosion rate in the fi eld scale reached: 200 t·ha–1 of translocated material and 70 t·ha–1 of carried material, fi eld surface lowering by 5 mm and convex parts of slope by 8 cm. Deposition of material, in form of fans and proluvial covers took place in dry valley fl oors. Concentrated runoff formed here episodic channels: transport and deposition in channels being fl at and erosional channels in crops with uncovered soil. Below roads crossing the channels, potholes with the capacity to 50 m3 and bars of eroded material were formed. Most of moved soil material was left within dry valleys whereas water runoff was the main source of fl ood waters in river valleys. Specifi c outfl ow from dry valley catch ments, with the area of 5 square km, reached 1–2.5 m3·(s·km2)–1. In valleys of small perennial fl ows with catchment area less than 50 square km (for instance: Skrzyniczanka, upper Stawek and Sierotka Streams), located in zone of the highest rainfall, local fl oods appeared. They caused losses in road and hydrotechnical infrastructure. Waves from these catchments, with specifi c outfl ow to 0.8 m3·(s·km2)–1, caused relatively smaller fl ood waters in higher valleys in next days (Fig. 2). Five-times growth of fl ow in Biskupice on the Giełczew River and seven-times one in Sobianowice on the Bystrzyca river occurred. On 4th–11th August period, about 12 mm of water fl owed from these catchments but in the Czerniejówka catchment, level of groundwater raised about 30–70 cm.
Spitsbergen glaciers react rapidly to changes in the polar environment, which is expressed in differences in extent of their fronts and surface geometry. The Scott Glacier, which is situated in the NW part of Wedel Jarlsberg Land, is an example of the glacier that has undergone almost continuous recession since the Little Ice Age, interrupted by surges. The variations in recession are characterised based on multiannual data with particularly consideration of the period 1990-2005 and the season 2005/2006. Acceleration of front recession and lowering the surface was found only within the tongue up to a height of about 220 m a.s.l. Whereas, in the area situated in the zone of rock steps and above in the ablation zone, the change of glacier surface ablation (∆h) has been recorded compared to the mean annual recession for the period 1990-2005. Moreover, for the upper firn field, the positive surface ablation (∆AhS7 = +0.19 m) was observed. As the result of progressive reduction of the Scott Glacier mass, with the participation of other factors (bedrock relief among others), new surfaces of roche moutonnée are uncovering particularly in the tongue zone.
Measurements of pollutants scavenged from air masses over southern Svalbard in summer precipitation are presented. Rainfall was sampled in July and August 2002 at Calypsobyen, Bellsund. Specific conductivity (SpC) and pH were measured and ion concentrations were determined by ion chromatography. Ions of marine origin were subtracted, assuming that all chlorides were of marine origin. The FLEXTRA trajectory model was applied to discover the sources of air masses arriving at Svalbard and track the paths of pollutant transport. Average (v/w) rainfall pH was 4.94, mean SpC amounted to 34.8µS cm-1. Total dissolved solids concentration (TDS) ranged from 12.6 to 67 mg L-1, with ions of marine origin (Cl-, Na+, Mg2+) prevailing. Rains with the highest percentage of marine salts occurred with winds from the East at above average velocities. Non-sea salt (nss) sulphate concentrations ranged from 0.5µeq L-1 to 23µeq L-1, (v/w) average was 17µeq L-1. Nitrate concentrations ranged from 0 to 24µeq L-1. The highest concentrations of nss-SO42- and NO3- were measured on 25 August, when the highest rainfall occurred (27 mm) and pH was the lowest (4.65). Rainfall at Calypsobyen deposited 194 kg km-2 of acidifying anions and 263 kg km-2 of base cations over the recording period. The polluted air masses were mostly from northern and central Europe. Rainfalls scavenging air masses formed over Greenland and Norwegian Seas displayed similar concentrations, being probably polluted by SOx and NOx from ship emissions.
The work contains results of observations on the relationship between precipitation and surface runoff and slopewash on the surface plots in UMCS Science Station in Guciów. Observations come from a period of 6 years (2000-2006). Tests were conducted on three plots with typical use of the area. Two plots, with meadow and fallow land, were on the south slope and inclination of 3-5°. The third plot was established in the forest, whose slope was inclined at an angle of 13-18° and east display. Cover of soil in the station area, are eroded podsol soil, with silty sand in the arable layer. Obtained results of the observations were included in the form of regression equations describing the relationship between rainfall during the summer and surface runoff, runoff and slopewash of soil's, rainfall erosivity factor and slopewash.
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