Plant cover recolonization in the Raessaare milled bog SWEstonia - PowerPoint PPT Presentation

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Plant cover recolonization in the Raessaare milled bog SWEstonia

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Drained for forestry ca 310 000 ha. Drained for agriculture ca 420 000 ha. Still not drained ca 270 000 ha(mainly bogs), but all surrounded by marginal ditches ... – PowerPoint PPT presentation

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Title: Plant cover recolonization in the Raessaare milled bog SWEstonia


1
Plant cover recolonization in the Raessaare
milled bog (SW-Estonia)
  • Mati Ilomets
  • Laimdota Truus
  • Elve Lode
  • Institute of Ecology at Tallinn University,
  • Estonia

2
Some facts about Estonian peatlands
  • 1900
  • Total area of peatlands ca 1 mil ha and
    paludified areas some 250 000 ha
  • 2000
  • Drained for forestry ca 310 000 ha
  • Drained for agriculture ca 420 000 ha
  • Still not drained ca 270 000 ha(mainly bogs), but
    all surrounded by marginal ditches
  • Protected some 170 000 ha

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Study site
  • Abandoned and forested cranberry plantation with
    area of some 9,5 ha in SW Estonia.
  • Under the southwestern margin of the protected
    Raessaare bog (ca 1260 ha)
  • Belongs to Sookuninga Nature Reserve

5
Protected mires in Estonia
6
Study site
  • The Nigula Nature Reserve, as the manager of the
    site, made a decision to remove the tree layer
    and close the ditches on the site

7
Study site
8
Study aims
  • Main aim was to describe the starting situation
    and conditions for the futher monitoring
  • Our task was to understand more about
    relationships between plant cover stucture and
    habitat conditions
  • water level,
  • pore water pH and conductivity,
  • peat type
  • tree canopy

9
Study aims
  • And to present our opinion about the vegetation
    response to rising up the water level and cutting
    the trees

10
Recent history of the site
11
1967 - 1969
  • 1967 -plantation was established all trees and
    bushes removed
  • Mire surface milled and material removed
  • September 1968 - surface milled once more, but
    material left
  • Ditches cut and dams constructed
  • Oxycoccus palustris and O. macrocarpus sets
    planted
  • 1969 - O. macrocarpus disappeared

12
1968
13
1970 - 1972
  • 1970 first Sphagnum patches established
  • Dense grass cover formed - Calamagrostis
    palustris, Comarum palustre, Menyanthes
    trifoliata, Phragmites australis, several Carex
    species
  • 1971 - some Eriophorum vaginatum, Cirsium
    palustre appeared
  • Plantation fertilized with P
  • 1972 first cranberry crop

14
1973
  • The site looks like a bog with Calluna vulgaris
    and Sphagnum
  • Share of fen species was unimportant
  • Young trees and tree seedlings removed
  • Cranberry yield ca 1000 - 1500 kg per hectare

15
1973
16
Later
  • The plantation was managed up to end of
    1980-ties, but trees were not cut any more
  • Dams started to leak at mid 90-ties
  • Tree canopy more dense
  • Water table decreased slowly

17
2004
18
2004
19
1968
20
1973
21
methods
  • on 1x1 m2 plots 100 plant cover analyses
  • We found
  • species composition and coverage
  • On 10x10 m2 plots tree layer species composition,
    height, canopy coverage
  • Irradiation on surface and field layer
  • Depth to water level, pore water pH and
    conductivity
  • Annual dynamics of water level in 10 stations on
    three of four fields and in 7 stations outside
    the fields

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Some results
25
Species composition
26
Ordination - Nonmetric Multidimensional Scaling
(NMS) field layer
  • Significant factors
  • Peat type bog Sphagnum versus fen Carex peat
  • Pore water pH and conductivity
  • Tree canopy density

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Multiple Regression Analyses
29
Ordination - Nonmetric Multidimensional Scaling
(NMS) moss layer
  • Significant factors
  • Peat type
  • Tree canopy density

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Multiple Regression Analyses
32
Indicator species
  • By peat type, IVgt33
  • Sphagnum peat
  • S. magellanicum
  • Calluna vulgaris
  • Phragmites australis
  • Carex peat
  • Agrostis canina
  • Potentilla palustris
  • Viola palustris

33
Indicator species
  • Water level lt 10 cm
  • Carex lasiocarpa
  • Carex rostrata
  • Carex nigra
  • Agrostis stolonifera

34
Classification, field layer
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classification
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Conclusions
  • Even after 40 years the species structure of
    communities is not stabilized
  • More variable is the situation on fen peat than
    on bog peat
  • After removing the tree layer the cover of
    Calluna vulgaris, Sphagnum fuscum and S.
    magellanicum should increase
  • This means increasing competition between the two
    groups of plants

39
Conclusions
  • 5. On the bog peat part the rising up the water
    level should give more advantage to Sphagnum and
    to decrease competitional ability of Calluna
    vulgaris
  • 6. On the fen peat part the vegetation response
    is more complicated, but in the moss layer the
    cover of species other than Sphagnum should
    decrease

40
Merci de votre attention
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