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Wielkopolska belongs to the regions with the poorest water resources both on Polish and European scales. This region features the lowest precipitation in Poland. Water resources in rivers running across Wielkopolska are also small. A considerable fraction of water resources is in lakes, but they are distributed unevenly, with the prevailing fraction in the northern, part of the region. Generally, more than 70% of river length are outside any water purity classification. Water contamination in lakes, especially larger ones, is not good, either. Small lakes siuated in forests, which are not used for recreation, have the purest water. Safe swimming is possible only in every fifth lake of Wielkopolska.
Our paper reports the phyto- and zooplankton changes studied in Lake Uzarzewskie in 2010-12 under the influence of a restoration procedure. It is a small (10.6 ha), not deep (up to 7.3 m) but thermally stratified, natural, kettle-shaped lake fed with waters from the Cybina River. Water of the tributary rich in nutrients was responsible for the hypertrophic state of the lake. To improve the condition of the lake, some restoration measures were applied. They included the iron treatment method used for phosphorus inactivation. The second method used for the lake restoration was transport of the water rich in nitrates flowing from the springs at the bottom of the slope near the lake by special pipes to the deepest part of the lake, to increase the redox potential at the sediments-water interface. The most abundant group of phytoplankton were cyanobacteria, (especially in summer and autumn months), diatoms, cryptophytes, and chrysophytes. Chlorophytes were the most numerous in respect to the number of taxa. The most important taxa were Planktothrix agardhii, Aphanizomenon gracile, Pseudanabaena limnetica, Limnothrix redekei, Cyclotella, Stephanodiscus, Rhodomonas lacustris, Cryptomonas marssonii, and C. reflexa. Comparing with mean abundance and biomass of phytoplankton in 2010, a small statistically significant decrease was noted in 2011, but an increase in 2012. Some improvement in water quality judged by Shannon-Weaver diversity index and species composition, abundance, and biomass in the lake plankton was observed. Zooplankton was dominated by rotifers. Among cladocerans the most abundant were Bosmina longirostris and Eubosmina coregoni, which were not effective enough in phytoplankton control.
Sediments, being the most important source of phosphorus (P) in the shallow (max. depth 7.2 m), polymictic Swarzędzkie Lake during the summer, were thoroughly studied in laboratory experiments with intact cores sampled at 7 stations in four seasons of the year. Under anaerobic conditions P release rates peaked in the samples from the deepest part of the lake at 26.86 mgP m⁻²d⁻¹. However, the highest rates were determined at one of the littoral sites (near the mouth of a polluted stream) at 59.5 mgP m⁻²d⁻¹. Littoral P release coincided with occasionally low oxygen concentrations (0.2 mgO₂ l⁻¹) above the bottom. On the scale of the whole lake, P release from the littoral zone, where both temperature and oxygen concentration were highly variable, had the strongest influence on the trophic state. It accounted for 63% of the annual internal load but only 55% of total lake area.
The aim of this study was to determine the microbiological quality of runoff from an urban area with different catchment land use flowing into the Cybina River in Poznań, Poland. Water samples were taken from October 2009 to March 2011 at five research stations situated at the outlets of sewers draining a road surface, a car park, and residential and industrial areas. Microbiological analyses included: total bacterial count at 22ºC and at 37ºC, coliform group and faecal coliform bacteria. In each sample the coliform group and faecal coliform bacteria, probably of animal origin, were present. MPN coliform group ranged from 48 to 24·10⁵ cells in 100 ml. The results indicated that quality of stormwater depended on such factors as duration of the rainless period, season, and size and state of the impervious area. High microbiological contamination betokens an adverse influence on the water quality of the Cybina, and therefore treatment of this sewage before the outlets to the receiver is necessary.
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