<?xml version="1.0" encoding="utf-8"?><rss version="2.0"><channel><title>DWESD - Latest Articles</title><link>http://www.drink-water-eng-sci-discuss.net/</link><description>Drinking Water Engineering and Science Discussions Latest Articles</description><language>en</language><item><title>Metals releases and disinfection byproduct formation in domestic wells following shock chlorination</title><link>http://www.drink-water-eng-sci-discuss.net/3/177/2010/</link><description>&lt;b&gt;Metals releases and disinfection byproduct formation in domestic wells following shock chlorination&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 177-198, 2010&lt;br /&gt;&lt;br /&gt;Author(s): M. Walker and J. Newman&lt;br /&gt;&lt;br /&gt;Shock chlorination is used for rapid disinfection to control pathogens and
nuisance bacteria in domestic wells. A typical shock chlorination procedure
involves adding sodium hypochlorite in liquid bleach solutions to achieve
concentrations of free chlorine of up to 200 ppm in the standing water of a
well. The change in pH and oxidation potential may bring trace metals from
aquifer materials into solution and chlorine may react with dissolved
organic carbon to form disinfection byproducts. We carried out experiments
with four wells to observe and determine the persistence of increased
concentrations of metals and disinfection byproducts. Water samples from
shock chlorinated wells were analyzed for Pb, Cu, As, radionuclides and
disinfection byproducts (haloacetic acids and trihalomethanes), immediately
prior to treatment, after sufficient contact time with chlorine had elapsed,
and at intervals determined by the number of casing volumes purged, for up
to four times the well casing volume.

&lt;br&gt;&lt;br&gt;
Elevated concentrations of lead and copper dissipated in proportion to free
chlorine (measured semi-quantitatively) during the purging process.
Trihalomethanes and haloacetic acids were formed in wells during
disinfection. In one of two wells tested, disinfection byproducts dissipated
in proportion to free chlorine during purging. However, one well retained
disinfection byproducts and free chlorine after four well volumes had been
purged. Although metals returned to background concentrations in this well,
disinfection byproducts remained elevated, though below the MCL, likely
because purging volume was insufficient. Simple chlorine test strips may be
a useful method for indicating when purging is adequate to remove metals and
disinfection by-products mobilized and formed by shock chlorination.</description><pubDate>Fri, 04 Jun 2010 00:00:00 +0200</pubDate></item><item><title>Understanding and managing large sensor networks</title><link>http://www.drink-water-eng-sci-discuss.net/3/149/2010/</link><description>&lt;b&gt;Understanding and managing large sensor networks&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 149-175, 2010&lt;br /&gt;&lt;br /&gt;Author(s): D. D. Ediriweera and I. W. Marshall&lt;br /&gt;&lt;br /&gt;The water supply industry is trialing a range of sensor network
designs for monitoring distributed infrastructure. The paper investigates
the performance of such a sensor system deployed to monitor a water
distribution network. The study reveals up to one fifth of the data intended
to be collected either to be missing or erroneous. Findings reinforce the
importance of in-depth design consideration of all aspects of large scale
sensor systems, and the necessity for expertise on every detail of the
system, or access to a rule set which embeds this knowledge allowing
non-specialists to make near optimal choices. First steps towards defining
such a rule set is presented here with supporting evidence.</description><pubDate>Mon, 12 Apr 2010 00:00:00 +0200</pubDate></item><item><title>Negative pressures in full-scale distribution system: field investigation, modelling, estimation of intrusion volumes and risk for public health</title><link>http://www.drink-water-eng-sci-discuss.net/3/133/2010/</link><description>&lt;b&gt;Negative pressures in full-scale distribution system: field investigation, modelling, estimation of intrusion volumes and risk for public health&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 133-148, 2010&lt;br /&gt;&lt;br /&gt;Author(s): M. C. Besner, G. Ebacher, B. S. Jung, B. Karney, J. Lavoie, P. Payment, and M. Prévost&lt;br /&gt;&lt;br /&gt;Various investigations encompassing microbial characterization of external
sources of contamination (soil and trenchwater surrounding water mains,
flooded air-valve vaults), field pressure monitoring, and hydraulic and
transient analyses were conducted in the same distribution system where two
epidemiological studies showing an increase in gastrointestinal illness for
people drinking tap water were conducted in the 1990's. Interesting results
include the detection of microorganisms indicators of fecal contamination in
all external sources investigated but at a higher frequency in the water
from flooded air-valve vaults, and the recording of 18 negative pressure
events in the distribution system during a 17-month monitoring period.
Transient analysis of this large and complex distribution system was
challenging and highlighted the need to consider field pressure data in the
process.</description><pubDate>Fri, 12 Mar 2010 00:00:00 +0100</pubDate></item><item><title>Effects of ozonation and temperature on biodegradation of natural organic matter in biological granular activated carbon filters</title><link>http://www.drink-water-eng-sci-discuss.net/3/107/2010/</link><description>&lt;b&gt;Effects of ozonation and temperature on biodegradation of natural organic matter in biological granular activated carbon filters&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 107-132, 2010&lt;br /&gt;&lt;br /&gt;Author(s): L. T. J. van der Aa, L. C. Rietveld, and J. C. van Dijk&lt;br /&gt;&lt;br /&gt;Four pilot (biological) granular activated carbon ((B)GAC) filters were
operated to quantify the effects of ozonation and water temperature on the
biodegradation of natural organic matter (NOM) in (B)GAC filters. Removal of
dissolved organic carbon (DOC), assimilable organic carbon (AOC) and oxygen
and the production of carbon dioxide were taken as indicators for NOM
biodegradation. Ozonation stimulated DOC and AOC removal in the BGAC
filters, but had no significant effect on oxygen removal and carbon dioxide
production. The temperature had no significant effect on DOC and AOC
removal, while oxygen removal and carbon dioxide production increased with
increasing temperature. Multivariate linear regression was used to quantify
these relations. In summer the ratio between oxygen consumption and DOC
removal exceeded the theoretical maximum of 2.5 g O&lt;sub&gt;2&lt;/sub&gt;&amp;middot;g C&lt;sup&gt;&amp;minus;1&lt;/sup&gt;
and the ratio between carbon dioxide production and DOC removal exceeded the
theoretical maximum of 3.7 g CO&lt;sub&gt;2&lt;/sub&gt;&amp;middot;g C&lt;sup&gt;&amp;minus;1&lt;/sup&gt;. Bioregeneration of
large NOM molecules could explain this excesses and the non-correlation
between DOC and AOC removal and oxygen removal and carbon dioxide
production. However bioregeneration of large NOM molecules was considered
not likely to happen, due to sequestration.</description><pubDate>Mon, 01 Feb 2010 00:00:00 +0100</pubDate></item><item><title>Rapid evaluation of water supply project feasibility in Kolkata, India</title><link>http://www.drink-water-eng-sci-discuss.net/3/65/2010/</link><description>&lt;b&gt;Rapid evaluation of water supply project feasibility in Kolkata, India&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 65-105, 2010&lt;br /&gt;&lt;br /&gt;Author(s): K. Dutta Roy, B. Thakur, T. S. Konar, and S. N. Chakrabarty&lt;br /&gt;&lt;br /&gt;Mega cities in developing countries are mostly dependent on external funding
for improving the civic infrastructures like water supply. International and
sometimes national agencies stipulate financial justifications for
infrastructure funding. Expansion of drinking water network with external
funding therefore requires explicit economic estimates. A methodology
suitable for local condition has been developed in this study. Relevant
field data were collected for estimating the cost of supply. The artificial
neural network technique has been used for cost estimate. The willingness to
pay survey has been used for estimating the benefits. Cost and benefit have
been compared with consideration of time value of money. The risk and
uncertainty have been investigated by Monte Carlo's simulation and
sensitivity analysis. The results in this case indicated that consumers were
willing to pay for supply of drinking water. It has been also found that
supply up to 20 km from the treatment plant is economical after which new
plants should be considered. The study would help to plan for economically
optimal improvement of water supply. It could be also used for estimating
the water tariff structure for the city.</description><pubDate>Fri, 22 Jan 2010 00:00:00 +0100</pubDate></item><item><title>MUWS (Microbiology in Urban Water Systems) – an interdisciplinary approach to study microbial communities in urban water systems</title><link>http://www.drink-water-eng-sci-discuss.net/3/43/2010/</link><description>&lt;b&gt;MUWS (Microbiology in Urban Water Systems) – an interdisciplinary approach to study microbial communities in urban water systems&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 43-64, 2010&lt;br /&gt;&lt;br /&gt;Author(s): P. Deines, R. Sekar, H. S. Jensen, S. Tait, J. B. Boxall, A. M. Osborn, and C. A. Biggs&lt;br /&gt;&lt;br /&gt;&lt;b&gt;M&lt;/b&gt;icrobiology in &lt;b&gt;U&lt;/b&gt;rban &lt;b&gt;W&lt;/b&gt;ater &lt;b&gt;S&lt;/b&gt;ystems
(MUWS) is an integrated project, which aims to characterize the
microorganisms found in both potable water distribution systems and sewer
networks. These large infrastructure systems have a major impact on our
quality of life, and despite the importance of these systems as major
components of the water cycle, little is known about their microbial
ecology. Potable water distribution systems are large, highly interconnected
and dynamic, and difficult to control. Sewer systems are also large and
subject to time varying inputs and demands. Their performance also faces
increasing loading due to increasing urbanization and longer-term
environmental changes. Therefore, understanding the link between microbial
ecology and any potential impacts on short or long-term engineering
performance is important. By combining the strengths and research expertise
of civil-, biochemical engineers and molecular microbial ecologists, we aim
to link the abundance and diversity of microorganisms to physical and
engineering variables so that novel insights into the ecology of
microorganisms within both water distribution systems and sewer networks can
be explored. By presenting the details of this multidisciplinary approach,
and the principals behind the molecular microbiological methods and
techniques that we use, this paper will demonstrate the potential of an
integrated approach to better understand urban water system function and so
meet future challenges.</description><pubDate>Fri, 22 Jan 2010 00:00:00 +0100</pubDate></item><item><title>I-WARP: individual water main renewal planner</title><link>http://www.drink-water-eng-sci-discuss.net/3/25/2010/</link><description>&lt;b&gt;I-WARP: individual water main renewal planner&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 25-41, 2010&lt;br /&gt;&lt;br /&gt;Author(s): Y. Kleiner and B. Rajani&lt;br /&gt;&lt;br /&gt;I-WARP is based upon a nonhomogeneous Poisson approach to model breakage
rates in individual water mains. The structural deterioration of water mains
and their subsequent failure are affected by many factors, both static
(e.g., pipe material, pipe size, age (vintage), soil type) and dynamic
(e.g., climate, cathodic protection, pressure zone changes). I-WARP allows
for the consideration of both static and dynamic factors in the statistical
analysis of historical breakage patterns. This paper describes the
mathematical approach and demonstrates its application with the help of a
case study. The research project within which I-WARP was developed, was
jointly funded by the National Research Council of Canada (NRC), and the
Water Research foundation (formerly known as the American Water Works
Association Research Foundation – AwwaRF) and supported by water utilities
from USA and Canada.</description><pubDate>Wed, 13 Jan 2010 00:00:00 +0100</pubDate></item><item><title>A bottom-up approach of stochastic demand allocation in water quality modelling</title><link>http://www.drink-water-eng-sci-discuss.net/3/1/2010/</link><description>&lt;b&gt;A bottom-up approach of stochastic demand allocation in water quality modelling&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 3, 1-24, 2010&lt;br /&gt;&lt;br /&gt;Author(s): E. J. M. Blokker, J. H. G. Vreeburg, H. Beverloo, M. Klein Arfman, and J. C. van Dijk&lt;br /&gt;&lt;br /&gt;An &quot;all pipes&quot; hydraulic model of a DMA-sized drinking water
distribution system was constructed with two types of demand allocations.
One is constructed with the conventional top-down approach, i.e. a demand
multiplier pattern from the booster station is allocated to all demand nodes
with a correction factor to account for the average water demand on that
node. The other is constructed with a bottom-up approach of demand
allocation, i.e., each individual home is represented by one demand node
with its own stochastic water demand pattern.
&lt;br&gt;&lt;br&gt;
The stochastic water demand patterns are constructed with an end-use model
on a per second basis and per individual home. The flow entering the test
area was measured and a tracer test with sodium chloride was performed to
measure travel times. The two models were evaluated on the predicted sum of
demands and travel times, compared with what was measured in the test area.
&lt;br&gt;&lt;br&gt;
The new bottom-up approach performs at least as well as the conventional
top-down approach with respect to total demand and travel times, without the
need for any flow measurements or calibration measurements. The bottom-up
approach leads to a stochastic method of hydraulic modelling and gives
insight into the variability of travel times as an added feature beyond the
conventional way of modelling.</description><pubDate>Mon, 04 Jan 2010 00:00:00 +0100</pubDate></item><item><title>Online modelling of water distribution systems: a UK case study</title><link>http://www.drink-water-eng-sci-discuss.net/2/279/2009/</link><description>&lt;b&gt;Online modelling of water distribution systems: a UK case study&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 279-294, 2009&lt;br /&gt;&lt;br /&gt;Author(s): J. Machell, S. R. Mounce, and J. B. Boxall&lt;br /&gt;&lt;br /&gt;Hydraulic simulation models of water distribution networks are routinely
used for operational investigations and network design purposes. However,
their full potential is often never realised because, in the majority of
cases, they have been calibrated with data collected manually from the field
during a single historic time period and, as such, reflect the network
operational conditions that were prevalent at that time, and they are then
applied as part of a reactive, desktop investigation. In order to use a
hydraulic model to assist proactive distribution network management its
element asset information must be up to date and it should be able to access
current network information to drive simulations. Historically this advance
has been restricted by the high cost of collecting and transferring the
necessary field measurements. However, recent innovation and cost reductions
associated with data transfer is resulting in collection of data from
increasing numbers of sensors in water supply systems, and automatic
transfer of the data to point of use. This means engineers potentially have
access to a constant stream of current network data that enables a new era
of &quot;online&quot; modelling that can be used to continually assess standards of
service compliance for pressure and reduce the impact of network events,
such as mains bursts, on customers. A case study is presented here that
shows how an online modelling system can give timely warning of changes from
normal network operation, providing capacity to minimise customer impact.</description><pubDate>Wed, 23 Dec 2009 00:00:00 +0100</pubDate></item><item><title>Fluorescence spectroscopy as a tool for determination of organic matter removal efficiency at water treatment works</title><link>http://www.drink-water-eng-sci-discuss.net/2/259/2009/</link><description>&lt;b&gt;Fluorescence spectroscopy as a tool for determination of organic matter removal efficiency at water treatment works&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 259-278, 2009&lt;br /&gt;&lt;br /&gt;Author(s): M. Z. Bieroza, J. Bridgeman, and A. Baker&lt;br /&gt;&lt;br /&gt;Organic matter (OM) in drinking water treatment is a common
impediment responsible for increased coagulant and disinfectant dosages,
formation of carcinogenic disinfection-by products, and microbial re-growth
in distribution system. The inherent heterogeneity of OM implies the
utilization of advanced analytical techniques for its characterization and
assessment of removal efficiency. Here, the application of simple
fluorescence excitation-emission technique to OM characterization in
drinking water treatment is presented. The fluorescence data of raw and
clarified water was obtained from 16 drinking water treatment works. The
reduction in fulvic-like fluorescence was found to significantly correlate
with OM removal measured with total organic carbon (TOC). Fluorescence
properties, fulvic- and tryptophan-like regions, were found to discriminate
OM fractions of different removal efficiencies.

&lt;br&gt;&lt;br&gt;
The results obtained in the study show that fluorescence spectroscopy
provides a rapid and accurate characterization and quantification of OM
fractions and indication of their treatability in conventional water
treatment.</description><pubDate>Wed, 23 Dec 2009 00:00:00 +0100</pubDate></item><item><title>NOM characterization and removal at six Southern African water treatment plants</title><link>http://www.drink-water-eng-sci-discuss.net/2/231/2009/</link><description>&lt;b&gt;NOM characterization and removal at six Southern African water treatment plants&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 231-257, 2009&lt;br /&gt;&lt;br /&gt;Author(s): J. Haarhoff, M. Kubare, B. Mamba, R. Krause, T. Nkambule, B. Matsebula, and J. Menge&lt;br /&gt;&lt;br /&gt;Organic pollution is a major concern during drinking water treatment. Major
challenges attributed to organic pollution include the proliferation of
pathogenic micro-organisms, prevalence of toxic and physiologically
disruptive organic micropollutants, and quality deterioration in water
distribution systems. A major component of organic pollution is natural
organic matter (NOM). The operational mechanisms of most unit processes are
well understood. However, their interaction with NOM is still the subject of
scientific research. This paper takes the form of a metastudy to capture
some of the experiences with NOM monitoring and analysis at a number of
Southern African Water Treatment Plants. It is written from the perspective
of practical process selection, to try and coax some pointers from the
available data for the design of more detailed pilot work. NOM was tracked
at six water treatment plants using dissolved organic carbon (DOC)
measurements. Fractionation of the DOC based on biodegradability and
molecular weight distribution was done at a water treatment plant in
Namibia. A third fractionation technique using ion exchange resins was used
to assess the impact of ozonation on DOC. DOC measurements alone did not
give much insight into NOM evolution through the treatment train. The more
detailed characterization techniques showed that different unit processes
preferentially remove different NOM fractions. Therefore these techniques
provide better information for process design and optimisation than the DOC
measurement which is routinely done during full scale operation at these
water treatment plants. Further work will focus on streamlining and
improving the reproducibility of selected fractionation techniques,
characterization of NOM from different water sources, and synthesis of the
results into a systematic, practical guideline for process design and
optimisation.</description><pubDate>Tue, 10 Nov 2009 00:00:00 +0100</pubDate></item><item><title>Optimized conditions for application of organic flocculant aids in water purification</title><link>http://www.drink-water-eng-sci-discuss.net/2/205/2009/</link><description>&lt;b&gt;Optimized conditions for application of organic flocculant aids in water purification&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 205-229, 2009&lt;br /&gt;&lt;br /&gt;Author(s): P. Polasek&lt;br /&gt;&lt;br /&gt;The application of organic flocculant aid (OFA) to a system undergoing
aggregation has a direct effect on the quality of purified water as well as
the settleability of resultant agglomerates. The optimum conditions for OFA
application exist when the formation of aggregates by means of
destabilisation (aggregation – CPE) reagent reaches flocculation optimum,
i.e. the measure of flocculation &amp;gamma;=1, prior to OFA addition. Such method of
OFA application is called the Post-Orthokinetic Agglomeration (POA) process.
The POA process results in the formation of the fastest settleable
agglomerates and the best quality of purified water matching that attainable
without the use of OFA. Recirculation of the sludge conditioned by OFA back
to the process of particle aggregation was found undesirable as it adversely
affects the purified water quality as well as the settleability of produced
agglomerates.</description><pubDate>Tue, 03 Nov 2009 00:00:00 +0100</pubDate></item><item><title>Development of a predictive model to determine micropollutant removal using granular activated carbon</title><link>http://www.drink-water-eng-sci-discuss.net/2/189/2009/</link><description>&lt;b&gt;Development of a predictive model to determine micropollutant removal using granular activated carbon&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 189-204, 2009&lt;br /&gt;&lt;br /&gt;Author(s): D. J. de Ridder, M. McConville, A. R. D. Verliefde, L. T. J. van der Aa, S. G. J. Heijman, J. Q. J. C. Verberk, L. C. Rietveld, and J. C. van Dijk&lt;br /&gt;&lt;br /&gt;The occurrence of organic micropollutants in drinking water and its sources
has opened up a field of study related to monitoring concentration levels in
water sources, evaluating their toxicity and estimating their removal in
drinking water treatment processes. Because a large number of organic
micropollutants is currently present (although in relatively low
concentrations) in drinking water sources, a method should be developed to
select which micropollutants has to be evaluated with priority. In this
paper, a screening model is presented that can predict solute removal by
activated carbon, in ultrapure water and in natural water. Solute removal
prediction is based on a combination of solute hydrophobicity (expressed as
log D, the pH corrected log &lt;i&gt;K&lt;sub&gt;ow&lt;/sub&gt;&lt;/i&gt;), solute charge and the carbon dose.
Solute molecular weight was also considered as model input parameter, but
this solute property appeared to relate insufficiently to solute removal.
&lt;br&gt;&lt;br&gt;
Removal of negatively charged solutes by preloaded activated carbon was
reduced while the removal of positively charged solutes was increased,
compared with freshly regenerated activated carbon. Differences in charged
solute removal by freshly regenerated activated carbon were small,
indicating that charge interactions are an important mechanism in adsorption
onto preloaded carbon. The predicted solute removal was within 20
removal-% deviation of experimentally measured values.</description><pubDate>Tue, 13 Oct 2009 00:00:00 +0200</pubDate></item><item><title>NOM removal technologies – Norwegian experiences</title><link>http://www.drink-water-eng-sci-discuss.net/2/161/2009/</link><description>&lt;b&gt;NOM removal technologies – Norwegian experiences&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 161-187, 2009&lt;br /&gt;&lt;br /&gt;Author(s): H. Ødegaard, S. Østerhus, E. Melin, and B. Eikebrokk&lt;br /&gt;&lt;br /&gt;The paper gives an overview of the methods for removal of natural organic
matter (NOM), particularly humic substances (HS), in water with focus on the
Norwegian experiences. It is demonstrated that humic substances may be
removed by a variety of methods, such as; molecular sieving through
nanofiltration membranes, coagulation with subsequent floc separation
(including granular media or membrane filtration), oxidation followed by
biofiltration and sorption processes including chemisorption (ion exchange)
and physical adsorption (activated carbon). All these processes are in use in
Norway and the paper gives an overview of the operational experiences.</description><pubDate>Fri, 09 Oct 2009 00:00:00 +0200</pubDate></item><item><title>Water quality and treatment of river bank filtrate</title><link>http://www.drink-water-eng-sci-discuss.net/2/127/2009/</link><description>&lt;b&gt;Water quality and treatment of river bank filtrate&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 127-159, 2009&lt;br /&gt;&lt;br /&gt;Author(s): W. W. J. M. de Vet, C. C. A. van Genuchten, M. C. M. van Loosdrecht, and J. C. van Dijk&lt;br /&gt;&lt;br /&gt;In drinking water production, river bank filtration has the advantages of
dampening peak concentrations of many dissolved components, substantially
removing many micropollutants and removing, virtually completely, the
pathogens and suspended solids. The production aquifer is not only fed by
the river bank infiltrate but also by water percolating through covering
layers. In the polder areas, these top layers consist of peat and deposits
from river sediments and sea intrusions.

&lt;br&gt;&lt;br&gt;
This paper discusses the origin and fate of macro pollutants in river bank
filtrate, based on extensive full-scale measurements in well fields and
treatment systems of the Drinking Water Company Oasen in the Netherlands.
First, it clarifies and illustrates redox reactions and the mixing of river
bank filtrate and polder water as the dominant processes determining the raw water
quality for drinking water production. Next, full-scale results are
elaborated on to evaluate trickling filtration as an efficient and proven
one-step process to remove methane, iron, ammonium and manganese. The
interaction of methane and manganese removal with nitrification in these
systems is further analyzed. Methane is mostly stripped during trickling
filtration and its removal hardly interferes with nitrification. Under
specific conditions, microbial manganese removal may play a dominant
role.</description><pubDate>Tue, 06 Oct 2009 00:00:00 +0200</pubDate></item><item><title>Impact of decreasing water demand on bank filtration in Saxony, Germany</title><link>http://www.drink-water-eng-sci-discuss.net/2/101/2009/</link><description>&lt;b&gt;Impact of decreasing water demand on bank filtration in Saxony, Germany&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 101-126, 2009&lt;br /&gt;&lt;br /&gt;Author(s): T. Grischek, D. Schoenheinz, C. Syhre, and K. Saupe&lt;br /&gt;&lt;br /&gt;Bank filtration has been of main importance for the drinking water supply in
Germany for many decades. The water quality of pumped raw water from bank
filtration sites depends to a high degree on the water quality of the
infiltrating surface water and the landside groundwater, the mixing portion
of both as well as the flow and transport conditions in the aquifer. Since
the improvement of river water quality and a drastic decrease in water
demand during the last 15 years in Germany, the influence of landside
groundwater quality has become more important for the raw water quality of
waterworks relying on bank filtration. The hydrogeologic analysis of three
bank filtration sites in Saxony and the management of abstraction rates and
well operation in response to fluctuating water demand are discussed. In
conclusion, a general overview on management options for bank filtration
sites is provided.</description><pubDate>Thu, 27 Aug 2009 00:00:00 +0200</pubDate></item><item><title>Removal of radio &lt;i&gt;N&lt;/i&gt;-nitrosodimethylamine (NDMA) from drinking water by coagulation and Powdered Activated Carbon (PAC) adsorption</title><link>http://www.drink-water-eng-sci-discuss.net/2/79/2009/</link><description>&lt;b&gt;Removal of radio &lt;i&gt;N&lt;/i&gt;-nitrosodimethylamine (NDMA) from drinking water by coagulation and Powdered Activated Carbon (PAC) adsorption&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 79-100, 2009&lt;br /&gt;&lt;br /&gt;Author(s): J. Chung, Y. Yoon, M. Kim, S.-B. Lee, H.-J. Kim, and C.-K. Choi&lt;br /&gt;&lt;br /&gt;The presence of &lt;i&gt;N&lt;/i&gt;-nitrosodimethylamine (NDMA) in drinking water supplies has
raised concern over its removal by common drinking water treatment processes.
A simple detection method based on scintillation spectroscopy has been used
to quantify the concentration of &lt;sup&gt;14&lt;/sup&gt;C-labeled NDMA at various ratios of
sample to scintillation liquid. Without sample pretreatment, the method
detection limits are 0.91, 0.98, 1.23, and 1.45 ng/L of NDMA at
scintillation intensity ratios of 10:10, 5:15, 15:5, and 2.5:17.5 (sample:
scintillation liquid), respectively. The scintillation intensity in all cases
is linear (&lt;i&gt;R&lt;/i&gt;&lt;sup&gt;2&lt;/sup&gt;&gt;0.99) and is in the range of 0 to 100 ng/L of NDMA. In
addition, because scintillation intensity is independent of solution pH,
conductivity, and background electrolyte ion types, a separate calibration
curve is unnecessary for NDMA samples at different solution conditions.
Bench-scale experiments were performed to simulate individual treatment
processes, which include coagulation and adsorption by powdered activated
carbon (PAC), as used in a drinking water treatment plant, and biosorption, a
technique used in biological treatment of waste water. The commonly used
coagulation process for particulate control and biosorption is ineffective
for removing NDMA (&lt;10% by coagulation and &lt;20% by biosorption).
However, high doses of PAC may be applied to remove NDMA.</description><pubDate>Tue, 31 Mar 2009 00:00:00 +0200</pubDate></item><item><title>Technical Note: Community of bacteria attached on the PVDF MF membrane surface fouled from drinking water treatment, in Seoul, Korea</title><link>http://www.drink-water-eng-sci-discuss.net/2/65/2009/</link><description>&lt;b&gt;Technical Note: Community of bacteria attached on the PVDF MF membrane surface fouled from drinking water treatment, in Seoul, Korea&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 65-77, 2009&lt;br /&gt;&lt;br /&gt;Author(s): Kyongmi Chon, Kangmin Chon, Jin-Soo Chang, Heekyong Oh, Euisin Lee, and Jaeweon Cho&lt;br /&gt;&lt;br /&gt;Alpha, beta, and gamma proteobacteria comprise approximate 68, 16, and 7%
of all identified bacteria. In this study, bacterial communities that
had fouled polyvinylidene fluoride microfiltration membranes, which are used
for drinking water treatment, over an 18 month period were analyzed using
the 16s rRNA gene clone library method. The alpha, beta, and gamma
proteobacteria were composed of mainly &lt;i&gt;Bradyrhizobium&lt;/i&gt; and &lt;i&gt;Rhodopseudomonas&lt;/i&gt;,
&lt;i&gt;Ralstonia&lt;/i&gt;, and &lt;i&gt;Legionella&lt;/i&gt;, respectively. The
presence of a relatively high amount of alpha proteobacteria was due to the
oligotrophic condition of the drinking water source, the Han River, tested
in this specific case study. The second most prominent bacteria community
was the beta proteobacteria, which are typically found in a freshwater
environment. This finding supports the notion that the drinking water source
was relatively clean. Analyses of the organic foulants indicated that the
they were most likely from extra cellular polymers and/or cell fractured
chemicals from bacteria or micro-organisms, as identified using organic
characterizing tools, including 3 dimensional fluorescence
excitation-emission matrix and Fourier transform IR analyses.</description><pubDate>Mon, 02 Mar 2009 00:00:00 +0100</pubDate></item><item><title>Arsenic in drinking water: not just a problem for Bangladesh</title><link>http://www.drink-water-eng-sci-discuss.net/2/51/2009/</link><description>&lt;b&gt;Arsenic in drinking water: not just a problem for Bangladesh&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 51-64, 2009&lt;br /&gt;&lt;br /&gt;Author(s): D. van Halem, S. A. Bakker, G. L. Amy, and J. C. van Dijk&lt;br /&gt;&lt;br /&gt;For more than a decade it has been known that shallow tube wells in
Bangladesh are frequently contaminated with arsenic concentrations at a
level that is harmful to human health. By now it is becoming clear that a
disaster of an unheard magnitude is going on: the World Health Organization
fears that in the near future 1 in every 10 adult deaths in Bangladesh will
be caused by arsenic-related cancers. Other studies show that problems with
arsenic in groundwater/drinking water occur in many more countries
worldwide, such as in the USA and China. In Europe the focus on arsenic
problems is confined to countries with high arsenic levels in their
groundwater, such as Romania, Hungary and Italy. In most other European
countries, the naturally occurring arsenic concentrations are lower than the
drinking water standard of 10 μg L&lt;sup&gt;&amp;minus;1&lt;/sup&gt;. However, from the literature
review presented in this paper, it may also be concluded that using the
European standard, health risks cannot be excluded. It is therefore
recommended that the current arsenic standard be reconsidered.</description><pubDate>Thu, 26 Feb 2009 00:00:00 +0100</pubDate></item><item><title>Spatial and temporal variability of heavy metals in streams of the Flint Creek and Flint River Watersheds from non-point sources</title><link>http://www.drink-water-eng-sci-discuss.net/2/25/2009/</link><description>&lt;b&gt;Spatial and temporal variability of heavy metals in streams of the Flint Creek and Flint River Watersheds from non-point sources&lt;/b&gt;&lt;br /&gt;&lt;br /&gt;Drinking Water Engineering and Science Discussions, 2, 25-49, 2009&lt;br /&gt;&lt;br /&gt;Author(s): I. Abdi, T. Tsegaye, M. Silitonga, and W. Tadesse&lt;br /&gt;&lt;br /&gt;Throughout the United States, non-point pollution is responsible for large
quantities of heavy metals entering bodies of water. Pollution as a result
of heavy metals can impact drinking water supplies, recreation, fisheries,
and aquatic species. Presence of heavy metals such as lead (Pb), cadmium
(Cd), and chromium (Cr), in surface water may pose great risks to human
health as well as to aquatic animals. In order to understand water quality
changes due to heavy metal elements and pH as a result of spatial and
temporal variability and land use/land cover changes, there is a need to
monitor water bodies on a constant basis. The purpose of this investigation
was to assess the impacts of spatial and temporal variability on heavy
metals and pH as a result of land use/land cover changes and provide a
baseline for future water quality study from non-point sources in two
watersheds. Spatial and temporal variability factors were not significant
for all the heavy metal elements. Significant water quality changes occurred
between 2003 and 2004 for the two of the five heavy metals (Pb, and Ni) and
pH. However, this was not true for the other of heavy metals investigated
(Cd, Cr, and Zn). There was no influence of watershed observed for any of
the heavy metals and pH in this study. To accurately quantify environmental
impacts of heavy metals as well as pH, land use changes, and natural
processes leading to spatial and temporal variability of water quality
variables, continuous monitoring of surface water is necessary to improve
the water quality of these watersheds.</description><pubDate>Mon, 23 Feb 2009 00:00:00 +0100</pubDate></item></channel></rss>