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 inFreshwater biology Vol. 46; no. 7; pp. 883 - 902
Main Authors Willby, Nigel J., Pygott, Eaton
Format Journal Article
LanguageEnglish
Published Oxford UK Blackwell Science Ltd 01.07.2001
Blackwell Science
Subjects
Online AccessGet full text
ISSN0046-5070
1365-2427
DOI10.1046/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.
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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  surname: Eaton
  fullname: Eaton
  organization: School of Biological Sciences, University of Liverpool, Liverpool, U.K
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Models
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Biodiversity
Environmental management
Species richness
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Blackwell Science
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– name: Blackwell Science
References Carpenter S.R. & McCreary N.J. (1985) Effects of fish nests on pattern and zonation of submersed vegetation in a softwater lake. Aquatic Botany, 22, 21-32.
Willig M.R. & Lyons S.K. (1998) An analytical model of latitudinal gradients of species richness with an empirical test for marsupials and bats in the New World. Oikos, 81, 93-98.
Barrat-Segretain M.H., Bornette G., HeringVilasBoas A. (1998) Comparative abilities of vegetative regeneration among aquatic plants growing in disturbed habitats. Aquatic Botany, 60, 201-211.DOI: 10.1016/s0304-3770(97)00091-0
Henry C.P. & Amoros C. (1996) Are the banks a source of recolonization after disturbance: an experiment on aquatic vegetation in a former channel of the Rhône River. Hydrobiologia, 330, 151-162.
Janes R.A., Eaton J.W., Hardwick K. (1996) The effects of floating mats of Azolla filiculoides Lam. & Lemna minuta Kunth on the growth of submerged macrophytes. Hydrobiologia, 340, 23-26.
Murphy K.J. & Eaton J.W. (1983) Effects of pleasure-boat traffic on macrophyte growth in canals. Journal of Applied Ecology, 20, 713-729.
Muotka T. & Virtanen R. (1995) The stream as a habitat templet for bryophytes: species distributions along gradients in disturbance and substratum heterogeneity. Freshwater Biology, 33, 141-160.
Grime J.P. (1977) Evidence for the existence of three primary strategies in plants and its relevance to ecological and evolutionary theory. American Naturalist, 111, 1169-1194.
Rørslett B. (1991) Principal determinants of aquatic macrophyte richness in northern European lakes. Aquatic Botany, 39, 173-193.
Best E.P.H. (1994) The impact of mechanical harvesting regime on the aquatic and shore vegetation in water courses of aquatic areas of the Netherlands. Vegetatio, 112, 57-72.
Steneck R.S. & Dethier M.N. (1994) A functional group approach to the structure of algal dominated communities. Oikos, 69, 476-498.
Vermaat J.E. & De Bruyne R.J. (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. Journal of Vegetation Science, 7, 615-622.
1981; 91
2000; 43
1991; 97
1995; 33
1995; 76
1997; 277
1976
1994; 69
1998; 81
1977; 65
1999; 41
1996; 340
1975; 10
1985; 22
1998; 84
1999; 80
1959; 1
1993; 4
1979
1979; 113
1999; 18
1991; 42
1993; 31
1993; 30
1983; 20
1986
1985
1996; 330
1982
1981
1980
1994; 70
1905
1996; 7
1988
1994; 112
1995; 51
1991; 39
1973; 242
1998
1997
1978; 199
1995
1996; 122
1994
1993
1998; 60
1991
1988; 53
1981; 21
1987; 24
1990; 2
1980; 8
1994; 13
1977; 52
1996; 84
1994; 18
1977; 111
1985; 34
1967
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Wilson J.B. (e_1_2_6_69_2) 1994; 18
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Richards A.J. (e_1_2_6_46_2) 1975; 10
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Byfield A. (e_1_2_6_10_2) 1990; 2
Twigg H. (e_1_2_6_57_2) 1959; 1
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Willby N.J. (e_1_2_6_65_2) 1993; 31
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Murphy K.J. (e_1_2_6_36_2) 1981; 91
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Briggs J.D. (e_1_2_6_9_2) 1996; 7
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References_xml – reference: Wiegleb G., Brux H., Herr W. (1991) Human impact on the ecological performance of Potamogeton species in Northern Germany. Vegetatio, 97, 161-172.
– reference: 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
– reference: Grime J.P. (1997) Biodiversity and ecosystem function: the debate deepens. Science, 277, 1260-1261.DOI: 10.1126/science.277.5330.1260
– reference: Lawton J.H. (1998) Are there general laws in ecology? Oikos, 84, 177-192.
– reference: Twigg H. (1959) Freshwater studies in the Shropshire Union Canal. Field Studies, 1, 116-242.
– reference: 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.
– reference: Henry C.P. & Amoros C. (1996) Are the banks a source of recolonization after disturbance: an experiment on aquatic vegetation in a former channel of the Rhône River. Hydrobiologia, 330, 151-162.
– reference: Carpenter S.R. & McCreary N.J. (1985) Effects of fish nests on pattern and zonation of submersed vegetation in a softwater lake. Aquatic Botany, 22, 21-32.
– reference: Stevens M.H.H. & Carson W.P. (1999) Plant density determines species richness along an experimental fertility gradient. Ecology, 80, 455-465.
– reference: Henry C.P., Amoros C., Bornette G. (1996) Species traits and recolonisation processes after flood disturbances in riverine macrophytes. Vegetatio, 122, 13-27.
– reference: Huston M.A. (1979) A general hypothesis of species diversity. American Naturalist, 113, 81-101.
– reference: 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
– reference: Muotka T. & Virtanen R. (1995) The stream as a habitat templet for bryophytes: species distributions along gradients in disturbance and substratum heterogeneity. Freshwater Biology, 33, 141-160.
– reference: Vermaat J.E. & De Bruyne R.J. (1993) Factors limiting the distribution of submerged waterplants in the lowland River Vecht (The Netherlands). Freshwater Biology, 30, 147-157.
– reference: Steneck R.S. & Dethier M.N. (1994) A functional group approach to the structure of algal dominated communities. Oikos, 69, 476-498.
– reference: Briggs J.D. (1996) Canals - wildlife value and restoration issues. British Wildlife, 7, 365-377.
– reference: Barrat-Segretain M.H., Bornette G., HeringVilasBoas A. (1998) Comparative abilities of vegetative regeneration among aquatic plants growing in disturbed habitats. Aquatic Botany, 60, 201-211.DOI: 10.1016/s0304-3770(97)00091-0
– reference: 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.
– reference: 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.
– reference: Oksanen J. (1996) Is the humped relationship between species richness and biomass an artifact due to plot size? Journal of Ecology, 84, 293-295.
– reference: Rørslett B. (1991) Principal determinants of aquatic macrophyte richness in northern European lakes. Aquatic Botany, 39, 173-193.
– reference: Grime J.P. (1973) Competitive exclusion in herbaceous vegetation. Nature, 242, 344-347.
– reference: 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.
– reference: 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.
– reference: Connor E.F. & McCoy E.D. (1979) The statistics and biology of the species-area relationship. American Naturalist, 113, 791-833.
– reference: 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.
– reference: Grubb P.J. (1977) The maintenance of species-richness in plant communities: the importance of the regeneration niche. Biological Review, 52, 107-145.
– reference: Willig M.R. & Lyons S.K. (1998) An analytical model of latitudinal gradients of species richness with an empirical test for marsupials and bats in the New World. Oikos, 81, 93-98.
– reference: Abrams P.A. (1995) Monotonic or unimodal diversity-productivity gradients: what does competition theory predict? Ecology, 76, 2019-2027.
– reference: 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.
– reference: 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.
– reference: 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.
– reference: Janes R.A., Eaton J.W., Hardwick K. (1996) The effects of floating mats of Azolla filiculoides Lam. & Lemna minuta Kunth on the growth of submerged macrophytes. Hydrobiologia, 340, 23-26.
– reference: Connell J.H. (1978) Diversity in tropical rain forests and coral reefs. Science, 199, 1302-1309.
– reference: Richards A.J. & Blakemore J. (1975) Factors affecting the germination of turions in Hydrocharis morus-ranae L. Watsonia, 10, 273-275.
– reference: Bornette G. & Amoros C. (1996) Disturbance regimes and vegetation dynamics: role of floods in riverine wetlands. Journal of Vegetation Science, 7, 615-622.
– reference: Wilson S.D. & Keddy P.A. (1988) Species richness, survivorship and biomass accumulation along an environmental gradient. Oikos, 53, 375-380.
– reference: 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.
– reference: Murphy K.J. & Eaton J.W. (1983) Effects of pleasure-boat traffic on macrophyte growth in canals. Journal of Applied Ecology, 20, 713-729.
– reference: 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
– reference: Wilson J.B. (1994) The intermediate disturbance hypothesis of species coexistence is based on patch dynamics. New Zealand Journal of Ecology, 18, 176-181.
– reference: Byfield A. (1990) The Basingstoke canal. British Wildlife, 2, 13-21.
– reference: 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.
– reference: 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.
– reference: Best E.P.H. (1994) The impact of mechanical harvesting regime on the aquatic and shore vegetation in water courses of aquatic areas of the Netherlands. Vegetatio, 112, 57-72.
– reference: Willby N.J. & Eaton J.W. (1996) Backwater habitats and their role in nature conservation on navigable waterways. Hydrobiologia, 340, 333-338.
– reference: 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.
– reference: Grime J.P. (1977) Evidence for the existence of three primary strategies in plants and its relevance to ecological and evolutionary theory. American Naturalist, 111, 1169-1194.
– reference: 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.
– year: 1985
– year: 1981
– volume: 13
  start-page: 125
  year: 1994
  end-page: 139
  article-title: Environmental stability and community persistence – a multivariate perspective
  publication-title: Journal of the North American Benthological Society
– volume: 65
  start-page: 759
  year: 1977
  end-page: 791
  article-title: A quantitative analysis of shoot phenology and dominance in herbaceous vegetation
  publication-title: Journal of Ecology
– volume: 30
  start-page: 147
  year: 1993
  end-page: 157
  article-title: Factors limiting the distribution of submerged waterplants in the lowland River Vecht (The Netherlands)
  publication-title: Freshwater Biology
– volume: 7
  start-page: 365
  year: 1996
  end-page: 377
  article-title: Canals – wildlife value and restoration issues
  publication-title: British Wildlife
– volume: 340
  start-page: 333
  year: 1996
  end-page: 338
  article-title: Backwater habitats and their role in nature conservation on navigable waterways
  publication-title: Hydrobiologia
– volume: 21
  start-page: 197
  year: 1981
  end-page: 229
  article-title: The demography and flora of the Ouse Washes, England
  publication-title: Biological Conservation
– volume: 81
  start-page: 93
  year: 1998
  end-page: 98
  article-title: An analytical model of latitudinal gradients of species richness with an empirical test for marsupials and bats in the New World
  publication-title: Oikos
– year: 1979
– volume: 97
  start-page: 161
  year: 1991
  end-page: 172
  article-title: Human impact on the ecological performance of species in Northern Germany
  publication-title: Vegetatio
– volume: 242
  start-page: 344
  year: 1973
  end-page: 347
  article-title: Competitive exclusion in herbaceous vegetation
  publication-title: Nature
– volume: 1
  start-page: 116
  year: 1959
  end-page: 242
  article-title: Freshwater studies in the Shropshire Union Canal
  publication-title: Field Studies
– year: 1994
– volume: 10
  start-page: 273
  year: 1975
  end-page: 275
  article-title: Factors affecting the germination of turions in L
  publication-title: Watsonia
– year: 1998
– volume: 43
  start-page: 43
  year: 2000
  end-page: 74
  article-title: An attribute‐based classification of European hydrophytes and its relationship to habitat utilisation
  publication-title: Freshwater Biology
– year: 1986
– volume: 199
  start-page: 1302
  year: 1978
  end-page: 1309
  article-title: Diversity in tropical rain forests and coral reefs
  publication-title: Science
– volume: 22
  start-page: 21
  year: 1985
  end-page: 32
  article-title: Effects of fish nests on pattern and zonation of submersed vegetation in a softwater lake
  publication-title: Aquatic Botany
– year: 1982
– year: 1997
– volume: 53
  start-page: 375
  year: 1988
  end-page: 380
  article-title: Species richness, survivorship and biomass accumulation along an environmental gradient
  publication-title: Oikos
– volume: 18
  start-page: 457
  year: 1999
  end-page: 467
  article-title: Rolling stones and mosses: effects of substrate stability on bryophyte communities in streams
  publication-title: Journal of the North American Benthological Society
– volume: 7
  start-page: 769
  year: 1996
  end-page: 776
  article-title: Recolonization of cleared patches by riverine macrophytes: investigation on the border effect
  publication-title: Journal of Vegetation Science
– volume: 84
  start-page: 177
  year: 1998
  end-page: 192
  article-title: Are there general laws in ecology?
  publication-title: Oikos
– volume: 80
  start-page: 455
  year: 1999
  end-page: 465
  article-title: Plant density determines species richness along an experimental fertility gradient
  publication-title: Ecology
– year: 1976
– year: 1993
– volume: 8
  start-page: 307
  year: 1980
  end-page: 322
  article-title: The effect of channel maintenance on the aquatic macrophytes of the drainage channels of the Monmouthshire Levels, South Wales 1840–1976
  publication-title: Aquatic Botany
– volume: 41
  start-page: 493
  year: 1999
  end-page: 506
  article-title: Competitive abilities and related strategies in four aquatic plant species from an intermediately disturbed habitat
  publication-title: Freshwater Biology
– volume: 20
  start-page: 713
  year: 1983
  end-page: 729
  article-title: Effects of pleasure‐boat traffic on macrophyte growth in canals
  publication-title: Journal of Applied Ecology
– volume: 60
  start-page: 201
  year: 1998
  end-page: 211
  article-title: Comparative abilities of vegetative regeneration among aquatic plants growing in disturbed habitats
  publication-title: Aquatic Botany
– volume: 277
  start-page: 1260
  year: 1997
  end-page: 1261
  article-title: Biodiversity and ecosystem function: the debate deepens
  publication-title: Science
– volume: 340
  start-page: 23
  year: 1996
  end-page: 26
  article-title: The effects of floating mats of Lam. & Kunth on the growth of submerged macrophytes
  publication-title: Hydrobiologia
– volume: 122
  start-page: 13
  year: 1996
  end-page: 27
  article-title: Species traits and recolonisation processes after flood disturbances in riverine macrophytes
  publication-title: Vegetatio
– volume: 22
  start-page: 165
  year: 1985
  end-page: 172
  article-title: On the germination of turions and the life cycle of Cham. 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
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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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Volume 46
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