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Durham E-Theses Durham E-Theses An investigation into the ground-living spider communities of Hamsterley forest Bentley, Christopher How to cite: Bentley, Christopher (1997) An investigation into the ground-living spider communities of Hamsterley forest, Durham theses, Durham University. Available at Durham E-Theses Online: http://etheses.dur.ac.uk/4802/ Use policy The full-text may be used and/or reproduced, and given to third parties in any format or medium, without prior permission or charge, for personal research or study, educational, or not-for-prot purposes provided that: • a full bibliographic reference is made to the original source • a link is made to the metadata record in Durham E-Theses • the full-text is not changed in any way The full-text must not be sold in any format or medium without the formal permission of the copyright holders. Please consult the full Durham E-Theses policy for further details. Academic Support Oce, Durham University, University Oce, Old Elvet, Durham DH1 3HP e-mail: [email protected] Tel: +44 0191 334 6107 http://etheses.dur.ac.uk 2 An Investigation into the Ground-living Spider Communities of Hamsterley Forest. The copyright of this thesis rests with the author. No quotation from it should be published without the written consent of the author and information derived from it should be acknowledged. by Christopher Bentley A Thesis submitted in fulfilment of the requirements for the degree of Master of Science (Ecology) Department of Biological Sciences The University of Durham 1997 " 5 nAR 1938 An Investigation into the Ground-living Spider Communities of Hamsteriey Forest. Christopiier Bentley MSc (Ecology), 1997 A study was made of the ground-living spider communities of a commercial forest, using sites at various stages of the management cycle to represent different stages of succession. Clear-felling resulted in an increase in the abundance of large polyphagous cursorial hunters associated with open habitats, and a corresponding reduction in the numbers of small web-building litter species, with a more limited prey range, which characterised the later stages of succession. The most important factor in this change appeared to be the removal of the canopy, resulting in a modification of microclimatic conditions, and degradation of the litter layer. In the first nine years after clear-felling, there were clear and relatively rapid changes in community structure associated with successional age. The observed changes were considered to be mainly due to the increasing vegetation density in this period, which provided both panicular structures and a more favourable microclimate for certain species. Associated changes were also found in species richness, abundance, diversity and eveness, which increased during this period. These attributes decreased into late succession, though the pattern was less clear for species abundance, and the oldest sites were less species rich, diverse and even than those of eariy succession. In late succession, the rate of community change slowed, the most mature sites being very similar in terms of their communities. In general, the differences that did exist were not related to the position of the site on the successional gradient. It was considered that these differences were not due to a single factor, but rather reflected the importance of different factors at each site. CONTENTS Acknowledgements 1. INTRODUCTION 1 2. STUDY AREAS 5 2.1. Hamsterley Forest 5 2.1.1. Study Sites 6 2.2. Wilton Moor 12 2.2.1. Study Site 13 3. METHODS 17 3.1. Pitfall Trapping 17 3.2. Vegetation Density 18 3.3. Data Analysis 19 3.3.1. Ordination 19 3.3.2. Classification 21 3.3.3. Guild Distribution 22 3.3.4. Diversity and Species Abundance 22 3.3.4.1. Diversity Indices 22 3.3.4.2. Species Abundance Models' 26 3.3.5. Border Transition Categories 29 4. RESULTS 32 4.1. Ordination 32 4.1.1. Ordination of Hamsterley sites based on their spider 32 assemblages II 4.1.2. Ordination of Hamsterley species based on their 34 relative abundance at the sampled sites 4.1.3. Derivation of ordination axes 38 4.2. Classification 40 4.2.1. Grouping of Hamsterley sites based on their spider 40 assemblages 4.2.2. Distribution of Common species across Hamsterley 43 sites 4.2.3 The relationship between the classification of 53 Hamsterley sites and their position on the succcssional gradient 4.3. Distribution of the six major spider guilds across 54 Hamsterley sites 4.4. Diversity and species abundance 65 4.4.1. Diversity indices 65 4.4.1.1 Ranking of sites 65 4.4.1.2 Correlation between indices 68 4.4.1.3. The use of pitfall trap data in relation to the 70 calculation of diversity indices 4.4.1.4. The performance of individual diversity indices 71 with the Hamsterley data 4.4.2. Species abundance models 73 4.4.2.1. Log abundance on rank plots 73 Ill 4.4.2.2. Performance of individual species abundance 77 models with the Hamsteriey data 4.4.2.3. The suitability of goodness-of-fit tests for assessing 79 the fit of species abundance models 4.4.2.4. The relative merits of the four species abundance 79 models in relation to their performance with the Hamsteriey data 4.4.3. Changes in diversity and species abundance in 84 relation to successional age 4.5. Border transition categories 85 4.5.1. Distribution of species richness, diversity and number 85 of individuals across the habitat boundary at Wilton Moor 4.5.2. Distribution of individual species 89 4.5.3. Distribution of major guilds 102 4.5.4. A discussion of the results of the Wilton Moor study 103 5. DISCUSSION 111 5.1. The use of pitfall traps in community studies 111 5.2. Changes in spider communities during succession 112 5.3. Rate of change of spider communities during 123 succession 5.4. Changes in the attributes of spider life cycles 125 with succession 6. REFERENCES 136 IV APPENDIX 152 V LIST OF TABLES Table 1. Characteristics of the 11 Hamsterley Forest sites 8 sampled during 1992. Table 2. Summary information for the six major spider guilds 23 defined at Hamsterley Forest. Table 3. Distribution of species trapped in numbers exceeding 44 19 individuals across Hamsterley sites, based on TWINSPAN output. Table 4. Means (± SE) at each TWINSPAN Endgroup 47 for each of the 36 species trapped in numbers exceeding 19 individuals, based on Table 3. Table 5. Percentage contribution of each major guild to the 58 catch at each site, showing TWINSPAN Endgroups. Table 6. Contribution of each guild to the total number of 59 species at each site, showing TWINSPAN Endgroups. Table 7. Mean numbers of species (± SE) for the major 60 guilds at each TWINSPAN Endgroup. Table 8. Species richne.ss and abundance data for each of the 11 66 Hamsterley sites, with the values of the four diversity indices calculated. Table 9. Probabilities and direction of correlation obtained from 69 comparisons between species richness, abundance and four diversity indices using Spearman's Rank Correlation Coefficient. VI Table 10. Chi-square values, degrees-of-freedom and probabilities 78 for the fit of four species abundance models to the species abundance data at each site. Table 11. Mean number of individuals, species richness and 88 species diversity per trap for each row position at Wilton Moor with results of ANOVA. Table 12. Mean number of individuals per trap (± SE) from 95 grassland and plantation for the 25 spider species trapped in numbers exceeding 19 individuals at Wilton Moor and showing the results of significance testing using student's t-test. Table 13. Mean number of individuals per trap (± SE) at each row 97 for each of the nine species trapped in significantly greater numbers in the grassland at Wilton Moor, with results of ANOVA analysis. Table 14. Mean number of individuals per trap (± SE) at each row 98 for each of the seven species trapped in significantly greater numbers in the plantation at Wilton Moor, with results of ANOVA analysis. Table 15. Mean number of individuals per trap (± SE) for each 99 of the nine species which showed no significant difference in mean catch between grassland and plantation at Wilton Moor, with results of ANOVA analysis. VII Table 16. Representation of the results of the Tukey multiple 101 comparison tests on the species in Table 12 which gave significant F values in the initial ANOVA. Table 17. Mean number of individuals per trap (± SE) from 104 grassland and plantation for each of the six major spider guilds identified at Wilton Moor, and showing results of significance testing using student's t-test. Table 18. Mean number of individuals per trap (± SE) at each 105 row for each of the six major guilds at Wilton Moor, and with results of ANOVA analysis. VIII LIST OF FIGURES Fig. 1. Map of Hamsteriey Forest showing position of study 7 sites. Fig. 2. Map of Wilton Moor showing study area. 14 Fig. 3. Diagram showing arrangement of pitfall-traps at Wilton 16 Moor. Fig. 4. Diagram showing the six types of border transition 30 category proposed by Duelli et al., (1990), and based on the same. Fig. 5. CANOCO ordination diagram (Axis 1 by Axis 2) of 33 Hamsteriey sites based on the distribution of those species with numbers greater than five individuals and showing major habitat groups. Fig. 6. CANOCO ordination diagram (Axis 1 by Axis 2) of 35 Harasterley species on those occurring in numbers greater than five individuals and showing those with numbers greater than 19. Fig. 7. Dendrogram derived from TWINSPAN analysis of 41 Hamsteriey spider data for those species present in numbers exceeding five individuals and showing indicator species for each division.
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