Database release:

SDF

NATURA 2000 - STANDARD DATA FORM

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

SITE	HUKN20013
SITENAME	Fülöpszállás - Soltszentimre - csengődi lápok

1. SITE IDENTIFICATION
2. SITE LOCATION
3. ECOLOGICAL INFORMATION
4. SITE DESCRIPTION
5. SITE PROTECTION STATUS
6. SITE MANAGEMENT
7. MAP OF THE SITE

1. SITE IDENTIFICATION

1.1 Type

1.2 Site code

HUKN20013

1.3 Site name

Fülöpszállás - Soltszentimre - csengődi lápok

1.4 First Compilation date

2003-12

1.5 Update date

2012-10

1.6 Respondent:

Name/Organisation:	Kiskunsgi National Park Directorate
Address:
Email:

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

2. SITE LOCATION

2.1 Site-centre location [decimal degrees]:

Longitude:	19.248889
Latitude:	46.742778

2.2 Area [ha]

3122.9900

2.3 Marine area [%]

0.0000

2.4 Sitelength [km]:

0.00

2.5 Administrative region code and name

NUTS level 2 code	Region Name
HU33	Dél-Alföld

2.6 Biogeographical Region(s)

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

3. ECOLOGICAL INFORMATION

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
						Representativity	Relative Surface	Conservation	Global
6210			12	0.00	G	B	C	B	B
6260			375	0.00	G	B	C	B	B
6410			500	0.00	G	A	B	B	B
6440			343	0.00	G	B	C	B	B
7230			22	0.00	G	A	C	B	B
91E0			125	0.00	G	A	C	B	B

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
						Min	Max				Pop.	Con.	Iso.	Glo.
A	1188	Bombina bombina			p				C	P	C	B	C	B
P	4081	Cirsium brachycephalum			p	1000000	1100000	i		G	C	B	C	B
R	1220	Emys orbicularis			p				C	P	C	B	C	B
M	1355	Lutra lutra			p				V	P	D
I	1060	Lycaena dispar			p	100	200	i		M	C	B	C	B
I	1059	Maculinea teleius			p				C	P	C	B	C	B
F	1145	Misgurnus fossilis			p	251	500	i		M	C	B	B	B
A	1993	Triturus dobrogicus			p				C	P	C	B	C	B
F	2011	Umbra krameri			p	251	500	i		M	C	B	A	B

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)

Species					Population in the site				Motivation
Group	CODE	Scientific Name	S	NP	Size		Unit	Cat.	Species Annex		Other categories
					Min	Max		C\|R\|V\|P	IV	V	A	B	C	D
I		Acherontia atropos						V			X
I		Acrida hungarica						C			X
B		Acrocephalus arundinaceus						C					X
B		Acrocephalus scirpaceus						C					X
B		Ardea cinerea						C					X
I		Argyronetra aquatica						C			X
P		Aster punctatus						V			X
P		Astragalus asper						C			X
B		Athene noctua						R					X
I		Boloria selene						V			X
A		Bufo bufo						C					X
A		Bufo viridis						C					X
B		Buteo buteo						C					X
I		Carabus cancellatus						C			X
P		Carex appropinquata						P			X
P		Centaurea sadleriana						C				X
I		Chariaspilates formosarius						C			X
B		Coturnix coturnix						C					X
B		Cuculus canorus						C					X
P		Dactylorhiza incarnata						P					X
B		Dendrocopos maior						R					X
P		Dianthus superbus						P			X
B		Emberiza calandra						C					X
P		Epipactis palustris						P					X
M		Erinaceus concolor						C			X
P		Eriophorum angustifolium						P			X
P		Eriophorum latifolium						P			X
B		Falco subbuteo						V					X
B		Falco tinnunculus						C					X
P		Festuca wagneri						P				X
B		Gallinago gallinago						C					X
I		Gampsocleis glabra						C			X
P		Gentiana pneumonanthe						P			X
P		Gymnadenia conopsea						P					X
I		Helix pomatia						C					X
I		Hemaris tityus						R			X
P		Hottonia palustris						C			X
A		Hyla arborea						C					X
I		Inachis io						C			X
I		Iphiclides podalirius						R			X
P		Iris sibirica						P			X
P		Iris spuria						P			X
P		Iris variegata						P			X
R		Lacerta agilis						C					X
R		Lacerta viridis						R					X
P		Lathyrus palustris						P			X
B		Limosa limosa						P					X
I		Locusta migratoria						R			X
B		Locustella fluviatilis						C					X
B		Luscinia megarhynchos						R					X
I		Maculinea alcon						V			X
I		Mantis religiosa						C			X
B		Merops apiaster						C					X
B		Motacilla flava						C					X
M		Mustela erminea						R					X
R		Natrix natrix						C					X
B		Numenius arquata						R					X
P		Nymphaea alba						P			X
P		Ophioglossum vulgatum						P			X
P		Ophrys apifera						V					X
P		Ophrys sphegodes						C					X
P		Orchis coriophora						P					X
P		Orchis laxiflora ssp. palustris						P					X
B		Oriolus oriolus						R					X
I		Papilio machaon						C			X
A		Pelobates fuscus						C					X
R		Podarcis taurica						R					X
B		Rallus aquaticus						C					X
A		Rana arvalis						C					X
A		Rana esculenta						C					X
A		Rana ridibunda						C					X
P		Ranunculus lingua						P			X
I		Rhyparioides metelkanus						C			X
B		Saxicola rubetra						C					X
P		Schoenus nigricans						C			X
P		Senecio paludosus						P			X
M		Sorex araneus						C					X
P		Stipa borysthenica						R			X
M		Talpa europaea						C			X
P		Thelypteris palustris						P			X
A		Triturus vulgaris						C					X
B		Tyto alba						R					X
B		Upupa epops						C					X
B		Vanellus vanellus						C					X
I		Vanessa atalanta						C			X
P		Veratrum album						P			X

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

4. SITE DESCRIPTION

4.1 General site character

Habitat class	% Cover
N03	1.00
N07	11.00
N09	14.00
N10	40.00
N14	4.00
N15	18.00
N16	5.00
N20	1.00
N21	3.00
N23	3.00
Total Habitat Cover	100

Other Site Characteristics

The site consists of wetlands and - for the lesser part - dry sand grassland habitats on higher elevations. Most of the natural habitats are treeless. The site is characterised by high biodiversity both on species and habitat level. Unfortunately it was exposed to intensive drainage, and until recently this was one of the most serious damaging effects (however its intensity has decreased). Its most important wetland habitats are: tussock and non-tussock sedge communities, reedbeds, alluvial meadows, Molinia meadows, euhydrophyte habitats, willows and - in lesser extension - an alder bog wood. Artificial woodlands largely consist of Robinia pseudo-acacia and Populus x euramericana. "Other land" types are mainly small farms, canals, motor roads, railway and agricultural buildings.

4.2 Quality and importance

Kiemelt fontossg cl a kvetkezo fajok kedvezo termszetvdelmi helyzetnek fenntartsa: Bombina bombina (vrshas unka), Triturus dobrogicus (dunai gote). Kiemelt fontossg cl a kvetkezo fajok/lohelyek kedvezo termszetvdelmi helyzetnek helyrelltsa: 6410 (kkperjs rtek), 6440 (mocsrrtek), 7230 (de sklprtek), 91E0 (lperdok), Lycaena dispar (nagy tuzlepke), Maculinea teleius (vrfu-boglrkalepke), Misgurnus fossilis (rti csk). It has great importance and in general good quality. It is one of the most important wetlands in the Great Hungarian Plain. It is part of an important ecological corridor consisting of wetlands and passing from north to south across the Carpathian basin. It still has a lot of habitats of good quality, however in the past decades it has become significantly drier owing to intensive drainage, and the expansion of degraded habitats increases year by year. Burning, overgrazing, not appropriate mowing practices and improving or ploughing of grasslands are also serious damaging factors. It has a lot of plant and animal species protected by national law.

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
Rank	Threats and pressures [code]	Pollution (optional) [code]	inside/outside [i\|o\|b]
H	A03.01		i
M	A04.01		i
L	A04.03		i
H	A06		i
M	A07		i
M	A08		i
M	B01		b
M	E01		o
L	G01		i
H	I01		b
M	J01.01		i
H	J02		b
M	J03		i
M	K01		i
M	K02		i
M	K03.04		i
M	K05		i
H	M01		b

Positive Impacts
Rank	Activities, management [code]	Pollution (optional) [code]	inside/outside [i\|o\|b]
M	A03		i
L	A04		i

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

The most important documentation about the natural values of the site is a recent research study: Kun, A. s Mt, A.(2002): A Kiskunsgi Nemzeti Park ex lege nyilvntartsba vett, egyes Turjn-vidki terleteinek botanikai llapotfelmrse. (Manuscript)

5. SITE PROTECTION STATUS

6. SITE MANAGEMENT

6.2 Management Plan(s):

An actual management plan does exist:

	Yes
	No, but in preparation
X	No

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. Rszletes clkituzsek: A jello lohelyek kiterjedse ne cskkenjen, kivve ha ez a vltozs msik, az eltuno lohelyrszhez hasonl termszetessgu jello lohely kiterjedsnek nvekedse miatt kvetkezik be. Az erosebb vzhatst ignylo jello lohelyek llomnya ne cskkenjen a gyengbb vzhatst ignylo jello lohelyek kiterjedsnek nvekedse miatt. A jello lohelyek termszetessge ne cskkenjen, kivve ha ez kzvetlenl elhrthatatlan klso ok (pldul idojrsi szlsosg, fogyasztszervezet gradcija), vagy erdei lohely esetn a fallomny engedlyezett vghasznlata miatt kvetkezik be. Erdei lohelyek megvand termszetes tulajdonsgai kz tartozik egyebek kztt a heterogn tr- s korszerkezet, a legyenglt egszsgu fk jelenlte, az ll s fekvo holtfk jelenlte, a fajgazdag cserje- s gyepszint. A tjidegen fafajok elegyarnya ne nvekedjen a jello erdei lohelyek llomnyaiban. A 91E0 (lperdo) erdei lohely llomnyainak sszessgn a tjidegen fafajok elegyarnya felmrsi idoszakonknt (hat venknt) legalbb 10%-al cskkenjen. A jello lohelyek invzis veszlyeztetsnek mrtke ne nvekedjen. Ennek rdekben a jello lohelyekkel rintkezo, az adott helyen tnyleges invzis fenyegetst jelento tjidegen fsszr llomnyok teleptse kerlendo. jonnan teleptett, vagy erdofeljts sorn ltestett tjidegen fsszr llomny s a jello lohelyek kztt legalbb 20 m szles vdoznt szksges ltesteni oshonos fsszr nvnyzetbol, vagy legalbb 30 m szles vdoznt lgyszr nvnyzetbol. A jello 91E0 erdei lohely tz ves felbonts korosztlyszerkezetben ne cskkenjen a trsgben szoksos erdogazdlkodsi gyakorlat szerint mr vghasznlatra elorhat korosztlyok, tovbb az oket eggyel megelozo korosztly sszestett terleti kiterjedse. Ne kerljn teht vghasznlatra tbb idos erdollomny, mint amennyi korosodsval belp a hasonl kolgiai funkcit elltni kpes korosztlyokba. A clkituzs megvalsulsa tz ves erdotervezsi ciklusonknt vizsgland. Erdotervezsi ciklusonknt 30%-os arnynl jobban ne cskkenjen vghasznlat rvn egyetlen korosztly terleti rszarnya sem. Azokon a jello erdei lohelyeken, amelyeken az erdollomny kpes feljulni a maga termszetes kolgiai folyamataira jellemzo mdon (termszetes sebessggel, llomnysurusggel, llomnyszerkezettel), ott biztostani szksges a termszetszeru feljtsok lehetosgt. Legyenek elhrtva az olyan, termszetszeru feljtsokat akadlyoz hatsok kzttk a tltartott nagyvadllomny kedvezotlen hatsa -, amelyek gyengtsnek s megszntetsnek technolgija ismert, s relisan kivitelezheto. A 91E0 (lperdok s puhafs ligeterdok) jello lohely termszetessge felmrsi idoszakonknt (hat venknt), legalbb sszestett terletnek 10%-n nvekedjen, elsosorban az elegyedo tjidegen nvnyfajok irtsa s a termszetes vzhztartsi viszonyok helyrelltsa rvn. Az erosebb vzhatst ignylo, javtand termszetvdelmi helyzetu lohelyek (6410 kkperjs rtek, 6440 mocsrrtek, 7230 de sklprtek) kolgiai llapota, termszetessge tpusonknt kln vizsglva, felmrsi idoszakonknt (hat venknt), legalbb az sszestett terletk 10%-n javuljon, elsosorban a termszetes vzhztartsi viszonyok helyrelltsa, a tjidegen invzis nvnyfajok irtsa, a szntterletekrol eredo zavar hatsok mrsklse s a gyepkezelsi gyakorlat javtsa gy a legeltetett llatok mennyisgnek, fajnak s fajtjnak optimalizlsa, a szksgtelen tiszttkaszlsok visszaszortsa, a mozaikos, hagysterletes kaszlsi gyakorlat s az lovilgot kmlo kaszlgptpusok terjesztse, a kaszlsi mdok diverzifiklsa rvn. A meglvo lohelyek kolgiai llapotnak, termszetessgnek javtsa kivlthat jello vizes lohelyek jonnan trtno kialaktsval, rekonstrukcijval is (a termszetessgnvelsi clkituzs teljes egszben a meglvo vizes lohelyek kiterjedsnek 10%-t kitevo rekonstrukcival helyettestheto). A pannon homoki gyepek (6260) termszetessge felmrsi idoszakonknt (hat venknt), legalbb az sszestett terletk 10%-n nvekedjen, elsosorban a tjidegen nvnyfajok visszaszortsval s termszetvdelmi kezelsk legeltetsk, kaszlsuk javtsval. Az Alfld egyik legjelentosebb szak-dli irny kolgiai folyosjnak rszt kpezo terleten ne cskkenjen a jello lohelyek s fajok llomnyainak konnektivitsa. A jello fajok llomnynagysga s llomnyainak terleti kiterjedse ne cskkenjen. A vonalas vziltestmnyek karbantartsa sorn pldul flszelvnyu kotrsok, vagy kotrs helyett hnrkaszls alkalmazsval, vagy kiszlestett s karbantarts nlkl marad refgium-blk kialaktsval, illetve a karbantarts idopontjnak megfelelo kivlasztsval - biztostani szksges a bennk elofordul jello fajok llomnyainak rdemi mrtku tllst. A vonalas vziltestmnyek clnak megfelelo vzkormnyzsval gy a vzhinyos idoszakokban vzmegorzssel - biztostani szksges a bennk elofordul jello fajok, gy a Bombina bombina (vrshas unka), Triturus dobrogicus (dunai gote), Emys orbicularis (mocsri teknos), Misgurnus fossilis (rti csk), Umbra krameri (lpi pc), llomnyainak tllst, tovbb a jello vizes lohelyek termszetes vzhztartsi viszonyait. A Lycaena dispar (nagy tuzlepke) s a Maculinea teleius (vrfu-boglrka) llomnyainak mrett felmrsi idoszakonknt (hat venknt) legalbb 10%-al nvelni szksges, elsosorban az lohelyeiken foly termszetvdelmi kezels kaszls s legeltets javtsval, az llomnyok trbeli kapcsolatainak javtsval, az lohelyek termszetes hidrolgiai viszonyainak helyrelltsval, az alkalmas lohelyek kiterjedsnek nvelsvel. A Misgurnus fossilis (rti csk) llomnyainak termszetvdelmi helyzett javtani szksges, elsosorban a vonalas vziltestmnyek nem megfelelo karbantartsa s nem megfelelo vzkormnyzsa miatt bekvetkezo llomnypusztulsok mrsklsvel, valamint a tarts felszni vzbortsnak kitett lohelyek kiterjedsnek nvelsvel, illetve a tarts vzhats erossgnek nvelsvel. There are plans for protecting natural water conditions and stopping the negative effects of channel network in the research study mentioned in the field "Documentation" - Kun, A. s Mt, A.(2002): A Kiskunsgi Nemzeti Park ex lege nyilvntartsba vett, egyes Turjn-vidki terleteinek botanikai llapotfelmrse. (Manuscript) -, but there is not an overall management plan available yet.

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