Emerging contaminants in groundwater - NERC Open Research ...
Emerging contaminants in groundwater - NERC Open Research ...
Emerging contaminants in groundwater - NERC Open Research ...
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OR/11/013<br />
A feature of some emerg<strong>in</strong>g <strong>contam<strong>in</strong>ants</strong> is their recalcitrance to sewage treatment or<br />
dr<strong>in</strong>k<strong>in</strong>g water treatment which allows them to pass through <strong>in</strong>to the treated water. Filtration<br />
us<strong>in</strong>g granulated activated carbon (GAC) has been used widely to remove organic<br />
micropollutants from dr<strong>in</strong>k<strong>in</strong>g water. However, small and/or very polar molecules can be<br />
difficult to remove by this method. Stackelberg et al. (2007) showed that there was<br />
substantial but not complete degradation or removal of 113 organic micropollutants by<br />
conventional DWT. Gibs et al. (2007) showed that 50 out of 98 such <strong>contam<strong>in</strong>ants</strong> did not<br />
substantially degrade <strong>in</strong> the presence of chlor<strong>in</strong>e dur<strong>in</strong>g typical residence times <strong>in</strong> dr<strong>in</strong>k<strong>in</strong>g<br />
water distribution systems.<br />
The octanol/water partition coefficient (Kow) has been used to provide an analogue of removal<br />
recalcitrance, with polar compounds hav<strong>in</strong>g a low or negative log (Kow). Figure 2.1 shows the<br />
time taken for breakthrough of selected pesticides us<strong>in</strong>g GAC annotated with the Kow value. A<br />
number of widely used compounds are poorly removed. Johnson et al. (2007b) demonstrate<br />
that removal of some oestrogens can be as low as 30%.<br />
Other treatment options can be:<br />
use of powdered active carbon (PAC) which has a higher surface area<br />
ozonation<br />
nano-filtration. Verliefde et al. (2007) assess nano-filtration as a solution us<strong>in</strong>g a<br />
priority list of micropollutants<br />
However it has been questioned whether advanced treatment to remove endocr<strong>in</strong>e disrupt<strong>in</strong>g<br />
compounds and pharmaceuticals from wastewater is cost-effective due to the <strong>in</strong>creased energy<br />
consumption and associated economic costs and CO2 emissions (Jones et al., 2007; 2005).<br />
Pesticide concentration (µg/L)<br />
Figure 2.1 Concentration versus GAC performance annotated with log Kow for selected pesticides<br />
(after Hall, 2010)<br />
2.3 ‘RECEPTOR’ CONCEPTS: HAZARDS<br />
Receptors can be humans dr<strong>in</strong>k<strong>in</strong>g tap water, other liv<strong>in</strong>g creatures such as <strong>in</strong>vertebrates and<br />
fish, or the environment more widely. Risks to the receptor depend upon the hazards related<br />
to the contam<strong>in</strong>ant <strong>in</strong> question and the frequency and concentration of exposure to that<br />
substance. Here we give an overview of two hazards, toxicity and endocr<strong>in</strong>e disruption,<br />
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