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46

DECEMBER 2014

WORLD AQUACULTURE

WWW.WA S.ORG

for salmonids, diadromous fish and cage culture was subtracted.

Assuming an average feed conversion ratio (FCR) for salmonids

and other diadromous fishes of 1.2 (Marine Harvest 2013) and that

the production of these fish totaled 3.73 million t (FAO 2011), 4.48

million t of feed were consumed by these species. Cage culture

production was 3.4 million t in 2005 (Tacon and Halwart 2007), but

this production included salmonids and diadromous fish. Thus, cage

culture production of other species probably was around 1.1 million

t. At a typical FCR of 1.75 (Beveridge 1993), 1.92 million t of feed

were consumed by fish in cages. Subtracting the total feed used

for salmonids, diadromous fishes, and other cage culture species

(6.3 t) is from the total aquaculture feed production, suggests that

27.6 t were used for pond aquaculture. Multiplying the amount of

feed used in pond aquaculture by the average land area required for

plant meals for feed (0.274 ha/t), around 7.6 million ha of land were

used for producing plant-based feed ingredients for feed applied to

aquaculture ponds.

Adding the land for plant crop production (7.6 million ha) to

the adjusted water surface area and support area required for farms

estimated above (24.8 million ha), indicates that about 32.4 million

ha of land are dedicated to pond aquaculture. The production of

non-pond fish that was removed before calculating land use for

plant feed ingredients for pond aquaculture also requires land for

feed. Even cage culture in natural lakes requires land to support

production in cages.

Global Implications

The estimates of pond water surface (Verdegem and Bosma

2009) and the land to water ratios and area needed for plant

ingredients are subject to considerable uncertainty. However, even if

estimates are 25 to 50 percent too low, aquaculture still uses a very

small area of land compared to world agriculture usage of 4,920

million ha (Boyd

et al.

2013). Although aquaculture is probably not

a major land use in any country, it can bring significant changes

to the landscape, redirect other land uses and cause ecological

problems. As aquaculture production increases in the coming

years, so will production from terrestrial agriculture. Thus, despite

having a small impact of total land use at present and in the future

compared to terrestrial agriculture, pond aquaculture is and will

continue to be of vital importance to the food security of many

developing countries, and an important component of the world

food system.

Ecolabel certification is becoming more popular among

farmers as the demand for such products increases. These

certification programs have specific standards intended to avoid

negative environmental impacts, but they also are used to make

farms more efficient in feed, energy, and water use (Boyd

et al.

2013). Certification standards could be extended to include a

standard related to the maximum allowable land to water surface

area ratio. The standards for ecolabel certification typically require

farmers to improve on current management practices. The standard

for land to water surface area ratio would no doubt be less than the

average found by this survey.

Notes

Lauren N. Jescovitch and Claude E. Boyd, School of Fisheries,

Aquaculture and Aquatic Sciences

Philip Chaney, Department of Geology

Auburn University, Auburn, Alabama 36849 USA

1

www.fao.org/fishery/statistics/en

2

faostat.fao.org

3

www.alltech.com/sites/default/files/2013-feed-tonnage-report.pdf

References

Alonso-Perez, F., A. Ruiz-Luna, J. Turner, C.A. Berlanga-Robles

and G. Mitchelson-Jacob. 2003. Land cover changes and impact

of shrimp aquaculture on the landscape in the Ocean and Coastal

Management 46:583-600.

Beveridge, M.C.M. 1993. Cage and pen fish farming: Carrying

capacity models and environmental impact. FAO Fisheries

Technical Paper 255. FAO, Rome, Italy.

Boyd, C.E. and M. Polioudakis. 2006. Land use for aquaculture

production. Global Aquaculture Advocate 9(2):64-65.

Boyd, C.E. and J. L. Shelton, Jr. 1984. Observations on the hydrology

and morphometry of ponds on the Auburn University Fisheries

Research Unit. Bulletin 558, Alabama Agricultural Experiment

Station, Auburn University, Alabama, USA.

Boyd, C.E., J. Queiroz and A.A. McNevin. 2013. Perspectives on the

responsible aquaculture movement. World Aquaculture 44(4):14-21.

FAO (Food and Agriculture Organization of the United Nations).

2011. Yearbook of Fisheries Statistics, Summary Tables:

Aquaculture Production 2011.

Giap, D. H., Y. Yi and A. Yakupitiyage. 2005. GIS for land evaluation

for shrimp farming in Haiphong of Vietnam. Ocean and Coastal

Management 48:51-63.

Green, E.P., P.J. Mumby, A.J. Edwards and C.D. Clark. 1996. A

review of remote sensing for the assessment and management of

tropical coastal resources. Coastal Management 24:1-40.

Marine Harvest. 2013. Salmon Farming Industry Handbook 2013.

Bergen, Norway.

hugin.info/209/R/1698446/559980.pdf

.

Sapkota, A., A. R. Sapkota, M. Kucharski, J. Burke, S. McKenzie,

P. Walker and R. Lawrence. 2008. Aquaculture practices and

potential human health risks: Current knowledge and future

priorities. Environment International 34:1215-1226.

Tacon, A.G.J. and M. Halwart. 2007. Cage aquaculture: a global

overview. FAO Fisheries Technical Paper 498. FAO, Rome, Italy.

Verdegem, M.C.J. and R.H. Bosma. 2009. Water withdrawal for

brackish and inland aquaculture, and options to produce more

fish in ponds with present water use. Water Policy (Supplement 1)

11:52-68.

On intensive farms, ponds tend to be smaller than on extensive and semi-intensive farms, and this

means a relatively greater area for roads and canals on intensive farms. The intensity of pond

aquaculture has been increasing as better management practices were developed and implemented.