West Polesie Biosphere Reserve - Poland
Basic Information
Site Name
West Polesie Biosphere Reserve
Short name
West Polesie Biosphere Reserve
Country
Poland
Site Manager
Site Description
The 'West Polesie' Biosphere Reserve has been created in 2002. Reserve area (140 000 ha) covers almost whole Łęczna-Włodawa Lake District as well as its near vicinity. It is situated about 40 km north-east of Lublin adjacent to Ukraine’s Shatski Biosphere Reserve. West Polesie includes Poleski National Park, three Landscape Parks: Sobiborski, Łęczna Lake District and Chełmski. The most important protected area in the Reserve is Poleski National Park, with natural resources of lakes (e.g. Łukie, Moszne, Długie) and peatbogs (Orłowskie, Durne Bagno, Bagno Bubnów). Many kinds of endangered species of fauna and flora can be found in the West Polesie area. Villages in this rural area show many examples of traditional wooden architecture and still maintain a cultural and folklore life.
The 'West Polesie' Biosphere Reserve is located in the eastern part of Lubelskie voivodship and consist 25 administrative units (3 towns and 22 communes).
Last modified
2021-11-23 11:11:21
General Characteristics and Status
Site Status
Operational
Year Established
2002
Observed properties
Affiliation and Network Specific Information
Affiliation
ILTER✔This site is a verified "ILTER" member.
LTER Europe✔This site is a verified "LTER Europe" member.
LTER Poland✔ (LTER_EU_PL_019)This site is a verified "LTER Poland" member.
EuroMAB✖The affiliation of this site with "EuroMAB" is not verified by the network on DEIMS-SDR.
Projects
Geographic
Centroid/Representative Coordinates
Latitude: 51.5083 Longitude: 22.415
Size
ca. 139000.00ha
Elevation (average)
170.00msl
Elevation (min)
1365.00msl
Elevation (max)
2028.00msl
GEO-BON Biome
Fresh water lakes
Terrestrial
Biome
Mixed Forest
Ecosystem Type
Biogeographical Region
Continental Bio-geographical Region
EUNIS habitat
Air Temperature: Average Annual
7.63°C
Precipitation Annual
521.90mm
Geology
The ?West Polesie? Biosphere Reserve is located within the Podlasie-Lublin structure, which is a south-west marginal part of the Precambrian East European Platform formed of crystalline rocks. It occupies the central part of the W?odawa trench emitted from NW by dodge Hanna, from the SE by Udal dodge and from SW Kock dodge. Carboniferous deposits were formed in the condition of epicontinental reservoir as alternate layers of limestone, claystone, siltstone, sandstone and carbon. They were formed without breaks from the Visean to Westphalian, gradually changing from the domination of inland marine facies to the facies of upper Westphalian. Carbons are present in the whole profile of the Carboniferous, but the complex importance of reservoir have only layers of upper Namur and lower Westphalian as a the result of lake, river and marsh sedimentation. Structure reconstruction of the Carboniferous basin in Asturian (perm - older Mesozoic) led to forming a synclinal form filling marginal sinkhole along the East-European platform called Nadbu?a?ska trough. An asymmetric syncline called Radzy?-Bogdanka is a part of this structure. This syncline is cutted by transverse faults with NE-SW referring to Brittany tectonic. The first coal mine called "Bogdanka" SA is located in the axial part of the syncline. A large part of the ?West Polesie? Biosphere Reserve, outside the 10-15 km strip along the Bug River valley devoided of prospective resources of coal, lies within the Lublin Coal Basin. Coal seams occurring among siltstones and claystones of the lower Westphalian (A and B), which formed the so-called layers of Lublin have industrial importance. The thickness is approximately 400 metres and gradually decreasing to the east and north-east. Among 18 coal seams balance occurring in Lublin layers, 8 was recognized as industrial, which only two of them are currently operated. Uplifting movements of Cretaceous Age resulted in regression of the sea and initiated another cycle of denudation, which lasted until the upper Eocene in the Cenozoic. In the eastern area denudation has removed the youngest Cretaceous cells. They survived only in the axial part of the through. In the Upper Eocene the area of the ?West Polesie? Biosphere Reserve was covered by the sea transgression, the last in the history of the geological development of the region. During the Upper Eocene and Oligocene sands and silts were deposited here, often with glauconite and marl, loam subordinate. They are preserved in the form of isolated patches around W?odawa city and central parts of the ??czna ? W?odawa Lakeland and in a more compact cover in the west, close to Parczew city. These deposits reach thickness up to 40 m. In these sediments phosphates and amber occur, which locally can have a complex character. The sea withdrew in the middle or upper Oligocene and the area of the Biosphere Reserve came into the land stage of the development of the geological structure and morphogenesis, lasting to this day. In the surface sediments regional differences indicates quite clearly. The western part is dominated by sandy sediments and sandy silt accumulation of fluvial - lacustrine and periglacial - wetland, associated with the Vistula and Warta glaciation. Here, pleistocene sediments have the greatest thickness whereas the vertical profile is dominated by sands, gravels and silts. Organogenic Holocene sediments of valley bogs and plains close to lakes occurr here. In the geomorphological view of the Biosphere Reserve zonation is marked very clearly. In the eastern part, from the north (Garb Wlodawski) and south (Wa? Uhruski as a part of the northern part of Pagóry Chelmskie) zones formed plains and glacial moraine of Odra glaciation. Moraine landscape, in a rudimentary form also occurs in west parts, on the west of the Ty?mienica river valley. Outwash plains filled with accumulation, lakes and bogs plains are extended between them. Among them reduced forms of glaciofluvial and glacial accumulation and older surfaces are locally distributed.
Vegetation
The area of the ?West Polesie? Biosphere Reserve is characterized by a great diversity of habitats. This is reflected in the plant species richness. Flora of this area includes following ecological groups: waters, plants amphibians, rushes, meadows, transitional and high bogs, alder forests and riparian alder, hornbeam, coniferous forests (typical, mixed and dry), grasslands, scrub and steppe grasslands, synanthropic plants (growing and ruderal). Among approximately 2200 species of vascular plants reported from the area of Poland and neighboring lands, in the Polesie there are about 1200 species (Fija?kowski et al. 2002). Flora of bryophytes is also rich and varied. According to Karczmarza (2002) in the area of the Polesye Lublin there is 251 taxa of bryophytes, among which there are 182 taxa of mosses, liverworts ? 43 and peat plants ? 24.The main components of bryoflora of the Reserve are lowland and boreal species, including forest and peat Holarctic elements. Other interesting species occur at low peat bogs rich in calcium carbonate. Examples of this flora: Bryum neodamense, Calliergon trifarium, Cinclidium stygium, Drepanocladus lycopodioides, Meesia triquetra, Scorpidium scorpioides. On transitional and high moors there are: Helodium blandowii, Palludella squarrosa, Pohlia sphagnicola, Tomenthypnum nitens. Group of Atlantic moss is represented by: Aulacomnium androgynum, Callicladium baldanianum, Fissidens bryoides, Mnium bornum, Plagiomnium elatum, Plagiotheciella latebricola, Platygyrium repens, Tortula papillosa, Ulota crispa (Karczmarz 2002). In the area of the ?West Polesie? Biosphere Reserve occur species belonging to different geographical and floristic elements (Fija?kowski 1963, Fija?kowski, Izdebski 1996, 2002; Fija?kowski et al. 2002). An important component of the flora of this area is a boreal species group represented by approximately 150 taxa. Relict boreal species occur primarily on transitional and high bogs, as well as meadows and pine forests. On the transitional and high bogs following species occur: Salix lapponum, Rhynchospora alba, Ledum palustre, Scheuchzeria palustris, Rhynchospora alba, Drosera anglica, D. rotundifolia, Eriophorum gracile, Carex chordorrhiza, C. heleonastes i C. limosa, Andromeda polifolia, Ledum palustre i Calamagrostis stricta. On the low moors and in alder habitats there are: Betula humilis, Salix nigricans, Dianthus superbus, Trollius europaeus, Iris sibirica, Pedicularis sceptrum-carolinum, Dryopteris austriaca, Hippuris vulgaris, Achillea ptarmica, Equisetum variegatum, Botrychium lunaria, wheres in lakes - Nymphaea candida. On the poor sands in coniferous forests dried and fresh quite common are boreal species like: Silene lithuanica, Silene tatarica, Arctostaphylos uva-ursi, Deschampsia flexuosa, Equisetum hyemale, Antennaria dioica and Diphiasiastrum complanatum. The second group in terms of number of species is a part of the Central European elements (about 135 species). Predominant are forest and grassland species, less frequent water and steppe species. In the alder and alluvial forests are: Anemone ranunculoides, Cephalanthera rubra, C. longifolia, Platanthera chlorantha, Listera ovata, Thalictrum aquilegiifolium, Carex remota, C. brizpides, Lathraea squamaria, Melandrium rubrum. Others: Corydalis Cava, Aquilegia vulgaris, Digitalis grandiflora, Anthericum ramosum, Hierochloe austrialis, Hedera helix, Liparis loeselii, Scutellaria hastifolia, Petasites hybridus. In grain crops (ground rich in calcium) grow: Melamphyrum arvense Lithospremum arvense, Consolida regalis and Fumaria vaillanti. Group of atlantic species is less numerous (about 25 species), e.g.: Lycopodiella inundata, Hydrocotyle vulgaris, Isopepis setacea, Juncus squarrosus; Drosera intermedia; Teesdalea nudicaulis, Hypocheris glabra; Elatine alsinastrum, Myriophyllum alternifolium; Illecebrum verticillatum, Radiola linoides. Mountainous plant species are represented by 12 species, e.g. Abies alba and Picea abies, Huperzia selago, Aconitum variegatum, Phyteuma orbiculare and Tofieldia calyculata. Among steppe plants there are: Dianthus arenarius, Gypsohila fastigiata and Filipendula hexapetala. A numerous plants species among all species in the Reserve constitute rare species in region and national scale (Kucharczyk, Urban 1994; Kucharczyk, Wójciak 1995), like: Linnaea borealis, Adenophora lillfolia, Polemonium coeruleum, Liparis Loeselii, Hammarbya paludosa. Species on CORINE list: Betula humilis, Cypripedium calceolus, Gentianella uliginosa, Hammarbya paludosa, Liparis loeselii, Pulsatilla patens, Senecio congestus, Trapa natans, Adenophora liliifora, Aldrovanda vesiculosa and Pinguicula vulgaris subsp. bicolor. From the II Appendix of Habitat Directive of NATURA 2000 there are Aldrovanda vesiculosa, Pulsatilla patens, Adenophora liliifora, Ostericum palustre, Cypripedium calceolus and Liparis loeselii. There are also species from Polish Red Book of Species (Ka?mierczakowa, Zarzycki 2001) e.g.: Salix myrtilloides, Salix lapponum, Betula humilis, Nymphaea candida, Pulsatilla patens, Aldrovanda vesiculosa, Trapa natans, Ostericum palustre, Polemonium coeruleum, Pinguicula vulgaris subsp. bicolor, Succisella inflexa, Carex chordorrhiza, Carex limosa, Cypripedium calceolus, Cephalanthera rubra, Liparis loeselii and Hammarbya paludosa. References: 1.Fija?kowski D. 1963. Ro?liny rzadkie Polesia Lubelskiego. Mat. z Sesji Nauk. Pol. Tow. Geogr., Lublin: 65-88. 2.Fija?kowski D., Andrijenko T., Onyszczenko W., ?wi?s F., Urban D. 2002. Ekosystemy l?dowe - le?ne, kserotermiczne i synantropijne Polesia (Flora i fitocenozy). Acta Agrophysica, 66, 147-177. 3.Fija?kowski D., Izdebski K. 1996. Szata ro?linna Lubelszczyzny. Lub. Tow. Naukowe. Lublin: 1-88. 4.Fija?kowski K. 2002. Flora Poleskiego Parku Narodowego. Ro?liny naczyniowe. Poleski Park Narodowy. Wyd. MORPOL: 103-114. 5.Karczmarz K. 2002. Flora Poleskiego Parku Narodowego. Mszaki. Poleski Park Narodowy. Wyd. MORPOL: 99-103. 6.Ka?mierczakowa R., Zarzycki K., 2001. Polska czerwona ksi?ga ro?lin. Inst. Bot. im. Szafera PAN, Kraków: 1-664. 7.Kucharczyk M., Urban D. 1994. Walory, zagro?enia i problemy ochrony szaty ro?linnej woj. lubelskiego W: Diagnoza stanu ?rodowiska przyrodniczego w województwie lubelskim (red. Wilgat T, Chmielewski T.), UW w Lublinie, WFPi GW w Lublinie, TWWP Oddz. w Lublinie, s: 89-103. 8.Kucharczyk M., Wójciak J. 1995. Gin?ce i zagro?one gatunki ro?lin naczyniowych Wy?yny Lubeskiej, Roztocza, Wo?ynia Zachodniego i Polesia Lubelskiego. Ochr. Przyr., 52: 33-46.
Soils
Soils of the ?West Polesie? Biosphere Reserve are closely linked to the geological structure, water relations, biocenosis?development in the Holocene and anthropogenic environmental transformations. The diversity of bedrock and soil-forming factors have contributed to the diverse soil cover. Here there are hydrogenic soils: peat, muck, black earth, glial cells, soil autogenous and a small space of chalk rock outcrop and lithogenic soils (calcareous). Soils of this area are very susceptible to changes in groundwater levels and eutrophication associated with excessive mineral fertilization. Podzols soils occupy the largest area of the Biosphere Reserve. Generated from silty sands they occur in the north-western and northern parts of the Reserve. Podzols soils occurring in the central and northern part developed on sands and loamy sands loose. The humus content does not exceed 1.5%, they are very acidic, low in potassium and phosphorus, and have low sorption capacity. These soils are incomplete, forming mostly good rye complex. Brown soils co-occur with podzols soils. These are usually incomplete soil on a bed of sand, poor in humus, acidic, poor in calcium, magnesium, potassium and phosphorus. An interesting phenomenon is the occurrence of these soils developed on a bog high in the reserve called Durne Swamps. In areas of reclamation carried out on marshy land and marshy soil organic muck soils are formed. Moor soils, developed mainly on low moors, are located in the northern part of the compact complex of the Krowie Swamp, in the Lake U?ciwierz , in a broad Zielawy river valley and peat parts of the Ty?mienica valley.
Hydrology
The area of the ?West Polesie? Biosphere Reserve is located within the Lublin Polesie, in the region of very shallow groundwater occurrence, numerous lakes, ponds and a dense network of drainage ditches. Observations of land give impressions of wealth of water, whereas in fact it is a large area of its deficits, very strongly noticeable during the long summer rainless periods. Field factors decide about small resistance of environment - unique in Europe. Its high value and attractiveness of science, nature and landscape is mainly determined by water relations. In historic times the area of the Polesie were numerous in swamps, marshes and bogs, as well as large areas of forests, which determined the practical unavailability of the land for human. This area for centuries was very sparsely populated and extensive economy did not cause significant changes in the environment. The origins of human intervention was associated with both the cutting of the forest and the drying of moors. This resulted in the formation of specific islands - developed areas on a small part of the Polesie. It should be clearly emphasized that the conditions of the geographical environment decided that till the mid-twentieth century this region was a sparsely populated with traditional agricultural and livestock economy. Determined severity of human intervention occurred after 1954 - after the commencement of the construction of the Canal Wieprz-Krzna and the associated with it, early planned drying the area (Wilgat et al. 1997). In the region more and more visible changes caused by: intensification of agriculture, increase the availability of communications, the increasing tourism and recreation, and investments related to the exploration for and the acquisition of rock materials and energy, as well as the construction and operation of large quantities of groundwater intakes began to occur. Water relations in the area of the Biosphere Reserve, as well as the whole Polesie are formed under the influence of terrain and climate factors, mainly geological structure and permeability of the soil, relief, precipitation and evaporation. Rocks of the Cretaceous age that are formed as marl and writer chalk and surging on them Quaternary deposits are the main factors decided about Polesie? water resources. Ceiling of Cretaceous carbonates generally decreases toward the north, which is important for the water relations area. These rocks in the ground elevation areas appear almost on the surface. Their shallow occurrence is highlighted by the numerous karst forms appearing on the hummocks constructed from Cretaceous rocks. Power conditions and water flow are relatively weak , because the flow of water occurs through different lithological Quaternary deposits, sometimes very poorly permeable. In zones of outcrop of the Cretaceous rocks free water table is maintained on the depth of several meters, and outside these areas water of Cretaceous levels have thrusting character. Size of hydrostatic pressure depends on the size of backfilling by quaternary sediments. Waters of the Chalk level are drilled at a depth of 10-50 m, locally up to 80 m, and usually stabilize at a depth of several meters. Filter coefficients reach most often several meters per day, and the yields obtainable from wells ranges from a dozen to 100 m3/h. The amplitude of groundwater range is very diverse and has little relation with the depth of water occurrence. Lifting and lowering of the water table is fairly quick, and high states last short. In the long-term periods a seasonal and annual variability of water levels is marked, as well as the abundance of water the area is heavily dependent on atmospheric supply. In the rhythm of seasonal, the maximum water levels usually fall in April. In the following months, the water table is lowered to the minimum conditions noted at the beginning of autumn. During the fall and winter a replenishment of water resources throughout the region takes place. In the summer months, although the highest rainfall, structural water deficits, mainly due to high evapotranspiration are observed in the region of the Polesie. The mean amplitude of fluctuations in the water level exceeds 1 m, and the extreme differences in water levels reach 3 m It should be underline that, despite the diversity of lithological aquifers and variable thickness of the vadose zone, underground water table fluctuations take place synchronously (Wilgat et al. 1984). This indicates a hydraulic relationship of aquifers and the dominant role of the power of rain and melting in rectifying water resources. The main component of the hydrosphere of the ?West Polesie? Biosphere Reserve are numerous lakes and other surface water reservoirs. A group of lakes of the ??czna - Wlodawa Lakeland in the 80?s XX century consisted 67 lakes (Wilgat et al. 1991), 61 of which are natural lakes, and 6 were converted into reservoirs. The vast majority of those tanks are small - the largest has 284 hectares - but with poorly developed shoreline. The depths of the lakes are varied, but shallow and very shallow dominated, and the deepest exceed 30 m. Capacity of individual lakes are small, usually 1-2 million m3. Reservoirs and lakes that storage waters in nig quantity are: Lake White near to W?odawa - 15.0 million m3, Lake Piaseczno 10.7 million m3 and 9.2 million m3 ? Lake Usciwierz. The volume of water stored in all the natural lakes and converted into reservoirs is only 107 million m3. Most lakes are heavily overgrown, and numerous depressions now are filled with peat and gytia what indicate advanced stage of lakes dissapearance process. They represent various trophic types, thermal and hydrochemical and are characterized by slow water exchange. The archival materials include only limited information regarding to fluctuations in lakes? water level. In the years 1957-1967 for the Forestry Research Institute water levels in the lake Perespilno were recorded. In contrast, observations made by the Institute of Meteorology and Water Management were performed from August 1 1971 to July 1982 in two lakes: Piaseczno and White Wlodawskie. In the following years, fixed or periodic numbers of water levels in the lake have been performed in the Lake Piaseczno by the Department of Hydrography, University UMCS in Lublin (Wilgat et al. 1991). In the period 1990-1992 workers of the Bogdanka Coal Mine were performed to level measurements of water levels in several lakes, in 1991 in 16 lakes water measurements tolls were established - by the Hydrographic Department, the Coal Mine Bogdanka and Poleski National Park in Urszulin. In 1993, the Head of the Chelm Landscape Parks launched - first systematic and in recent years only temporary - readings of water levels in 29 lakes of the eastern part of the ??czna ? W?odawa Lakeland. In total, in 1991-2005 water levels were recorded in the 38 lakes. The amplitudes of the water levels in the lakes vary widely - from 42 to 171 cm, and their size varies with increasing of observation period, that is, the periods of appearance of extremely dry or humid. A small amount of outflowing water, and the great flatness of the region is not conducive to natural erosion processes leading to the creation of networks drain. Rivers of the Polesie flowin the valleys of poorly formation, and the amplitude of fluctuations in the water level in the trough reaches 2-3 m. The largest river, W?odawka, poured into the Bug river average of 2.2 m3 / s of water, variability of flows of 0.12 m3/ s to 48.2 m3 / s. With no other rivers within the Biosphere Reserve does not carry 1 m3 / s. Average outflow unit is about 3.5 l / s ? km2. In some periods flows fall to very low values and drain the unit does not reach 1 l / s ? km2 , and during long-term drought even 0.5 l / s ? km2. These values underline the scarcity of Polesie waters. The outflow from the basin shows a clear annual cyclicity, the seasonal rhythm of the river runoff typical of rain-snow power. After strongly marked maximum outflow in March, the minimum occurs in late summer and autumn (Michalczyk, Wilgat 1998). This is a consequence of the rapid depletion of scarce underground resources. During the spring (March-May) flows 41 % of water, much less in summer (June-August) - 18% and even less in the autumn (IX - XI) - 16%. Considering the International Biosphere Reserve, consisted of Polish, Belarus and Ukrainian part of the Polesie, by its centre flows the Bug river, taking beginning in Go?ogóry in Ukraine. Bug river valley on section of the Polesie has a meridian course, and its width in some places exceeds 10 km. Rating of width of the valley is quite difficult, because the surface of the terraces lagoons often passes without clear boundary in the broad area of denudation and accumulation. At the height of the Wola Uhruska and W?odawa cities, valley has a groundbreaking character. Narrowing and expansion of the valley are characteristic for this section and its sculpture stands out wide from 1.5 to 4 km flood plain with numerous meanders cutted off in part filled with water. Its amount ranges from 1.5 to 3.0 m above the mean water level in the trough. Over a contemporary valley botton of the terrace, a level rises to a height lagoons from 3 to 7 m (Szwajgier et al. 2002). According to materials given by ImiGW, the average flow of Bug in a profile in W?odawa was 54.5 m3 / s , and the extreme values varied over a very large range of values - from 8,01 m3 / s to 769 m3 / s. The lowest recorded state was 62 cm and 506 cm the highest. With increase in water levels, the width of the river increases, in extreme cases even up to several kilometers.
Site Type
Platform
Design of Experimentation
no experimentation
Scale of Experimentation
not applicable
Design of Observation
partly observation
Scale of Observation
entire catchment
Permanent Power Supply
Yes
Equipment
Energy and data transmission infrastructure » Data transmission » Data Transmission Type (from site) » Telephone line
Energy and data transmission infrastructure » Data transmission » Data Transmission Type (within site) » Cable based
Accessible All Year
Yes
All parts of Site Accessible
Yes
Access Type
regular car
Permanent Operation
No
Site Visit Interval
30
Maintenance Interval
30
LTER Site Classification
Regular
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Projected Near Surface Specific Humidity Change | RCP26 | RCP45 | RCP85 |
Projected Precipitation Change | RCP26 | RCP45 | RCP85 |
Projected Sea Level Pressure Change | RCP26 | RCP45 | RCP85 |
Projected Surface Downwelling Shortwave Radiation | RCP26 | RCP45 | RCP85 |
Projected Near-Surface Wind Speed | RCP26 | RCP45 | RCP85 |
Projected Near-Surface Air Temperature | RCP26 | RCP45 | RCP85 |
Projected Daily Maximum Near-Surface Air Temperature | RCP26 | RCP45 | RCP85 |
Projected Daily Minimum Near-Surface Air Temperature | RCP26 | RCP45 | RCP85 |
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