Chapter 3 Decision Support Model (IUWS-DSM) - Tubdok
Chapter 3 Decision Support Model (IUWS-DSM) - Tubdok
Chapter 3 Decision Support Model (IUWS-DSM) - Tubdok
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
<strong>Chapter</strong> 2 · New Conception 35<br />
irrigate the restricted green area in the neighbourhood. In some situations, the treatment is<br />
even unnecessary. On the contrary, the larger pipe system can be required. Importantly for<br />
both cases, if the reclaimed water may expose to human beings, it must be hygienic safe.<br />
Indirect potable reuse. It is defined as after being buffered and recovered in nature for<br />
certain period, the reclaimed water is used for raw water supply. Unconsciously, water is<br />
already being reused in such manner. For example, the treated or even untreated sewage<br />
discharged upriver will be used as source water for water consumers downstream. By<br />
treating the used water into very high quality (Quality A(1)), the recovering period of used<br />
water is accelerated, whereby the local area gains more source water, and at the same time<br />
the risks can be better monitored and hereby reduced. Several methods are practised for<br />
indirect potable water reuse, typically groundwater recharge and river bank filtration. The<br />
additional treatment is added to the mixture of raw and reclaimed water before distribution as<br />
drinking water (Metcalf & Eddy 2007).<br />
The reclaimed water can be also directly reused as drinking water without intervening<br />
storage. There are only a few cases of direct potable reuse implemented in situations of<br />
extreme water scarcity, e.g. in Windhoek, Namibia (Du Pisani 2006), However, it is still not<br />
universally accepted by our society and in fact the public often rejects water recycling<br />
activities (Dolnicar and Schäfer 2006). Thus, direct potable reuse is not involved in <strong>IUWS</strong>.<br />
Source separated collection system (SSCS). For enhancing the efficiency of water<br />
reuse system, one method is to control the pollution sources. Particularly, the urban toilet<br />
system needs to be rethought, as it contains most hygienic dangerous substances. Hence,<br />
SSCS becomes an option for sewer systems.<br />
Since different domestic sewage streams have different water characteristics (see §<br />
2.1.4.1), they should be collected separately, so that they can be better handled with<br />
specified methods. SSCS has significant advantages. First of all, the reclamation and reuse<br />
of greywater become easier, as it contains less hygienically dangerous substances. If<br />
vacuum toilets are installed, plenty of water can be saved. Meantime, valuable nutrients can<br />
be regained such as N and P, and the renewable energy (i.e. biogas) can be generated, as<br />
well.<br />
However, SSCS requires an additional and costly collection system as well as the<br />
additional treatment and storage systems for blackwater (or for brownwater + urine). As a<br />
result, the total system can be quite expensive. Therefore, the SSCS would be the proper<br />
option for water entities having medium or small sizes, whereby the large collection system<br />
can be avoided.<br />
Separate or combined sewerage. Separate sewerage systems transport urban sewage<br />
and storm water in two independent systems, where combined sewerage systems gather<br />
them together in one system. Both types have advantages and disadvantages, and they are<br />
widely implemented. Furthermore, there are more possible types, e.g. the hybrid sewer<br />
system. Which kind of sewer system is better or more appropriate depends very much on the<br />
actual situations, such as city locations, geological conditions, system scales, local economy<br />
level and local regulations, etc. The general priorities and selecting rules are set up<br />
particularly for <strong>IUWS</strong> and shown in § 3.3.3.