Inter-relationships between standing crop, biodiversity and trait attributes of hydrophytic vegetation in artificial waterways
1. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes. 2. The standing crop and species...
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Published in | Freshwater biology Vol. 46; no. 7; pp. 883 - 902 |
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Main Authors | , , |
Format | Journal Article |
Language | English |
Published |
Oxford UK
Blackwell Science Ltd
01.07.2001
Blackwell Science |
Subjects | |
Online Access | Get full text |
ISSN | 0046-5070 1365-2427 |
DOI | 10.1046/j.1365-2427.2001.00722.x |
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Abstract | 1. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes.
2. The standing crop and species composition of aquatic plants were measured in summer at 396 sites distributed randomly over the canal network. We also quantified the number of rare species and ‘attribute groups’ (groups of species sharing similar suites of biological traits). These data were analysed in relation to standing crop, assumed to indicate a disturbance gradient.
3. Consistent with unimodal models and the Intermediate Disturbance Hypothesis, maximum hydrophyte species richness occurred at an intermediate biomass (50–200 g DWm−2). This corresponded to a low frequency of low magnitude disturbance (light boat traffic) on navigable sections, or occasional high magnitude disturbance (the post‐interventionist phase) on sections currently unnavigable and subject to active vegetation management. The frequency of rare species was also the greatest under these conditions, reflecting the availability of regeneration niches.
4. Sorting of species into attribute groups revealed that the overall relationship between species richness and standing crop comprised of closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation of Potamogeton pectinatus, together with greater representation of filamentous algae, lemnids and elodeids with increasing standing crop (i.e. assumed low disturbance). High species richness was associated with the overlap of functionally different groups of species, rather than with disturbance‐mediated coexistence of functionally similar plants.
5. The analysis of a matrix of sites and the representation of plant traits weighted by the biomass of species that displayed them, in relation to different aspects of disturbance, highlighted a shift from traits associated with resilience (turions, unanchored floating or submerged leaves, low body flexibility, budding, small body size), or competitiveness (entire leaves, low reproductive output, high biomass density, large body size) at high standing crop, through to attributes more associated with resistance to disturbance (rhizomes, tubers, streamlining of foliage, low biomass density) at low standing crop.
6. Comparison with a stochastic null model of change in species number along a constrained gradient, after correction for variation in sampling effort, indicated that sites towards the tails of the gradient (excluding those with extremely low biomass) supported more species than might be expected from chance alone, while the most species‐rich sites in mid‐gradient generally supported many fewer species than expected.
7. We suggest that a disturbance regime that maintains intermediate standing crops would be appropriate for the conservation of species‐rich aquatic vegetation. Precise definition of this regime, under a range of circumstances, requires the study of temporal change at representative sites. |
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AbstractList | Summer biomass and species composition of aquatic plants were assessed at 396 sites in the UK's extensive canal network. Numbers of rare species and <">attribute groups<"> (i.e., groups of species with similar biological traits) were also recorded. Total species richness and the number of rare species were greatest at an intermediate biomass (50200 g dry weight/m super(2)). Intermediate biomass occurred in navigable sections with low-frequency, low-intensity disturbances (i.e., light boat traffic) and in unnavigable sections at mid-successional stages following intensive vegetation management. The relationship between species richness and biomass reflected closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation cover of Potamogeton pectinatus, and an increasing representation of filamentous algae, lemnids, and eloideids with increasing biomass. High species richness was associated with an overlap of functionally different species groups rather than with disturbance-mediated coexistence of functionally similar species. At high biomass, plant traits associated with resilience or competitiveness predominated, whereas at low biomass, traits associated with resistance to disturbance were more common. Aquatic-plant conservation implications are discussed. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes. The standing crop and species composition of aquatic plants were measured in summer at 396 sites distributed randomly over the canal network. The number of rare species and "attribute groups" (groups of species sharing similar suites of biological traits) were also quantified. These data were analysed in relation to standing crop, assumed to indicate a disturbance gradient. Consistent with unimodal models and the Intermediate Disturbance Hypothesis, maximum hydrophyte species richness occurred at an intermediate biomass (50-200 g DWm super(-2)). This corresponded to a low frequency of low magnitude disturbance (light boat traffic) on navigable sections, or occasional high magnitude disturbance (the post-interventionist phase) on sections currently unnavigable and subject to active vegetation management. The frequency of rare species was also greatest under these conditions, reflecting the availability of regeneration niches. Sorting of species into attribute groups revealed that the overall relationship between species richness and standing crop comprised of closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation of Potamogeton pectinatus, together with greater representation of filamentous algae, lemnids and elodeids with increasing standing crop (i.e. assumed low disturbance). High species richness was associated with the overlap of functionally different groups of species, rather than with disturbance-mediated coexistence of functionally similar plants. The analysis of a matrix of sites and the representation of plant traits weighted by the biomass of species that displayed them, in relation to different aspects of disturbance, highlighted a shift from traits associated with resilience (turions, unanchored floating or submerged leaves, low body flexibility, budding, small body size), or competitiveness (entire leaves, low reproductive output, high biomass density, large body size) at high standing crop, through to attributes more associated with resistance to disturbance (rhizomes, tubers, streamlining of foliage, low biomass density) at low standing crop. 1. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes. 2. The standing crop and species composition of aquatic plants were measured in summer at 396 sites distributed randomly over the canal network. We also quantified the number of rare species and ‘attribute groups’ (groups of species sharing similar suites of biological traits). These data were analysed in relation to standing crop, assumed to indicate a disturbance gradient. 3. Consistent with unimodal models and the Intermediate Disturbance Hypothesis, maximum hydrophyte species richness occurred at an intermediate biomass (50–200 g DWm −2 ). This corresponded to a low frequency of low magnitude disturbance (light boat traffic) on navigable sections, or occasional high magnitude disturbance (the post‐interventionist phase) on sections currently unnavigable and subject to active vegetation management. The frequency of rare species was also the greatest under these conditions, reflecting the availability of regeneration niches. 4. Sorting of species into attribute groups revealed that the overall relationship between species richness and standing crop comprised of closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation of Potamogeton pectinatus , together with greater representation of filamentous algae, lemnids and elodeids with increasing standing crop (i.e. assumed low disturbance). High species richness was associated with the overlap of functionally different groups of species, rather than with disturbance‐mediated coexistence of functionally similar plants. 5. The analysis of a matrix of sites and the representation of plant traits weighted by the biomass of species that displayed them, in relation to different aspects of disturbance, highlighted a shift from traits associated with resilience (turions, unanchored floating or submerged leaves, low body flexibility, budding, small body size), or competitiveness (entire leaves, low reproductive output, high biomass density, large body size) at high standing crop, through to attributes more associated with resistance to disturbance (rhizomes, tubers, streamlining of foliage, low biomass density) at low standing crop. 6. Comparison with a stochastic null model of change in species number along a constrained gradient, after correction for variation in sampling effort, indicated that sites towards the tails of the gradient (excluding those with extremely low biomass) supported more species than might be expected from chance alone, while the most species‐rich sites in mid‐gradient generally supported many fewer species than expected. 7. We suggest that a disturbance regime that maintains intermediate standing crops would be appropriate for the conservation of species‐rich aquatic vegetation. Precise definition of this regime, under a range of circumstances, requires the study of temporal change at representative sites. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes. The standing crop and species composition of aquatic plants were measured in summer at 396 sites distributed randomly over the canal network. The number of rare species and "attribute groups" (groups of species sharing similar suites of biological traits) were also quantified. These data were analysed in relation to standing crop, assumed to indicate a disturbance gradient. Consistent with unimodal models and the Intermediate Disturbance Hypothesis, maximum hydrophyte species richness occurred at an intermediate biomass (50-200 g DWm super(-2)). This corresponded to a low frequency of low magnitude disturbance (light boat traffic) on navigable sections, or occasional high magnitude disturbance (the post-interventionist phase) on sections currently unnavigable and subject to active vegetation management. The frequency of rare species was also greatest under these conditions, reflecting the availability of regeneration niches. Sorting of species into attribute groups revealed that the overall relationship between species richness and standing crop comprised of closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation of Potamogeton pectinatus, together with greater representation of filamentous algae, lemnids and elodeids with increasing standing crop (i.e. assumed low disturbance). High species richness was associated with the overlap of functionally different groups of species, rather than with disturbance-mediated coexistence of functionally similar plants. The analysis of a matrix of sites and the representation of plant traits weighted by the biomass of species that displayed them, in relation to different aspects of disturbance, highlighted a shift from traits associated with resilience (turions, unanchored floating or submerged leaves, low body flexibility, budding, small body size), or competitiveness (entire leaves, low reproductive output, high biomass density, large body size) at high standing crop, through to attributes more associated with resistance to disturbance (rhizomes, tubers, streamlining of foliage, low biomass density) at low standing crop. Comparison with a stochastic null model of change in species number along a constrained gradient, after correction for variation in sampling effort, indicated that sites towards the tails of the gradient (excluding those with extremely low biomass) supported more species than might be expected from chance alone, while the most species-rich sites in mid-gradient generally supported many fewer species than expected. It is suggested that a disturbance regime that maintains intermediate standing crops would be appropriate for the conservation of species-rich aquatic vegetation. Precise definition of this regime, under a range of circumstances, requires the study of temporal change at representative sites. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes. The standing crop and species composition of aquatic plants were measured in summer at 396 sites distributed randomly over the canal network. We also quantified the number of rare species and 'attribute groups' (groups of species sharing similar suites of biological traits). These data were analysed in relation to standing crop, assumed to indicate a disturbance gradient. Consistent with unimodal models and the Intermediate Disturbance Hypothesis, maximum hydrophyte species richness occurred at an intermediate biomass (50-200 g DWm super(-2)). This corresponded to a low frequency of low magnitude disturbance (light boat traffic) on navigable sections, or occasional high magnitude disturbance (the post-interventionist phase) on sections currently unnavigable and subject to active vegetation management. The frequency of rare species was also the greatest under these conditions, reflecting the availability of regeneration niches. Sorting of species into attribute groups revealed that the overall relationship between species richness and standing crop comprised of closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation of Potamogeton pectinatus, together with greater representation of filamentous algae, lemnids and elodeids with increasing standing crop (i. e. assumed low disturbance). High species richness was associated with the overlap of functionally different groups of species, rather than with disturbance-mediated coexistence of functionally similar plants. The analysis of a matrix of sites and the representation of plant traits weighted by the biomass of species that displayed them, in relation to different aspects of disturbance, highlighted a shift from traits associated with resilience (turions, unanchored floating or submerged leaves, low body flexibility, budding, small body size), or competitiveness (entire leaves, low reproductive output, high biomass density, large body size) at high standing crop, through to attributes more associated with resistance to disturbance (rhizomes, tubers, streamlining of foliage, low biomass density) at low standing crop. Comparison with a stochastic null model of change in species number along a constrained gradient, after correction for variation in sampling effort, indicated that sites towards the tails of the gradient (excluding those with extremely low biomass) supported more species than might be expected from chance alone, while the most species-rich sites in mid-gradient generally supported many fewer species than expected. We suggest that a disturbance regime that maintains intermediate standing crops would be appropriate for the conservation of species-rich aquatic vegetation. Precise definition of this regime, under a range of circumstances, requires the study of temporal change at representative sites. 1. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying relationships between disturbance intensity (largely from boat traffic) and communities of aquatic macrophytes. 2. The standing crop and species composition of aquatic plants were measured in summer at 396 sites distributed randomly over the canal network. We also quantified the number of rare species and ‘attribute groups’ (groups of species sharing similar suites of biological traits). These data were analysed in relation to standing crop, assumed to indicate a disturbance gradient. 3. Consistent with unimodal models and the Intermediate Disturbance Hypothesis, maximum hydrophyte species richness occurred at an intermediate biomass (50–200 g DWm−2). This corresponded to a low frequency of low magnitude disturbance (light boat traffic) on navigable sections, or occasional high magnitude disturbance (the post‐interventionist phase) on sections currently unnavigable and subject to active vegetation management. The frequency of rare species was also the greatest under these conditions, reflecting the availability of regeneration niches. 4. Sorting of species into attribute groups revealed that the overall relationship between species richness and standing crop comprised of closely overlapping unimodal responses of nine attribute groups, superimposed on a core vegetation of Potamogeton pectinatus, together with greater representation of filamentous algae, lemnids and elodeids with increasing standing crop (i.e. assumed low disturbance). High species richness was associated with the overlap of functionally different groups of species, rather than with disturbance‐mediated coexistence of functionally similar plants. 5. The analysis of a matrix of sites and the representation of plant traits weighted by the biomass of species that displayed them, in relation to different aspects of disturbance, highlighted a shift from traits associated with resilience (turions, unanchored floating or submerged leaves, low body flexibility, budding, small body size), or competitiveness (entire leaves, low reproductive output, high biomass density, large body size) at high standing crop, through to attributes more associated with resistance to disturbance (rhizomes, tubers, streamlining of foliage, low biomass density) at low standing crop. 6. Comparison with a stochastic null model of change in species number along a constrained gradient, after correction for variation in sampling effort, indicated that sites towards the tails of the gradient (excluding those with extremely low biomass) supported more species than might be expected from chance alone, while the most species‐rich sites in mid‐gradient generally supported many fewer species than expected. 7. We suggest that a disturbance regime that maintains intermediate standing crops would be appropriate for the conservation of species‐rich aquatic vegetation. Precise definition of this regime, under a range of circumstances, requires the study of temporal change at representative sites. |
Author | Pygott Eaton Willby, Nigel J. |
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(1993) Factors limiting the distribution of submerged waterplants in the lowland River Vecht (The Netherlands). Freshwater Biology, 30, 147-157. Connell J.H. (1978) Diversity in tropical rain forests and coral reefs. Science, 199, 1302-1309. Richards A.J. & Blakemore J. (1975) Factors affecting the germination of turions in Hydrocharis morus-ranae L. Watsonia, 10, 273-275. Grime J.P. (1973) Competitive exclusion in herbaceous vegetation. Nature, 242, 344-347. Wilson J.B. (1994) The intermediate disturbance hypothesis of species coexistence is based on patch dynamics. New Zealand Journal of Ecology, 18, 176-181. Al-Mufti M.M., Sydes C.L., Furness S.B., Grime J.P., Band S.R. (1977) A quantitative analysis of shoot phenology and dominance in herbaceous vegetation. Journal of Ecology, 65, 759-791. Grime J.P. (1997) Biodiversity and ecosystem function: the debate deepens. Science, 277, 1260-1261.DOI: 10.1126/science.277.5330.1260 Wiegleb G., Brux H., Herr W. (1991) Human impact on the ecological performance of Potamogeton species in Northern Germany. Vegetatio, 97, 161-172. Henry C.P., Amoros C., Bornette G. (1996) Species traits and recolonisation processes after flood disturbances in riverine macrophytes. Vegetatio, 122, 13-27. Wilson S.D. & Keddy P.A. (1988) Species richness, survivorship and biomass accumulation along an environmental gradient. Oikos, 53, 375-380. Garcia L.V., Maranon T., Moreno A., Clemente L. (1993) Above-ground biomass and species richness in a Mediterranean salt marsh. Journal of Vegetation Science, 4, 417-424. Gough L., Grace J.B., Taylor K.L. (1994) The relationship between species richness and community biomass: the importance of environmental variables. Oikos, 70, 271-279. Briggs J.D. (1996) Canals - wildlife value and restoration issues. British Wildlife, 7, 365-377. Oksanen J. (1996) Is the humped relationship between species richness and biomass an artifact due to plot size? Journal of Ecology, 84, 293-295. Murphy K.J., Hanbury R.G., Eaton J.W. (1981) The ecological effects of 2-methylthio triazine herbicides used for aquatic weed control in navigable canals. I. Effects on aquatic flora and water chemistry. Archiv fü r Hydrobiologie, 91, 294-331. Huston M.A. (1979) A general hypothesis of species diversity. American Naturalist, 113, 81-101. Willby N.J. & Eaton J.W. (1996) Backwater habitats and their role in nature conservation on navigable waterways. Hydrobiologia, 340, 333-338. Wade P.M. & Edwards R.W. (1980) The effect of channel maintenance on the aquatic macrophytes of the drainage channels of the Monmouthshire Levels, South Wales 1840-1976. Aquatic Botany, 8, 307-322. Barrat-Segretain M.H. & Amoros C. (1996) Recolonization of cleared patches by riverine macrophytes: investigation on the border effect. Journal of Vegetation Science, 7, 769-776. Van der Steen W.J. & Scholten M. (1985) Methodological problems in evolutionary biology. IV. Stress and stress tolerance, an exercise in definitions. Acta Biotheoretica, 34, 81-90. Thomas G.J., Allen D.A., Grose M.P.B. (1981) The demography and flora of the Ouse Washes, England. Biological Conservation, 21, 197-229. Duarte C.M. & Roff D.A. (1991) Architectural and life history constraints to submersed macrophyte community structure: a simulation study. Aquatic Botany, 42, 15-29. Abrams P.A. (1995) Monotonic or unimodal diversity-productivity gradients: what does competition theory predict? Ecology, 76, 2019-2027. Grubb P.J. (1977) The maintenance of species-richness in plant communities: the importance of the regeneration niche. Biological Review, 52, 107-145. Twigg H. (1959) Freshwater studies in the Shropshire Union Canal. Field Studies, 1, 116-242. Toivonen H. & Huttunen P. (1995) Aquatic macrophytes and ecological gradients in 57 small lakes in southern Finland. Aquatic Botany, 51, 197-221.DOI: 10.1016/0304-3770(95)00458-c Lawton J.H. (1998) Are there general laws in ecology? Oikos, 84, 177-192. Willby N.J. & Eaton J.W. (1993) The distribution, ecology and conservation of Luronium natans (L.) Raf. in Britain. Journal of Aquatic Plant Management, 31, 70-76. Van Wijk R.J. & Trompenaars H.J.A.J. (1985) On the germination of turions and the life cycle of Potamogeton trichoides Cham. Et Schld. Aquatic Botany, 22, 165-172. Greulich S. & Bornette G. (1999) Competitive abilities and related strategies in four aquatic plant species from an intermediately disturbed habitat. Freshwater Biology, 41, 493-506.DOI: 10.1046/j.1365-2427.1999.00395.x Byfield A. (1990) The Basingstoke canal. British Wildlife, 2, 13-21. Death R.G. & Winterbourn M.J. (1994) Environmental stability and community persistence - a multivariate perspective. Journal of the North American Benthological Society, 13, 125-139. Connor E.F. & McCoy E.D. (1979) The statistics and biology of the species-area relationship. American Naturalist, 113, 791-833. Murphy K.J., Fox A.M., Hanbury R.G. (1987) A multivariate assessment of plant management impacts on macrophyte communities in a Scottish canal. Journal of Applied Ecology, 24, 1063-1079. Stevens M.H.H. & Carson W.P. (1999) Plant density determines species richness along an experimental fertility gradient. Ecology, 80, 455-465. Willby N.J., Abernethy V.J., Demars B.O.L. (2000) An attribute-based classification of European hydrophytes and its relationship to habitat utilisation. Freshwater Biology, 43, 43-74.DOI: 10.1046/j.1365-2427.2000.00523.x Suren A.M. & Duncan M.J. (1999) Rolling stones and mosses: effects of substrate stability on bryophyte communities in streams. Journal of the North American Benthological Society, 18, 457-467. Bornette G. & Amoros C. (1996) Disturbance regimes and vegetation dynamics: role of floods in riverine wetlands. 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Et Schld publication-title: Aquatic Botany – volume: 39 start-page: 173 year: 1991 end-page: 193 article-title: Principal determinants of aquatic macrophyte richness in northern European lakes publication-title: Aquatic Botany – volume: 4 start-page: 417 year: 1993 end-page: 424 article-title: Above‐ground biomass and species richness in a Mediterranean salt marsh publication-title: Journal of Vegetation Science – volume: 69 start-page: 476 year: 1994 end-page: 498 article-title: A functional group approach to the structure of algal dominated communities publication-title: Oikos – volume: 111 start-page: 1169 year: 1977 end-page: 1194 article-title: Evidence for the existence of three primary strategies in plants and its relevance to ecological and evolutionary theory publication-title: American Naturalist – volume: 51 start-page: 197 year: 1995 end-page: 221 article-title: Aquatic macrophytes and ecological gradients in 57 small lakes in southern Finland publication-title: Aquatic Botany – volume: 31 start-page: 70 year: 1993 end-page: 76 article-title: The distribution, ecology and conservation of (L.) Raf. in Britain publication-title: Journal of Aquatic Plant Management – volume: 52 start-page: 107 year: 1977 end-page: 145 article-title: The maintenance of species‐richness in plant communities: the importance of the regeneration niche publication-title: Biological Review – volume: 24 start-page: 1063 year: 1987 end-page: 1079 article-title: A multivariate assessment of plant management impacts on macrophyte communities in a Scottish canal publication-title: Journal of Applied Ecology – volume: 112 start-page: 57 year: 1994 end-page: 72 article-title: The impact of mechanical harvesting regime on the aquatic and shore vegetation in water courses of aquatic areas of the Netherlands publication-title: Vegetatio – year: 1980 – year: 1967 – volume: 76 start-page: 2019 year: 1995 end-page: 2027 article-title: Monotonic or unimodal diversity‐productivity gradients: what does competition theory predict? publication-title: Ecology – year: 1988 – volume: 84 start-page: 293 year: 1996 end-page: 295 article-title: Is the humped relationship between species richness and biomass an artifact due to plot size? publication-title: Journal of Ecology – volume: 34 start-page: 81 year: 1985 end-page: 90 article-title: Methodological problems in evolutionary biology. IV. 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Snippet | 1. The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying... Summer biomass and species composition of aquatic plants were assessed at 396 sites in the UK's extensive canal network. Numbers of rare species and... The extensive British canal system potentially provides a favourable habitat for aquatic plants and, because of its uniformity, it is ideal for studying... |
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SubjectTerms | Animal and plant ecology Animal, plant and microbial ecology aquatic plant Biological and medical sciences conservation disturbance Fresh water ecosystems Freshwater Fundamental and applied biological sciences. Psychology hump-backed models management Synecology |
Title | Inter-relationships between standing crop, biodiversity and trait attributes of hydrophytic vegetation in artificial waterways |
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