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Klimat w okresie wegetacyjnym w Puszczy Zielonka oraz w Wielkopolskim Parku Narodowym w latach 1848-2016

Miler A. T.

Infrastruktura i Ekologia Terenów Wiejskich

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2018

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nr II/1

361--375

PL

Puszcza Zielonka i Wielkopolski Park Narodowy stanowią duże kompleksy leśne w sąsiedztwie aglomeracji poznańskiej. Przyjęto jako referencyjne dane meteorologiczne dla Puszczy Zielonka i dla Wielkopolskiego Parku Narodowego dane ze stacji meteorologicznej w IMGW-PIB Poznaniu-Ławicy. Klimat w Puszczy Zielonka i Wielkopolskim Parku Narodowym wykazuje stosunkowo dużą stacjonarność. Temperatura powietrza (T) dla tych obszarów leśnych, w latach 1848-2016, wykazuje w okresach wegetacyjnych, dodatni trend 0,004 0 C/rok (Sen’s slope) na poziomie istotności α = 0,05. Natomiast opady atmosferyczne (P) oraz wskaźnik hydrotermiczny Sielianinova (HTC) nie wykazują istotnych statystycznie zmian. Analiza Fouriera okresowości temperatury powietrza (T) wskazuje na dominujące cykle: 84,5-; 56,3-; 15,4-; 3,5 - i 3,3-letnie. Analogiczne analizy wskazują na okresowości opadu atmosferycznego (P): 7,0-; 4,0-; 3,6-; 3,3 - i 2,8-letnie. Bardzo podobne, okresowości dominujące uzyskano dla wskaźnika hydrotermicznego Sielianinova (HTC) tj.: 7,0-; 3,9-; 3,3-; 2,8 - i 2,1 - letnie. Można wskazać, iż w Poznaniu, a zatem również w Puszczy Zielonka i w Wielkopolskim Parku Narodowym, w okresach wegetacyjnych, w latach 1848-2016 (nieomal 170 lat) temperatura powietrza (T) wzrosła o około 0,7 0 C, natomiast opad atmosferyczny (P) pozostał na niezmienionym poziomie. Wskaźnik hydrotermiczny Sielianinova (HTC), będący kompleksową oceną warunków opadowych i termicznych, również pozostał na niezmienionym poziomie.

EN

The Puszcza Zielonka and the Wielkopolski National Park are a big forest complex near the Poznan city. Is taken as the reference meteorological data for the Puszcza Zielonka and the Wielkopolski National Park based on data from the Poznan gauge station. The climate in the Puszcza Zielonka and in the Wielkopolski National Park shows relatively high stationarity. Air temperature (T) for these forest areas, from 1848-2016, shows in vegetation seasons, the positive trend of 0.004 0 C/year (Sen’s slope) on the significance level α = 0.05. While precipitation (P) and Sielianinov’s hydrothermal coefficient (HTC) do not exhibit statistically significant changes. Fourier analysis of periodicity of air temperature indicates the dominant cycles: 84.5-; 56.3-; 15.4-; 3.5 - and 3.3-years. An analogous analysis indicate the periodicity of precipitation: 7.0-; 4.0-; 3.6-; 3.3 - and 2.8-years. Very similar, periodicity dominant was obtained for Sielianinov’s hydrothermal coefficient ie.: 7.0-; 3.9-; 3.3-; 2.8 - and 2.1- year. You can indicate that in Poznan, and therefore also in the Puszcza Zielonka and in the Wielkopolski National Park, in vegetation seasons, between 1848-2016 (almost 170 years) air temperature has increased by about 0.7 0 C, while precipitation remained on unchanged level. Sielianinov’s hydrothermal coefficient, which is a comprehensive assessment of the conditions falls and thermal, also remained on unchanged level.

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Zmiany stanów wód gruntowych w Puszczy Zielonka w okresie 1970–2009

Grajewski S., Miler A. T., Krysztofiak-Kaniewska A.

Rocznik Ochrona Środowiska

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2013

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Tom 15, cz. 2

1594--1611

EN

The aim of this study is demonstrate trends of groundwater level changes in Zielonka Forest on the Experimental Forest District Potasze example. The study included a period of 40 years (1970–2009). Variability of groundwater conditions is basis of water relation ratings, or trends of changes on given area, particularly on forest area. The Zielonka Forest is situated in the middle section of the Warta river catchment, in the central part of the Wielkopolska region, and its western border lies about 6 kilometres north-east of Poznan. The area is situated in the western part of the Wielkopolska-Mazovian climatic region. The natural landscape is of early glacial type of Pleistocene and Holocene formation. Postglacial drifts, deposits from the Poznan stage of the Würm glaciations, are the main parent materials of the soils in this area. The granulometric composition is formed by sands with a low clay content, overlying loose sands with admixture of gravel and slightly sandy clay. Scots pine (Pinus silvestris L.) is the dominant tree species but also oak (Quercus robur. L., Q. petrea (Matt.) Liebl.), alder (Alnus glutinosa (L.) Gaertn., Alnus incana (L.) Moench.), larch (Larix sp. Mill.) and rarely spruce (Picea abies (L.) Karst) occur there. The predominant forest site types are: fresh mixed coniferous forest, fresh coniferous forest, wet coniferous forest and alder swamp forest. The greatest yearly fluctuations in groundwater level were observed in alder/ash swamp forest site types, where groundwater level was the highest (in shallow groundwater). Extended the meteorological observations on Zielonka station for 1970–1985, based on meteorological observation from Poznan station are reasonable. The resulting regression and correlation coefficients relation for precipitation sum, mean air temperature (monthly and annual) are statistically significant on customarily accepted levels of significance α = 0.05. Consequently complete data of precipitation and air temperatures have been obtained for the study period 1970–2009 for the Zielonka Forest representative meteorological station in Zielonka village. Time trend for annual precipitation sum in Zielonka Forest in the period 1970–2009 is not statistically significant. However, time trend over that period of the average annual air temperature in the Zielonka Forest is statistically significant and amounts to about +0.05°C/year. These trends for the last 10 years during the study period are respectively -0.28 mm/year and +0.11°C/year. These figures can be considered as a confirmation of the adverse climate changes described in the IPCC Report (2007), in relation to the studied area. For the analysis of groundwater conditions selected years 1970, 2002 and 2009. According to the meteorological conditions (precipitation, air temperature), these three years can be regarded as the average (normal). Average groundwater levels in Zielonka Forest (based on Forest District Potasze analyses) throughout the 40-year study period (1970–2009) fell by about 50 cm, while in the last seven- years, fell by 20 cm. Assuming an average porosity of the aquifer layers to 34%, respectively in these periods decreases the ground retention were thus about 160 mm and 60 mm. Variability of groundwater levels has been reduced twice (variation coefficient of groundwater levels dropped by half). The largest groundwater decreases recorded on forest site types. Much lower on coniferous forest and alder/ash alder swamp forest site type. Groundwater lowering in Zielonka Forest can be associated with intensified adverse climate changes. But this is not the only explanation. The second factor, adversely effect on groundwater conditions in Zielonka Forest and its buffer zone, which was not the subject of this paper, is so-called anthropopressure. For example residential and recreational buildings, manufacture and process plant, etc.

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Tendencje zmian położenia zwierciadła wody gruntowej w wybranych zlewniach na obszarze Puszczy Zielonka

Liberacki D., Szafrański C.

Rocznik Ochrona Środowiska

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2013

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Tom 15, cz. 3

2425--2436

EN

The aim of the study was to assess changes in the position of the groundwater table in selected catchments in the Zielonka forest. The paper presents the results of researches carried out at Hutka small catchment up to Huta Pusta cross section and Potaszka small catchment up to Potasze cross station. Analyzed catchments of investigated watercourses are located in the central part of the Wielkopolska region, approx. 20 km north-east of Poznań, in the Zielonka Forest, at a distance of approx. 7 km from each other. The catchment of the Hutka watercourse, with an area of 0.52 km2, is forested in 89%, the other 11% being covered by swamps and wasteland. The predominant sites are fresh mixed coniferous forest (BMśw), fresh coniferous forest (Bśw) and alder swamp forest (Ol). The catchment of the Potaszka watercourse is over two times bigger, with an area of 1.33 km2. Here forest cover only 14.7% catchment area, arable land (GO) occupies approx. 75%, while grassland (UZ) constitutes 10.3%. Landscape in both catchments is characterized by a large number of interior depressions, filled partly with rainwater or peat bogs, with poorly developed natural drainage During the research detailed analyses were made for the dynamics of the ground water level. The researches curried out in different habitat conditions in watercourses Hutka and Potaszka catchement indicated that the highest amplitudes oscillations ground-water levels, in winter and summer hydrological half-year, occurred in older swamp forest, whereas the smallest in fresh mixed coniferous forest. The research proved, that the dynamics of the soils humidity variation and ground water level in analyzed drainage catchment is described by similar cyclist and depends mostly on the course of meteorological conditions, especially on the distribution and dimension of rainfalls. It was confirmed that the low level of groundwater table in the vegetation season does not affect significantly the water reserves of the surface layer of soil. Additional elements affecting the level of ground water are also: the distance between measuring wells and the watercourse, site type and the layout of the land.

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Krajobraz sakralny związany z ciekami wodnymi, na przykładzie "Szlaku kościołów drewnianych wokół Puszczy Zielonka"

Raszeja E., de Mezer E.

Architektura Krajobrazu

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2010

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nr 1

25--33

EN

Sacred landscape is inseparably linked with the revelation of sanctity in human life space (hierophany and teophany in some cases). Profanum has to be symbolically submitted to res sacra to enable the element of sacrum to act in a proper way. It involves an appropriate exposition of sacred landscape elements, especially churches. They are not only visible dominants, but also domus dei and axis mundi in cultural landcape. For that reason churches are often situated in the most prominent places, making good use of natural landform features, first of all hills usually connected with valleys of water flows. 'The trail of wooden churches around Zielonka forest' consists of twelve churches that have become an inherent part of Wielkopolska cultural landscape. Seven of them are located in the area of river valleys, which determines landscape exposition. The aim of this article is to attract attention to the vital role of small water flows in the exposition of churches and the influence of valley forms on sacred landscape perception.