Newsletter and Technical Publications
<International Source Book On Environmentally Sound Technologies
for Wastewater and Stormwater Management>
8.3 Economic factors
Sound practices require that costs are optimised. An indication of relative
costs of technologies described in this Source Book is provided in table 2.5 and
in Appendix 2. Optimising the cost of technology for wastewater management needs
to consider (1) availability of land, (2) labour costs, (3) land uses and (4)
economy of scale. Land is required for wastewater and stormwater management
either underground to lay pipes or on the ground for a treatment plant or for
land-based disposal. If low cost land is available a lower cost technology
utilising more land can be chosen rather than a higher cost technology using
less land area. Lagoons, for example, can be installed rather than an Activated
Sludge Treatment Plant, because both can achieve the same standard for final BOD
and SS. Labour cost for construction and maintenance is an important
consideration. On-site treatment systems are generally more conducive to the use
of manual labour for construction and maintenance, whereas off-site treatment
systems generally require specialised equipment and skilled labour.
Availability of land, when an on-site system is used, enables reuse of
treated wastewater at the site. Similarly when an off-site system is used,
nearby agriculture, horticulture, forestry or industrial activities can present
an opportunity for reusing the wastewater.
Economy of scale may be taken advantage when total cost of treatment is
considered. Individual on-site systems do not present an opportunity for economy
of scale for cost reduction, unless they are constructed in standard sizes and
prefabricated components are manufactured in large quantities. Off-site
treatment of wastewater from many households provides an opportunity for
cost-saving in treatment. The cost of treatment per unit volume of wastewater
will decrease with an increase in population served. The cost of collection
will, however, increase, because larger diameter pipes and additional pumps and
pumping stations are required. This will counter the cost saving in centralised
treatment. In centralised collection and treatment systems with deep sewerage,
the cost of pipes and pumps is generally a substantial proportion of the capital
cost (up to 85%). There will be an optimum size of population served by an
off-site treatment system when the combined cost of collection and treatment are
considered. When opportunities for water reuse are also considered (piping of
reuse water, availability of land or opportunities for reuse) there seems to be
an optimum to the size of population served (Figure 2.46).
The economics of wastewater management needs to consider the benefits of
improvement to public health and long-term affordability of sanitation services
to the community. The benefits of improved public health to the economy of a
country is difficult to quantify, although estimates have been made on the cost
to the economy as a result of people suffering from illnesses from waterborne
diseases (Appendix 1). Similarly the economic benefits of the protection of the
environment from improper disposal of wastewater and stormwater is difficult to
estimate. A case for subsidy to communities to install wastewater treatment
facilities has been put forward (The all beneficiaries contribute (abc)
principle).

Figure 2.46: Cost of treatment as a function of population served
From a community’s point of view the affordability of a
wastewater collection and treatment system is an important factor. A percentage
of the average person's income in a community, or of the average value of
housing appears to be a figure that can be used as a measure of what a community
can afford. What the percentage figure should be is determined by the importance
given by community members to having the wastewater system in their community.
The priority given to wastewater management in turn is dependent on the
community having the information that will help them decide on its importance
relative to other household and community needs. Hygiene promotion and education
is needed to provide this information. An example of an excellent hygiene
promotion is a publication by WHO (WSSCC Working Group on Promotion of
Sanitation, 1998).
Selection of technology
Procedures to consider economic and environmental factors in a
systematic way have been developed. These range from a single decision-making
flowsheet to a computer software package.
Figure 2.47 and Figure 2.48 illustrate flowsheets that have been
developed for selection of wastewater technology in developing countries in both
urban and rural communities. Computerised decision making software is based on
the same methodology as illustrated in the flowsheets. Two programs (SANEX and
WAWTTAR) are briefly described in the accompanying boxed sections to illustrate
their advantages and limitations.

Figure 2.47: Simple decision making flowsheet for choosing wastewater treatment
systems (Pickford, 1995)
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