An innovative greywater treatment system for urban areas ... - SuSanA
An innovative greywater treatment system for urban areas ... - SuSanA
An innovative greywater treatment system for urban areas ... - SuSanA
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Only the legislative requirements <strong>for</strong> wastewater <strong>treatment</strong> technologies (H3) were<br />
counted within this main group. This criterion refers to regulations and directives <strong>for</strong> treated<br />
<strong>greywater</strong> and <strong>for</strong> reuse applications in evaluated countries. In this regard, the ratings “highly<br />
en<strong>for</strong>ced” = 10, “medium en<strong>for</strong>ced” = 5, “low en<strong>for</strong>ced” = 1, and “no requirements” = 0 were<br />
given. If there are highly en<strong>for</strong>ced requirements on the quality of purified <strong>greywater</strong>, then it is<br />
a strong motivation to use high-tech <strong>treatment</strong> via MBR. In the weighting of utility analysis,<br />
legislative requirements are included with 6 %.<br />
Economic issues (E) are given a high weighting of 39 % within the utility analysis. This is<br />
because there are holistic cost approaches that always provide strong reasons <strong>for</strong> the<br />
decision of <strong>greywater</strong> <strong>treatment</strong> plant implementation.<br />
Direct governmental funding <strong>for</strong> <strong>treatment</strong> plants (E1) by e.g. subsidies, allowances,<br />
loans <strong>for</strong> plant investment, or financial support is the first sub issue. It was weighted with 4 %<br />
within this group. The indirect incentives on <strong>greywater</strong> <strong>treatment</strong> <strong>system</strong>s (E2) add<br />
another 4 % to the weighting. It includes e.g. tax reductions, discounts, minimised fresh<br />
and/or wastewater charges, reimbursements of taxes, or charges. For both criteria, the<br />
appraisal is: “high support” = 10, “medium support” = 5, “low support” = 1 and “no support” =<br />
0.<br />
Investment costs of the <strong>system</strong> (E3), which include the <strong>treatment</strong> plant, a separate<br />
piping <strong>system</strong>, and all installations necessary <strong>for</strong> the <strong>greywater</strong> <strong>treatment</strong> <strong>system</strong>, were<br />
weighted with 4 % in the utility analysis. Membrane bioreactor <strong>treatment</strong> plants are relatively<br />
expensive. It is expected that the investment expenses are to be amortised at least within 7 -<br />
8 years of operation, then it is possible to save enough money within the next 7 - 8 years to<br />
substitute the plant; (lifecycle 15 years). Otherwise there is no stimulus to install such a<br />
technology in a building. There<strong>for</strong>e, this sub criterion was only weighted with 4 %, as an<br />
economic feasibility of the <strong>system</strong> was presumed. The estimation is: “high price” = 1,<br />
“medium price” = 5 and “low price” = 10.<br />
Operating expenses (E4), including maintenance, spare parts, and working time, were<br />
weighted with an influence of 5 %. For the appraisal, the regular payments were weighted<br />
with a bit more influence than investment cost: This is due to the fact that regular payments<br />
are an important factor which stands <strong>for</strong> a big amount of money which must be spent on a<br />
regular basis. The classification is as follows: “high expenses” = 1, “medium expenses” = 5<br />
and “low expenses” = 10.<br />
If the energy price (E5) is very high, there is no incentive to implement a MBR <strong>treatment</strong><br />
<strong>system</strong>, because of relatively high energy consumption of the plant (see energy calculation in<br />
section 3.53.5.1). There<strong>for</strong>e, the appraisal of criterion is: “high expenses” = 1, “medium<br />
expenses” = 5 and “low expenses” = 10. To assess those issues, the energy price can<br />
generally be considered in the country or region. Together with operating expenses, it is a<br />
regular payment that can be a high cost factor; hence it was assessed with 5 %.<br />
In contrary, there are charges <strong>for</strong> drinking and wastewater (E6 & E7) which can be<br />
saved by <strong>greywater</strong> <strong>treatment</strong>. Both criteria are classified with “high charges” = 10, “medium<br />
charges” = 5 and “low charges” = 1. If high expenses can be avoided, it is an appeal to<br />
implement a recycling <strong>system</strong>. Each criterion (charge <strong>for</strong> drinking and wastewater) was<br />
weighted with 7 %. The idea behind it was to have a balanced situation of costs, which need<br />
to be spent, and expenses that can be saved. The assessment counts 14 % in total <strong>for</strong><br />
investment, maintenance and energy costs. In contrary, 14 % <strong>for</strong> drinking and wastewater<br />
that can be saved.<br />
Often the charge <strong>for</strong> drinking water (E6) is very high because of water scarcity or<br />
missing water pipes. There<strong>for</strong>e, supply by tank vehicles is necessary. In this case, it is very<br />
useful to recycle <strong>greywater</strong> in order to use water several times within a building. However, in<br />
some countries the price of water is low due to governmental subsidies, despite critical water<br />
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