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Effects of grazing as anthropogenic environmental factor of natural grasslands in the Hungarian Great Plain, near Bugac
39-41Views:59The coenological quadrats were made in 1997, 2005, 2010 and 2021 in a sandy grassland which is used as cattle pasture. The quadrats can be sort in three groups. The first group of quadrats was made close to the cattle pen (Zone A: 0-50 m). The second group was made farther (Zone B: 50-150), where the grazing is not so intensive. The third group contains the quadrats which were made farther than 150m (Zone C). The animals use this area rarely, therefor this part of the pasture is undergrazed (Penksza et al., 2010a). The coenological survey was carried out with 2×2 meter squares, recording the cover value. The species names follow the nomenclature of Király (2009) and Engloner et al. (2001).
The rate of species which indicate degradation is the highest near to the cattle pen (0-50m). But farther than 50m the rate of species which indicates naturalness is higher. Lower nature conservation value can be observed near to the cattle pen. In this area weeds and degradation tolerant species can be found in the highest amount. Their ratio grew in the second zone (50-150m) too in the past few years, but the species which compose the natural vegetation also survived, so the species composition is able for regeneration. With the decreasing of grazing intensity the sample area could meet the requirements of nature conservation.
Data evaluation was made with considering naturalness state in case of habitats; and on the other hand, according to relative ecological factors of occurring species. A significant change in species composition could be detected. Particularly, deterioration of areas could be experienced. These negative processes are extremely heavy inside and near the animal husbandry farm. Even aggressive, invasive plant species occurred. Among dominant grass species, dominance relations and covering rate of disturbance tolerant Cynodon dactylon and Lolium perenne species have increased, caused partly by overgrazing and trampling as well. A new species, Poa humilis, appeared in the zone “A” in 2020, which is a degradation indicator species and tolerates overgrazing and trampling (Penksza and Böcker, 1999/200; Penksza, 2009). Farther from the farm, rate of degradation showed by vegetation has decreased compared to the areas closer to the farm, however, it has increased even on the farther area between the two time periods. During the preparation of management plans for the grasslands, these data should be considered at a higher rate in favor of preserving natural values,
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Examination of coenological and grassland management of sheep- and cattle pasture in lands of Kiskunság
39-45Views:159The coenological relevés were prepared in 2007 and 2008 on two pasture-lands in the Great Hungarian Plain. areas situated inside and near (0 to 50 meters far from) an animal husbandry farm belong to the first group. Coenological relevés gained from areas situated 50 to 150 meters far from intensively used areas belong to the second group. Data evaluation was made with considering naturalness state in case of habitats, and on the other hand, according to relative ecological factors of occurring species. Primarily, degradation of areas could be experienced. These negative processes are extremely heavy inside and near the animal husbandry farm.
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Fajösszetétel és diverzitás változás kiskunsági száraz és nedves fekvésű legelőkön
15-30Views:193Investigations were carried out in wet – next to Tatárszentgyörgy, and dry grass pasture – next to Bugac, both located in Kiskunság, in the central region of Carpathian Basin. Recordings were taken every June of 2007, 2008, 2009 and 2010 from Tatárszentgyörgy – where cattle were grazed, and 1997, 2005 and 2010 from Bugac, where cattle and sheep were grazed. Coenological recordings were taken in three zones. The first zone ("A" zone) located 0-50 m near the stable, second zone ("B" zone) located 50-150 m from the stable, while the third zone ("C" zone) located farther then 150m from the stable. Analyses of ecological and environmental factors were based on Borhidi’s relative ecological indicators. Life form analyses were performed by Pignatti life form types. For statistical evaluation, R software was applied. Shannon diversity. Based on our results for both dry and wet grasslands, quadrates of "A" zone were well isolated from the rest of the zones. Overgrazing, which involves considerable trampling, vanishes differences among vegetations, thereby promotes weed and disturbance tolerant rich vegetation. The lowest species number and diversity could be found here. Recordings for "B" and "C" zones separated from recordings of "A" zone, furthermore, quadrates of wet and dry grasslands formed separate groups. From recordings of "B" and "C", zone perennial grass species (H caesp) and the emerging perennial (H wrap) species multiplied and these species were the indicators of grazing. The greatest lifeform richment were presented among "B" zone recordings. The amount of intensive grazing indicator species, such as creeping perennials (Hrep) was significant in "B" zone recordings of Tatárszentgyörgy. Grazing stabilised the local vegetation, but increased the ratio of disturbance tolerant species, which was confirmed by conservation evaluation. This is due to the conversion of grassland types, the transition from free grazing to switch grazing, which resulted in an intensive involvement of the more distant "C" zone as well. "A" zones fully converted; they changed into fully reliefs. Further located sample area vegetations were not homogenised by grazing and even helped the preservation of characteristic species. In the aspect of environmental protection, vigorous grazing led to a more valuable vegetation in "B" zone in an arid grassland (Bugac). According to the sample area, wet grasslands from the sandy areas of Kiskunság, preserve nature protection values and grass composition better moving away from stables, due to less grazing pressure. Drier backgrounds tolerate stronger grazing pressure (Bugac), while in case of wetter areas (Tatárszentgyörgy) – considering sustainability – grazing should be carried out with caution.
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Magyar szürke szarvasmarhával végzett legeltetés hatása a vegetáció fajösszetételére Balaton-felvidéki mintaterületeken
73-79Views:155A jelen dolgozatban a magyar szürke szarasmarha legeltetésének vegetációra gyakorolt hatását vizsgáltuk Balatonfelvidéki száraz és mezofil gyepekben. A száraz termőhelyek Gyulakeszi, az üde mintaterületek Badacsonytördemic település mellett találhatók. Célunk az volt, hogy a magyar szürke szarvasmarha-legelőkön megvizsgáljuk a növényzet fajössztételét, megállapítsuk, melyek a leggyakoribb fajok, elsősorban termőhelytől függetlenül. Elemezzük, hogy az eltérő termőhelyi viszonyok hogyan befolyásolják a fajösszetételt a két vizsgált élőhely-típusban, mennyire adódik eltérés, illetve a legeltetés homogenizálja-e a területek növényeggyüttesét? Badacsonytördemicen két mezofil mintaterületet vizsgáltunk. Legelőt, ahol az állatok, a kihajtástól a behajtásig egy hónap kivételével tartózkodnak. Kiegészítő legelőt, ahová a szarvasmarhákat egy hónapra, augusztusban hajtják át. Gyulakeszi határában a Csobánc lábánál lévő mintaterület lejtős térszínen fekszik. Itt a lejtő felső (LFH) és alsó harmadában (LAH) végeztünk felméréseket. Mind a négy mintaterületen havonta készültek cönológia vizsgálatok 10-10 felvételben, és ezeket az összesített adatokat értékeltük. A felvételi területek közül a száraz termőhelyeken volt jelentősen nagyobb a fajszám. A lejtő felső harmadában ez átlagosan 40-56 fajt, míg az alsó harmadban 39-51 növényfajt jelentett. Az üdébb fekvésben a kiegészítő legelőn csak 25-28 faj volt átlagosan a felvételekben, a legelőn magasabb volt a fajszám: 28-33. Minden mintaterületet elemezve a leggyakoribb 10 növényfaj zömében pázsitfű volt. A mintaterületek – különösen a gyakoribb fajok tekintetében a felvételek fajösszetétele és a fajok dominancia viszonyai – nagy hasonlóságot mutattak, amik az uralkodó pázsitfüvek és pillangós fajok jelenlétéből és borítási értékeiből adódtak. A domináns pázsifű és pillangós fajokon túl az egyéb fajok alapján az üde és a száraz mintaterületek jobban eltértek. A magyar szürke szarvasmarha legelésével a domináns pázsitfüvek és pillangós fajok alapján homogenizálja a felvételeket. A többi növényfaj esetében pedig megőrzi a fajok változatosságát. Összességében elmondható, hogy a magyar szürke szarvasmarha alkalmas mind a száraz, és mind az üde termőhelyek fajgazdagságának fenntartására.