Economic evaluation of the successful biological control of Azolla filiculoides in South Africa

Abstract Azolla filiculoides (red waterfern) is a floating fern native to South America which has invaded aquatic ecosystems in South Africa. Thick mats of A. filiculoides on dams and slow-moving water bodies cause economic losses to water-users. Affected water-users were surveyed using a questionnaire to assess the importance of the weed. Among those most seriously affected were farming (71%), recreational (24%), and municipal (5%) users. The average water area covered by A. filiculoides (per water-user) was 2.17 ha, with an expansion rate of 1.33 ha per year. The frond-feeding weevil Stenopelmus rufinasus was released as a biological control agent at the end of 1997. Within 3 years, the weevil had reduced the weed population to the point that it was no longer considered a problem in South Africa. Based on year 2000 data, the cost savings (per user per hectare) resulting from the biological control program included a reduction of on-site damages caused by the weed to the value of US$589 per hectare per year. The average cost per hectare per year for the biological control program for the period 1995–2000 amounted to US$278, excluding investment costs of USD$7700 in 1995. These historic costs and benefits were adjusted to constant year 2000 values. The predicted spread of the weed was calculated on the basis of a sigmoid-curve rate of spread model. The net present value (NPV) of the program was calculated from 1995 onwards and discounted at 8%. This resulted in a NPV of US$1093 per hectare and US$206 million for South Africa as a whole. For the year 2000, the benefit–cost ratio was calculated at 2.5:1, increasing rapidly to 13:1 in 2005, and 15:1 in 2010 as the costs of the biological control program are expected to decrease. These indicators reinforce the overall economic viability of biological control, but do not necessarily confirm the viability of biological control on each management unit itself. The results reflect the dynamics of biological control on site-specific survey information, and place higher benefit–cost ratios achieved in other national level studies in a better context. It also raises the important policy question of who is responsible to finance such control programs in future, because on-site benefits of control are enough to justify the program in its own right. The paper concludes with recommendations on a financial mechanism to address biological control of invasive species in a sustainable manner.

[1]  M. Hill Herbivorous insect fauna associated with Azolla species (Pteridophyta : Azollaceae) in southern Africa , 1998 .

[2]  B. Gratwicke,et al.  The impact of Azolla filiculoides Lam. on animal biodiversity in streams in Zimbabwe , 2001 .

[3]  F. W. Pettey The cochineal (Dactylopius opuntiae). Its history, distribution, biology, and what it has accomplished in the control of prickly pear in South Africa. , 1950 .

[4]  J. C. Headley COST-BENEFIT ANALYSIS: DEFINING RESEARCH NEEDS , 1985 .

[5]  M. Hill Life history and laboratory host range of Stenopelmus rufinasus, a natural enemy for Azolla filiculoides in South Africa , 1998, BioControl.

[6]  N. Hanley,et al.  Cost–Benefit Analysis and the Environment , 1994 .

[7]  Jacobus A. Doeleman,et al.  Biological Control of Salvinia molesta in Sri Lanka: An Assessment of Costs and Benefits , 1989 .

[8]  T. Olckers,et al.  Biological control of red water fern, Azolla filiculoides Lamarck (Pteridophyta: Azollaceae), in South Africa. , 1999 .

[9]  M. Okwakol Changes in termite (Isoptera) communities due to the clearance and cultivation of tropical forest in Uganda , 2000 .

[10]  M. D. Wit,et al.  Conflicts of Interest in Environmental Management: Estimating the Costs and Benefits of a Tree Invasion , 2001, Biological Invasions.

[11]  B. W. van Wilgen,et al.  Costs and benefits of biological control of invasive alien plants: case studies from South Africa , 2004 .

[12]  R. Norgaard,et al.  Biological control of the blue gum psyllid proves economically beneficial , 1998 .

[13]  R. Sharma,et al.  Studies on Evapotranspiration of Some Aquatic Weeds , 1973, Weed Science.

[14]  L. A. Andres,et al.  The economics of biological control of weeds , 1977 .

[15]  D. Andow,et al.  Ecological Interactions and Biological Control , 1997 .

[16]  H. Radtke,et al.  Economic and regional benefits from the biological control of tansy ragwort, Senecio jacobaea, in Oregon. , 1996 .

[17]  R. Cheke,et al.  Workshop on research priorities for migrant pests of agriculture in Southern Africa, Plant Protection Research Institute, Pretoria, South Africa, 24–26 March 1999 , 2000 .

[18]  M. Hoy,et al.  Biological Control in Agricultural IPM Systems. , 1986 .

[19]  C. B. Huffaker,et al.  3 – THE THEORETICAL AND EMPIRICAL BASIS OF BIOLOGICAL CONTROL , 1976 .

[20]  Erwin H. Bulte,et al.  The Economics of Nature: Managing Biological Assets , 2000 .

[21]  T. Lumpkin,et al.  Azolla as a Green Manure: Use and Management in Crop Production , 1982 .

[22]  C. B. Huffaker,et al.  Theory and practice of biological control , 1976 .

[23]  M. Julien,et al.  Biological Control of Weeds: Theory and Practical Application , 1997 .