1
A novel application of the Urban River Survey Investigating physical habitat and biotic quality across Greater London Naresh B. Patel MSc Aquatic Resource Management 3. Research Aims Investigate relationship between physical habitat quality and biotic quality in Greater London’s urban rivers. Potentially validate a novel methodology using URS in conjunction to macroinvertebrate bio-indicators. References [1] Walsh, C., Roy, A., Feminella, J., Cottingham, P., Groffman, P. and Morgan, R. (2005) The urban stream syndrome: current knowledge and the search for a cure. Journal of the North American Benthological Society, 24(3), 706. [2] Vaughan, I., Diamond, M., Gurnell, A., Hall, K., Jenkins, A., Milner, N., Naylor, L., Sear, D., Woodward, G. and Ormerod, S. (2009) Integrating ecology with hydromorphology: a priority for river science and management. Aquatic Conservation: Marine and Freshwater Ecosystems, 19(1), 113-125. [3] Shuker, L. J., Gurnell, A. M. and Raco, M. (2011) Some simple tools for communicating the biophysical condition of urban rivers to support decision making in relation to river restoration. Urban Ecosystems, 15(2), 389-408. [4] Naura, M., Clark, M. J., Sear, D. A. and Carter, M. G. (2016) Mapping habitat indices across river networks using spatial statistical modelling of River Habitat Survey data. Ecological Indicators, 66, 20-29. [5] Langhans, S., Hermoso, V., Linke, S., Bunn, S. and Possingham, H. (2014) Cost-effective river rehabilitation planning: Optimizing for morphological benefits at large spatial scales. Journal of Environmental Management, 132, 296-303. 4. Methods 15 sites over 9 rivers selected (Figure 2). URS, macroinvertebrate kick-sample, water physio-chemistry assessed. Stretch Habitat Quality Index (SHQI) indicating physical habitat quality from 3 (Very Good) to 18 (Very Poor). Shannon Diversity Index (H) and BMWP scores indicating macroinvertebrate biotic quality. Phosphate analysis of water quality. 2. The Urban River Survey Urban specific EA-based river habitat survey (RHS) Hydromorphological quality and river restoration assessment [3] but untested in relation to biotic quality. 1. The Issue of Urban Rivers Engineering/modification for flood control, waste disposal and water abstraction objectives are often prioritised within densely populated areas with high levels of impervious surface cover (ISC) (Figure 1). Resulting “flashy” hydrologic regime, reduced rainwater absorption, urban pollution loading and degraded biotic richness is termed The Urban Stream Syndrome [1] Disjointed understanding between physical habitat and biotic quality limits ecological quality improvements [2] . Figure 1. The River Brent at Tokyngton Park (site A). 6. Management Implications Comprehensive, integrated monitoring and assessment towards EU WFD objectives. High resolution, continuous catchment mapping of London’s urban rivers [4] . More cost-effective targeting for physical habitat restoration or water quality improvements [5] . Citizen science and behavioural change applications via MoRPh survey. Naresh B. Patel, BSc (Hons) [email protected] [email protected] 07531246038 5. Results Strong negative relationships (r = -0.634, p<0.05) (r= -0.716, p<0.05) (Figure 3) indicated as urban river physical habitat improves an increase in biotic quality of macroinvertebrates is also observed (Figure 4). PCA specifically described bank-naturalness and in-channel heterogeneity across the 15 sites as strong predictors of biotic quality. Water quality influence also key within urban systems adding interaction complexity. Figure 4. Ewell Court Park, Hogsmill (site I). Figure 2. Map of study sites across Greater London.

WATERWISE POSTER

Embed Size (px)

Citation preview

Page 1: WATERWISE POSTER

A novel application of the Urban River Survey – Investigating physical habitat

and biotic quality across Greater London Naresh B. Patel MSc Aquatic Resource Management

3. Research Aims

• Investigate relationship between physical habitat quality and biotic quality in Greater London’s urban rivers.

• Potentially validate a novel methodology using URS in conjunction to macroinvertebrate bio-indicators.

References[1] Walsh, C., Roy, A., Feminella, J., Cottingham, P., Groffman, P. and Morgan, R. (2005) The urban stream syndrome: current knowledge and the search for a cure. Journal of the North American Benthological Society, 24(3), 706. [2] Vaughan, I., Diamond, M., Gurnell, A., Hall, K., Jenkins, A., Milner, N., Naylor, L., Sear, D., Woodward, G. and Ormerod, S. (2009) Integrating ecology with hydromorphology: a priority for river science and management. Aquatic Conservation: Marine and Freshwater Ecosystems, 19(1), 113-125.[3] Shuker, L. J., Gurnell, A. M. and Raco, M. (2011) Some simple tools for communicating the biophysical condition of urban rivers to support decision making in relation to river restoration. Urban Ecosystems, 15(2), 389-408. [4] Naura, M., Clark, M. J., Sear, D. A. and Carter, M. G. (2016) Mapping habitat indices across river networks using spatial statistical modelling of River Habitat Survey data. Ecological Indicators, 66, 20-29. [5]Langhans, S., Hermoso, V., Linke, S., Bunn, S. and Possingham, H. (2014) Cost-effective river rehabilitation planning: Optimizing for morphological benefits at large spatial scales. Journal of Environmental Management,

132, 296-303.

4. Methods

• 15 sites over 9 rivers selected (Figure 2).

• URS, macroinvertebrate kick-sample, water physio-chemistry assessed.

• Stretch Habitat Quality Index (SHQI) indicating physical habitat quality from 3 (Very Good) to 18 (Very Poor).

• Shannon Diversity Index (H) and BMWP scores indicating macroinvertebrate biotic quality. Phosphate analysis of water quality.

2. The Urban River Survey

• Urban specific EA-based river habitat survey (RHS)

• Hydromorphological quality and river restoration assessment[3] but untested in relation to biotic quality.

1. The Issue of Urban Rivers

• Engineering/modification for flood control, waste disposal and water abstraction objectives are often prioritised within densely populated areas with high levels of impervious surface cover (ISC) (Figure 1).

• Resulting “flashy” hydrologic regime, reduced rainwater absorption, urban pollution loading and degraded biotic richness is termed The Urban Stream Syndrome[1]

• Disjointed understanding between physical habitat and biotic quality limits ecological quality improvements[2].

Figure 1. The River Brent at TokyngtonPark (site A).

6. Management Implications

• Comprehensive, integrated monitoring and assessment towards EU WFD objectives.

• High resolution, continuous catchment mapping of London’s urban rivers[4].

• More cost-effective targeting for physical habitat restoration or water quality improvements[5].

• Citizen science and behavioural change applications via MoRPh survey.

Naresh B. Patel, BSc (Hons)[email protected] [email protected] 07531246038

5. Results

• Strong negative relationships (r = -0.634, p<0.05) (r= -0.716, p<0.05) (Figure 3) indicated as urban river physical habitat improves an increase in biotic quality of macroinvertebrates is also observed (Figure 4).

• PCA specifically described bank-naturalnessand in-channel heterogeneity across the 15 sites as strong predictors of biotic quality.

• Water quality influence also key within urban systems adding interaction complexity.

Figure 4. Ewell Court Park, Hogsmill (site I).

Figure 2. Map of study sites across Greater London.