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What have we learned from 50-year large scale field study on the biodiversity in an agricultural...

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What What have we have we learn learn ed ed from 50 from 50 - - year large scale field study year large scale field study on the biodiversity in an on the biodiversity in an agricultural landscape? agricultural landscape? Krzysztof Kujawa, Jerzy Karg Krzysztof Kujawa, Jerzy Karg Institute for Agricultural and Institute for Agricultural and Forest Environment, Polish Academy Forest Environment, Polish Academy of Sciences, Poznań of Sciences, Poznań 1
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What What have wehave we learn learneded from 50 from 50--year year large scale field study on the biodiversity large scale field study on the biodiversity

in an agricultural landscape?in an agricultural landscape?

Krzysztof Kujawa, Jerzy KargKrzysztof Kujawa, Jerzy Karg

Institute for Agricultural and Forest Environment, Institute for Agricultural and Forest Environment, Polish Academy of Sciences, PoznańPolish Academy of Sciences, Poznań

11

General view of the study areaDezydery Chlapowski Landscape Park

Small fields Wooded patches Shelterbelts

Fot. J. Karg

Field Station in Turew

22

Main study area:

the Dezydery Chłapowski Landscape Park

Photo K. Kujawa

• Gen. Dezydery Chłapowski• Origin: 1810-1820• For crop protection and wood

• Gen. Dezydery Chłapowski• Origin: 1810-1820• For crop protection and wood

• Mid-field tree lines: why so many ?

• Mid-field tree lines: why so many ?

Photo K. Kozłowski

Unique feature of the area: large variety of windbreaks, tree lines, hedgerows and other small wooded patches

Photo K. Kujawa

Study on biodiversity carried out by IAFE Study on biodiversity carried out by IAFE near Turewnear Turew

Effect of habitat and landscape structure Effect of habitat and landscape structure

Long-term changes – 50 yearsLong-term changes – 50 years

Effect of prey-predator relationships (insects, Red Fox vs birds)Effect of prey-predator relationships (insects, Red Fox vs birds)

44

Taxa studied:Taxa studied: vascular plantsvascular plants

macrofungi macrofungi

insectsinsects

spidersspiders

other invertebratesother invertebrates

fishfish

amphibiansamphibians

birdsbirds

mammalsmammals

Methods (main) – insects

For migrating insects – tower with passive trap

For epigeic insects – suction trap:

For flying insects – motor-net:

55Photo K. Kujawa

Methods – other taxa

Birds:

• Sampling plots, points and transects

Plants and macrofungi:

• Sampling plots and long routes across a variety of habitats

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Key results:Key results:

1. High biological diversity 1. High biological diversity

77

88

Number of species in Turew area and Poland

0

1000

2000

3000

4000

5000

Macrofungi Lepidoptera Vascular plants

Spiders Bees

PolandTurew area0.05% of Poland

0

100

200

300

Breeding birds

Butterflies Mammals Dragonflies Amphibians

PolandTurew area

Number of species in Turew area and Poland

0.05% of Poland

Vascular plants

• No. of species – 828 spp. (54% of regional list)

• 85 spp. of special care,

• 1 sp. from II Annex of HD,

• 2 spp. from Red Data Book,

• 44 spp. protected by law

Vascular plants

• No. of species – 828 spp. (54% of regional list)

• 85 spp. of special care,

• 1 sp. from II Annex of HD,

• 2 spp. from Red Data Book,

• 44 spp. protected by law

1010

Common CorncockleAgrostemma githagoPhoto K. Kujawa

B o ry T u ch o l ski e

P o le ski S ło wiń skiŚ wię to krzyskiW ig i e rski

T a trza ń ski

O j co wski W ie l ko p o l skiP ie n iń ski

B a b io g ó rskiB ie szcza d zki

B ia ł o wie ski

T u re w

0 10000 20000 30000

Area (ha)

0

200

400

600

800

1000

1200

1400

1600

No

. o

f sp

ecie

sNumber of macrofungi species in Turew area and in Polish national parks in relation to their area

Crowned EarthstarGeastrum coronatum

Photo K. Kujawa

4

1 1

1

11

2

3

1

2

1 1

2 4 6 8 10 12 14 16 18 20 22

Area (km2 )

0

10

20

30

40

50

60

70

80

90

No

. o

f sp

eci

es

r = 0 .61 ; p = 0 .06

1212

Number of breeding bird species in Polish farmlands in relation to study area size (no. of years is given)

Turew

Red-backed ShrikeLanius collurio

Photo K. Kujawa

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Key results:Key results:

2. Key factor for preserving biodiversity:2. Key factor for preserving biodiversity:

habitat and landscape diversity habitat and landscape diversity

40 aquatic communites (180 spp.)

82 terrestrial communites (648 spp.)

• 122 plant communities, • 54 endangered regionally• 39 indicators of habitat from II Annex of Habitat Directive

Daisyleaf grape-fernBotrychium matricariifoliumPhoto K. Kujawa

Photo K. Kozłowski

0

5

10

15

20

25

30

35

Forest Parks Tree belts Tree clump Tree alley OthersHabitat category

Nu

mb

er

of s

ites

Number of sites of 16 species protected by law (Poland – ca. 100 spp. ) in various habitats of agricultural landscape near Turew

1515

Photo K. Kujawa

1616

1717

Diversity (H’) of spider assemblages in various crop fields and two landscape types

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Relationships between share of small wooded islands and bird density in Polish farmland

Turew

1919

Key results:Key results:

3. Potential for biological control related to 3. Potential for biological control related to habitat and landscape diversityhabitat and landscape diversity

2020

SpidersSpiders

Fot. K. Kujawa

Effect of distance from shelterbelt on species numbers of plant-dwelling spiders in crop fields (3-years study)

?Photo K. Kujawa

Effect of landscape type on share of types of spiders webs in sugar beet plantations (3-years studies)

InsectsInsects

Fot. K. Kujawa

Effect of tree belt on density of insect larvae infected by parasitic insects (Ichneumonidae and Chalcidoidea)

2525

Trophic structure of insect assemblages wintering in crop fields and shelterbelts

2626

Key results (unexpected!):Key results (unexpected!):

4. In contrary to our previous conlusions, 4. In contrary to our previous conlusions, high and constant landscape diversity high and constant landscape diversity seems to be seems to be not sufficient for preserving not sufficient for preserving biodiversitybiodiversity when intensity of farming when intensity of farming practices is above some thresholdpractices is above some threshold

R² = 0.82

R² = 0.24

0

10

20

30

40

50

60

70

1984 1988 1992 1996 2000 2004 2008

HeterogenicUniform

Long term trends in diversity (number of families ) of epigeic insectsin cereals in heterogenic and uniform landscapes

Long-term changes – insects

H > UH > U H = UH = U H < U !!H < U !!

Long-term changes – birds

0

10

20

30

40

50

1964-66 1991-1994 1999-2000 2001-2002 2005-2006

Long-term changes in number of breeding bird species in wooded patches in agricultural landscape near Turew in 1964-2006

2828

Long-term changes – birds

0

4

8

12

16

20

1964-66 1991-94 1999 2000 2001 2002 2005 2006

Den

sity

(pai

rs/h

a)

Wood spp.Farmland spp.Total

Long-term changes in bird density in wooded patchesin agricultural landscape near Turew

2929

3030

Key results:Key results:

(by the way ...)(by the way ...)

5. A conservation paradox? 5. A conservation paradox? One of most abundant tree species in One of most abundant tree species in the Turew area is Black Locust, listed in the Turew area is Black Locust, listed in 100 worst invasive species in Europe 100 worst invasive species in Europe

Black Locust in Turew areaBlack Locust in Turew area

Insect taxonomical richness in „native” and Black Locust tree belts Insect taxonomical richness in „native” and Black Locust tree belts

Phot. K. Kujawa

Native (multi-species) Black Locust

Birds – species richness in „native” and Black Locust wood islandsBirds – species richness in „native” and Black Locust wood islands

Number of wooded islands

Native Locust

• Agricultural landscape near Turew is inhabited by a variety of species-rich communities, that among others include species of high conservation priority

• High diversity and abundance of predatory and parasitic species create favorable condition for application of biological control

• High and stable landscape heterogeneity supports high biodiversity level, however long term analysis indicates that it is not able to counteract intensification of agriculture when it is above some threshold that seems to be crossed . Thus, also potential for biological control may be strongly impoverished

SUMMARY & CONCLUSIONS:

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Thank you for attention

3535

Authors (of published and unpublished data):• Dr Hanna Gołdyn and Dr Ewa Arczyńska-Chudy (plants)• Prof. Jerzy Karg (insects)• Dr. Anna Kujawa (macrofungi), • Dr. Krzysztof Kujawa (birds)• Dr. Maria Oleszczuk (spiders)• Dr. M. Rybacki (amphibians)• M. Sc. Dariusz Sobczyk (butterflies)• and others


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