WWW.DISSERTATION.XLIBX.INFO
FREE ELECTRONIC LIBRARY - Dissertations, online materials
 
<< HOME
CONTACTS



«Author names: S. M. Crooks Date: 2011 WATCH is an Integrated Project Funded by the European Commission under the Sixth Framework Programme, Global ...»

Technical Report No. 53

FLOOD STUDIES AT THE RIVER BASIN SCALE:

CASE STUDY OF THE THAMES AT KINGSTON (UK)

Author names: S. M. Crooks

Date: 2011

WATCH is an Integrated Project Funded by the European Commission under the Sixth Framework

Programme, Global Change and Ecosystems Thematic Priority Area (contract number: 036946).

The WATCH project started 01/02/2007 and will continue for 4 years.

Flood studies at the river basin scale: case study of the Thames at

Title:

Kingston (UK) S M Crooks

Authors:

Centre for Ecology and Hydrology

Organisations:

2011

Submission date:

This report is an output from Work Block 4; task 4.1 – 10b

Function:

WATCH deliverable 4.1.2 Deliverable Technical Report No. 53 -2-

1. Introduction The Thames catchment in Southern England was used as a test basin for modelling and testing of high flow extremes and floods. The catchment to the lowest gauging station has an area of 9948 km2 with an annual average rainfall of 719 mm (1961-1990). The mean annual naturalised flow (gauged flow adjusted for water usage) is 35% of the annual average rainfall (i.e. 65% of rainfall falling on the catchment is lost through evaporation). The river basin hydrological model used was CLASSIC (Crooks and Naden, 2007), which is applied on a grid-square framework. The model has three main modules for soil moisture, soil drainage and channel routing with a grid to outlet structure in which simulated runoff from each grid square is routed directly to the catchment outlet. The catchment boundary, main rivers, modelling grid boxes (20 km) and grid boxes for Watch Forcing Data (0.5 degree) are shown in Figure 1, together with a map showing the location of the Thames catchment within Great Britain.

Technical Report No. 53 -3- Kingston (gauging station) Figure 1 Catchment boundary for the River Thames to the lowest gauging station at Kingston; modelling grid boxes (20 km) are shown in red, Watch Forcing Data grid boxes (0.5 degree) in black. The map on the right shows the location of the Thames catchment within Great Britain.

Calibration of the model for the Thames is part of a two-stage procedure where a generalised method, developed for the whole of Great Britain using land use, soils and digital terrain databases is used initially, followed by fine tuning of the channel routing parameters to observed flow data. Objective Technical Report No. 53 -4functions used in calibration include water balance (seasonal, annual and overall volume error), NashSutcliffe efficiency (Nash and Sutcliffe, 1970), and fit of flow duration and flood frequency curves.

Climatic inputs of rainfall and potential evaporation (PE) are required for each grid square. The mean daily average rainfall for a grid square is calculated from observed point data with monthly PE data obtained from MORECS (Met Office Rainfall and Evaporation Calculation System, Thompson et al., 1982), which uses a modified form of the Penman-Monteith equations.

2. Modelling with Watch Forcing Data

CLASSIC was run using local data (observed rainfall and MORECS PE) and Watch Forcing Data (WFD) for 1961 to 2001 and results compared. To run CLASSIC with WFD, area weights were applied to translate from the 0.5 degree WFD grid boxes to the 20 km grid boxes. The same model calibration was used with both sets of data as recalibration is not appropriate with the generalised calibration method developed for CLASSIC. This allows direct comparison of the impact of using different input data.

Rainfall from WFD used combined data for rainfall and snow. Two sets of PE based on WFD data were used in the modelling: using Penman-Monteith equations (WFD_Pen-Mon) and using the equation developed by Oudin (Oudin et al., 2005) based on mean daily temperature and latitude (WFD_Oudin).

Oudin PE was also calculated using local observed temperature data but as there was very little difference between the Oudin PE values calculated with WFD or local temperature data only WFD_Oudin was used in the modelling. The impacts on the flow regime of using the different sets of input data on simulated flow are shown in Figure 2 (mean monthly input data and percentage difference on mean monthly flow), Figure 3 (flow duration curves), Figure 4 (flood frequency curves) and Figure 5 (average number of days per year above a flow threshold. Flood frequency is determined using a peaks-over-threshold method for an average of 3 peaks per year (POT3), Naden, 1993).

Figure 2, left, mean monthly rainfall and PE from local data and WFD: rainfall (solid lines), PE (dashed lines); local rainfall (black solid), WFD rainfall (red solid), local PE (black dashed), WFD_ Pen-Mon (red dashed), WFD_Oudin (green dashed).

Figure 2, right, percentage difference between observed mean monthly flow and modelled using different combinations of input data: using local rainfall (solid lines), using WFD rainfall (dashed lines);

local rainfall and local PE (black solid), WFD rainfall and local PE (black dashed); local rainfall and WFD_Pen-Mon (red solid), WFD rainfall and WFD Pen-Mon (red dashed); local rainfall and WFD_Oudin (green solid), WFD rainfall and WFD_Oudin (green dashed).





Figure 2, left, shows that there is little difference between average monthly local and WFD rainfall but some differences between the three PE methods. The three sets of lines in Figure 2, right, show that the comparatively small differences in PE from the three methods (MORECS, WFD_Pen-Mon and WFD_Oudin) generate differences between observed and modelled mean monthly flow of up to 40%.

The pattern of differences in flow reflects the relative differences between the sets of PE data.

Technical Report No. 53 -5WFD_Pen-Mon values are less than MORECS in all months, hence there is always a positive difference between modelled and observed flows. The continuous underestimate of WFD_Pen-Mon compared with MORECS results in the high percentage difference in mean monthly flow. The impact of the higher PE from WFD_Oudin, compared with MORECS, from June to August is evident in the negative difference between modelled and observed flows by October.

Figure 3 Flow duration curves (mean daily flow in m3s-1). Observed flow (thick black line), modelled with local rainfall and local PE (thin black), modelled with WFD rainfall and WFD_Pen-Mon (red), modelled with WFD rainfall and WFD_Oudin (green).

Figure 4 Flood peaks (POT3) and fitted flood frequency curves (mean daily flow in m3s-1). Observed flow (black crosses and thick black line), modelled with local rainfall and local PE (black circles and thin black line), modelled with WFD rainfall and WFD_Pen-Mon (red circles and red line), modelled with WFD rainfall and WFD_Oudin (green circles and green line).

–  –  –

Figures 3, 4 and 5 show that, for the Thames catchment, the different PE series impact on modelled flow rates across the flow range, including the simulation of flood peaks. Although it is likely that using data series other than those with which the model was calibrated will result in higher differences between modelled and observed, if the balance between seasonal rainfall and PE data is not realistic then recalibration will result in neither sensible values of model parameters nor good model performance.

Results presented in Figure 2 to Figure 5 show that:

 Observed (local) and WFD mean monthly rainfall data are very similar  PE calculated using Penman-Monteith equations with WFD is lower in all months compared with MORECS PE  Oudin PE, being temperature based, has higher rates in the summer impacting on simulation of flows through the autumn  Use of PE data, other than with local observed climate data (MORECS), leads to an overestimate of flow across the whole flow range, including flood flows  The Thames catchment is very sensitive to differences in PE data – there is a critical balance between rainfall and evaporation.

3. Comparison between River Basin Hydrological Model and Global Models

Daily discharge data from three Global Models (GMs) were extracted for 1963 to 2001 for grid box

51.25N and 0.25W (which includes Kingston gauging station on the Thames) and statistics of flow compared with those from the River Basin Hydrological Model, CLASSIC. The three GMs are JULES (Land Surface Hydrological Model (LSHM)), WaterGap (Global Hydrological Model (GHM)) and MPI-HM (composite LSHM/GHM). Note different evaporation accounting schemes (and when relevant, different PE estimates) are used in the different GMs.

The analyses of daily discharge are shown in Figure 6, mean monthly flow, Figure 7, flow duration curves, Figure 8, mean annual flow for 1963 to 2001, Figure 9, flood frequency curves, Figure 10 flood hydrograph and Figure 11 average number of days above a threshold. The flood hydrograph shows flows through the winter of 2000/01 following a number of heavy rainfall events during the autumn of

–  –  –

Figure 6 Mean monthly flow; observed (thick black), CLASSIC local data (dashed black), CLASSIC WFD (Oudin PE) (thin black), JULES (red), WaterGAP (green), MPI-HM (blue) Figure 7 Flow duration curves; observed (thick black), CLASSIC local data (dashed black), CLASSIC WFD (Oudin PE) (thin black), JULES (red), WaterGAP (green), MPI-HM (blue)

–  –  –

Figure 9 Flood peaks (POT3) and fitted flood frequency curves; observed (black circles and thick black line), CLASSIC local data (dashed black), CLASSIC WFD (Oudin PE) (thin black), JULES (red circles and red line), WaterGAP (green circles and green line), MPI-HM (blue circles and blue line). (For clarity flood peaks for CLASSIC with local and WFD data are not shown but are shown in Figure 4.)

–  –  –

Figure 11 Average number of days per year flow exceeds a threshold, with the threshold defined by Q1 to Q10 where Qn is the observed flow exceeded n% of the time; observed (thick black), CLASSIC local data (dashed black), CLASSIC WFD (Oudin PE) (thin black), JULES (red), WaterGAP (green), MPI-HM (blue) Comparison of statistics of mean daily flow from observed, modelled with an RBHM (using local

observed and WFD data), LSHM, GHM and LSHM/GHM shows that:

 The GHM (WaterGAP) simulates well the seasonal variation (mean monthly flow) and flow range (flow duration curve)  All GMs reproduce the year-to-year variation in flow but may consistently underestimate the mean annual flow (JULES and MPI-HM) Technical Report No. 53 - 10 None of the GMs reproduce well the flood frequency curve; the GHM overestimates the peak flows while the LSHM and LSHM/GHM underestimate the peaks  The shape of the flood hydrograph is also difficult to reproduce with the GMs; the shape is too smoothed with the LSHM and LSHM/GHM and too peaked with the GHM  The RBHM using either local observed data or WFD, compared with the three GMs considered, provides the best simulation of high flows and flood events  For average flows the GHM, WaterGap, performs as least as well as the RBHM using WFD data  The best overall simulation across the full flow range is provided by the RBHM using local observed data. This is partly to be expected given that observed data were used in the calibration and parameters are calibrated to simulate high flows  The different simulations show the requirement for having a realistic seasonal balance between rainfall and PE and that how PE is estimated can impact on simulation of flows, including the high end of the flow range. Some of the differences in simulated hydrographs could result from their internal estimation of potential and actual evapotranspiration.

4. References

CEH, Met Office, 2001. To what degree can the October/November 2000 flood events be attributed to climate change? Defra FD2304 Technical Report, Centre for Ecology and Hydrology, Wallingford, UK.

Crooks, S.M. and Naden, P.S., 2007, CLASSIC, a semi-distributed modelling system, Hydrology and Earth System Sciences, 11(1), 516-531.

Naden, P.S.,1993. Methods and techniques for peaks-over-threshold analysis. Report to Ministry of Agriculture, Fisheries and Food, Institute of Hydrology, 36pp.

Nash, J.E. and Sutcliffe, J.V., 1970. River flow forecasting through conceptual models. Part I. A discussion of principles. Journal of Hydrology, 10, 282-290 Oudin, L., Hervieu, F., Michel, C., Perrin, C., Andréassian, V., Anctil, F. And Loumagne, C., 2005. Which potential evapotranspiration input for a lumped rain-runoff model? Part 2 – Towards a simple and efficient potential evapotranspiration model for rainfall-runoff modelling. Journal of Hydrology, 303(1-4), 290-306.

Thompson, N., Barrie, I.A. and Ayles, M., 1982. The Meteorological Office Rainfall and Evaporation Calculation System: MORECS (July 1981). Hydrological Memorandum No 45, Met Office, Bracknell, UK.

Technical Report No. 53 - 11 -



Similar works:

«2 Globalisation and sustainable development: a political ecology strategy to realize ecological justice John Byrne*, Leigh Glover and Hugo F. Alrøe Introduction Organic farming and the challenge of sustainability Political ecology as one approach to globalisation and sustainable development.53 Growth without borders Growth within limits Growth and ecological injustice Commons as the basis of ecological justice Defining commons in the contemporary era State and corporate solutions to commons...»

«Thames Water Utilities Ltd 2W0H Lower Thames Operating Agreement Final Confidential TECHNICAL APPENDIX D ECOLOGICAL DATA AND LITERATURE REVIEW Cascade Consulting Technical Appendix D Thames Water Utilities Ltd 2W0H Lower Thames Operating Agreement Final Confidential Table of Contents Summary D.1  Overview – Literature and Data Collation and Review D.1.1  Introduction D.1.2  Methodology for Stage 1 Review D.2  Fish Communities of the Lower Freshwater River Thames D.2.1  Literature Review...»

«The Ecological Impacts of Homestead Settlements in the Negev: Final Report Daniel Orenstein, Elli Groner, Omrat Lihod, Wamuyu L. Muithui, Eitan Krukowski, Ofer Arnon, Alon Tal The Blaustein Institutes for Desert Research, Ben Gurion University of the Negev The Faculty of Architecture and Town Planning, The Technion, Israel Institute of Technology Submitted to: The Israel Ministry of Environmental Protection, Jerusalem November, 2009 2 Acknowledgements: The authors would like to thank the...»

«Transport Research Laboratory Creating the future of transport PUBLISHED PROJECT REPORT PPR636 A83 Rest and be Thankful: Ecological and Related Landslide Mitigation Options M G Winter (TRL) and A Corby (Transport Scotland) Prepared for: Transport Scotland, Trunk Road and Bus Operations Project Ref: TRTC 2000-097 Quality approved: B Shearer R Woodward (Project Manager) (Technical Referee) © Queen's Printer for Scotland 2012 Disclaimer This report has been produced by the Transport Research...»

«Christensen, V. and D. Pauly. 1992. ECOPATH II a software for balancing steadystate ecosystem models and calculating network characteristics. Ecological Modelling 61: 169-185. 169 Ecological Modelling, 61 (1992) 169-185 Elsevier Science Publishers B.V., Amsterdam ECOPATH II a software for balancing steady-state ecosystem models and calculating network characteristics * V. Christensen and D. Pauly International Center for Living Aquatic Resources Management (ICLARM), MC P.O. Box 1501, Makati,...»

«Advice to the Minister for the Environment, Heritage and the Arts from the Threatened Species Scientific Committee (the Committee) on an Amendment to the list of Threatened Ecological Communities under the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) 1 Name of the ecological community Natural grasslands on basalt and fine-textured alluvial plains of northern New South Wales and southern Queensland.This advice follows the assessment of: i. A nomination to list the...»

«Topics in Functional and Ecological Vertebrate Morphology, pp. 139-151. P. Aerts, K. D’Août, A. Herrel & R. Van Damme, Eds. © Shaker Publishing 2002, ISBN 90-423-0204-6 Preliminary study on the ecomorphological signification of the sound-producing complex in Carapidae Eric Parmentier * & Michel Chardon & Pierre Vandewalle Laboratoire de Morphologie fonctionnelle et évolutive, Université de Liège, Belgium Abstract Carapidae can be classified in four ecological groups : pelagic, dermersal,...»





 
<<  HOME   |    CONTACTS
2016 www.dissertation.xlibx.info - Dissertations, online materials

Materials of this site are available for review, all rights belong to their respective owners.
If you do not agree with the fact that your material is placed on this site, please, email us, we will within 1-2 business days delete him.