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Biodiversity across the forest cycle in ash and Sitka spruce plantations: effects of Irish forestry on spider communities Anne Oxbrough, Tom Gittings,

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Presentation on theme: "Biodiversity across the forest cycle in ash and Sitka spruce plantations: effects of Irish forestry on spider communities Anne Oxbrough, Tom Gittings,"— Presentation transcript:

1 Biodiversity across the forest cycle in ash and Sitka spruce plantations: effects of Irish forestry on spider communities Anne Oxbrough, Tom Gittings, Paul Giller, John O’Halloran Dept Zoology, Ecology and Plant Science, University College Cork Xysticus cristatus ©Ed. Nieuwenhuys. Copyright 1996-2002

2 BIOFOREST BIOFOREST aims: Investigate the effect of afforestation on the biodiversity of three major taxanomic groups in Ireland »Plants »Invertebrates »Birds

3 Why use spiders as an indicator group? Enoplognatha ovata ©Ed Nieuwenhuyys. Copyright 1996 – 2002.

4 1.Abundant 2.Positively influenced by vegetation structure 1.Prey 2.Web attachment 3.Hiding places for active hunters 4.Protecton from predators 5.Suitable microclimates 3.Adopt many ecological strategies 4.Found in all layers of vegetation 5.Occupy a strategic position food webs 6.Taxonomically well known Spiders:

5 Aims of study: To investigate changes in spider communities over the forest cycle To investigate the difference in spider communities in Sitka spruce and ash To identify indicators of spider biodiversity

6 Study sites Sitka spruce and ash - Conifer and broadleaf - Widely planted A variety of age classes

7 Pitfall traps

8 Pitfalls Plastic cups (9cm depth by 7cm diameter) Antifreeze and drainage holes Five pitfalls per plot Five plots per site Plots at least 50m apart 2-3 weeks in the ground Three changes during the season

9 Habitat measures Cover abundance of plant structure Cover of deadwood Soil samples –Organic content –Moisture content Litter depth and cover

10 Results Linyphia triangularis ©Ed Nieuwenhuyys. Copyright 1996 – 2002

11 Results: 18730 individuals collected in 139 species Species classified by habitat preference: 15 forest habitat specialists 19 open habitat specialists

12 Mean species richness of spiders across the forest cycle. Bar indicate SE PrethicketThicket Closed maturing Re- opening Mature Prethicket PoleClosed maturing Semi- Mature Sitka spruceAsh Species richness

13 Species richness of habitat specialists. Bars indicate SE Open specialists Forest specialists Prethicket ThicketClosed maturing Re- opening Mature Sitka spruce Ash Prethicket Pole Closed maturing Semi- mature Mature

14 Species assemblages Cluster analysis indicated 5 groups: 1) Prethicket mix 2) Prethicket ash 3) Mature ash 4) Closed canopy spruce 5) Thicket/Mature open-spruce Ordination revealed similar groups as cluster analysis

15 Species NMS of sites with environmental variables

16 NMS of sites using habitat variables

17 Mean species richness among cluster groups. Bars indicate SE Prethicket mix Prethicket ash Mature ash Closed Canopy spruce Thicket/Mature open-spruce Species richness

18 Mean species richness of habitat specialists among cluster groups. Bars indicate SE Open specialists Forest specialists Species richness Prethicket mix Prethicket ash Mature ash Closed canopy spruce Thicket/Mature open-spruce

19 Trends in vegetation structure among cluster groups. Bars indicate SE Percentage cover Ground vegetationLower field layer Upper field layerCanopy Pre- thicket mix Pre- thicket ash Mature ash Closed canopy spruce Thicket/Mature open-spruce Pre- thicket mix Pre- thicket ash Mature ash Closed canopy spruce Thicket/Mature open-spruce

20 Correlations of total S and environmental variables Cluster groupEnvironmental variable Pearson correlation p (2-tailed) Prethicket mix (n=20) Organic content0.570.009 Lower field layer0.450.05 Prethicket ash (n=34) Soil cover-0.330.06 Lower field layer0.400.02 Dead wood cover-0.500.005 Closed canopy spruce (n=29) Soil cover-0.470.06 Thicket/mature open-spruce (n=44) Lower field layer0.260.06

21 Correlations of open specialist S and environmental variables Cluster groupEnvironmental variable Pearson correlation p (2-tailed) Prethicket ash (n=34) Deadwood cover-0.470.004 Soil cover-0.470.004 Closed canopy spruce (n=29) Canopy cover-0.310.04 Thicket /mature Open-spruce (n=44) Ground vegetation -0.320.04

22 Correlations of forest specialist S and environmental variables Cluster groupEnvironmental variable Pearson correlation p (2- tailed) Pure prethicket ash (n= 34) Twig cover0.340.05 Ground vegetation0.360.04 Leaf litter cover0.540.001 Soil cover0.450.007 Mature ash (n=16)Lower field layer-0.580.02 Closed canopy spruce (n= 59) Upper field layer-0.270.03 Thicket/mature open-spruce (n=44) Twig cover0.460.002 Ground vegetation0.450.002 Upper field layer-0.48<0.001

23 Discussion Meta mengei ©Ed Nieuwenhuyys. Copyright 1996 – 2002

24 Changes over the forest cycle Decrease in overall S in both ash and spruce: –Decrease in open species –Increase in forest species Early stages The pre-thicket sites have highest S and the highest S of open associated species Greatest cover of lower field layer vegetation –Prey availability –More web attachment points –Hiding places for active predators –Microclimate – stable moisture levels

25 Effects of canopy closure Decrease in lower field layer vegetation - Reduced light Increase in ground vegetation typical of forests habitats Effects on spiders: - Overall S and open species S is reduced - Forest species benefit from ground vegetation

26 Reopening of the canopy Mechanisms of reopening – Thinning – Wind throw event – Disease Outcomes of reopening – Increase in lower field layer –Open species recolonise –Thinning allows coexistence of both forest and open specialists –Thicket/mature open-spruce Highest total S of all the cluster groups

27 Differences between ash and spruce Prethicket ash and spruce do not form such a distinct group from each other as mature sites Minimal effect of trees Preplanting habitat type Soil differences

28 Mature sites Mature ash distinct in assemblage structure and low S: Leaf litter –Ash and spruce - equally high litter cover –Ash - low litter depth –Spruce - high litter depth –Litter dwelling forest species Field layer cover: –Both spruce and ash have high field layer cover –Spruce: grass, ferns, brambles – Ash: Ivy dominated – Structure of ivy –Finely tuned vegetation measurements required

29 Structural indicators of species richness Lower field layer cover: Important determinant of total spider species richness Diversification of habitat structure Evident in more open sites with high species richness

30 Effect of Canopy cover and upper field layer: Negative effect on lower field layer vegetation Allows colonisation of forest ground vegetation Increases S of forest spiders which are positively correlated with ground vegetation

31 Forest associated variables Such as: –Needle litter –Leaf litter –Deadwood –Litter depth Overall negative effect on total and open species richness However it must be noted that forest specialists are positively affected by these variables

32 Conclusions Sitka spruce and ash have different spider assemblages which change over the forest cycle: Canopy closure has profound effects on spider communities Species richness in spiders is strongly influenced by vegetation structure Sites with a more open canopy contain a more complex vegetation structure

33 Forest species must not be overlooked: Open and forest species show opposite trends over the forest cycle Paucity of natural woodlands in Ireland Plantations could be a potentially very important habitat for these species Balance between factors affecting open and forest species in management Only ground dwelling spiders studied Real data and structural indicators

34 Acknowledgements Many thanks to Myles Nolan, Bob Johnston and Peter Merrett for help with identification and verification of difficult specimens Thanks to Maire Buckley and Noreen Burke for help with sample sorting and field work Many thanks to Coillte for the use of their forests during this survey

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