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Human Settlements Review - Parliamentary Monitoring Group

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<strong>Human</strong> <strong>Settlements</strong> <strong>Review</strong>, Volume 1, Number 1, 2010<br />

option for the poor. This common assumption<br />

is based on hard facts about what it costs to<br />

construct the physical structure of the house<br />

and related infrastructure, but it ignores the<br />

cost of operating the house over its entire<br />

life-cycle. This is highly problematic in light<br />

of the fact that life-cycle operating costs are<br />

projected to rise faster than inflation due to<br />

declining supply of key input resources.<br />

The objective of this research was to<br />

demonstrate that a life-cycle approach<br />

rather than the more traditional once-off<br />

capital cost approach generates results that<br />

demonstrate that sustainable living is more<br />

affordable for both the household and the tax<br />

base of the city. This has been achieved by<br />

collecting data and information on life-cycle<br />

costs of both minimum standard conventional<br />

housing provision (hereafter referred to as the<br />

“current approach”) as well as a package of<br />

“sustainable living” applications. Conclusions<br />

were reached by measuring and comparing<br />

40-year life-cycle cost effectiveness of the two<br />

alternatives. The results are expressed as net<br />

present values, using a discount rate of 9%.<br />

According to Wrisberg, there are several “lifecycle”<br />

methodologies that are in use in the<br />

world today that have emerged in response<br />

to the global demand for “tools” to determine<br />

the material and energy content of particular<br />

production and consumption processes, as<br />

well as environmental impacts (Wrisberg et al.<br />

2002).<br />

A “life cycle” approach is necessary because<br />

it has become imperative to take into account<br />

the full capital and operational costs of a given<br />

production or consumption process over the<br />

life cycle of the process.<br />

Without this kind of analysis it will not be<br />

possible at the design stage to determine<br />

which process will<br />

contribute most towards achieving a more<br />

sustainable socioecological regime; or<br />

alternatively, which one<br />

will do the least damage. However, a wide<br />

range of life-cycle methodologies have<br />

emerged for different purposes. These<br />

included the following: Life Cycle Assessment,<br />

Material Input per Unit of Service (MIPS),<br />

Environmental Risk Assessment (ERA),<br />

Material Flow Accounting (MFA), Cumulative<br />

Energy Requirements Analysis (CERA),<br />

Environmental Input-Output Analysis (env.<br />

IOA), analytical tools for eco-design, Life<br />

Cycle Costing (LCC), Total Cost Accounting<br />

(TCA), Cost-Benefit Analysis (CBA) and Cost<br />

Effectiveness Analysis (CEA). It is not possible<br />

to describe and analyse these different<br />

methodologies here.<br />

Suffice it to say that a CEA approach has<br />

been adopted because this makes it possible<br />

to compare the “conventional approach” to<br />

housing delivery to a “sustainable living”<br />

alternative across the life-cycle. The essence<br />

of this approach, according to Wrisberg, et al<br />

(2002), is that it does not quantify benefits like<br />

CBA, even though they regard it as a derivative<br />

of CBA. Citing a report by RPA (1998) entitled<br />

Economic Evaluation of Environmental<br />

Policies and Legislation, Final Report for DG<br />

III of the European Commission, Contract<br />

Number: ETD/97/501287, Wrisberg, et al<br />

(2002) states that CEA aims at determining<br />

the least cost option of attaining a predefined<br />

target after the fundamental decision process<br />

has been finalised.<br />

103

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