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Aquaculture/Fisheries Center Research Highlights
Aquaculture Economics and Marketing
 
  1. Economic effect of stocker catfish (Ictalurus punctatus) production on farm profitability.
    Steeve Pomerleau and Carole Engle
     
    Traditionally, farmers understock 9-27 g fingerlings directly into growout ponds in multiple-batch production. However, some use a three-phase strategy, where fingerlings are raised to stocker-size (27-340 g) in single-batch for one growing season, before transfer to growout ponds. Does the use of stockers improve farm productivity and profitability? A series of pond studies were conducted at the University of Arkansas at Pine Bluff on fingerling and stocker production and performance in growout ponds. Enterprise budgets were developed based on three sizes of farm (65, 130, and 260-ha) and eight production strategies. Five strategies involved the production of stockers (114, 135, 176, 255, and 361-g) thereafter stocked in growout ponds at 11,250/ha, in single-batch production. The three other strategies involved understocking fingerlings (6, 12, and 37-g) directly into growout ponds at 15,000/ha with 1,369 kg/ha of large 580-g catfish to simulate multiple-batch production.

    Results indicated two principal profit-maximizing strategies (Table 1). One strategy was to understock 37-g fingerlings in multiple-batch growout ponds. The other was to produce 255-g stockers before transfer to growout ponds. Three main factors affected the relative profitability of the 255-g stocker versus the 37-g fingerling strategy. As farm size increased (Table 1) or pond size decreased, the stocker strategy became more profitable than the fingerling strategy because it used resources more efficiently. The stocker strategy was not as profitable for small farms or for larger ponds because it was more difficult to balance the number of stockers produced with the number stocked in growout ponds, resulting in wasted resources. The third factor was the growth rate of the stockers in growout ponds. As the growth rate of the stockers increased, the relative profitability of the stocker strategy increased.

    This static analysis indicated the profit-maximizing strategy for a single year. However, the analysis did not consider the effect of each strategy on farm profitability over multiple years, the increased risk of mortalities and off-flavor, nor the logistics of producing and stocking successive batches of stockers throughout the season across the whole farm. Additional research is needed in a dynamic framework to evaluate the effects of these additional factors.
     
  2. The economic impact of the catfish industry on Chicot County, Arkansas
    Aloyce R. Kaliba and Carole Engle
     
    This study analyzed the contribution of the catfish industry to the economy Chicot County, Arkansas, using an input-output model. The objective was to quantify the economic contribution of the industry in terms of creating new dollars, jobs, and income to the local community. Mail surveys and personal interviews were used to collect data from catfish farmers, processors and other businesses within the industry. For farmers, the information solicited included production and marketing costs, sales and employment. Out of approximately 85 catfish farms, 44 usable questionnaires were obtained for a response rate of 52%. Businesses directly related to the catfish industry provided information on employment and sales and included: processors, seiners and haulers, pond builders, tractor and equipment dealers, and feed bin manufacturers. Other businesses with indirect ties to the catfish industry included: input supply companies, banks, fertilizer and chemical companies, auto shops, electricians, and bookkeeping firms. The survey data were used to modify the IMPLAN database for Chicot County to reflect the 2001 level of catfish production, processing and services available to support the industry and to estimate the economic impact of the industry to the county's economy. In 2001, the 85 catfish farmers in the county operated about 7,859 ha(19,500 acres). The farm-gate value of catfish production exceeded $63 million. Employment on catfish farms was approximately 510. In addition, 34 other businesses depended on the catfish industry. The impact analysis results indicated that total employment created in Chicot County by businesses involved directly or indirectly with the catfish industry was 2,534 jobs. This represented 46% of all employment in Chicot County. Total tax revenue (federal, state, and local taxes) generated from both direct and indirect catfish businesses was $20 million. Combined, the total economic impact of the catfish industry in Chicot County, including direct, indirect and induced effects, was over $359 million. If current economic difficulties would result in contractions of 10-30% of the catfish acreage in Chicot County, unemployment rates would increase from 10.2% to 12.2-16.5%. This study demonstrates the importance of the catfish industry to the economy of Chicot County.
     
  3. Implications of import and price setting policies for the catfish industry
    Kwamena K. Quagrainie and Carole R. Engle

    Total imported fish fillets from Vietnam has increased by about 7000% since 1995 causing themarket share of U.S. catfish fillets to decline from about 99% in 1995 to about 85% by December of 2001. Consequently, the price of catfish that processors pay to farmers has declined to a ten-year low, threatening the sustainability of the industry. Price setting is a policy being considered by major producer groups such as the Mississippi Catfish Producers Marketing Association (MCPMA) and the Catfish Bargaining Association (CBA) to help enhance revenue and sustain the industry. Fixity of assets in the catfish industry suggest a relatively inelastic supply response from farmers therefore, revenue enhancement can be better achieved through price increases than quantity increases.
    This study investigates Vietnamese export of fish fillets to the United States and its impact on domestic catfish prices as well as the welfare implications for opting price-setting policies by producer groups. Structural equations and simulation models are used to accomplish these objectives.

    The results indicate that the desired price by both processors and farmers and the actual transacted price matched fairly closely until the last quarter of 2001. The desired price is what the price should have been given market conditions. This equilibrium desired price is found to have been affected negatively by excess supply, including the quantity of catfish processed, the quantity of catfish fillets sold, and the quantity of fish fillets imported from Vietnam. Estimates of lost farm revenue due to the non-realization of this desired price are $18, $11, and $88 million respectively in 1999, 2000, and 2001.

    Using a base scenario of P1 = $0.55/lb and Q1 = 43.59 million pounds, simulation results indicate that at a producer price of 0.60, 0.65, 0.70, and 0.75 cents/lb, processors will demand 42.28, 40.97, 39.66, and 38.35 million pounds respectively. The government can purchase any excess supply above these quantities to maintain the set price. These quantity levels suggest a welfare loss to processors that increase with a price increase and a welfare gain by farmers. However, the net societal gain, though positive, declines with high prices.
     
  4. An economic Analysis of Effluent Treatments in Hybrid Striped Bass Aquaculture
    Yong-Suhk Wui and Carole Engle

    The growth of aquaculture farming has resulted in increased scrutiny by regulatory agencies. The Environmental Protection Agency added aquaculture into the Effluent Limitation Guidelines (ELG) program in December 1999. The final rule is scheduled to be implemented in 2004. The ELG program bases its rulemaking effect on technology-based standards that are economically achievable.

    While there have been a number of studies on effluent treatment in aquaculture, few studies have focused on the economic feasibility of the effluent treatments that have been evaluated and that might be adopted by farmers (Kouka and Engle).

    The primary objective of this paper is to evaluate several effluent treatments that have been considered for Hybrid Striped Bass (HSB) farming. Farm-level impacts of proposed regulations were analyzed in terms of farm sizes and regions.

    The scope of the paper is limited to pond production systems for grow-out of HSB foodfish. A Mixed Integer Programming (MIP) analytical model for HSB farming was developed focusing on maximizing profit derived from HSB production subject to the imposition of several different effluent treatment options. Survey data were collected from HSB farmers across the United States. Experimental data for effluent treatment were obtained from the literature and from on-going projects. The primary treatment options considered in this paper include no treatment, newly-constructed settling basins with Hydraulic Residence Time (HRT) of 1 and 20 days, existing ponds converted to settling basins with HRT of 1 and 20 days, constructed wetlands, fixed film filtering by honeycomb and brush filter media, not flushing pond water, not draining pond water, and circulating pond water. Settling basins and constructed wetlands entail high costs for farmers with high reduction in effluents. Filtering treatments incur high cost without much reduction in nutrient concentration in effluents. Not flushing water from the pond or not draining the pond annually reduces effluent volume. Reduction in the amount of water flushed or drained from the pond also decreases operating costs without any additional investment cost associated with adoption of the treatments. Effluent treatment options would increase production costs in average by $0.00-6.79/kg.

    The main result of the MIP model is that no annual draining and not flushing the pond water are the best operational treatment. When a cost (tax) or effluent level standard regulations are imposed on effluent discharge, the model selected the no draining treatment. By not draining ponds, farms would minimize treatment cost by reducing effluent volume. However, additional work is needed on the long-term risks associated with not flushing or not draining HSB product ponds.
     
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