Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland)
Floristic studies were conducted in 15 abandonded villages in the Kampinos National Park during the years 1992—1995 and 2004— 2007. This paper presents interesting segetal species found in these areas. Thirty four rare segetal taxa were found, including 25 threatened and vulnerable species. In th...
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irk-123456789-1748712021-01-29T01:27:34Z Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) Kirpluk, I. Геоботаніка, охорона рослинного світу Floristic studies were conducted in 15 abandonded villages in the Kampinos National Park during the years 1992—1995 and 2004— 2007. This paper presents interesting segetal species found in these areas. Thirty four rare segetal taxa were found, including 25 threatened and vulnerable species. In the field margin habitats 110 species were found. Apophytes constitutied the major group of species (about 47 %) and archaeophytes were less numerous (about 38 %). The aims of the present study were to determine whether the surveyed sites can function as a potential source of diaspores of rare segetal species and to establish if abandoned villages are important for biodiverisity preservation. Флористичні дослідження були проведені в 15 залишених селах Кампіноського національного парку впродовж 1992—1995 та 2004—2007 років. Cтаття містить цікаву інформацію щодо сегетальних видів, знайдених на досліджуваній території (34 рідкісних таксони, які об’єднують 25 вразливих і загрозливих видів). На маргінальних місцезростаннях виявлено 110 видів. Апофізи становлять основну групу (близько 47 %), археофіти є менш чисельними (близько 38 %). Метою цього дослідження було обстеження ділянок, які можуть функціонувати як потенційні джерела діаспор рідкісних сегетальних видів, що є важливим для збереження біо різноманіття. Флористические исследования были проведены в 15 заброшенных селах Кампиноского национального парка в 1992—1995 и 2004—2007 годах. Статья содержит интересную информацию о сегетальних видах, выявленных на исследованной территории (34 редких таксона, включающих 25 видов, которые находятся под угрозой исчезновения). На маргинальных местообитаниях найдено 110 видов. Апофизы составляют основную группу (около 47 %), археофиты – немногочисленные (около 38 %). Цель исследования – изучение участков, которые могут функционировать как потенциальные источники диаспор редких сегетальных видов, что важно для сохранения биоразнообразия. 2012 Article Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) / I. Kirpluk // Український ботанічний журнал. — 2012. — Т. 69, № 5. — C. 662-670. — Бібліогр.: 11 назв. — англ. 0372-4123 http://dspace.nbuv.gov.ua/handle/123456789/174871 en Український ботанічний журнал Інститут ботаніки ім. М.Г. Холодного НАН України |
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Геоботаніка, охорона рослинного світу Геоботаніка, охорона рослинного світу |
| spellingShingle |
Геоботаніка, охорона рослинного світу Геоботаніка, охорона рослинного світу Kirpluk, I. Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) Український ботанічний журнал |
| description |
Floristic studies were conducted in 15 abandonded villages in
the Kampinos National Park during the years 1992—1995 and 2004—
2007. This paper presents interesting segetal species found in these areas. Thirty four rare segetal taxa were found, including 25 threatened
and vulnerable species. In the field margin habitats 110 species were
found. Apophytes constitutied the major group of species (about 47 %)
and archaeophytes were less numerous (about 38 %). The aims of the
present study were to determine whether the surveyed sites can function
as a potential source of diaspores of rare segetal species and to establish
if abandoned villages are important for biodiverisity preservation. |
| format |
Article |
| author |
Kirpluk, I. |
| author_facet |
Kirpluk, I. |
| author_sort |
Kirpluk, I. |
| title |
Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) |
| title_short |
Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) |
| title_full |
Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) |
| title_fullStr |
Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) |
| title_full_unstemmed |
Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) |
| title_sort |
rare elements of the segetal flora preserved in abandoned villages in the kampinos national park (central poland) |
| publisher |
Інститут ботаніки ім. М.Г. Холодного НАН України |
| publishDate |
2012 |
| topic_facet |
Геоботаніка, охорона рослинного світу |
| url |
http://dspace.nbuv.gov.ua/handle/123456789/174871 |
| citation_txt |
Rare elements of the segetal flora preserved in abandoned villages in the Kampinos National Park (Central Poland) / I. Kirpluk // Український ботанічний журнал. — 2012. — Т. 69, № 5. — C. 662-670. — Бібліогр.: 11 назв. — англ. |
| series |
Український ботанічний журнал |
| work_keys_str_mv |
AT kirpluki rareelementsofthesegetalflorapreservedinabandonedvillagesinthekampinosnationalparkcentralpoland |
| first_indexed |
2025-07-15T12:00:50Z |
| last_indexed |
2025-07-15T12:00:50Z |
| _version_ |
1837714218049077248 |
| fulltext |
662 ISSN 0372-4123. Ukr. Botan. Journ., 2012, vol. 69, № 5
I. KIRPLUK
University of Warsaw Botanic Garden,
Al. Ujazdowskie 4, PL-00-478 Warsaw, Poland
ikirpluk@biol.uw.edu.pl
RARE ELEMENTS OF THE SEGETAL
FLORA PRESERVED IN ABANDONED
VILLAGES IN THE KAMPINOS
NATIONAL PARK (CENTRAL POLAND)
K e y wo r d s: rare species, segetal flora, ruderal habitats, abandoned vi l-
la ges, Kampinos National Park
© I. KIRPLUK, 2012
Abstract. Floristic studies were conducted in 15 abandonded villages in
the Kampinos National Park during the years 1992—1995 and 2004—
2007. This paper presents interesting segetal species found in these ar-
eas. Thirty four rare segetal taxa were found, including 25 threatened
and vulnerable species. In the field margin habitats 110 species were
found. Apophytes constitutied the major group of species (about 47 %)
and archaeophytes were less numerous (about 38 %). The aims of the
present study were to determine whether the surveyed sites can function
as a potential source of diaspores of rare segetal species and to establish
if abandoned villages are important for biodiverisity preservation.
Introduction
The extinction of segetal species is nowadays a common effect of growing anthropo-
genic pressure. In the Kampinos National Park (hereinafter KNP), Central Poland,
we observed other processes exerting adverse effects on the segetal flora of this area.
The KNP to a large extent is almost free from long-term antropic pressure. Since
the mid–1970s the National Park Management has been repurchasing buildings and
agricultural lands located within the park boundaries. Due to this activity, as well as to
the natural secondary successions, the disappearance of traditional countryside land-
scapes becomes progressively frequent.
The aim of the present study was to survey rare elements of the ruderal flora in
abandoned villages within KNP. The second goal of this paper was to determine
whether the surveyed sites can function as a potential source of diaspores of rare seg-
etal species.
Material and methods
The material for this study was collected during 1992—1995 and 2004—2007 on ruderal
sites in abandoned villages in the Kampinos National Park (KNP). Fifteen villages
with an advanced depopulation process were selected. Most of them were situated in
the central part of the park, isolated by vast areas of forests and meadows, far away
from transportation and communication routes, and rarely visited by tourists. In the
recent years consecutive purchase of properties by the Park Management has caused a
decrease or disappearance of human population in most of these villages. The Park
663ISSN 0372-4123. Укр. ботан. журн., 2012, т. 69, № 5
Management actively re-naturalizes abandoned areas by destroying buildings, trans-
forming arable lands, and reforestation.
Observations were conducted in the following types of ruderal habitats: roadsides,
proximity of houses and fences, in the yards of abandoned households, or in places
where households used to be; on roadsides, in ruins, on rubble heaps, dumping sites,
and in the field plots adjacent to the mentioned sites, conventionally described here as
field margins. Field margins refer here to narrow strips of intermediate habitats on the
boundary of segetal and ruderal sites, being a mosaic of these two. In this paper I char-
acterize the flora of these transition zones in order to distinguish rare elements of the
segetal flora in abandoned villages of KPN.
In all these villages floristic inventories were made, with a special focus on the
frequency of occurrence of species. The term «site» was used when a given species was
observed in some spots, regardless of its population size. I considered all naturally oc-
curring species, including those which used to be planted and now tend to escape from
cultivation. Nomenclature of plant species is given according to the checklist of flow-
ering pants and pteridophytes of Poland (Mirek et al., 2002).
In accordance with the aim of this work, a list of rare segetal taxa found in all in-
vestigated sites is presented. It is based on the most up-to-date publications: «Rare,
endangered and protected plant species of synanthropic flora of the Kampinos Na-
tional Park» (Kirpluk, Bomanowska, 2008) and «Endangered and threatened segetal
plants of Kampinoski National Park» (Bomanowska, 2008).
Floristic lists were made on the basis of the collected data concerning the occur-
rence of species in field margins and their phytosociological affinity (Kropac, Mo-
chnacky, 2009, Matuszkiewicz, 2001; Zarzycki et al., 2002). The results were com-
pared with the data on threatened species of segetal habitats in KNP (Bomanowska,
2008) and with the existing floristic lists (Bomanowska, 2001).
Results and discussion
The flora of field margins encompassed 110 species, with a slight domination of apo-
phytes (47.3 %) over archaeophytes (38.2 %) in terms of species number. Epoecophytes
(10 %) as well as ergasiophygophytes (4.5 %) constituted a rather small fraction of the
flora. Alien species were slightly predominant over native species.
According to Bomanowska (2006), the majority of species of the segetal flora of
KPN were native (67.2 %), whereas the remaining species were of alien origin (32.8 %).
Archaeophytes constituted the largest fraction of the total segetal flora (19.06 %). This
is also true for abandoned villages in the KNP area. The total ruderal flora of the 15
studied villages comprised 500 species. Apophytes (about 64 % of the total flora) dom-
inated over anthropophytes (36 %), within which archaeophytes prevailed (14%) (Kir-
pluk 1996, 2003). For example, in the surroundings of the Roztocze National Park
(which has a segetal flora typical of Poland) the composition of synanthropic groups of
segetal species was as follows: apophytes – 57.1 %, archaeophytes – 34.3 %, epoeco-
phytes – 5.6 %, and ergasiophygophytes – 3 % (Ziemiсska-Smyk, 2006). A high pro-
por tion of archaeophytes is noteworthy, as well as the dominance of native species.
664 ISSN 0372-4123. Ukr. Botan. Journ., 2012, vol. 69, № 5
Table 1. List of species found in the field margins, according to their synanthropic group
Apophytes Archaeophytes Epoecophytes Ergasiophygophytes
52 42 11 5
Achillea millefolium Agrostemma githago Amaranthus hybridus Avena sativa
Agrimonia eupatoria Anchusa arvensis Amaranthus ret ro-
fle xus
Lupinus luteus
Anthoxanthum odoratum Anchusa officinalis Anthemis ruthenica Ornithopus sativus
Arnoseris minima Anthemis arvensis Chamomilla suaveo-
lens
Phacelia tanacetifolia
Artemisia campestris Apera-spica-venti Chenopodium
strictum
Secale cereale
Artemisia vulgaris Armoracia rusticana Conyza canadensis
Barbarea vulgaris Capsella bursa-pastoris Galinsoga parviflora
Berteroa incana Centaurea cyanus Impatiens parviflora
Bromus hordeaceus Chamomilla recutita Oxalis stricta
(Xanthoxalis stricta)
Cardaminopsis arenosa
(Arabidopsis arenosa)
Chenopodium murale Solidago canadensis
Carex hirta Cichorium intybus Xanthium albinum
Centaurea stoebe Consolida regalis
Chenopodium album Descurainia sophia
Convolvulus arvensis Digitaria sanguinalis
Corynephorus canescens Echinochloa crus-galli
Dactylis glomerata Euphorbia helioscopia
Polygonum lapathifolium
subsp. lapathifolium
Euphorbia peplus
Daucus carota Galeopsis ladanum
Echium vulgare Lactuca serriola
Elymus repens (Elytrigia
repens)
Lithospermum arvense
(Buglossoides arvensis)
Equisetum arvense Matricaria maritima
subsp. inodora
Equisetum pratense Myosotis arvensis
Equisetum sylvaticum Papaver argemone
Erodium cicutarium Papaver dubium
Erophila verna (Draba
verna)
Papaver rhoeas
Euphorbia cyparissias Papaver strigosum
Euphorbia esula Raphanus raphanistrum
Fallopia dumetorum Scleranthus annuus
Heracleum sibiricum Setaria pumila
665ISSN 0372-4123. Укр. ботан. журн., 2012, т. 69, № 5
The above-cited data showed that the flora of the field margins was more similar to
the typical segetal flora rather than the segetal or ruderal flora of KPN.
In this study I found a group of 34 rare segetal species (Table 2), 25 of which are
threatened on synanthropic sites in KNP (Kirpluk, Bomanowska, 2008), and 12 of
which were given the status of endangered species according to Bomanowska (2008).
Moreover, two species, Camelina microcarpa Andrz. and Filago arvensis L., have the
highest conservation EX/CR status (locally extinct in segetal habitats). Both of them
were registered in one site only.
Camelina microcarpa was found on a rubble heap in one of the villages in the
1990s. It was not observed in the following years, but now the site probably does not
exist any more. The village is now completely abandoned, the houses have been pulled
down and the surrounding fields are ploughed and reforested. The close vicinity of
forest communities favors the succesion at this site, and the human penetration is in-
End of Table 1
Apophytes Archaeophytes Epoecophytes Ergasiophygophytes
Knautia arvensis Setaria viridis
Leontodon autumnalis Sinapis arvensis
Lychnis flos-cuculi Sisymbrium officinale
Lysimachia nummularia Spergula arvensis
Lysimachia vulgaris Thlaspi arvense
Melandrium album Urtica urens
Mentha arvensis Veronica arvensis
Myosotis ramosissima Veronica triphyllos
Myosotis stricta Vicia angustifolia
Myosoton aquaticum Vicia hirsuta
Phleum pratense Vicia tetrasperma
Plantago lanceolata Vicia villosa
Polygonum aviculare Viola arvensis
Polygonum persicaria
(Persicaria maculosa)
Pulicaria vulgaris
Rhinanthus serotinus
Rubus plicatus
Rumex acetosella
Scleranthus polycarpos
Stachys palustris
Veronica verna
Vicia lathyroides
Viola tricolor
666 ISSN 0372-4123. Ukr. Botan. Journ., 2012, vol. 69, № 5
Table 2. Rare segetal plants species in ruderal sites of the Kampinos national Park
Species
Number of
observed sites
Found in the
field margins
KPN
2008 AB
Syntaxonomic unit
1 Agrostemma githago L. 6 Y LC Centauretalia cyani*
2 Anchusa arvensis (L.)
M. Bieb.
9 Y LC Stellarietea mediae*
3 Anthemis ruthenica
M. Bieb.
1 Y Eragrostion**
4 Anthemis tinctoria L. 2 N Festucetalia valesiaceae**
5 Arnoseris minima (L.)
Scweigg. & Korte
5 Y Arnoseridenion minimae*
6 Camelina microcarpa
Andrz.
1 N EX/CR Centauretalia cyani**
7 Centaurea cyanus L. 13 Y Centauretalia cyani*
8 Centunculus minimus L. 1 N CR Centunculo-Anthoceretum*
9 Cerastium semi decand-
rum L.
5 N Koelerio-Corynephoretea*
10 Chenopodium polysper-
mum L.
5 N NT Oxalido-Chenopodietum*
11 Chondrilla juncea L. 1 N Koelerion glaucae*
12 Consolida regalis Gray 7 Y NT Centauretalia cyani*
13 Cynoglossum officinale L. 5 N Onopordenion*
14 Digitaria sanguinalis (L.)
Scop.
7 Y LC Eragrostion*
15 Eryngium planum L. 5 N Festuco-Brometea**
16 Euphorbia peplus L. 1 Y Polygono-Chenopodietalia**
17 Filago arvensis L. 1 N EX/CR Vicio lathyroidis-Potenti llion*
18 Galeopsis ladanum L. 2 Y Centauretalia cyani***
19 Helichrysum arenarium
(L.) Moench
10 N Koelerio-Corynephoretea*
20 Herniaria glabra L. 2 N NT Vicio lathyroidis-Potentil lion*
21 Hypericum humifusum L. 1 N NT Radiolion linoidis*
22 Malva pusilla Sm. 14 N Urtico-Malvetum*
23 Myosotis ramosissima
Rochel
1 Y Koelerio-Corynephoretea*
24 Papaver argemone L. 8 Y VU Papaveretum argemones*
25 Papaver dubium L. 9 Y LC Aphanenion arvensis**
26 Papaver rhoeas L. 13 Y Centauretalia cyani*
27 Papaver strigosum
(Boenn.) Schur
1 Y Centauretalia cyani
28 Scabiosa ochroleuca L. 2 N Festucetalia valesiaceae*
667ISSN 0372-4123. Укр. ботан. журн., 2012, т. 69, № 5
significant. All these circumstances limit the possibility of protection of segetal spe-
cies, especially those with a high conservation status.
Filago arvensis was found in 2004 in one of the villages on a sandy road and on the
roadside. The site was quite large and contained a few dozen specimens. In 2006 it
doubled its area. The village has also been completely abandoned and pulled down,
but the surrounding fields sites remain and the road is still used, although not fre-
quently. These conditions are favorable for the growth of Filago arvensis, but it is not
known whether these conditions will change.
During her research of segetal habitats Bomanowska (2008) did not find either
Camelina microcarpa or Filago arvensis.
Centunculus minimus L., a critically endangered (CR) species, was found in the
first period of the studies, in one site, on rubble. The village had only one farm, which
was also abandoned in the following years. The site was not found during later studies.
Bomanowska noted another site where C. minimus was present. The existence of this
species in KNP is unstable.
Papaver argemone L., the only species with the VU status (vulnerable), was found
in eight villages. Bomanowska (2008) noted eight other localities of this plant. One
can assume that this species has a chance to survive within the KNP area.
I found four species with a lower conservation NT status (near threatened): Che-
nopodium polyspermum L., Consolida regalis Gray, Herniaria glabra L., and Hypericum
humifusum L.
Chenopodium polyspermum was found in five villages, but the sites were not numer-
ous. It occurred on roadsides, in the vicinity of houses and on rubble heaps. It was not
End of Table 2
Species
Number of
observed sites
Found in the
field margins
KPN
2008 AB
Syntaxonomic unit
29 Scleranthus polycarpos L. 1 Y Vicio lathyroidis-Poten-
tillion*
30 Sedum maximum (L.)
Hoffm.
7 N Festuco-Brometea**
31 Sinapis arvensis L. 13 Y Stellarietea mediae*
32 Thlaspi arvense L. 4 Y Stellarietea mediae*
33 Veronica verna L. 4 Y Vicio lathyroidis-
Potentillion*
34 Vicia lathyroides L. 1 Y Vicio lathyroidis-Poten-
tillion*
E x p l a n a t i o n s: KNP 2008 AB – threatened segetal species occurring in the Kampinos National
Park (Bomanowska 2008): EX/CR – locally extinct on segetal habitats, CR – critically endangered,
VU – vulnerable, NT – near threatened, LC – least concern; Y – Yes = found in the field margin; N –
No = not found in the field margin. Grey background markes taksons found only in ruderal sites in
the villages studied. Syntaxonomic unit according to: *Matuszkiewicz (2001), **Zarzycki et al.(2002),
*** Kropac, Mochnacky (2009)
668 ISSN 0372-4123. Ukr. Botan. Journ., 2012, vol. 69, № 5
observed in field margins. Bomanowska (2008) also lists 14 other sites. Consolida regalis
was observed as single specimens in 8 villages: on roadsides, along the fences, near
houses, on rubble heaps, and in field margins. Bomanowska (2008) observed 12 other
sites. Herniaria glabra was found in 2 villages. The sites, which were not numerous,
were located on roadsides and in close proximity to houses. Bomanowska (2008) noted
10 other sites where the species occurred. Hypericum humifusum was found at one site
only, on a roadside. Bomanowska (2008) listed 24 other sites in segetal habitats.
In the second stage of the studies, only Consolida regalis was found among the spe-
cies listed above. It occurred only in three localities of those identified earlier. Interestingly,
the preserved sites were typical ruderal habitats, not even field margins. Bomanowska
(2008) did not observe Consolida regalis in these places. This may suggest that the sites
suitable for this species no longer exist in segetal habitats in the villages studied.
Four species with the LC (least concern) status have been found: Agrostemma githago
L., Anchusa arvensis (L.) M. Bieb., Digitaria sanguinalis (L.) Scop., and Papaver dubium L.
Agrostemma githago was found in 6 villages on the roadsides, in the vicinity of
houses, and in the field margins. The sites were not numerous. In the second stage of
our research, the species was found only in two places (one specimen in the field mar-
gin!). According to Bomanowska (2008), the species is still frequent in KNP. In some
villages it occurs only in ruderal habitats.
Anchusa arvensis was found in most of the villages studied in the vicinity of house-
holds, on rubble heaps, and in field margins. Papaver dubium exhibited a similar pat-
tern of occurrence, although it was also noted on roadsides. Localities of Digitaria
sanguinalis were less frequent, although sometimes locally quite abundant. Bomanowska
(2008) noted several localities of these species in segetal habitats of KNP. Anchusa
arvensis and Digitaria sanguinalis were found only in ruderal habitats in four villages,
whereas Papaver dubium was recorded in six villages (Kirpluk, Bomanowska, 2008).
The remaining 22 taxa (Table 2) are not assigned to any conservation category.
Nevertheless, some of them are noteworthy since in the area studied they had only one or
two sites of occurrence and were found only in ruderal habitats (Kirpluk, Bomanowska,
2008). Anthemis tinctoria L. was recorded in two villages, in the vicinity of houses and
roads. Chondrilla juncea L. occurred at one site, also near houses and roads. Papaver stri-
gosum (Boenn.) Schur (a taxon not always distinguished from Papaver rhoeas L.; Mirek et
al. 2002) was found on the roadside and in the field margin of one of the villages. Scabiosa
ochroleuca L. was recorded at two sites, in the vicinity of houses and roads.
In this work the species found at the margins of the abandoned fields of KPN were
added to the list of rare segetal taxa when their syntaxonomical affinity allowed doing
so (Table 2). Arnoseris minima (L.) Scweigg. & Korte, Thlaspi arvense L. and Veronica
verna L. have been registered before in segetal habitats (Kirpluk, Bomanowska, 2008).
In this study they were found in four to five villages each. Anthemis ruthenica M. Bieb.,
Euphorbia peplus L., Galeopsis ladanum L., Myosotis ramosissima Rochel, Scleranthus
polycarpos L., Vicia lathyroides L. were not recorded in these habitats (Bomanowska
2001, Kirpluk, Boamnowska, 2008) and in the abandoned villages of KPN they had
one or two sites of occurrence.
669ISSN 0372-4123. Укр. ботан. журн., 2012, т. 69, № 5
Final remarks
The list of rare species of the segetal flora presented in this work comprises only 15
sites in KNP and thus is local in its scope. Representatives of a large group of 17 rare
taxa were found only on ruderal sites in the abandoned villages in KNP, and they have
not been noted in segetal habitats (indicated with a grey background in Table 2). Some
of the segetal species have not been found outside the ruderal habitats of KNP (Anthemis
ruthenica M. Bieb., Camelina microcarpa Andrz., Cynoglossum officinale L., Euphorbia
peplus L., Filago arvensis L., Galeopsis ladanum L., Malva pusilla Sm., Myosotis ramo-
sissima Rochel, Scleranthus polycarpos L., Vicia lathyroides L.).
The distribution pattern of the discussed taxa in the abandoned villages in KNP
reveals that ruderal habitats may function as a potential source of diaspores of segetal
species and as sites that preserve segetal flora together with its rare and endangered
elements. Unfortunately, segetal species tend to disappear gradually from KNP due to
the reduction or abandonment of cultivated fields. Many of the rare species were found
only in ruderal habitats at the sites investigated. The decrease of land cultivation can
have an effect similar to the intensification of agriculture in other areas. Progressive
secondary succession, together with the Park Management’s policy, has a negative ef-
fect on the status of the local segetal flora. Preserving some of the scarcely populated
villages and the practice of extensive agriculture seem to be the only good solution to
this problem.
Acknowledgments
I thank Dr Hanna Werblan-Jakubiec for the provided possibility to conduct the field
research and for her constructive remarks on the manuscript, and Krystyna Jкdrze-
jewska-Szmek for the English translation. I thank my Father and colleagues from the
Botanic Garden for all the help during field studies.
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Recommended for publication Submitted 14.12.2011
by S.L. Mosyakin
І. Кірплюк
Варшавський університет, Ботанічний сад, Польща
РІДКІСНІ ЕЛЕМЕНТИ СЕГЕТАЛЬНОЇ ФЛОРИ,
ЩО ЗБЕРЕГЛИСЯ В ЗАЛИШЕНИХ СЕЛАХ КАМПІНОСЬКОГО
НАЦІОНАЛЬНОГО ПАРКУ (ЦЕНТРАЛЬНА ПОЛЬЩА)
Флористичні дослідження були проведені в 15 залишених селах Кампіноського національ-
ного парку впродовж 1992—1995 та 2004—2007 років. Cтаття містить цікаву інформацію
щодо сегетальних видів, знайдених на досліджуваній території (34 рідкісних таксони, які
об’єднують 25 вразливих і загрозливих видів). На маргінальних місцезростаннях виявлено
110 видів. Апофізи становлять основну групу (близько 47 %), археофіти є менш чисельними
(близько 38 %). Метою цього дослідження було обстеження ділянок, які можуть функціону-
вати як потенційні джерела діаспор рідкісних сегетальних видів, що є важливим для збере-
ження біо різноманіття.
К л ю ч о в і с л о в а: рідкісні види, сегетальна флора, рудеральні місцезростання, залишені
села, Кампіноський національний парк, Центральна Польща.
И. Кирплюк
Варшавский университет, Ботанический сад, Польша
РЕДКИЕ ЭЛЕМЕНТЫ СЕГЕТАЛЬНОЙ ФЛОРЫ,
СОХРАНИВШИЕСЯ В ЗАБРОШЕННЫХ СЕЛАХ КАМПИНОСКОГО
НАЦИОНАЛЬНОГО ПАРКА (ЦЕНТРАЛЬНАЯ ПОЛЬША)
Флористические исследования были проведены в 15 заброшенных селах Кампиноского на-
ционального парка в 1992—1995 и 2004—2007 годах. Статья содержит интересную информа-
цию о сегетальних видах, выявленных на исследованной территории (34 редких таксона,
включающих 25 видов, которые находятся под угрозой исчезновения). На маргинальных
местообитаниях найдено 110 видов. Апофизы составляют основную группу (около 47 %),
ар хеофиты – немногочисленные (около 38 %). Цель исследования – изучение участков, ко-
торые могут функционировать как потенциальные источники диаспор редких сегетальных
видов, что важно для сохранения биоразнообразия.
К л ю ч e в ы е с л о в а: редкие виды, сегетальная флора, рудеральные местообитания,
заброшенные села, Кампиноский национальный парк, Центральная Польша.
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/NLD (Gebruik deze instellingen om Adobe PDF-documenten te maken die zijn geoptimaliseerd voor prepress-afdrukken van hoge kwaliteit. De gemaakte PDF-documenten kunnen worden geopend met Acrobat en Adobe Reader 5.0 en hoger.)
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/ENU (Use these settings to create Adobe PDF documents best suited for high-quality prepress printing. Created PDF documents can be opened with Acrobat and Adobe Reader 5.0 and later.)
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>>
/Namespace [
(Adobe)
(Common)
(1.0)
]
/OtherNamespaces [
<<
/AsReaderSpreads false
/CropImagesToFrames true
/ErrorControl /WarnAndContinue
/FlattenerIgnoreSpreadOverrides false
/IncludeGuidesGrids false
/IncludeNonPrinting false
/IncludeSlug false
/Namespace [
(Adobe)
(InDesign)
(4.0)
]
/OmitPlacedBitmaps false
/OmitPlacedEPS false
/OmitPlacedPDF false
/SimulateOverprint /Legacy
>>
<<
/AddBleedMarks false
/AddColorBars false
/AddCropMarks false
/AddPageInfo false
/AddRegMarks false
/ConvertColors /ConvertToCMYK
/DestinationProfileName ()
/DestinationProfileSelector /DocumentCMYK
/Downsample16BitImages true
/FlattenerPreset <<
/PresetSelector /MediumResolution
>>
/FormElements false
/GenerateStructure false
/IncludeBookmarks false
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/IncludeLayers false
/IncludeProfiles false
/MultimediaHandling /UseObjectSettings
/Namespace [
(Adobe)
(CreativeSuite)
(2.0)
]
/PDFXOutputIntentProfileSelector /DocumentCMYK
/PreserveEditing true
/UntaggedCMYKHandling /LeaveUntagged
/UntaggedRGBHandling /UseDocumentProfile
/UseDocumentBleed false
>>
]
>> setdistillerparams
<<
/HWResolution [2400 2400]
/PageSize [612.000 792.000]
>> setpagedevice
|