Phosphorus in UK Rivers: the Impact of Urban Waste Water Treatment Directive

Total Page:16

File Type:pdf, Size:1020Kb

Phosphorus in UK Rivers: the Impact of Urban Waste Water Treatment Directive Durham E-Theses Phosphorus in UK Rivers: The Impact of Urban Waste Water Treatment Directive CIVAN, AYLIN How to cite: CIVAN, AYLIN (2016) Phosphorus in UK Rivers: The Impact of Urban Waste Water Treatment Directive, Durham theses, Durham University. Available at Durham E-Theses Online: http://etheses.dur.ac.uk/11774/ Use policy The full-text may be used and/or reproduced, and given to third parties in any format or medium, without prior permission or charge, for personal research or study, educational, or not-for-prot purposes provided that: • a full bibliographic reference is made to the original source • a link is made to the metadata record in Durham E-Theses • the full-text is not changed in any way The full-text must not be sold in any format or medium without the formal permission of the copyright holders. Please consult the full Durham E-Theses policy for further details. Academic Support Oce, Durham University, University Oce, Old Elvet, Durham DH1 3HP e-mail: [email protected] Tel: +44 0191 334 6107 http://etheses.dur.ac.uk 2 Phosphorus in UK Rivers: The Impact of Urban Waste Water Treatment Directive Aylin Civan Erdogan Master of Science by Research Department of Earth Sciences Durham University 2016 Abstract Excessive phosphorus levels leading to eutrophication in natural waters as a result of growing population, urbanisation and intensified agriculture has long been a major environmental concern at a global scale. Many remediation strategies and actions have been undertken since the implementation of Urban Waste Water Treatment Directive (UWWTD) in 1992. The UWWTD was implemented to reduce direct phosphorus inputs into rivers from effluents of sewage treatment works. Nevertheless, the long-term outcomes and effectiveness of theses actions still remain unknown. An understanding of the prospective results and effectiveness of these implementations is only possible with a retrospective analysis of riverine phosphorus dynamics. Therefore, this thesis explored the evolution of P concentration and flux from across the UK with datasets available from 230 river sites between the period of 1974 and 2012. These datasets were examined with the purpose of detecting the traces of the events that are likely to be governing the changes in phosphorus levels over the this time period i.e. the implementation of the UWWTD. Trend and change point analyses conducted on Total reactive phosphorus (TRP) and Total phosphorus (TP) data indicated that the concentrations and fluxes have been declining since the mid- 1980s correlatingwith declining phosphate-fertilizer usage. The sites with the largest declines were from the Midlands and South East regions of England, whereas Scotland has seen almost no change. Significant step changes were encountered in most of the TRP concentration records, and most of these step changes were detected in the period 1993-1997 suggesting that the UWWTD was the key factor leading to these step changes. To validate this hyphothesis, Principal component analysis (PCA) was conducted to be able to track down the urban source contributor. Water quality (TRP, BOD, Suspended solids, Nitrate concentration and Conductivity) data from 5 example sites were analysed however, in none of the case examples was there an explicit principle component that could be construed with an urban or any other source contributor. Therefore, the PCA technique was not found to be a suitable technique to analyse this type of datasets. i Declaration and Copyright I confirm that no part of the material presented in this thesis has previously been submitted by me or any other person for a degree in this or any other university. Where relevant, material from the work of others has been acknowledged. Signed: Date: © Copyright, Aylin Civan Erdogan, 2016 The copyright of this thesis rests with the author. No quotation from it should be published without prior written consent and information derived from it should be acknowledged. ii Acknowledgements First and foremost, I would like to express my most sincere gratitude and appreciation to my supervisor Professor Fred Worrall for all his guidance, support and endless patience throughout this thesis work. I would like to thank The General Dictorate of State Hydraulic Works of Turkey for funding all my expenses and allowing me to have such a great working experience in Durham University. I am grateful to the Environment Agency for supplying all the HMS datasets that have been used in this thesis. Also, I would like to thank Sarah Wheater of Environment Agency for taking time to explain how to use the datasets. Thanks to all the all staff and postgraduates in Department of Earth Sciences at the University of Durham for creating such a nice atmosphere to work in. Many thanks to all my friends in the Department of Earth Sciences, but especially, Ines, Ilaria and Giacomo, thank you for all the coffee breaks, pizza and game nights, and many other joyful moments we shared – you certainly made it the best year of my life. I’d like to thank my parents, Sema and Sefer Civan, who deserve more than I can ever give in return for all kinds of support they have given. I owe them so much. Finally, my special gratitude goes to my best friend and husband, Ali Riza, who has been holding my hand for eight long years and has never stopped being loving, caring and patient with me. iii iv Table of Contents Chapter 1: ..................................................................................................................... 1 Introduction .................................................................................................................. 1 1.1. Overview and Rationale .................................................................................... 1 1.1.1. Phosphorus and its role .............................................................................. 1 1.1.2. Phosphorus as an important contributor of Eutrophication........................ 3 1.1.3. Sources of Phosphorus loadings into rivers ............................................... 4 1.1.4. Technologies for Phosphorus Removal and Recovery .............................. 7 1.1.5. Measures and implementations to reduce phosphorus inputs in the UK ... 9 1.2. Review on UK phosphorus levels ................................................................... 10 1.3. Aims and Objectives ....................................................................................... 11 Chapter 2: ................................................................................................................... 13 TRP and TP Concentration and Flux from the UK .................................................... 13 2.1. Introduction ..................................................................................................... 13 2.2. Methodology ................................................................................................... 14 2.2.1. Study Sites ................................................................................................ 14 2.2.2. Analysis of Variance (ANOVA) and Covariance (ANCOVA) ............... 17 2.2.3. Time Series and Trend Analysis .............................................................. 19 2.2.4. Change Point Analysis ............................................................................. 20 2.3. Results for Total Reactive Phosphorus ........................................................... 24 2.3.1. TRP Concentration ................................................................................... 24 v 2.3.2. TRP Flux .................................................................................................. 26 2.3.3. TRP Trend Analysis ................................................................................. 29 2.3.3.1. Overall Trends ....................................................................... 29 2.3.3.2. Trends in the Last Decade ..................................................... 33 2.3.4. Change Point Analysis ............................................................................. 37 2.4. Total Phosphorus ............................................................................................. 43 2.4.1. TP Concentration ...................................................................................... 43 2.4.2. TP Flux ..................................................................................................... 46 2.4.3. TP Trend Analysis .................................................................................... 48 2.4.3.1. Overall Trends ....................................................................... 48 2.4.3.2. Trends in the Last Decade ..................................................... 49 2.4.4. Change Point Analysis ............................................................................. 52 2.5. Discussion ....................................................................................................... 59 Chapter 3: ................................................................................................................... 65 Case Studies on Five Catchments .............................................................................. 65 3.1. Introduction ..................................................................................................... 65 3.2. Selection of Sites ............................................................................................. 66 3.3. Methodology ..................................................................................................
Recommended publications
  • Shropshire Biodiversity Action Plan
    Shropshire Biodiversity Action Plan Dipper (Cinclus cinclus) ©Dave Appleton Dippers feed almost exclusively on larvae that live on the stony beds of shallow fast flowing streams, usually at the rapids, and are never far from such waters. They usually stay on their breeding grounds throughout the year, and might be seen at any time, either bobbing up and down on the rocks in the middle of the stream, or flying low over the water. Breeding usually starts in late March or early April, sometimes earlier, and nesting pairs will attempt to raise two broods. Though some Dippers nest in natural cavities along the riverbank, others build nests on ledges on bridges, and they take readily to nest boxes located directly above the flowing water, where predators are unable to reach them. They are very territorial, so nests are evenly spaced on each stretch of river. In the south Shropshire Hills, the spacing is around 1 kilometre. Once some nests are found, and the average distance between them established, it is possible to work out if any territories are unoccupied. Because they are restricted to, and dependent on, food from the river, they are relatively easy to monitor and a good indicator of the water quality in the river. Pairs nesting along acidic streams tend to lay their eggs later, lay smaller clutches, raise smaller broods and raise only one brood. 1 Objectives and Targets 1.1 Objectives A. In the short term, maintain existing populations and range of Dipper in Shropshire. B. In the longer term, reverse the decline in Dipper population, and restore its previous population and range C.
    [Show full text]
  • Market Drayton NP Reg 16 Version 5
    1 MARKET DRAYTON Neighbourhood Development Plan 2016-2026 Regulation 15 Draft Plan No 2 APRIL 2017 Market Drayton Neighbourhood Development Plan 2016-2026 – Regulation 16 Submission Draft Plan, April 2017 2 Contents 1. Introduction and Background 2. Shropshire Local Plan (Core Strategy and SAMDev Plan) Context 3. Vision, Issues and Objectives 4. Plan Policies 5. Delivering the Plan Market Drayton Neighbourhood Development Plan 2016-2026 – Regulation 16 Submission Draft Plan, April 2017 3 1. Introduction and Background 1.1 Market Drayton Neighbourhood Development Plan (the NDP) is a new type of planning document introduced by the Localism Act of 2011. It is enables local communities to make a significant contribution to some of the planning decisions about how their areas should develop. 1.2 On 13th January 2015, Market Drayton Town Council made a formal submission to Shropshire Council to designate an area comprising the Market Drayton Town Council area and small parts of its adjacent parishes as a Neighbourhood Plan Area under the Localism Act 2011, with the intention of preparing this NDP. The area covered by this NDP is shown on Map 1. Following a consultation period, including discussions with those adjacent parish councils, Shropshire Council approved the application to be an appropriate basis for the development of a neighbourhood plan. This draft NDP has been prepared following the adoption of Shropshire Local Plan comprising its Core Strategy adopted in March 2011 and its Site Allocations and Management of Development (SAMDev) Plan in December 2015 both by Shropshire Council. 1.3 This draft NDP has been prepared on the basis of the evidence gathered including from a survey of residents and other relevant information.
    [Show full text]
  • Appendix a Environmental Baseline
    Appendix A Environmental Baseline . Introduction The data collected to characterise the baseline environment of Telford and Wrekin Borough has been derived from numerous secondary sources, which are referenced as footnotes in this report. No new investigations or surveys have been undertaken. In some instances, it has been noted that different secondary sources present conflicting information and it has not been possible to verify which sources are the most accurate. Where this has been identified, the limitations have been noted. It should be noted that there is an abundance of environmental information available. However, the information presented in this Appendix has been chosen on the basis that it may be influenced or affected by the Local Flood Risk Management Strategy (LFRMS). Steps have been taken to avoid including information which is of no clear relevance to the LFRMS. It may be necessary to collect further data against which to assess the potential environmental effects of the LFRMS with regard to monitoring requirements. Population .. Population The topic of population is considered first in the baseline information, since the over-arching purpose of the LFRMS is to reduce flood risk to people and property. The LFRMS also seeks to increase public awareness of flooding and promote individual and community level flood resilience. A number of properties in the Telford and Wrekin Area are in areas at risk of flooding and were affected by flooding during the Summer 2007 floods. Some of the properties were affected by flooding from fluvial sources (streams, rivers) but many properties were affected from surface water flooding from sewers and drainsi.
    [Show full text]
  • Presentation
    Geological Society - Hydrogeology Group Groundwater Asset Management Shropshire Groundwater Scheme Kevin Voyce Hydrogeologist Midlands Region Groundwater & Contaminated Land Team 10 September 2008 Presentation • SGS Role in Strategic Water Resource Planning & Operations – River Severn Regulation • Development of the Scheme to date • Environmental Management • System Management 1 LLYN CLYWEDOG OPERATIONS 2006 100 3 500 Flo od Drawdo wn 90 20 06 % Storage 3 000 80 Shro ps hire Temp orary Floo d Drawdo wn Ground wate r 70 2 500 60 Se ek Drought Orde r 2 000 50 1 500 40 Dro ug ht Orde r PERCENTAGE FULL PERCENTAGE In Fo rce FLOW AT BRYNTAIL (Ml/d) BRYNTAIL AT FLOW 30 1 000 Rele ase or Overflo w 20 5 00 10 0 0 1- Jan 1 -Feb 1-Mar 1-Apr 1- May 1- Jun 1- Jul 1- Aug 1-Sep 1-Oct 1- Nov 1- Dec 2 Clywedog: Proposed Control Curves 2006 - scenario from 21st Aug 100 90 80 70 60 50 S torage S(%) torage 40 Floo d Draw Dow n Zone Hydr opow er Release Zone 30 SGS Zon e 1 - up t o 75 Ml/d Net SGS Zon e 2 - up t o 150 Ml/d Net SGS Zon e 3 - up t o 225 Ml/d Net Auto matic Dro ught Or der Zone 20 % Stora ge 2 006 Forec ast Prof ile 250 Ml/d Forec ast Prof ile 300 Ml/d Forec ast Prof ile 350 Ml/d 10 Forec ast Prof ile 400 Ml/d Forec ast Prof ile 450 Ml/d Forec ast Prof ile 500 Ml/d 0 Jan Feb Mar A pr May Jun Jul Aug S ep Oct Nov Map derived from 1:250,000 scale BGS mapping under licence 2003/014 3 4 Shropshire Groundwater Scheme – Gross Deployable Yields and Operational Years Phase Gross Yield Regulation Seasons Requiring SGS Support Phase 1 45Ml/d 1984, 1989, 1995, 1996, 2006 (commissioned 1984/85) Phase 2 50Ml/d 1995, 1996, 2006 (commissioned 1991) Phase 3 50Ml/d 2006 (commissioned 1999) Phase 4 45-50Ml/d 2006 (commissioned 2005) Phase 5 60-65Ml/d est.
    [Show full text]
  • NEWSLETTER Newsletter of the Broseley Local History Society INCORPORATING the WI LKINSON SOCIETY
    NEWSLETTER Newsletter of the Broseley Local History Society INCORPORATING THE WI LKINSON SOCIETY NOVEMBER 2014 MEETINGS PROGRAMME Meetings of the Broseley Local History Society are 3 Dec Annual Dinner held on the first Wednesday of each month at 7.30pm 7 Jan Broseley Pipes by Rex Key at the Broseley Social Club, High Street, unless 4 Feb Ironbridge Institute Library by John Powell otherwise announced. Car parking is available at the 4 Mar Abraham Darby III by Michael Darby back of the Club. Members are requested to be seated by 7.30pm to Further details from Neil Clarke 01952 504135. allow our speakers a prompt start. Visitors are welcome but are asked to give a donation NEW MEMBERS towards Society funds. The Society would like to welcome the following new members: Mr. Chris Wilson, Broseley Mr. Arwyn Jones, Broseley CONTENTS Mr. David Springett, Broseley Mr. Lee Roberts, Broseley Programme P age 1 Mr. Brian Weston, Broseley New Members P age 1 Previous Meetings Page 2 CHRISTMAS DINNER Page 4 Bookshop Wednesday 3rd December Where’s Welly? Page 4 The Lion, High Street, 7.30pm for 7.45pm John Wilkinson Ballard Page 5 £18.95 per person The Society’s Christmas dinner is always an event Instone Building Page 5 which members look forward to. As in the past, it is to What’s On? Page 6 be held at The Lion Hotel in the High Street since it makes it easily accessible to most people. Mailbox Page 6 Please book your place by Friday 28th November at Subscription Form Page 9 the latest by completing the form on page 11 and Christmas Meal Menu Page 11 returning it with your payment to: Janet Robinson 26 Coalport Road Broseley TF12 5AZ.
    [Show full text]
  • Tern Valley Trail
    The ‘Discovering Wellington’ Project presents: The Tern Valley Trail A cycle trail linking the historic market town of Wellington to Thomas Telford’s lost canal country The Tern Valley Trail Between 1795 and 1796, Thomas Telford drove the Shrewsbury Canal through the lower Tern Valley near Wellington, rendering many changes to the local landscape that can still be viewed today. The year 2007 marks the 250th anniversary of the renowned Scottish civil engineer’s birth, so what better way to witness his impact in east Shropshire than to get out and see some of the changes he made first hand? Along the way you’ll uncover groundbreaking industrial heritage, medieval castle ruins, secret Second World War history and much more besides, so come with us now and discover the riparian wonders of Wellington Midsummer Fair, Market Square the Tern Valley. Wellington, then The Tern The Tern Valley Trail is a 14-mile, circular cycle route on quiet country roads, traffic-free paths and existing sections of the National Cycle Network. The trail begins and ends in the ancient market town of Wellington, the historic capital of east Shropshire. Wellington’s long and illustrious history stretches back to at least Anglo-Saxon times, while the town received its first market charter in 1244 and became a prosperous centre for industry and agriculture in the Victorian era. Today, the market is still at the centre of town life, while its comprehensive range of specialist shops, cafes, restaurants and pubs make Wellington Longdon Aqueduct an excellent place to start and end your adventure.
    [Show full text]
  • Hydraulic Conductivity for Each Core
    090116876 “Spatial variability in physical and geochemical properties of sediments affecting nitrogen attenuation in the hyporheic zone of the River Tern” Dissertation submitted as part requirement for the degree of Master of Sciences in Contaminant Hydrogeology By Hannah Wooldridge Supervisor: Dr Stephen Thornton The University of Sheffield Department of Civil and Structural Engineering 3 September 2010 1 090116876 Declaration of originality Hannah Wooldridge certifies that all the material contained within this document is all her own work except where it is clearly referenced to others. 2 090116876 Abstract Six riverbed cores from the River Tern, Shropshire were assessed for a range of physical and chemical properties, at a core and spatial scale, in order to determine the nitrogen attenuation potential. Acid digestions, wet and dry sieving and the Malvern Mastersizer 1E 2000 was used in order to determine the particle grain size distributions and average grain size for each core. The Hazen empirical formula was applied in order to derive hydraulic conductivity for each core. The fraction of organic carbon was determined using the modified Walkley Black method, along with pore water chemistry data to outline the chemical properties of each core. Depth profiles of both the physical and chemical properties were produced and statistically analysed using ANOVA in order to deduce correlations between the physical and chemical properties and to highlight areas of enhanced denitrification. Correlations were found between decreasing grain size and decreasing hydraulic conductivity and increased weight percentage organic carbon. From the statistical analysis hydraulic conductivity was found to be the physical property that exerts the most influence on the nitrate concentrations.
    [Show full text]
  • A Large Breeding Colony of River Tern Sterna Aurantia in Chilika Lake, Orissa (India)
    A large breeding colony of River Tern Sterna aurantia in Chilika Lake, Orissa (India) P. Sathiyaselvam & S. Balachandran Sathiyaselvam, P. & Balachandran, S. 2007. Largest nesting colony of River Tern Sterna aurantia in Chilika Lake, Orissa, India. Indian Birds 3 (2): 65–66. P. Sathiyaselvam, Bombay Natural History Society, Hornbill House, Shaheed Bhagat Singh Road, Mumbai 400023, Maharashtra, India. Email: [email protected] S. Balachandran, Bombay Natural History Society, Hornbill House, Shaheed Bhagat Singh Road, Mumbai 400023, Maharashtra, India. Email: [email protected] Mss received on 31.viii.2006. iver Tern Sterna aurantia distribution is restricted to size and incubation period. The sign strips were numbered to tropical Asia—from Iran east through Pakistan, India identify individual nests and nest locations were marked with Rand Thailand. It inhabits inland river systems, lakes a Global Positioning System (GPS). To minimize disturbance to and rarely, estuaries (Ali & Ripley 1983; Harrison 1983). the nesting / brooding birds, surveys were mostly done early Information on the breeding biology of the species is limited. morning and late evening. Care was taken to minimize the During our waterbird population monitoring study at disturbance while moving into the colony site. Chilika Lake (19º28’–19º54’N 85º05’–85º38’E), Orissa (India), In Chilika especially at Nalabana Island, the River Tern between 2001 and 2005, a breeding colony of three tern species population began to build up from February, as birds arrived namely Gull-billed Gelochelidon nilotica, Little Sterna albifrons to the Island for breeding, and peaked in April (Fig. 1). Though and River terns was recorded on Nalabana Island (19º42’36"N territory marking and mobbing behaviour occurred in late 85º28’48"E) located in Chilika Lake.
    [Show full text]
  • Catchment 49B: River Tern
    www.naturalengland.org.uk Capital Grant Scheme - Funding Priority Statement 2014/15 Catchment 49b: River Tern Only holdings within the capital grant scheme target Detailed maps for individual catchments must be area(s) will be eligible to apply for a grant. Due to viewed on the MAGIC website at http://magic.defra. limited funds, applications from outside of the target gov.uk/MagicMap.aspx. From this link tick the ‘I Agree areas will not be accepted for the 14/15 scheme. to the Terms...’ tick box and click OK. Then in the ‘Table of Contents’ select the ‘Designations > Land-Based An application is classed as in target if more than 50% of Designations > Non-statutory’ tick box. Then in the ‘Map the proposed capital items, are within the target area. Search’ text box select ‘Postcodes’ from the dropdown list, then enter your postcode into the text box. If you are unsure if you would be classed as in target please contact your CSFO to confirm, before This will load a map that will show if your land is in submitting an application. a priority catchment and target area. You may need to turn off some of the other designations using the Please see indicative map for target area boundaries. ‘Table of Contents’ buttons next to the map to see your land area more clearly. Crewe Target Areas Ellerton Brook, Bailey Brook, Stoke on Lonco Brook, Trent River Tern – Coal Whitchurch Brook to Bailey Brook, Bearstone Borehole Market Drayton Oswestry Stafford Newport Catchment Target Area Shrewsbury Telford Urban Area Major Roads Motorway Crown copyright.
    [Show full text]
  • Shropshire Middle Severn Abstraction Licensing Strategy
    Shropshire Middle Severn Abstraction Licensing Strategy A strategy to manage water resources sustainably July 2021 Page 1 of 41 We are the Environment Agency. We protect and improve the environment. We help people and wildlife adapt to climate change and reduce its impacts, including flooding, drought, sea level rise and coastal erosion. We improve the quality of our water, land and air by tackling pollution. We work with businesses to help them comply with environmental regulations. A healthy and diverse environment enhances people's lives and contributes to economic growth. We can’t do this alone. We work as part of the Defra group (Department for Environment, Food & Rural Affairs), with the rest of government, local councils, businesses, civil society groups and local communities to create a better place for people and wildlife. Published by: Environment Agency Horizon House, Deanery Road, Bristol BS1 5AH www.gov.uk/environment-agency © Environment Agency 2021 All rights reserved. This document may be reproduced with prior permission of the Environment Agency. Further copies of this report are available from our publications catalogue: http://www.gov.uk/government/publications or our National Customer Contact Centre: 03708 506 506 Email: [email protected] 2 of 41 Contents 1. About the licensing strategy ...................................................................................... 4 1.1. Overview ................................................................................................................
    [Show full text]
  • Shropshire Outline Water Cycle Study Final Report
    Sustaining & Improving the Quality of People’s Lives Shropshire Outline Water Cycle Study Final report Halcrow Group Limited Burderop Park Swindon SN4 0QD June 2010 01793 812479 http://www.halcrow.com/html/our_markets/watercycleplanning.htm Halcrow Group Limited has prepared this report in accordance with the instructions of their client, Shropshire Council, for their sole and specific use. Any other persons who use any information contained herein do so at their own risk. © Halcrow Group Limited 2010 iii Sustaining & Improving the Quality of People’s Lives iv Sustaining & Improving the Quality of People’s Lives Shropshire Outline Water Cycle Study Final report Halcrow Group Limited Burderop Park Swindon SN4 0QD March 2009 01793 812479 http://www.halcrow.com/html/our_markets/watercycleplanning.htm Halcrow Group Limited has prepared this report in accordance with the instructions of their client, Shropshire Council, for their sole and specific use. Any other persons who use any information contained herein do so at their own risk. © Halcrow Group Limited 2010 iii Sustaining & Improving the Quality of People’s Lives Shropshire Outline Water Cycle Study Final report Revision schedule Date Document reference Stage Author Approver 30/11/2009 WUSHWC Draft Ali Cotton Andy McConkey 14/05/2010 WUSHWC Draft Final Ali Cotton Andy McConkey 23/06/2010 WUSHWC Final Ali Cotton / Ali Cotton Emma Smith iv Sustaining & Improving the Quality of People’s Lives TABLE OF CONTENTS 1 Introduction 1 1.1 Background to the water cycle study 1 1.2 Water cycle processes
    [Show full text]
  • Dowles Brook Summary
    Aquatic Habitat Characterization and Use in Groundwater versus Surface Runoff Influenced Streams: Brown Trout ( Salmo trutta ) and Bullhead ( Cottus gobio ) Marie-Pierre Gosselin A thesis submitted in partial fulfilment of the University’s requirements for the degree of Doctor of Philosophy 2008 University of Coventry (University of Worcester/University of Birmingham) ABSTRACT Riverine physical habitats and habitat utilization by fish have often been studied independently. Varying flows modify habitat composition and connectivity within a stream but its influence on habitat use is not well understood. This study examined brown trout (Salmo trutta ) and bullhead ( Cottus gobio ) utilization of physical habitats that vary with flow in terms of size and type, persistence or duration, and frequency of change from one state to another, by comparing groundwater-dominated sites on the River Tern (Shropshire) with surface runoff-dominated lowland, riffle-pool sites on the Dowles Brook (Worcestershire). Mesohabitat surveys carried out at two-month intervals on a groundwater-dominated stream and on a surface runoff-influenced stream showed differences in habitat composition and diversity between the two types of rivers. The temporal variability in mesohabitat composition was also shown to differ between the two flow regime types. In the groundwater-influenced stream, mesohabitat composition hardly varied between flows whereas in the flashy stream it varied to a great extent with discharge. Habitat suitability curves for brown trout and bullhead were constructed to predict the potential location of the fish according to flow. The resulting prediction maps were tested in the field during fish surveys using direct underwater observation (snorkelling). Under the groundwater-influenced flow regime brown trout displayed a constant pattern of mesohabitat use over flows.
    [Show full text]