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Newsletter and Technical Publications
<Sourcebook of Alternative Technologies for
Freshwater Augumentation in Small Island Developing States>
PART D - ANNEXES
Annex 3
Cost Comparisons
Introduction
Details of costs for different methods of water resources development
are not readily available in the published literature. This type of
information is generally contained in unpublished reports and files. Thus,
while the cost details below should be considered only indicative of the
full range of costs, they reflect costs incurred over a wide range of
conditions and provide an idea of the relative costs of water resources
development on small islands. Two sets of comparisons are given in this
section. Firstly, the costs of alternative water source developments from
feasibility studies are considered for selected cases. Secondly, costs of
present (or recent) water production on a small number of islands are
considered. Because these costs are indicative only, no general
conclusions can be drawn. Each small island or group of small islands will
have its own particular conditions which influence costs of the various
alternatives.
Home Island, Cocos (Keeling) Islands
Cost comparisons for a number of water supply options were undertaken
for Home Island in 1988 (Falkland, 1988) and were summarised by UNESCO
(1991). These costs were based on estimated capital and recurrent costs of
supplying water at the rate of 115 m3/day to the Home Island
community, and are expressed in Table 15 as 1995 costs.
TABLE 15. Approximate Unit Costs of Alternative Freshwater
Augmentation Technologies.
| Alternative |
Unit cost ($/m3) |
| Groundwater supply plus emergency rainwater |
$ 1.20 |
| Desalination by reverse osmosis |
$ 8.60 |
| Importation by piping from South Island |
$ 2.90 |
| Importation by barging from West island |
$ 4.30 |
| Rainwater collection |
$ 12.10 |
The groundwater alternative required conversion of existing wells to
galleries, but no further infrastructural development. The two importation
alternatives required groundwater extraction on other islands on the atoll
(Figure 49) and transportation of the water to Home Island. Rainwater
collection was the most expensive option due to the need for very large
storages and catchment areas should rainwater be used as the sole (rather
than a supplementary) source of freshwater.
Subsequently, these costs were refined in 1994 (Falkland, 1994) on the
basis of additional information and operational experience. The refined
costs were based on supplying an additional 100 m3/day to Home
Island. These costs, converted to 1995 costs, are shown in Table 16.

Figure 49. Map of South Keeling atoll, Cocos (Keeling)
Islands, Indian Ocean.
TABLE 16. Refined Costs of Freshwater Augmentation Technologies.
| Alternative |
Unit Cost ($/m3) |
| Desalination by reverse osmosis |
$ 6.30 |
| Importation by piping from South Island |
$ 5.40 |
| Importation by barging from West island |
$ 6.00 |
From the above data, the costs of supplying water based on groundwater
development using infiltration galleries is the least costly option. After
this, importation from other parts of the island, using groundwater
abstracted from infiltration galleries, is the next most costly option.
Kiritimati (Christmas Island), Kiribati
Cost comparisons for a number of water supply options were undertaken
for Kiritimati in 1983 (Falkland, 1983,1984), and were also summarised by
UNESCO (1991). These options were based on supplying water at the rate of
50 m3/day to the population of London (Ronton). The unit costs shown in
Table 17 are expressed as 1995 costs.
TABLE 17. Approximate Unit Costs of Alternative Freshwater
| Alternative |
Unit cost ($/m3) |
| Groundwater supply from Decca lens |
$ 5.00 |
| Desalination by reverse osmosis |
$ 8.60 |
| Solar distillation |
$ 5.80 |
| Rainwater collection |
>$27.00 |
| Importation by barge from Washington Island (Teraina) |
$12.50 |
As for Home Island, but even more so, rainwater collection was the most
expensive option due to the need for very large storage and catchment
areas if rainwater is used as the sole (rather than a supplementary)
source of water. Similarly, the costs of supplying groundwater from
infiltration galleries is the cheapest option.
Costs
Table 18 shows the unit cost of water production for a number of small
islands. The marked differences in the unit costs of production are not
only due to the lack of local water resources but are also to the
efficiency of development.Costs shown are mid-1980s costs and reflect both
production costs and consumer costs as noted
Information Sources
Falkland, A.C. 1983. Christmas Island (Kiritimati) Water Resources
Study. Australian Department of Housing and Construction Report No.
HWR83/03, Australian Development Assistance Bureau, Canberra. 425 pp. +
appendices.
Falkland, A.C. 1988. Cocos (Keeling) Island Water Resources and
Management Study. ACT Electricity and Water Report No. HWR88/12, ACT
Electricity and Water, Canberra, Australia. 211 pp. + appendices.
Falkland, A.C. 1994. Home Island Water Supply Options. ACT
Electricity and Water Report No. HWR94/05, ACT Electricity and Water,
Canberra.
UNESCO [United Nations Education Scientific and Cultural Organization]
1991. Hydrology and Water Resources of Small Islands, A Practical
Guide. Studies and Reports on Hydrology No 49, UNESCO, Paris. 435 pp.
TABLE 18. Unit Costs of Water Production for Some Small Island
States.
| Island/Country |
Water Source |
Unit Cost ($ per m3) |
Reference |
| Anguilla |
Desalination (brackish RO) |
5.80 |
Wright (1984a) |
| Bahamas |
|
0.37 |
Dabbagh and Al-Saqabi (1989) |
| Barbados |
|
0.34 |
Dabbagh and Al-Saqabi (1989) |
| Bermuda |
Groundwater extraction (and pumping to reservoir, not
including treatment) |
0.55 |
|
| Desalination (RO) |
1.10 |
|
| Canary Islands |
Groundwater extraction (Gran Canaria) |
0.50 - 1.20 |
|
| Groundwater extraction (Tenerife) |
0.20 - 0.40 |
|
| Groundwater extraction (Gran Canaria) |
0.20 - 0.30 |
|
| Desalination - seawater (cost) |
1.50 -3.00 |
|
| Desalination (consumer charges) |
1.10 - 2.00 |
|
| Reused Wastewater (cost to farmers) |
0.05 |
|
| Cape Verde |
|
4.65 |
Dabbagh and Al-Saqabi (1989) |
| Cayman Islands |
Groundwater extraction |
2.50 |
|
| Desalination |
4.00 - 4.81 |
|
| Rainwater |
26.00 |
|
| Imported bottled water |
240 - 320 |
|
| Cook Islands |
|
0.40 |
Dabbagh and Al-Saqabi (1989) |
| Fiji |
Importation (from main islands) |
6.00 |
|
| Malta |
Groundwater extraction (boreholes and tunnels or
galleries) |
0.29 |
Spiteri Staines |
| Groundwater (boreholes only) |
0.22 |
|
| Desalination (MSF distillation) |
1.17 |
|
| Desalination (RO) |
1.20 |
|
| Mauritius |
|
0.29 |
Dabbagh and Al-Saqabi (1989) |
| St. Thomas, USVI |
Bulk importation (From Puerto Rico) |
4.65 |
Brewster and Buros (1985b) |
| Seychelles |
|
0.60 |
Dabbagh and Al-Saqabi (1989) |
| Singapore |
|
0.24 |
Dabbagh and Al-Saqabi (1989) |
| Taeawa, Kiribati |
Groundwater extraction |
1.00 |
Metutera (1989) |
| Tonga |
|
0.80 |
Dabbagh and Al-Saqabi (1989) |
| Western Samoa |
|
0.09 |
Dabbagh and Al-Saqabi (1989) |
| Caribbean islands |
Bulk importation (from Puerto Rico) |
1.50 - 5.70 |
de Hahn (1987) |
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