The impact of urban groundwater upon surface water - eTheses ...

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REFERENCES Vroblesky, D.A., & Hyde, W.T., 1997. Diffusion samplers as an inexpensive approach to monitoring VOCs in groundwater. Groundwater Monitoring and Remediation, Summer, pp 177-184. Winter, T. C.,2002. Subaqueous capping and natural recovery: Understanding the hydrogeologic setting at contaminated sites. DOER Technical Notes Collection (TN DOER-C26), U.S. Army Engineer Research and Development Center, Vicksburg, MS. www.wes.army.mil/el/dots/doer Winter, T.C., 1999. Relation of streams, lakes and wetlands to groundwater flow systems. Hydrogeology Journal 7, pp 28-45. Winter, T.C., Judson, W., Franke, O. L., & Alley, W.M., 1998. Groundwater and surface water a single resource. United States Geological Survey, Circular 1139. Winter, T.C., 1995. Recent advances in understanding groundwater/surface water interactions. US National report to IUGG, 1991-1994. Geophysics 33, American Geophysical Union. http://www.agu.org/revgeophys/winter01/node1.html Winter, T.C., 1983. The interaction of lakes with variably saturated porous media. Water Resources Research 19, pp 1203-1218. Woessner, W.W., 2000. Stream and fluvial plain ground water interactions: Rescaling hydrogeologic thought. Ground Water 2000, 38 (3) pp 423-429. Workman, S.R., Serrano, S.E., & Liberty, K., 1997. Development and application of an analytical model of stream/aquifer interaction. Journal of Hydrology 200, pp 149-163. Wroblicky, G.J., Campana, M.E., Valett, H.M., & Dahm, C.N., 1998. Seasonal variation in surfacesubsurface water exchange and lateral hyporheic area of two stream-aquifer systems. Water Resources Research 34 (3) pp 317-328. Young, C.P., Blackmore, K., Turrell, J., Godbold, P., Oakes, D.B., Clark, L. & Dempsey, 2002. Understanding geochemical fluxes between groundwater and surface water:scoping report. Research and development technical report P2-260/5. For the Environment Agency (UK).
REFERENCES Younger, P.L., 1989. Stream-aquifer systems of the Thames Basin: hydrogeology, geochemistry and modelling. Unpublished PhD thesis, Department of Civil Engineering, University of Newcastle Upon Tyne. Younger, P.L., Mackay R.J., & Connorton, B.J., 1993. Streambed sediment as a barrier to groundwater pollution: insights from fieldwork and modelling in the River Thames basin. Journal of the institution of water and environmental management 7, pp 577-585. Ziegler, A.C., Ross, H.C., Trombley, T.J., & Christensen, V.G., 2001. Effects of Artificial Recharge on Water Quality in the Equus Beds Aquifer, South-Central Kansas, 1995-2000. USGS fact sheet 096- 01.
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THE IMPACT OF URBAN GROUNDWATER UPO
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ABSTRACT A field-based research stu
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ACKNOWLEDGEMENTS I would like to th
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3.4.1 Solid Geology ...............
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5.5.2 Riverbed Sediment Core Data a
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6.10 Investigation of groundwater-s
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LIST OF FIGURES 2.1 Conceptual mode
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6.1 Schematic diagram for the analy
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LIST OF TABLES Table 3.1 Descriptio
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APPENDICES Appendices 1, 11, 19, 20
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1.1 Project outline CHAPTER 1. INTR
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4) to develop suitable monitoring m
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INTRODUCTION European Commission Wa
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REVIEW 2.1) and surface water may o
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REVIEW features of groundwater/surf
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REVIEW provide refuge to benthic in
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Abstraction For drinking water supp
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REVIEW occur such as biodegradation
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2.2.1 Water quality studies REVIEW
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REVIEW investigated groundwater/sur
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REVIEW owing to their widespread de
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REVIEW have been used to determine
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REVIEW and under conditions of non-
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(b) (a) River Tame 10 m topographic
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STUDY SETTING But under the General
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(a) Land Use In The River Tame Corr
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(a) (b) Figure 3.3 (a) Photograph o
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Figure 3.4 Schematic geology of the
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Table 3.1 Description of geological
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Wildmoor Sandstone Formation (middl
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STUDY SETTING Man-made excavations
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STUDY SETTING Tame were effluent to
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(a) (b) (c) Figure 3.9 (a) Postulat
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STUDY SETTING this restricts the le
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Figure 3.10 Schematic cross section
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STUDY SETTING water quality through
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STUDY SETTING (Ford, 1990) from nin
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STUDY SETTING dry cleaning industry
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MONITORING NETWORKS AND METHODS CHA
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2 9 4 0 0 0 2 8 8 0 0 0 4020000 410
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MONITORING NETWORKS AND METHODS The
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Water quality data were collected i
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MONITORING NETWORKS AND METHODS pie
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MONITORING NETWORKS AND METHODS pre
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MONITORING NETWORKS AND METHODS the
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MONITORING NETWORKS AND METHODS (Ga
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MONITORING NETWORKS AND METHODS Acc
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MONITORING NETWORKS AND METHODS bor
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MONITORING NETWORKS AND METHODS tha
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MONITORING NETWORKS AND METHODS des
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4.7.3 Grain size analyses by the Ha
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K = hydraulic conductivity (feet da
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MONITORING NETWORKS AND METHODS A s
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MONITORING NETWORKS AND METHODS Run
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MONITORING NETWORKS AND METHODS nex
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MONITORING NETWORKS AND METHODS Dif
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4.9.3 Radial Flow Analytical Soluti
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q = - k dh dx River Riverbed q = th
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Determinands Method of analyses Ana
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MONITORING NETWORKS AND METHODS dif
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5.2 Groundwater in the Tame Valley
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Total Monthly Volume Abstracted (m
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4020000 4100000 Bescot GS 91, 182 1
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5.3.2 Baseflow Analyses GROUNDWATER
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GROUNDWATER FLOW TO THE RIVER TAME
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Temperature C o 20 19.5 19 18.5 18
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5 cm Figure 5.16 (a) Riverbed core
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Frequency 9 8 7 6 5 4 3 2 1 0 10 20
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Summary of Darcy Specific Discharge
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Location Specific Discharge (md -1
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5.8 The Hydrogeological Setting of
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Level ( m.a.o.d ) Level ( m.a.o.d )
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5.9 Concluding Discussion GROUNDWAT
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CHAPTER 6. THE MODELLING OF GROUNDW
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6.2.1 Analytical Model, Steady Stat
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GROUNDWATER FLOW MODELLING The rive
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GROUNDWATER FLOW MODELLING 6.3.1 Re
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39 57 Figure 6.2 Regional Setting f
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GROUNDWATER FLOW MODELLING increase
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GROUNDWATER FLOW MODELLING general,
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Groundwater head contours (1m) 93.0
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GROUNDWATER FLOW MODELLING 6.4.3 Gr
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11 12 13 # # # # # # 96 97 98 Colum
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GROUNDWATER FLOW MODELLING unsatura
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River level data GROUNDWATER FLOW M
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GROUNDWATER FLOW MODELLING of geolo
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GROUNDWATER FLOW MODELLING The FAT3
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GROUNDWATER FLOW MODELLING and grav
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Elevation of cell centre (m.a.o.d)
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GROUNDWATER FLOW MODELLING transmis
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GROUNDWATER FLOW MODELLING on each
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GROUNDWATER FLOW MODELLING of 0.5md
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Analytical solution for the saturat
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GROUNDWATER FLOW MODELLING presence
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GROUNDWATER FLOW MODELLING in secti
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GROUNDWATER FLOW MODELLING The aver
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GROUNDWATER FLOW MODELLING would re
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GROUNDWATER FLOW MODELLING the aqui
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95 95 95 95 39 MODFLOW Particle Tra
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GROUNDWATER FLOW MODELLING Historic
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Discharge to the river m 3 d -1 % v
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GROUNDWATER FLOW MODELLING 6.10.2 A
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GROUNDWATER FLOW MODELLING investig
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GROUNDWATER FLOW MODELLING across t
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GROUNDWATER FLOW MODELLING by the F
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Specific discharge to the river fro
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GROUNDWATER FLOW MODELLING in time
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GROUNDWATER FLOW MODELLING unsatura
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GROUNDWATER FLOW MODELLING amplitud
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Depth (cm) -80 -100 -120 -140 -160
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Depth (cm) -40 -60 -80 -100 -120 -1
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GROUNDWATER FLOW MODELLING cycles o
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6.12 Conclusions GROUNDWATER FLOW M
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GROUNDWATER FLOW MODELLING consider
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WATER QUALITY INTERACTIONS CHAPTER
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Water Quality Data From Sutton Park
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WATER QUALITY INTERACTIONS 7.1 Indi
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WATER QUALITY INTERACTIONS (the fur
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WATER QUALITY INTERACTIONS Underlyi
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WATER QUALITY INTERACTIONS Oxygen l
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(a) (b) Eh (mv) DO (mgl -1 ) 600 50
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WATER QUALITY INTERACTIONS riverbed
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WATER QUALITY INTERACTIONS samples
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WATER QUALITY INTERACTIONS errors i
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WATER QUALITY INTERACTIONS industri
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(a) (b) (c) Depth below river bed (
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WATER QUALITY INTERACTIONS within 5
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WATER QUALITY INTERACTIONS The grea
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Cation Content (mgl -1 ) 300 250 20
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(a) (b) (c) Calcium Concentration m
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WATER QUALITY INTERACTIONS in the u
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7.5 Toxic Metals WATER QUALITY INTE
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WATER QUALITY INTERACTIONS parkland
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95 94 93 92 OD (meters) 91 90 89 88
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(a) (b) (c) Chloride (meql -1 ) Nit
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(a) (b) Depth below river bed (cm)
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(a) (c) (e) Depth below river bed (
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WATER QUALITY INTERACTIONS depth. T
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WATER QUALITY INTERACTIONS extent.
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Number of samples greater than dete
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WATER QUALITY INTERACTIONS The only
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WATER QUALITY INTERACTIONS source f
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WATER QUALITY INTERACTIONS The surf
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WATER QUALITY INTERACTIONS The Envi
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WATER QUALITY INTERACTIONS the bias
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WATER QUALITY INTERACTIONS The grou
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WATER QUALITY INTERACTIONS value of
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Depth below river bed (cm) 0 20 40
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WATER QUALITY INTERACTIONS There is
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WATER QUALITY INTERACTIONS Standard
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WATER QUALITY INTERACTIONS general
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WATER QUALITY INTERACTIONS attenuat
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WATER QUALITY INTERACTIONS these fa
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GROUNDWATER FLUX CHAPTER 8. ESTIMAT
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GROUNDWATER FLUX solution then the
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GROUNDWATER FLUX the riverbed piezo
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HCO3 - Determinant Mean Groundwater
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Residential roof run-off *1 General
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GROUNDWATER FLUX availability of sa
Page 347 and 348: Discharge MLd -1 350 330 310 290 27
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Page 367 and 368: CONCLUSIONS CHAPTER 9. CONCLUSIONS
Page 369 and 370: CONCLUSIONS surface-water quality b
Page 371 and 372: CONCLUSIONS 1945) which caused sign
Page 373 and 374: CONCLUSIONS Objective 4. To develop
Page 375 and 376: CONCLUSIONS On a catchment scale, g
Page 377 and 378: CONCLUSIONS other compounds of inte
Page 379 and 380: CONCLUSIONS groundwater and surface
Page 381 and 382: REFERENCES REFERENCES Allen, D.J.,
Page 383 and 384: REFERENCES Bredehoeft, J.D., & Papa
Page 385 and 386: REFERENCES De Marsily, G., 1986. Qu
Page 387 and 388: REFERENCES Ford, M., Tellam, J.H.,
Page 389 and 390: REFERENCES Hooda, P.S., Moynagh, M.
Page 391 and 392: REFERENCES Kuwabara, J., Berelson,
Page 393 and 394: REFERENCES Modica, E., 1993. Hydrau
Page 395 and 396: REFERENCES Rivett, M.O., Feenstra,
Page 397: REFERENCES Stagg, K.A., 2000. An in
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