Database release:

For Special Protection Areas (SPA),
Proposed Sites for Community Importance (pSCI),
Sites of Community Importance (SCI) and
for Special Areas of Conservation (SAC)



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1.1 Type


1.2 Site code


1.3 Site name

Kerecsendi Berek-erdő és Lógó-part

1.4 First Compilation date


1.5 Update date


1.6 Respondent:

Name/Organisation:Bkk National Park Directorate

1.7 Site indication and designation / classification dates

Date site proposed as SCI:2004-05
Date site confirmed as SCI: No data
Date site designated as SAC:2010-02
National legal reference of SAC designation:275/2004. (X. 8.) Kormnyrendelet


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2.1 Site-centre location [decimal degrees]:


2.2 Area [ha]


2.3 Marine area [%]


2.4 Sitelength [km]:


2.5 Administrative region code and name

NUTS level 2 code Region Name

2.6 Biogeographical Region(s)

Pannonian (0.00 %) Pannonian (0.00 %) Pannonian (100.00 %)
Pannonian (100.00 %) Pannonian (100.00 %) Pannonian (100.00 %)
Pannonian (0.00 %) Pannonian (100.00 %) Pannonian (0.00 %)
Pannonian (0.00 %) Pannonian (0.00 %) Pannonian (0.00 %)


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3.1 Habitat types present on the site and assessment for them

Annex I Habitat types Site assessment
Code PF NP Cover [ha] Cave [number] Data quality A|B|C|D A|B|C
      RepresentativityRelative SurfaceConservationGlobal
1530  info      1.34  0.00       
40A0  info      7.96  0.00 
6250  info      12.2  0.00 
91G0  info      2.92  0.00 
91I0  info      54.79  0.00 
91M0  info      43.87  0.00 
  • PF: for the habitat types that can have a non-priority as well as a priority form (6210, 7130, 9430) enter "X" in the column PF to indicate the priority form.
  • NP: in case that a habitat type no longer exists in the site enter: x (optional)
  • Cover: decimal values can be entered
  • Caves: for habitat types 8310, 8330 (caves) enter the number of caves if estimated surface is not available.
  • Data quality: G = 'Good' (e.g. based on surveys); M = 'Moderate' (e.g. based on partial data with some extrapolation); P = 'Poor' (e.g. rough estimation)

3.2 Species referred to in Article 4 of Directive 2009/147/EC and listed in Annex II of Directive 92/43/EEC and site evaluation for them

Species Population in the site Site assessment
G Code Scientific Name S NP T Size Unit Cat. D.qual. A|B|C|D A|B|C
      MinMax  Pop.Con.Iso.Glo.
A1188Bombina bombina    10  100         
I4028Catopta thrips    100  100   
I1088Cerambyx cerdo    50  50         
I4032Dioszeghyana schmidtii    1000  10000   
P4067Echium russicum    50  50         
I1074Eriogaster catax    500  500   
I4035Gortyna borelii lunata    1000  1000   
I1052Hypodryas maturna    100  1000   
I4048Isophya costata               
I1083Lucanus cervus    100  100         
I1060Lycaena dispar    100  100         
P2093Pulsatilla grandis    300  300         
M1335Spermophilus citellus           
P2120Thlaspi jankae    200  200   
  • Group: A = Amphibians, B = Birds, F = Fish, I = Invertebrates, M = Mammals, P = Plants, R = Reptiles
  • S: in case that the data on species are sensitive and therefore have to be blocked for any public access enter: yes
  • NP: in case that a species is no longer present in the site enter: x (optional)
  • Type: p = permanent, r = reproducing, c = concentration, w = wintering (for plant and non-migratory species use permanent)
  • Unit: i = individuals, p = pairs or other units according to the Standard list of population units and codes in accordance with Article 12 and 17 reporting (see reference portal)
  • Abundance categories (Cat.): C = common, R = rare, V = very rare, P = present - to fill if data are deficient (DD) or in addition to population size information
  • Data quality: G = 'Good' (e.g. based on surveys); M = 'Moderate' (e.g. based on partial data with some extrapolation); P = 'Poor' (e.g. rough estimation); VP = 'Very poor' (use this category only, if not even a rough estimation of the population size can be made, in this case the fields for population size can remain empty, but the field "Abundance categories" has to be filled in)

3.3 Other important species of flora and fauna (optional)


Population in the site


Group CODE Scientific Name S NP Size Unit Cat. Species Annex Other categories
     MinMax C|R|V|PIVVABCD
Centaurea sadleriana                   
Dictamnus albus                   
Doronicum hungaricum                   
Inula germanica                   
Lycaena alciphron                   
Mantis religiosa                   
Muscari botryoides                   
Parnassius mnemosyne                   
Peucedanum officinale                   
Phlomis tuberosa                   
Pseudolysimachion spurium                   
Stipa tirsa                   
Zerynthia polyxena                   
  • Group: A = Amphibians, B = Birds, F = Fish, Fu = Fungi, I = Invertebrates, L = Lichens, M = Mammals, P = Plants, R = Reptiles
  • CODE: for Birds, Annex IV and V species the code as provided in the reference portal should be used in addition to the scientific name
  • S: in case that the data on species are sensitive and therefore have to be blocked for any public access enter: yes
  • NP: in case that a species is no longer present in the site enter: x (optional)
  • Unit: i = individuals, p = pairs or other units according to the standard list of population units and codes in accordance with Article 12 and 17 reporting, (see reference portal)
  • Cat.: Abundance categories: C = common, R = rare, V = very rare, P = present
  • Motivation categories: IV, V: Annex Species (Habitats Directive), A: National Red List data; B: Endemics; C: International Conventions; D: other reasons


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4.1 General site character

Habitat class % Cover

Total Habitat Cover


4.2 Quality and importance

Kiemelt fontossg cl a kvetkezo fajok s lohelyek kedvezo termszetvdelmi helyzetnek fenntartsa, lehetosg szerinti fejlesztse: euro-szibriai erdossztyepptlgyesek tlgyfajokkal (Quercus spp.) (*91I0) pannon gyertynos-tlgyes (*91G0) sksgi pannon lszgyepek (*6250) magyar fsusbagoly (Dioszeghyana schmidtii) Janka tarska (Thlaspi jankae) The original zonal forest association of the Great Hungarian Plain was, supposedly, the loess steppe oak forest (Aceri tatarico - Quercetum). This one-time characteristic forest association has almost disappeared, due to the activity of man. Forests have been felled and turned into plough-lands and grazing lands. The most valuable populations that remain are found on the mountain fringes, the highest value among them being ("locus classicus") the Kerecsendi Berek-erdo ("Fcnos Berek"). The patchy forest - grassland complex enables the survival of heliophytic steppe elements in the clearings and glades of the forest. In smaller valleys there are smaller oak-hornbeam forests and elm populations. Lg-part, linked to the protected forest area from the south, has one of the most valuable steppe populations with the last occurrence of several montane steppe woodland plant species on the edges of the plain (Pulsatilla grandis, Adonis vernalis, Pseudolysimachion spurium etc.).

4.3 Threats, pressures and activities with impacts on the site

The most important impacts and activities with high effect on the site

Negative Impacts
RankThreats and pressures [code]Pollution (optional) [code]inside/outside [i|o|b]
Positive Impacts
RankActivities, management [code]Pollution (optional) [code]inside/outside [i|o|b]

Rank: H = high, M = medium, L = low
Pollution: N = Nitrogen input, P = Phosphor/Phosphate input, A = Acid input/acidification,
T = toxic inorganic chemicals, O = toxic organic chemicals, X = Mixed pollutions
i = inside, o = outside, b = both

4.5 Documentation

Selected bibliography: dmL. (1997): Bogarak Kerecsendrol (Coleoptera: Stahylinidae; Scarabaeoidea) - Folia Hist.-nat. Mus. Matr. 22: 257-264. Endes M. (1987): A Gyngys-Tarna hordalkkp-sksg gerincesllat-vilga. - Fol. Hist.-nat. Mus. Matr. 12: 107-117. Szujk-Lacza J. (1984): The flora of the Kerecsendi berek forest. - Studia bot. 17: 23-39. Szujk-Lacza J.- Rajczy M. (1986): Similarity investigation on a loess steppe fragment in a forest-steppe in Hungary. - Ann. Hist.-nat. Mus. Nat. Hung. 78: 49-62. Zlyomi B. - Fekete G. (1994): The Pannonian loess steppe: differentation in space and time. - Abstr. Bot. 18: 29-41. Zlyomi B. (1957): Der Tatarenahorn-Eichen-Lsswald der zonalen Waldsteppe. - Acta Bot. Hung. 3: 401-424. Zlyomi B. (1969): Fldvrak, sncok, hatrmezsgyk s a termszetvdelem. - Term. Vilga 100: 550-553.


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5.1 Designation types at national and regional level:

Code Cover [%]

5.3 Site designation (optional)

The Kerecsendi Berek-erdo ("Fcnos Berek") was declared protected in 1960 (reg. No. 330). Lg-part, joining the area from the south, was recommended for protection by NGOs and then designated for national protection by the Bkk National Park as part of the expansion of the Hevesi Fves Pusztk TK (Heves Steppe Grasslands Landscape Protection Area). The management plan of the area was prepared in 2001, declaration of the site protected is in progress. It is completely included in the National Ecological Network.


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6.2 Management Plan(s):

An actual management plan does exist:

No, but in preparation

6.3 Conservation measures (optional)

ltalnos clkituzsek: A Natura 2000 terlet termszetvdelmi clkituzse az azon tallhat, a kijells alapjul szolgl fajok s lohelytpusok kedvezo termszetvdelmi helyzetnek megorzse, fenntartsa, helyrelltsa, valamint a Natura 2000 terletek lehatrolsnak alapjul szolgl termszeti llapot s a kedvezo termszetvdelmi llapottal sszhangban lvo gazdlkods feltteleinek biztostsa. SPECIFIKUS CLOK 1. FO CLKITUZSEK A terleten tallhat termszetes, tatrjuharos lsztlgyes llomnyok (91I0) kedvezo termszetvdelmi helyzetnek fenntartsa / elrse, klnsen az idos llomnyrszek, faegyedek, valamint holt faanyag mennyisgnek nvelsvel (nagy hoscincr (Cerambyx cerdo) fenntartsa / kezelse rdekben); A erdollomnyokban felverodo lkek illetve a nyiladkok fenntartsa, vltozatos fa- s cserjesszettelnek biztostsa (elsosorban a Dioszeghyana schmidtii fenntartsa rdekben); A jelenleg nem oshonos fafajokbl ll erdollomnyok esetben az erdofeljts csak a termohelynek megfelelo oshonos fafajokkal, szerkezettalaktsknt vgezheto; Az agresszven terjedo invzis fa- s cserjefajok - elsosorban az akc, zldjuhar, blvnyfa visszaszortst nemcsak az erdorszletekben, hanem az utak mentn s az erdei tisztsokon is meg kell oldani; A tviskes cserjkkel zrd s siskanddal (Calamagrostis epigeios) fertoztt lszgyepek (6250) fenntartsa tisztt kaszlssal; A gyepterletek s cserjsek zrdsnak megakadlyozsa (elsosorban a Janka-tarska (Thlaspi jankae) s a terleten nem jello lenykkrcsin (Pulsatilla grandis) s piros kgyszisz (Echium russicum) megorzse rdekben); 2. TOVBBI CLOK A sziki magaskrs llomnyok fenntartsa, becserjsedsk megakadlyozsa elsosorban mechanikus kaszlsi technolgiai alkalmazsval (elsosorban a terleten nem jello nagy szikibagoly (Gortyna borelii) llomnyok megerostse rdekben); Az erdei, korbban parlagknt hasznostott zrvny szntk, parlagok erdostse honos fafajokkal, a felverodo invzis nvnyfajok (kanadai aranyvesszo, selyemkr) visszaszortsa rdekben; A site terletn kvlrol rkezo kros hatsok (pl. vegyszerbemosds, besznts, cserjsek krostsa) mrsklse, a puffert kpezo cserjsek fenntartsval, kialaktsval; A lszgyepeket s rvalnyhajas erdospusztarteket szeglyezo tviskes cserjsek (kknyes-galagonys cserjsek) foltokban trtno visszaszortsa, legeltethetov ttele; A gyepek rszarnynak nvelse, az arra alkalmas szntfldek visszagyepestsvel.



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