influence of vegetation type, soil properties and precipitation on the composition of soil mite and microbial communities at the landscape scale
We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in the community composition of five soil organism groups. Our aim was to determine whether the degree to which soil organisms respond to natural...
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| Published in | Journal of biogeography Vol. 37; no. 7; pp. 1317 - 1328 |
|---|---|
| Main Authors | , , , , |
| Format | Journal Article |
| Language | English |
| Published |
Oxford, UK
Oxford, UK : Blackwell Publishing Ltd
01.07.2010
Blackwell Publishing Ltd Blackwell Publishing Blackwell |
| Subjects | |
| Online Access | Get full text |
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| Abstract | We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in the community composition of five soil organism groups. Our aim was to determine whether the degree to which soil organisms respond to natural changes and/or induced changes (e.g. changes in land-use type and climate) in habitat is consistent across trophic and taxonomic groups in the context of conservation policies for birch woodland and heather moorland. Mainland Scotland. We sampled mesostigmatid mites, oribatid mites, fungi, bacteria and archaea in adjacent patches of birch woodland (dominated by Betula pubescens) and heather moorland (dominated by Calluna vulgaris) at 12 sites for which annual rainfall ranged between 713 and 2251 mm. Differences in community composition were visualized using non-metric multidimensional scaling based on Bray-Curtis dissimilarities. The factors contributing to differences between habitats within sites were explored using general linear models and those among sites using redundancy analysis. The communities of all groups differed between habitats within sites, but only the oribatid mites and fungi differed consistently between habitats across sites. Within sites, dissimilarity in fungal communities was positively related to the difference in C. vulgaris cover between habitats, whereas dissimilarities in bacteria and archaea were positively related to differences in soil pH and C:N ratio between habitats, respectively. The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms directly associated with plants (fungi), and organisms with microhabitat and resource preferences (Oribatida) were strongly responsive to changes in habitat type. The response of organisms not directly associated with plants (bacteria, archaea) depended on differences in soil properties, while organisms with less clear microhabitat and resource preferences (Mesostigmata) were not strongly responsive to either vegetation type or soil properties. These results show that it is possible to predict the impact of habitat change on specific soil organisms depending on their ecology. Moreover, the community composition of all groups was related to variation in precipitation within the study area, which shows that external factors, such as those caused by climate change, can have a direct effect on belowground communities. |
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| AbstractList | We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in the community composition of five soil organism groups. Our aim was to determine whether the degree to which soil organisms respond to natural changes and/or induced changes (e.g. changes in land-use type and climate) in habitat is consistent across trophic and taxonomic groups in the context of conservation policies for birch woodland and heather moorland. Mainland Scotland. We sampled mesostigmatid mites, oribatid mites, fungi, bacteria and archaea in adjacent patches of birch woodland (dominated by Betula pubescens) and heather moorland (dominated by Calluna vulgaris) at 12 sites for which annual rainfall ranged between 713 and 2251 mm. Differences in community composition were visualized using non-metric multidimensional scaling based on Bray-Curtis dissimilarities. The factors contributing to differences between habitats within sites were explored using general linear models and those among sites using redundancy analysis. The communities of all groups differed between habitats within sites, but only the oribatid mites and fungi differed consistently between habitats across sites. Within sites, dissimilarity in fungal communities was positively related to the difference in C. vulgaris cover between habitats, whereas dissimilarities in bacteria and archaea were positively related to differences in soil pH and C:N ratio between habitats, respectively. The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms directly associated with plants (fungi), and organisms with microhabitat and resource preferences (Oribatida) were strongly responsive to changes in habitat type. The response of organisms not directly associated with plants (bacteria, archaea) depended on differences in soil properties, while organisms with less clear microhabitat and resource preferences (Mesostigmata) were not strongly responsive to either vegetation type or soil properties. These results show that it is possible to predict the impact of habitat change on specific soil organisms depending on their ecology. Moreover, the community composition of all groups was related to variation in precipitation within the study area, which shows that external factors, such as those caused by climate change, can have a direct effect on belowground communities. Aim: We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in the community composition of five soil organism groups. Our aim was to determine whether the degree to which soil organisms respond to natural changes and/or induced changes (e.g. changes in land-use type and climate) in habitat is consistent across trophic and taxonomie groups in the context of conservation policies for birch woodland and heather moorland. Location: Mainland Scotland. Methods: We sampled mesostigmatid mites, oribatid mites, fungi, bacteria and archaea in adjacent patches of birch woodland (dominated by Betula pubescens) and heather moorland (dominated by Calluna vulgaris) at 12 sites for which annual rainfall ranged between 713 and 2251 mm. Differences in community composition were visualized using non-metric multidimensional scaling based on Bray-Curtis dissimilarities. The factors contributing to differences between habitats within sites were explored using general linear models and those among sites using redundancy analysis. Results: The communities of all groups differed between habitats within sites, but only the oribatid mites and fungi differed consistently between habitats across sites. Within sites, dissimilarity in fungal communities was positively related to the difference in C. vulgaris cover between habitats, whereas dissimilarities in bacteria and archaea were positively related to differences in soil pH and C: N ratio between habitats, respectively. Main conclusions: The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms directly associated with plants (fungi), and organisms with microhabitat and resource preferences (Oribatida) were strongly responsive to changes in habitat type. The response of organisms not directly associated with plants (bacteria, archaea) depended on differences in soil properties, while organisms with less clear microhabitat and resource preferences (Mesostigmata) were not strongly responsive to either vegetation type or soil properties. These results show that it is possible to predict the impact of habitat change on specific soil organisms depending on their ecology. Moreover, the community composition of all groups was related to variation in precipitation within the study area, which shows that external factors, such as those caused by climate change, can have a direct effect on belowground communities. Aim We used a landscape‐scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in the community composition of five soil organism groups. Our aim was to determine whether the degree to which soil organisms respond to natural changes and/or induced changes (e.g. changes in land‐use type and climate) in habitat is consistent across trophic and taxonomic groups in the context of conservation policies for birch woodland and heather moorland. Location Mainland Scotland. Methods We sampled mesostigmatid mites, oribatid mites, fungi, bacteria and archaea in adjacent patches of birch woodland (dominated by Betula pubescens ) and heather moorland (dominated by Calluna vulgaris ) at 12 sites for which annual rainfall ranged between 713 and 2251 mm. Differences in community composition were visualized using non‐metric multidimensional scaling based on Bray–Curtis dissimilarities. The factors contributing to differences between habitats within sites were explored using general linear models and those among sites using redundancy analysis. Results The communities of all groups differed between habitats within sites, but only the oribatid mites and fungi differed consistently between habitats across sites. Within sites, dissimilarity in fungal communities was positively related to the difference in C. vulgaris cover between habitats, whereas dissimilarities in bacteria and archaea were positively related to differences in soil pH and C:N ratio between habitats, respectively. Main conclusions The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms directly associated with plants (fungi), and organisms with microhabitat and resource preferences (Oribatida) were strongly responsive to changes in habitat type. The response of organisms not directly associated with plants (bacteria, archaea) depended on differences in soil properties, while organisms with less clear microhabitat and resource preferences (Mesostigmata) were not strongly responsive to either vegetation type or soil properties. These results show that it is possible to predict the impact of habitat change on specific soil organisms depending on their ecology. Moreover, the community composition of all groups was related to variation in precipitation within the study area, which shows that external factors, such as those caused by climate change, can have a direct effect on belowground communities. AbstractAim We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in the community composition of five soil organism groups. Our aim was to determine whether the degree to which soil organisms respond to natural changes and-or induced changes (e.g. changes in land-use type and climate) in habitat is consistent across trophic and taxonomic groups in the context of conservation policies for birch woodland and heather moorland.Location Mainland Scotland.Methods We sampled mesostigmatid mites, oribatid mites, fungi, bacteria and archaea in adjacent patches of birch woodland (dominated by Betula pubescens) and heather moorland (dominated by Calluna vulgaris) at 12 sites for which annual rainfall ranged between 713 and 2251 mm. Differences in community composition were visualized using non-metric multidimensional scaling based on Bray-Curtis dissimilarities. The factors contributing to differences between habitats within sites were explored using general linear models and those among sites using redundancy analysis.Results The communities of all groups differed between habitats within sites, but only the oribatid mites and fungi differed consistently between habitats across sites. Within sites, dissimilarity in fungal communities was positively related to the difference in C. vulgaris cover between habitats, whereas dissimilarities in bacteria and archaea were positively related to differences in soil pH and C:N ratio between habitats, respectively.Main conclusions The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms directly associated with plants (fungi), and organisms with microhabitat and resource preferences (Oribatida) were strongly responsive to changes in habitat type. The response of organisms not directly associated with plants (bacteria, archaea) depended on differences in soil properties, while organisms with less clear microhabitat and resource preferences (Mesostigmata) were not strongly responsive to either vegetation type or soil properties. These results show that it is possible to predict the impact of habitat change on specific soil organisms depending on their ecology. Moreover, the community composition of all groups was related to variation in precipitation within the study area, which shows that external factors, such as those caused by climate change, can have a direct effect on belowground communities. The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms directly associated with plants (fungi), and organisms with microhabitat and resource preferences (Oribatida) were strongly responsive to changes in habitat type. The response of organisms not directly associated with plants (bacteria, archaea) depended on differences in soil properties, while organisms with less clear microhabitat and resource preferences (Mesostigmata) were not strongly responsive to either vegetation type or soil properties. These results show that it is possible to predict the impact of habitat change on specific soil organisms depending on their ecology. Moreover, the community composition of all groups was related to variation in precipitation within the study area, which shows that external factors, such as those caused by climate change, can have a direct effect on belowground communities. |
| Author | Nielsen, Uffe N. Osler, Graham H. R. van der Wal, René Campbell, Colin D. Burslem, David F. R. P. |
| Author_xml | – sequence: 1 givenname: Uffe N. surname: Nielsen fullname: Nielsen, Uffe N. – sequence: 2 givenname: Graham H. R. surname: Osler fullname: Osler, Graham H. R. – sequence: 3 givenname: Colin D. surname: Campbell fullname: Campbell, Colin D. – sequence: 4 givenname: David F. R. P. surname: Burslem fullname: Burslem, David F. R. P. – sequence: 5 givenname: René surname: van der Wal fullname: van der Wal, René |
| BackLink | http://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=22919236$$DView record in Pascal Francis https://res.slu.se/id/publ/43643$$DView record from Swedish Publication Index |
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| Issue | 7 |
| Keywords | Archaeobacteria Biogeography Scotland Mesostigmata Woodland Fungi Precipitation Acari Dicotyledones Angiospermae community composition Bacteria Gamasida Betulaceae Microbial community Parasitiformes Community structure Composition Landscape Betula pubescens Archaea Property of soil Oribatida Soils heather moorland Acariformes Arachnida Vegetation type Arthropoda Spermatophyta birch woodland Invertebrata |
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| Notes | http://dx.doi.org/10.1111/j.1365-2699.2010.02281.x ark:/67375/WNG-JQS36HPL-C ArticleID:JBI2281 istex:FF8F2C6BD95779B7704D053D48CC7C824D2400A0 ObjectType-Article-1 SourceType-Scholarly Journals-1 ObjectType-Feature-2 content type line 23 |
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| PublicationDate | July 2010 |
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| PublicationPlace | Oxford, UK |
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| PublicationTitle | Journal of biogeography |
| PublicationYear | 2010 |
| Publisher | Oxford, UK : Blackwell Publishing Ltd Blackwell Publishing Ltd Blackwell Publishing Blackwell |
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| References | Miles, J. (1981) Effect of birch on moorlands. Institute of Terrestrial Ecology, Cambridge, UK. Keith, A.M., van der Wal, R., Brooker, R.W., Osler, G.H.R., Chapman, S.J. & Burslem, D.F.R.P. (2006) Birch invasion of heather moorland increases nematode diversity and trophic complexity. Soil Biology and Biochemistry, 38, 3421-3430. Zhang, W., Parker, K.M., Luo, Y., Wan, S., Wallace, L.L. & Hu, S. (2005) Soil microbial responses to experimental warming and clipping in a tallgrass prairie. Global Change Biology, 11, 266-277. Minor, M.A. & Cianciolo, J.M. (2007) Diversity of soil mites (Acari: Oribatida, Mesostigmata) along a gradient of land use types in New York. Applied Soil Ecology, 35, 140-153. Wall, D.H. (ed.) (2004) Sustaining biodiversity and ecosystem services in soil and sediments. SCOPE 64. Island Press, Washington, DC. Bardgett, R.D. (2005) The biology of soil: a community and ecosystem approach. Oxford University Press, Oxford. Ramette, A. & Tiedje, J.M. (2007) Multiscale responses of microbial life to spatial distance and environmental heterogeneity in a patchy ecosystem. Proceedings of the National Academy of Sciences USA, 104, 2761-2766. Čoja, T. & Bruckner, A. (2003) Soil microhabitat diversity of a temperate Norway spruce (Picea abies) forest does not influence the community composition of gamasid mites (Gamasida, Acari). European Journal of Soil Biology, 39, 79-84. Huntley, B., Daniell, J.R.G. & Allen, J.R.M. (1997) Scottish vegetation history: the Highlands. Botanical Journal of Scotland, 49, 163-175. Robertson, P.A., Park, K.J. & Barton, A.F. (2001) Loss of heather Calluna vulgaris moorland in the Scottish uplands: the role of red grouse Lagopus lagopus scoticus management. Wildlife Biology, 7, 11-16. Satchell, J.E. (1980) Soil and vegetation changes in experimental birch plots on a Calluna podzol. Soil Biology and Biochemistry, 12, 303-310. Coleman, D.C., Crossley, D.A., Jr & Hendrix, P.F. (2004) Fundamentals of soil ecology, 2nd edn. Academic Press, New York. Lindberg, N., Bengtsson, J. & Persson, T. (2002) Effects of experimental irrigation and drought on the composition and diversity of soil fauna in a coniferous stand. Journal of Applied Ecology, 39, 924-936. Nielsen, U.N., Osler, G.H.R., van der Wal, R., Campbell, C.D. & Burslem, D.F.R.P. (2008) Soil pore volume and the abundance of soil mites in two contrasting habitats. Soil Biology and Biochemistry, 40, 1538-1541. Wardle, D.A. (2002) Communities and ecosystems: linking the aboveground and belowground components. Monographs in Population Biology, 34. Princeton University Press, Princeton, NJ. Mitchell, R.J., Campbell, C.D., Chapman, S.J., Osler, G.H.R., Vanbergen, A.J., Ross, L.C., Cameron, C.M. & Cole, L. (2007) The cascading effects of birch on heather moorland: a test for the top-down control of an ecosystem engineer. Journal of Ecology, 95, 540-554. Osler, G.H.R., Cole, L. & Keith, A.M. (2006) Changes in oribatid mite community structure associated with the succession from heather (Calluna vulgaris) moorland to birch (Betula pubescens) woodland. Pedobiologia, 50, 323-330. Dimbleby, G.W. (1952) Soil regeneration on the north-east Yorkshire moors. Journal of Ecology, 40, 331-341. Nüsslein, K. & Tiedje, J.M. (1999) Soil bacterial community shift correlated with changes from forest to pasture vegetation. Applied and Environmental Microbiology, 65, 3622-3626. Kielak, A., Pijl, A.S., van Veen, J.A. & Kowalchuk, G.A. (2008) Differences in vegetation composition and plant species identity lead to only minor changes in soil-borne microbial communities in a former arable field. FEMS Microbial Ecology, 63, 372-382. Wauthy, G. (1982) Synecology of forest soil oribatid mites of Belgium (Acari, Oribatida). III. Ecological groups. Acta Oecologia, 3, 469-494. Anderson, I.C., Campbell, C.D. & Prosser, J.I. (2003) Diversity of fungi in organic soils under a moorland - Scots pine (Pinus sylvestris L.) gradient. Environmental Microbiology, 5, 1121-1132. Fierer, N. & Jackson, R. (2006) The diversity and biogeography of soil bacterial communities. Proceedings of the National Academy of Sciences USA, 103, 626-631. Yao, H., He, Z., Wilson, M.J. & Campbell, C.D. (2000) Microbial biomass and community structure in a sequence of soils with increasing fertility and changing land use. Microbial Ecology, 40, 223-237. Beare, M.H., Neely, C.L., Coleman, D.C. & Hargrove, W.L. (1990) A substrate-induced respiration (SIR) method for measurement of fungal and bacterial biomass on plant residue. Soil Biology and Biochemistry, 22, 585-594. Sinsabaugh, R.L., Lauber, C.L., Weintraub, M.N. et al. (2008) Stoichiometry of soil enzyme activity at global scale. Ecology Letters, 11, 1-13. Ponge, J.-F. (1993) Biocenoses of Collembola in Atlantic temperate grass-woodland ecosystems. Pedobiologia, 37, 223-244. Thompson, D.B.A., MacDonald, A.J., Marsden, J.H. & Galbraith, C.A. (1995) Upland heather moorland in Great Britain: a review of international importance, vegetation change and some objectives for nature conservation. Biological Conservation, 71, 163-178. Singh, B.K., Nazaries, L., Munro, S., Anderson, I.C. & Campbell, C.D. (2006) Use of multiplex-terminal restriction fragment length polymorphism for rapid and simultaneous analysis of different components of the soil microbial community. Applied and Environmental Microbiology, 72, 7278-7285. Johnson, D., Vandenkoornhuyse, P.J., Leake, J.R., Golbert, L., Booth, R.E. & Grime, J.P. (2003) Plant communities affect arbuscular mycorrhizal diversity and community composition in grassland microcosms. New Phytologist, 161, 503-515. Wauthy, G., Noti, M.-I. & Dufrêne, M. (1989) Geographic ecology of soil oribatid mites in deciduous forests. Pedobiologia, 33, 399-416. Weis-Fogh, T. (1948) Ecological investigations of mites and collemboles in the soil. Nature Jutlandica, 1, 135-277. Kaneko, N. (1988) Feeding habits and cheliceral size of oribatid mites in cool temperate forest soils in Japan. Revue d'Ecologie et de Biologie du Sol, 25, 353-363. Pella, E. & Colombo, B. (1973) Study of carbon, hydrogen and nitrogen by combustion gas chromatography. Mikrochimica Acta, 5, 697-719. Wardle, D. (2006) The influence of biotic interactions on soil biodiversity. Ecology Letters, 9, 870-886. Girvan, M.S., Bullimore, J., Pretty, J.N., Osborn, A.M. & Ball, A.S. (2003) Soil type is the primary determinant of the composition of the total and active bacterial communities in arable soils. Applied and Environmental Microbiology, 69, 1800-1809. Bridges, E.M. (1997) World soils, 3rd edn. Cambridge University Press, Cambridge. Coleman, D.C. & Whitman, W.B. (2005) Linking species richness, biodiversity and ecosystem function in soil systems. Pedobiologia, 49, 479-497. ter Braak, C.J.F. & Šmilauer, P. (2002) CANOCO reference manual and CanoDraw for Windows user's guide: software for canonical community ordination (ver. 4.5). Microcomputer Power, Ithaca, NY. Campbell, C.D., Chapman, S.J., Cameron, C.M., Davidson, M.S. & Potts, J.M. (2003) A rapid microtiter plate method to measure carbon dioxide evolved from carbon substrate amendments so as to determine the physiological profiles of soil microbial communities by using whole soil. Applied and Environmental Microbiology, 69, 3593-3599. Rinnan, R., Michelsen, A., Bååth, E. & Jonasson, S. (2007) Fifteen years of climate change manipulations alter soil microbial communities in a subarctic heath ecosystem. Global Change Biology, 13, 28-39. De Deyn, G.B. & Van der Putten, W.H. (2005) Linking aboveground and belowground diversity. Trends in Ecology and Evolution, 20, 625-633. Ettema, C.H. & Wardle, D.A. (2002) Spatial soil ecology. Trends in Ecology and Evolution, 17, 177-183. Ruf, A. & Beck, L. (2005) The use of predatory soil mites in ecological soil classification and assessment concepts, with perspectives for oribatid mites. Ecotoxicology and Environmental Safety, 62, 290-299. Colwell, R.K. (2006) EstimateS: statistical estimation of species richness and shared species from samples. Version 8.0. User's guide and application published at: http://viceroy.eeb.uconn.edu/estimates. Tipping, R. (1994) The form and fate of Scotland's woodlands. Proceedings of the Society of Antiquaries of Scotland, 124, 1-54. Chan, O.C., Casper, P., Sha, L.Q., Feng, Z.L., Fu, Y., Yang, X.D., Ulrich, A. & Zou, X.M. (2008) Vegetation cover of forest, shrub and pasture strongly influences soil bacterial community structure as revealed by 16S rRNA gene T-RFLP analysis. FEMS Microbial Ecology, 64, 449-458. Irmler, U. (2006) Climatic and litter fall effects on collembolan and oribatid mite species and communities in a beech wood based on a 7 years investigation. European Journal of Soil Biology, 42, 51-62. Horner-Devine, M.C., Lage, M., Hughes, J.B. & Bohannan, B.J.M. (2004) A taxa-area relationship for bacteria. Nature, 432, 750-753. Eom, A.-H., Hartnett, D.C. & Wilson, G.W.T. (2000) Host plant species effects on arbuscular mycorrhizal fungal communities in tallgrass prairie. Oecologia, 122, 435-444. Hester, A.J., Miles, J. & Gimingham, C.H. (1991) Succession from heather moorland to birch woodland. I. Experimental alteration of species environmental conditions in the field. Journal of Ecology, 79, 303-315. Migliorini, M., Petrioli, A. & Bernini, F. (2002) Comparative analysis of two edaphic zoocoenoses (oribatid mites and carabid beetles) in five habitats of the 'Pietraporciana' and 'Lucciolabella' Nature Reserves (Orcia Valley, central Italy). Acta Oecologica, 23, 361-374. Miles, J. & Young, W.F. (1980) The effects on heathland and moorland soils in Scotland and northern England following colonization by birch (Betula spp.). Bulletin d'Ecologie, 11, 233-242. 2002; 17 2007; 104 1995; 71 2006; 72 2006; 38 2005; 62 2005; 20 1997; 49 2007; 35 1993; 37 1989; 33 1948; 1 1982; 3 2003; 161 2003; 5 1982 2000; 122 2008; 63 1981 2008; 64 2002; 39 2006; 50 1991; 79 2006; 9 1997 2006 1999; 65 2005 2003; 39 2004 2008; 11 2007; 95 2002 2005; 49 2007; 13 1994; 124 1990; 22 2006; 42 2004; 432 2001; 7 1988; 25 2002; 23 1980; 12 1980; 11 1952; 40 1965 2003; 69 2000; 40 1973; 5 2008; 40 2005; 11 2006; 103 e_1_2_7_3_1 e_1_2_7_9_1 Miles J. (e_1_2_7_31_1) 1981 e_1_2_7_7_1 Colwell R.K. (e_1_2_7_12_1) 2006 e_1_2_7_19_1 Kaneko N. (e_1_2_7_25_1) 1988; 25 e_1_2_7_17_1 e_1_2_7_15_1 e_1_2_7_41_1 e_1_2_7_13_1 e_1_2_7_43_1 e_1_2_7_45_1 e_1_2_7_47_1 e_1_2_7_26_1 Weis‐Fogh T. (e_1_2_7_54_1) 1948; 1 e_1_2_7_28_1 Ponge J.‐F. (e_1_2_7_39_1) 1993; 37 Wauthy G. (e_1_2_7_53_1) 1989; 33 Sinsabaugh R.L. (e_1_2_7_46_1) 2008; 11 Nüsslein K. (e_1_2_7_36_1) 1999; 65 Tipping R. (e_1_2_7_48_1) 1994; 124 Wardle D.A. (e_1_2_7_51_1) 2002 e_1_2_7_50_1 e_1_2_7_23_1 e_1_2_7_33_1 e_1_2_7_21_1 e_1_2_7_35_1 e_1_2_7_56_1 e_1_2_7_37_1 Wauthy G. (e_1_2_7_52_1) 1982; 3 Wall D.H. (e_1_2_7_49_1) 2004 Miles J. (e_1_2_7_32_1) 1980; 11 ter Braak C.J.F. (e_1_2_7_5_1) 2002 Gardner W.H. (e_1_2_7_18_1) 1965 e_1_2_7_4_1 e_1_2_7_8_1 e_1_2_7_16_1 e_1_2_7_40_1 e_1_2_7_2_1 e_1_2_7_14_1 e_1_2_7_42_1 e_1_2_7_44_1 e_1_2_7_10_1 e_1_2_7_27_1 Bridges E.M. (e_1_2_7_6_1) 1997 Coleman D.C. (e_1_2_7_11_1) 2004 e_1_2_7_30_1 e_1_2_7_24_1 e_1_2_7_55_1 e_1_2_7_22_1 e_1_2_7_34_1 e_1_2_7_20_1 e_1_2_7_38_1 McLean E.O. (e_1_2_7_29_1) 1982 |
| References_xml | – reference: Kaneko, N. (1988) Feeding habits and cheliceral size of oribatid mites in cool temperate forest soils in Japan. Revue d'Ecologie et de Biologie du Sol, 25, 353-363. – reference: Coleman, D.C. & Whitman, W.B. (2005) Linking species richness, biodiversity and ecosystem function in soil systems. Pedobiologia, 49, 479-497. – reference: Colwell, R.K. (2006) EstimateS: statistical estimation of species richness and shared species from samples. Version 8.0. User's guide and application published at: http://viceroy.eeb.uconn.edu/estimates. – reference: Pella, E. & Colombo, B. (1973) Study of carbon, hydrogen and nitrogen by combustion gas chromatography. Mikrochimica Acta, 5, 697-719. – reference: Wauthy, G., Noti, M.-I. & Dufrêne, M. (1989) Geographic ecology of soil oribatid mites in deciduous forests. Pedobiologia, 33, 399-416. – reference: Bardgett, R.D. (2005) The biology of soil: a community and ecosystem approach. Oxford University Press, Oxford. – reference: ter Braak, C.J.F. & Šmilauer, P. (2002) CANOCO reference manual and CanoDraw for Windows user's guide: software for canonical community ordination (ver. 4.5). Microcomputer Power, Ithaca, NY. – reference: Nüsslein, K. & Tiedje, J.M. (1999) Soil bacterial community shift correlated with changes from forest to pasture vegetation. Applied and Environmental Microbiology, 65, 3622-3626. – reference: Huntley, B., Daniell, J.R.G. & Allen, J.R.M. (1997) Scottish vegetation history: the Highlands. Botanical Journal of Scotland, 49, 163-175. – reference: Zhang, W., Parker, K.M., Luo, Y., Wan, S., Wallace, L.L. & Hu, S. (2005) Soil microbial responses to experimental warming and clipping in a tallgrass prairie. Global Change Biology, 11, 266-277. – reference: Wall, D.H. (ed.) (2004) Sustaining biodiversity and ecosystem services in soil and sediments. SCOPE 64. Island Press, Washington, DC. – reference: Fierer, N. & Jackson, R. (2006) The diversity and biogeography of soil bacterial communities. Proceedings of the National Academy of Sciences USA, 103, 626-631. – reference: Yao, H., He, Z., Wilson, M.J. & Campbell, C.D. (2000) Microbial biomass and community structure in a sequence of soils with increasing fertility and changing land use. Microbial Ecology, 40, 223-237. – reference: Coleman, D.C., Crossley, D.A., Jr & Hendrix, P.F. (2004) Fundamentals of soil ecology, 2nd edn. Academic Press, New York. – reference: Ponge, J.-F. (1993) Biocenoses of Collembola in Atlantic temperate grass-woodland ecosystems. Pedobiologia, 37, 223-244. – reference: Thompson, D.B.A., MacDonald, A.J., Marsden, J.H. & Galbraith, C.A. (1995) Upland heather moorland in Great Britain: a review of international importance, vegetation change and some objectives for nature conservation. Biological Conservation, 71, 163-178. – reference: Miles, J. (1981) Effect of birch on moorlands. Institute of Terrestrial Ecology, Cambridge, UK. – reference: Tipping, R. (1994) The form and fate of Scotland's woodlands. Proceedings of the Society of Antiquaries of Scotland, 124, 1-54. – reference: Johnson, D., Vandenkoornhuyse, P.J., Leake, J.R., Golbert, L., Booth, R.E. & Grime, J.P. (2003) Plant communities affect arbuscular mycorrhizal diversity and community composition in grassland microcosms. New Phytologist, 161, 503-515. – reference: Migliorini, M., Petrioli, A. & Bernini, F. (2002) Comparative analysis of two edaphic zoocoenoses (oribatid mites and carabid beetles) in five habitats of the 'Pietraporciana' and 'Lucciolabella' Nature Reserves (Orcia Valley, central Italy). Acta Oecologica, 23, 361-374. – reference: Irmler, U. (2006) Climatic and litter fall effects on collembolan and oribatid mite species and communities in a beech wood based on a 7 years investigation. European Journal of Soil Biology, 42, 51-62. – reference: Miles, J. & Young, W.F. (1980) The effects on heathland and moorland soils in Scotland and northern England following colonization by birch (Betula spp.). Bulletin d'Ecologie, 11, 233-242. – reference: Sinsabaugh, R.L., Lauber, C.L., Weintraub, M.N. et al. (2008) Stoichiometry of soil enzyme activity at global scale. Ecology Letters, 11, 1-13. – reference: Campbell, C.D., Chapman, S.J., Cameron, C.M., Davidson, M.S. & Potts, J.M. (2003) A rapid microtiter plate method to measure carbon dioxide evolved from carbon substrate amendments so as to determine the physiological profiles of soil microbial communities by using whole soil. Applied and Environmental Microbiology, 69, 3593-3599. – reference: Girvan, M.S., Bullimore, J., Pretty, J.N., Osborn, A.M. & Ball, A.S. (2003) Soil type is the primary determinant of the composition of the total and active bacterial communities in arable soils. Applied and Environmental Microbiology, 69, 1800-1809. – reference: Dimbleby, G.W. (1952) Soil regeneration on the north-east Yorkshire moors. Journal of Ecology, 40, 331-341. – reference: Satchell, J.E. (1980) Soil and vegetation changes in experimental birch plots on a Calluna podzol. Soil Biology and Biochemistry, 12, 303-310. – reference: Bridges, E.M. (1997) World soils, 3rd edn. Cambridge University Press, Cambridge. – reference: Ettema, C.H. & Wardle, D.A. (2002) Spatial soil ecology. Trends in Ecology and Evolution, 17, 177-183. – reference: Ramette, A. & Tiedje, J.M. (2007) Multiscale responses of microbial life to spatial distance and environmental heterogeneity in a patchy ecosystem. Proceedings of the National Academy of Sciences USA, 104, 2761-2766. – reference: Eom, A.-H., Hartnett, D.C. & Wilson, G.W.T. (2000) Host plant species effects on arbuscular mycorrhizal fungal communities in tallgrass prairie. Oecologia, 122, 435-444. – reference: Anderson, I.C., Campbell, C.D. & Prosser, J.I. 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| Snippet | We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and in... Aim: We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and... Aim We used a landscape‐scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and... Aim We used a landscape‐scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil properties and... AbstractAim We used a landscape-scale study of birch invasion onto heather moorland to determine the consistency of changes in vegetation type and soil... The influence of vegetation type and soil properties differed between groups of soil organisms, albeit in a predictable manner, across the 12 sites. Organisms... |
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| SubjectTerms | Animal and plant ecology Animal, plant and microbial ecology Arachnida Archaea bacteria Betula pubescens Biological and medical sciences birch woodland Calluna vulgaris carbon nitrogen ratio climate climate change community composition community structure Forest soils Fundamental and applied biological sciences. Psychology fungal communities fungi General aspects Habitats heather moorland heathlands Invertebrates issues and policy land use change landscapes linear models Markvetenskap Mesostigmata microhabitats Mites Moorlands multidimensional scaling Oribatida rain Responses to habitat alteration and loss Sarcoptiformes Scotland Soil composition Soil ecology Soil microorganisms soil pH Soil properties Soil Science Synecology Vegetation Woodlands |
| Title | influence of vegetation type, soil properties and precipitation on the composition of soil mite and microbial communities at the landscape scale |
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