Publications
132 results found
Bond T, Templeton MR, Mokhtar Kamal NH, et al., 2015, Nitrogenous disinfection byproducts in English drinking water supply systems: Occurrence, bromine substitution and correlation analysis, Water Research, Vol: 85, Pages: 85-94, ISSN: 0043-1354
Minas K, Karunakaran E, Bond T, et al., 2015, Biodesalination: an emerging technology for targeted removal of Na<sup>+</sup>and Cl<sup>−</sup>from seawater by cyanobacteria, Desalination and Water Treatment, Vol: 55, Pages: 2647-2668, ISSN: 1944-3994
Ellis K, Mounce SR, Ryan B, et al., 2015, Improving root cause analysis of bacteriological water qualityfailures at water treatment works, 13th International Conference on Computing and Control for the Water Industry, CCWI2015, Leicester, UK
Chu W, Li D, Gao N, et al., 2015, The control of emerging haloacetamide DBP precursors with UV/persulfate treatment, Water Research, Vol: 72, Pages: 340-348, ISSN: 0043-1354
Grimes JET, Templeton MR, 2015, Geostatistical modelling of schistosomiasis prevalence, The Lancet Infectious Diseases, Vol: 15, Pages: 869-870, ISSN: 1474-4457
Templeton MR, Hammoud AS, Butler AP, et al., 2015, Nitrate pollution of groundwater by pit latrines in developing countries, AIMS Environmental Science, Vol: 2, Pages: 302-313
Grimes JET, Croll D, Harrison WE, et al., 2015, The roles of water, sanitation and hygiene in reducing schistosomiasis: a review, Parasites and Vectors, Vol: 8:156
Chu W, Li C, Gao N, et al., 2015, Terminating pre-ozonation prior to biological activated carbon filtration results in increased formation of nitrogenous disinfection by-products upon subsequent chlorination, Chemosphere, Vol: 121, Pages: 33-38, ISSN: 0045-6535
Gormley-Gallagher A, Amezaga J, Shucksmith J, et al., 2015, Briefing: Negotiating value at the research–practice interface in the water sector, Proceedings of the Institution of Civil Engineers - Management, Procurement and Law, Vol: 168, Pages: 8-11, ISSN: 1751-4304
<jats:p> Lessons from experiences of managing an engineering doctorate programme are delineated in this paper, with particular emphasis on the relationship between research and practice. The paper reports on applied, practice-oriented research at the UK's industrial doctoral centre for the water sector. A descriptive account of the negotiating value at the research–practice interface is presented based on decades of collective practice, during which the engineering doctorate model has matured and grown. Conclusions focus on recommendations pertaining to project management, knowledge transfer and the effective and consistent translation of academic and practitioner project details. </jats:p>
Todman LC, van Eekert MHA, Templeton MR, et al., 2015, Modelling the fill rate of pit latrines in Ifakara, Tanzania, Journal of Water, Sanitation and Hygiene for Development, Vol: 5, Pages: 100-106
Ritson JP, Bell M, Graham NJD, et al., 2014, Simulated climate change impact on summer dissolved organic carbon release from peat and surface vegetation: Implications for drinking water treatment, Water Research, Vol: 67, Pages: 66-76, ISSN: 0043-1354
Xue C, Wang Q, Chu W, et al., 2014, The impact of changes in source water quality on trihalomethane and haloacetonitrile formation in chlorinated drinking water, Chemosphere, Vol: 117, Pages: 251-255, ISSN: 0045-6535
Bond T, Templeton MR, Rifai O, et al., 2014, Chlorinated and nitrogenous disinfection by-product formation from ozonation and post-chlorination of natural organic matter surrogates, Chemosphere, Vol: 111, Pages: 218-224, ISSN: 0045-6535
Bond T, Mokhtar Kamal NH, Bonnisseau T, et al., 2014, Disinfection by-product formation from the chlorination and chloramination of amines, Journal of Hazardous Materials, Vol: 278, Pages: 288-296, ISSN: 0304-3894
Honsbein A, Madsen MA, Amezaga JM, et al., 2014, ’Biodesalination’: a synthetic biology approach for the use of photosynthetic bacteria in water treatment, New Biotechnology, Vol: 31, Pages: S140-S141, ISSN: 1871-6784
Ritson JP, Graham NJD, Templeton MR, et al., 2014, The impact of climate change on the treatability of dissolved organic matter (DOM) in upland water supplies: A UK perspective, Science of The Total Environment, Vol: 473-474, Pages: 714-730, ISSN: 0048-9697
Bond T, Huang J, Graham NJD, et al., 2014, Examining the interrelationship between DOC, bromide and chlorine dose on DBP formation in drinking water — A case study, Science of The Total Environment, Vol: 470-471, Pages: 469-479, ISSN: 0048-9697
Grimes JET, Croll D, Harrison WE, et al., 2014, The relationship between water, sanitation and schistosomiasis: a systematic review and meta-analysis, PLOS Neglected Tropical Diseases, Vol: 8, Pages: e3296-e3296, ISSN: 1935-2735
Furlong C, Templeton MR, Gibson WT, 2014, Processing of human faeces by wet vermifiltration for improved on-site sanitation, Journal of Water, Sanitation and Hygiene for Development, Vol: 4, Pages: 231-239
Yang F, Zhang J, Chu W, et al., 2014, Haloacetamide versus halomethane formation and toxicity in chloraminated drinking water, Journal of Hazardous Materials, Vol: 274, Pages: 156-163
Mayor-Smith I, Templeton MR, 2014, Methodological considerations when conducting bench scale polychromatic ultraviolet irradiation of water, Water Science and Technology: Water Supply, Vol: 14, Pages: 291-298, ISSN: 1607-0798
The use of a bench scale apparatus (often referred to as a ‘collimated beam’) to apply fluences to water samples is common practice in disinfection research and in validating the performance of full-scale UV disinfection reactors. This study investigated the sources of potential experimental variations in the calculation of fluence when conducting polychromatic collimated beam exposures. Spectral variations associated with lamp operating conditions (e.g. cooling of the lamp), the angle of the spectroradiometer relative to the lamp when measuring the UV fluence rate, and the shape of the arc within the lamp are important to consider in order to achieve reproducible UV fluences when using a polychromatic collimated beam. Specific recommendations are provided to encourage greater experimental rigour and reproducibility in polychromatic UV disinfection studies, including taking spectral output measurements before and after UV exposures and monitoring the lamp voltage as an indication of lamp output stability.
Amezaga JM, Amtmann A, Biggs CA, et al., 2014, Biodesalination: a case study for applications of photosynthetic bacteria in water treatment, Plant Physiology, Vol: 164, Pages: 1661-1676
Villanueva CM, Kogevinas M, Cordier S, et al., 2014, Assessing exposure and health consequences of chemicals in drinking water: current state of knowledge and research needs, Environmental Health Perspectives, Vol: 122, Pages: 213-221
Bond T, Roma E, Foxon KM, et al., 2013, Ancient water and sanitation systems - applicability for the contemporary urban developing world, Water Science and Technology, Vol: 67, Pages: 935-941
Todman LC, Ireson AM, Butler AP, et al., 2013, Water vapor transport in soils from a pervaporative irrigation system, Journal of Environmental Engineering, Vol: 139, Pages: 1062-1069
Ellis K, Ryan B, Templeton MR, et al., 2013, Bacteriological water quality compliance and root cause analysis: an industry case study, Water Science and Technology: Water Supply, Vol: 13, Pages: 1034-1045
Ellis K, Mounce SR, Ryan B, et al., 2013, Use of on-line water quality monitoring data to predict bacteriological failures, 12th International Conference on Computing and Control for the Water Industry, CCWI2013, Perugia, Italy
Sule M, Jiang J, Templeton M, et al., 2013, Salt rejection and water flux through a tubular pervaporative polymer membrane designed for irrigation applications, Environmental Technology, Vol: 34, Pages: 1329-1339, ISSN: 0959-3330
Liu X, Wei X, Zheng W, et al., 2013, An optimized analytical method for the simultaneous detection of iodoform, iodoacetic acid, and other trihalomethanes and haloacetic acids in drinking water, PLOS One, Vol: 8, ISSN: 1932-6203
An optimized method is presented using liquid-liquid extraction and derivatization for the extraction of iodoacetic acid (IAA) and other haloacetic acids (HAA9) and direct extraction of iodoform (IF) and other trihalomethanes (THM4) from drinking water, followed by detection by gas chromatography with electron capture detection (GC-ECD). A Doehlert experimental design was performed to determine the optimum conditions for the five most significant factors in the derivatization step: namely, the volume and concentration of acidic methanol (optimized values = 15%, 1 mL), the volume and concentration of Na2SO4 solution (129 g/L, 8.5 mL), and the volume of saturated NaHCO3 solution (1 mL). Also, derivatization time and temperature were optimized by a two-variable Doehlert design, resulting in the following optimized parameters: an extraction time of 11 minutes for IF and THM4 and 14 minutes for IAA and HAA9; mass of anhydrous Na2SO4 of 4 g for IF and THM4 and 16 g for IAA and HAA9; derivatization time of 160 min and temperature at 40°C. Under optimal conditions, the optimized procedure achieves excellent linearity (R2 ranges 0.9990–0.9998), low detection limits (0.0008–0.2 µg/L), low quantification limits (0.008–0.4 µg/L), and good recovery (86.6%–106.3%). Intra- and inter-day precision were less than 8.9% and 8.8%, respectively. The method was validated by applying it to the analysis of raw, flocculated, settled, and finished waters collected from a water treatment plant in China.
Todman LC, Ireson AM, Butler AP, et al., 2013, Modelling vapor flow from a pervaporative irrigation system, Vadose Zone Journal
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