[From the U.S. Government Printing Office, www.gpo.gov]
78* 76* 36* 74c IN :@,_ eX @1_ . @n_ 6, CA -4 -4k North Carolina CAPE LOOKOUT. FINANCIAL VIABH, OF 36o 74' PENAEUS ,STING 41,MVE S W UITTH "SO "CA'A"OLIN-AA, WILMING @k !7 "Ae @61 7 TU ipzi 61;Aw - South Carolina 0@ 3z z VL3t 0 34 tni,C. law a shwar -,Cjr'r ii@ikjf-- e-, 4 @ _d W`SfW6i' -Bj CHARLESTO N@ 82 Marine Resources Divis!bh-4,-,,1--@.'--. Technical Report,, -849, SAV@NNAH PM 36 Georg 2. 3 I "A" RUNSWICAU OP JACK ONVILLE -South Carolina q. Department of Natural Resources "'ST. A'U TINE. Q) Florida 0 SH222 .S6S6 DAY A BE CH no .84 82o 80* 780 FINANCIAL VIABILITY OF PENAEUS SETIFERUS VERSUS PENAEUS VANNAMEI WITH CONTINUOUS LIVE HARVESTING AND ONE FINAL HARVEST STRATEGIES IN SOUTH CAROLINA S. Sureshwaran, C. Greene, R.J. Rhodes Craig L. Browdy and Al Stokes Marine Resources Division Technical Report Number 84 December, 1994 CAR @A 01P NAVJ 13 South Carolina /71 Cn Department of Natural Resources LIBRARy NOAA/cCEH 1990 HOBSON AVE. '6 CHAS. SC 2.9408-2623 FINANCIAL VIABILITY OF PENAEUS SETIFERUS VERSUS PENAEUS VAAW"V WITH CONTINUOUS LIVE HARVESTING AND ONE FINAL HARVEST STRATEGIES IN SOUTH CAROLINA by S. Sureshwaran' Carol Greene' and Raymond J. Rhodes' Craig L. Browdy' Al Stok& Technical Report Number 84 December, 1994 'Department of Agribusiness and Economics South Carolina State University Campus Post Office Box 7282 Orangeburg, SC 29117 and 'Economic Analysis and Seafood Marketing Program Office of Fisheries Management Division of Marine Resources S. C. Department of Natural Resources Post Office Box 12559 Charleston, SC 29422-2559 and 3Waddell Mariculture Research and Development Center Marine Resources Research Institute Division of Marine Resources S.C. Department of Natural Resources Post Office Box 809 Bluffton, SC 29910 This work was partially funded by the U.S. Department of Agriculture as administered by the Oceanic Institute/Gulf Coast Research Laboratory Consortium. The views expressed in this report do not necessarily reflect those of the U.S. Department of Agriculture, Oceanic Institute, S.C. Department of Natural Resources, or S.C. State University. Any commercial product or trade name mentioned herein is not to be construed as an endorsement. Table of Contents Page List of Tables .................................................... iv List of Figures ................................................... iv Summary ....................................................... I Introduction ..................................................... I Literature Review ................................................. 2 Methods and Data ......................... ........................ 3 Facility Design and Equipment ................................... 3 Production Assumptions ........................................ 5 Major Financial and Operating Assumptions .......................... 5 Production Scenarios .......................................... 5 Results ......................................................... 6 Base Scenarios .............................................. 6 Alternative Scenarios ......................................... 10 Discussion ..................................................... 10 Literature Cited .................................................. 12 Appendix 1: Shrimp Harvest Weight Model ............................. 13 List of Tables Table Page 1 Summary of Facility and Equipment Costs for a Hypothetical Shrimp Farm in South Carolina, 1993 ................................... 7 6 2 Projected Annual Income Statement for Operating Years Three Through Ten, and Discounted Cash Flow Analysis in the Base Scenario for a Hypothetical Penaeus vannamei Shrimp Farm in South Carolina ........ 8 3 Projected Annual Income Statement for Operating Years Three Through Ten and Discounted Cash Flow Analysis in the Base Scenario for a Hypothetical Penaeus setiferus Shrimp Farm in South Carolina ......... 9 4 Discounted Cash Flow Analysis for the Alternative Scenarios for Hypothetical Penaeus setiferus and Penaeus vannamei Shrimp Farm in South Carolina, 1993 .............................................. 11 5. Regression Coefficients for the Harvest Weight Model .................. 15 List of Figures Figure I Hypothetical Shrimp Farm Design ................................. 4 iv SUNMARY The ten-year (after tax) internal rate of return (IRR) for P. vannamei is 15.1 %. The It is anticipated that prospective aquacult- projected IRR is greater than the assumed urists, investors, and perhaps lending insti- base-scenario after-tax discount rate of 10% tutions and policy makers will desire informa- for P.vannamei. However, the projected IRR tion on the financial feasibility of producing for P. setiferus, -4.9 %. This is less than the indigenous Penaeus setiferus versus specific base-scenario discount rate. Net present value pathogen free Penaeus vannamei. This report (NPV) in ten years for P. vannamei is was undertaken to provide an accurate and $232,000 and for P. setiferus is a negative objective picture of the profit or loss from $568,000. The negative NPV indicates that at farming these species. In addition, an evalua- current prices, technology, and the assumed tion is made of the effects of a continuous discount rate, P. setiferus is n-ot profitable. live harvesting strategy versus a single final harvest strategy on the profitability of the two The IRR and NPV are highly sensitive to species. the assumed stocking densities, survival rates and expected prices at harvest. Given a dis- The hypothetical shrimp farm described in count rate of 10%, small changes in stocking this report includes 24 ponds, each I hectare densities, survival rates and prices can result in in size, located on 31 hectares of land that is large losses even for a P. vannamei shrimp leased near a saltwater source. The base sce- farm. However, continuous live harvesting nario assumes one final harvest strategy, stoc- has positive effects on net cash flows. king density of 80 postlarvae/meter', an ag- Because of the limited market for live shrimps, gregate survival rate of 70%, and a price of producers should remain alert for over-supply $4.95/kg for P. vannamei and $4.73/kg for P. conditions that can have a negative impact on setiferus. The effects of alternative stocking prices. With continuous live harvesting, IRR densities, survival rates, prices, and live har- increases to 16.4% for P. vannamei and to vesting are investigated in 7 other scenarios. 2.2 % for P. setiferus. Even with continuous All the 8 scenarios assume a feed conversion live harvesting, P. setiferus remains an un- rate of 2: 1, and the length of the grow-out profitable enterprise. cycle as 5 months. Commercial shrimp farms utilizing Initial investment in facility and equip- specific pathogen free P, vannamei postlarvae ment is approximately $1 million. Because of (PL) can be profitable in South Carolina. differences in growth rates and resulting feed Farms can have larger profits by practicing costs, total initial investment for both constru- continuous live harvesting strategies. cting and operating the facility depends on However, the indigenous P. setiferus is not species produced. In the base scenario, total profitable. Therefore, regulatory actions that initial investment including operating costs, hinder the import of specific pathogen free P. for P. vannamei is $1.38 million and for P. vannamei PL from out-of-state hatcheries setiferus is $1.35 million'. After the third could have adverse impacts on the South Caro- year, when the farm produces at full capacity, lina commercial shrimp farms. net cash flow after estimated taxes for P. vannamei is $250,000 and for P. setiferus is MRODUCTION $103,000. In 1993, 26 farms in South Carolina, Hawaii and Texas produced a record crop of farm-raised shrimp, approximately 2,500 metric tons, 25 % more than the estimated 'This assumes operating at 50% of full capacity in 2,000 tons in 1992 (Rosenberry, 1993). year 1. However, the United States remained a rela- tively small producer of farm-raised shrimp, accounting for less than 2 % of the production 2 in the Western Hemisphere. In 1993, South of aquaculture projects, including discounted Carolina with 14 fanns and about 100 hectares cash-flow technique, is discussed in Rhodes (ha) in commercial production, accounted for (1991). approximately 20% of the nation's cultured shrimp output (unpublished data, S.C. Depart- LITERATURE REVIEW ment of Natural Resources, 1994). Sandifer, et al. (1993) conducted pond The profitability of South Carolina's (SC) experiments at Waddell Mariculture Center to shrimp mariculture industry is dependent on compare production characteristics of the many factors including the availability of native P. setiferus and Pacific P. vannamei viable postlarvae (PL) at a competitive price. white shrimp in South Carolina. The produc- The SC farms have been generally dependent tion levels achieved in 1989 are thought to be on out-of-state suppliers for PL of the species among the highest achieved with P. setiferus in of choice, P. vannamei, a non-indigenous pond culture. Their results suggest that P. marine shrimp (Rhodes, et al. 1992). Howev- setiferus may be a viable alternative to P. er, farmers have become apprehensive about vannamei for intensive cultivation in the con- future supply and quality of imported PL. In tinental U.S. when P. vannamei are unavail- 1989, many farms had to reduce planned able. They suggest that further evaluation of stocking densities and/or not stock all their this potential is needed. ponds due to an apparent shortage of quality PL's (McGovem-Hopkins et al. 1991). In Griffin, et al. (1984) used a conceptual addition, environmental concerns have incre- model that included production, engineering, ased in recent years regarding the perceived marketing, environment and profit as sub- impacts of farming non-indigenous shrimp in models and a bioeconomic factors simulation the United States. Industry awareness has also model to evaluate a projected penaeid shrimp increased relative to possible negative impacts maricultural operation on the Texas coast. of shrimp diseases carried by PL from out-of- The results showed that the operation would state hatcheries. Consequently, as concerns prove marginally economically feasible based have increased, research has been conducted to on assumptions of the study. A 2 % chance of evaluate the financial feasibility of producing loss and a 4.5 % annual return on investment commercial quantities of indigenous P. setif- were predicted by using baseline simulations. erus versus specific pathogen-free P. vannamei in South Carolina. In addition, the effects of Adams, et al. (1980) developed a bio- continuous live harvesting versus one final economic engineering model for shrimp mari- harvest on the profitability of the two species culture systems for a hypothetical grow-out is evaluated. The information in this report operation in Brazoria County on the northern should be of use to prospective aquaculturists, Texas coast. A budget simulation was devel- investors, and perhaps lending institutions and oped to examine economies of size. Budgeting policy makers. and cash-flow statements were used to examine penaeid shrimp mariculture systems. Their Capital budgeting decisions, i.e., all ac- results suggest that the size of the individual tions relating to the planning and financing of pond which captures most economies of size is capital outlays for the purpose of purchasing 2.5 acres and the number of ponds which equipment and facilities, are a key factor in the achieves most of the economies of size for the long-term profitability of the shrimp farm. In firm is 24. For this operation, IRR to total this study, discounted cash flow analysis, one investment is 17%. of the financial tools that is used to aid an investor in making wise capital budgeting Hollin and Griffin (1985) examined the decisions, is used to compare the profitability economies of: (1) growing one crop of large of P. setiferus versus P. vannamei and contin- shrimp per year versus two crops of medium uous live versus one final harvesting strategies. size shrimp, and (2) small, intensive ponds The application of financial feasibility analysis versus large, sen-ii-intensive ponds. The after- 3 tax internal rate of return (IRR) in the base of total facilities and pond size generally in- scenario for the 500 acre system was 14.61 % crease IRR. For example, a 40 ha facility and for the 40 acre system was 9.1 %. When with 4 ha ponds had a mean after-tax IRR of the production strategy was changed from one 0.75 %, while a 400 ha facility with 20 ha crop to two crops, the IRR on the 500 acre pond sizes had a mean IRR of 13.31 system increased to 22.8 %. The most signifi- cant change in the IRR was brought about by MIETHODS AND DATA increasing the survival rates. When the sur- vival rate was increased from 50 to 70%, IRR The hypothetical farm described in this increased from 14.6 to 25%. paper is based on recommended best manage- ment practices. Production and cost estimates Pardy, et al. (1983) estimated density are predicated upon experience at Waddell dependent growth equations for two species of Mariculture Center (WMC), South Carolina penaeid shrimps, P. stylirostris and P. van- commercial shrimp farms and vendors of namei. Based on these equations, a simulation supplies and services to the aquaculture indus- model was developed to examine the effects of try. Other agencies, such as USDA-Soil Con- alternative stocking densities and cropping servation Service, U.S. Army Corps of Engi- schemes on various variables including gross neers, and S.C. Department of Health and revenue and revenue above total selected costs. Environmental Control, provided data on pond They found that the one harvest production construction costs, licenses, permits, etc. strategy resulted in the greatest gross revenue, no matter what stocking densities were chosen. Facilfty Desigg and Eatdpment The one crop system generally results in larger shrimp and thus, greater market price and The hypothetical facility analyzed in this higher revenue above selected costs. report consists of 24 ponds each of I hectare in size constructed on a 31 hectare farm that is Griffin and Lambregts (1993) evaluated leased near a saltwater source. The average the effects of pond design (pond size, pond pond depth is 1.3 m. A 3-m levee (wide shape, levee crown size and canal bank slope) enough for service vehicles) separates each on the after-tax IRR of a 40 ha shrimp farm. pond. It is assumed that the use of the land Regression analysis was used to examine the was to grow row crops and consequently there relationship between pond design variables and are few stands of trees. the IRR. Results suggest that pond shape, fol- Water exchange is made available to im- lowed by pond size, were the most influential prove water quality (such as dissolved oxygen variables. An increase in pond size from 2 to and water temperature). A minimum water 10 ha increased IRR from 17.2 to 21.3%. exchange rate of 5 % is used in this study. The results are specific to the design, size of However, the farm has the capacity to the farm and soil type and therefore, can not exchange a maximum of 20% of the water in be extrapolated outside the analyzed designs. any one pond. Therefore, the farm has six The authors also addressed the possibility of pumps with flow ratings of 9.1 in' of water increasing operating risks associated with large per minute and 25 horsepower motors. A 12 ponds. in levee separates each pond from the fill and the discharge canals (Figure 1). The fill canal Hanson, et al. (1985) analyzed the effects water will be gravity fed into each pond via an of 12 different facility sizes on the profitability intake riser and released through a discharge of producing a single species of shrimp, P. riser into the discharge canal (Figure 1). stylirostris. Stochastic processing of the model These risers regulate water flow with a system permitted random fluctuations in prices, pro- of boards. Two 10-horsepower paddle-wheel duction, weather and survival rates within their aerators will be placed in each pond. All probability density functions. However, risks electrical wiring for pumps and aerators will associated with larger pond sizes are not exam- be 3 phase. ined. The results suggest that increased sizes 4 Discharge P S.,,,...,pettling Basin Structure-,, Intake Structure - ------ ------ Intake Canal Discharge Canal Arrows indicate direc- tion of water flow. SCALE 0.5 inch = 110 yds. Legend 12M (39ft.) Levee Acres (1 HA) 3 M (1 Oft.) Levee F Each pond is approx. 2.5 Figure 1 - Hypothetical Shrimp Farm Design (Gravity Feed Water System) 5 Other facilities and equipment include: (1) third year onwards production is at 100 % of an office trailer, (2) a 1,000 square feet lab/sh- capacity; and (7) the actual operating time is a op, (3) a 2,000 square feet warehouse, (4) six month season. The straight-line deprecia- three medium sized silos each holding 50,000 tion method is used. A business manager, a pounds of feed, (5) one longbed pickup truck technical manager, a clerk/typist/receptionist and one flatbed truck, (6) one 23 horsepower and two pond management and maintenance tractor for light work and towing feeder and crew work full time. Part time employees are one 52 horsepower tractor for canal and pond a security officer, and harvest and other sea- maintenance, (7) one feed blower, (8) one ice sonal labor. It is also assumed that this hypo- machine, (9) harvest, office, lab equipment, thetical facility is not funded by debt capital, and (10) pre-start up project and survey re- i.e., no loans. The annual financial projec- ports. tions for this facility are generated using a Lotus 1-2-3 spreadsheet template prepared by Production AssumRti :ons Applied Analysis, Inc. (AAI), (Leung and Rowland, 1989). The model does not account Specific pathogen free (SPF) P. vannamei for natural disasters such as droughts, hurri- is used in this study. SPF P. vannamei be- canes, etc. came available for distribution to the United States in 1989 (Wyban, et al. 1993). It has Production Scenaxios been found that use of SPF P. vannamei has increased survival rate, feed efficiency, pro- In the base scenarios, Scenario S and S2A, duction and profitability for the shrimp indus- ponds are stocked at 80 PL/ml in late April. try (Wyban, et al. 1992). An aggregate survival rate of 70% is assumed. Based on the growth model, harvest weights The length of grow-out cycle is 5.0 for P. vannamei and P. setiferus were estimat- months. Risks associated with growing shrimp ed. In addition, it is assumed that all shrimps include natural disasters nutritional and envi- are produced for normal market sales, i.e., no ronmental factors, such as low quality feed, live shrimp sales. These shrimps are sold poor water quality, pollution, and associated head-on to individuals, restaurant distributors, low dissolved oxygen events. The risks of and wholesalers. Prices are those that pre- growing shrimp are not examined in this vailed in South Carolina in 1993 for the esti- study. A feed conversion rate of 2.0:1 is used mated harvest weights. in this study. The harvest weight is estimated using a density dependent growth model (see The following 7 scenarios for the two Appendix 1). This growth model was estimat- species are developed to evaluate the effects of ed using data collected at Waddell Mariculture alternative stocking densities, survival rates, Center and adjusted for commercial grow-out and prices' (see Table 4): experience. Scenario S: Stocking density of 80 Major Fmmcial and ORtratima PL/m, aggregate survival rate of Assppjgfions 70%, price of $4.95/kg for P. vanna- mei and $4.73/kg for P. setiferus The major financial and operating assum- ptions are the following: (1) the price of PL Scenario SIA: Stocking density of 60 including transportation is $10.00 per 1,000; PL/m@, aggregate survival rate of (2) cost of feed (F.O.B., farm site) is $0.55 70%, price of $4.95/kg for P. vanna- per kilogram (kg); (3) electricity cost is mei and $4.73/kg for P. setiferus $0.07/kilowatt-hour(kwh); (4) discount rate is 10%; (5) planning horizon is 10 years; (6) initial investment starts in year 0, first year 11994 prices reported by SC shrimp producers were output is 50% of maximum capacity, second significantly higher than 1993 prices. year output is 75% of maximuirn capacity, and 6 Scenario S1B: Stocking density of species produced. For P. vannamei, operating 100 PL/ml, aggregate survival rate of cost in year 1 is $0.38 million. Therefore, P. 70%, price of $4.95/kg for P. vanna- vannamei requires a total initial investment of mei and $4.73/kg for P. setiferus $1.36 million before any revenue from sales is received. For P. setiferus, projected operating Scenario S2A: Stocking density of 80 cost in year 1 is $0.35 million with a total PL/ml, aggregate survival rate of initial investment of $1.33 million. 70%, price of $4.73/kg. A simple, pro forma annual income state- Scenario S2B: Stocking density of 80 ment for operating years three through ten was PL/m@, aggregate survival rate of generated for the hypothetical P. vannamei 70%, price of $5.28/kg. shrimp farm (Table 2). Projected annual sales are $ 1. 11 million at full capacity and total cash Scenario S3A: Stocking density of 80 operating cost is $0.77 million. Feed and PL PL/ne, aggregate survival rate of accounted for the largest percentage of operat- 65%, price of $4.95/kg. ing cost, 3 3 % and 25 %, respectively. Energy accounted for 10% of the operating cost. Scenario S3B: Stocking density of 80 Total annual cash outflow is $0.86 million. PL/rre, aggregate survival rate of Net cash flow after taxes is $0.25 million. 75 %, price of S4.95/kg. The ten-year (after estimated income tax- Another scenario, Scenario S4 (see Table es) internal rate of return (IRR) and net pres- 4), evaluates the effects of live harvesting on ent value are projected. The ten-year IRR is IRR and NPV. The marketing experience of 15. 1 % (Table 2), which is greater than the S.C. shrimp growers have shown that these base-scenario after-tax discount rate of 10%. buyers are seafood distributors or "live haul- Net present value (NPV) in ten years is pro- ers" selling to Oriental restaurants in the jected to be $232,000. Northeastern United States (Rhodes, et al. 1994). The projected aggregate demand for The pro forma annual income statement live marine shrimp by restaurants in the conti- for operating years three through ten for a nental U.S. is quite small, approximately 30% hypothetical P. setiferus shrimp farm in South of the 1993 U.S. farmed shrimp production. Carolina was generated (Table 3). Projected Therefore, in Scenario S4, only 5 % of produc- annual sales are $0.81 million. Total cash tion is assumed as live marketed. VvIen har- operating cost is $0.71 million. Feed and PL vesting shrimp for live shrimp buyers, it is accounted for the largest percentage of pro- assumed that labor costs $200 for a 250 kg jected operating cost, 27%. Energy accounted shipment. In this analysis, no other changes in for 12% of the operating cost. Total annual operating costs are associated with live shrimp cash outflow is $0.71 million. Net cash flow marketing. after taxes is $0. 10 million. RESLTLTS The ten-year IRR is negative 4.9% and NPV is negative $568,000. The negative NPV Base Scenarios for P. setiferus indicates that this operation will not generate a positive return on equity if Initial investment in facilities and equip- all shrimp are used for normal market sales. ment is $998,000 (Table 1). Equipment costs Unless prices rise above $5.48 per kg, an were approximately 49% of this cost. Land increase of approximately 16% above levels clearing and construction costs account for for 1993, producing P. setifents will not be approximately 48 %. profitable based upon this analysis. In con- trast, the positive NPV for P. vannamei shows Due to differences in growth rates and the potential profitability of culturing this resulting feed costs, operating costs depend on species. Prices in 1993 are approximately 7 Table 1. Summary of Facility and Equipment Costs for a Hypothetical Shrimp Farm in South Carolina, 1993. Item Cost Percent' Useful Years DEVELOPMENT COST Project Report 10,000 20 Project Manager 20,000 Subtotal $ 30,000 3.0 LAND CLEARING AND FACILITIES Land Clearing 85,800 20 Pond Construction 180,000 10 Discharge and Intake System 96,000 10 Buildings 44,000 20 Other 71,955 Subtotal $ 477,755 47.9 EQUIPMENT Harvest Equipment 15,000 10 Feed Storage Bins 36,000 10 Paddlewheels 240,000 5 Trucks/Tractors 50,000 5 Feeding System 40,500 5 Power Equipment 11,000 10 Pumps 82,800 5 Other 15,000 Subtotal $ 490,300 49.1 TOTAL COSTS 998,055 100.0 Percent of total cost 8 Table 2. Projected Annual Income Statement for Operating Years Three Through Ten, and Discounted Cash Flow Analysis in the Base Scenario for a Hypothetical Penaeus vannamei Shrimp Farm in South Carolina. Item Value or Cost Percent' (In Thousands) Proiected Annual Sales $ 1,108 (223,910 kilograms at $4.95/kg) Projected Annual Expenses Juveniles 192 25 Feed 252 33 Energy 80 10 Lease Rent 60 8 Labor 59 8 Salaried Personnel 83 11 Contingency 8 1 Other 33 4 TOTAL OPERATING COST $ 767 100 Projected Depreciation 129 Total Operating Costs with Depreciation 897 Projected Taxable Income 212 (Sales Minus Total Operating Costs) Taxes (Federal. and Local) 79 Income After Taxes 132 (Taxable Income Minus Taxes) Total Annual Cash Outflow 847 (Total Operating Costs plus Taxes) Net Cash Flow 262 (Sales Minus Annual Cash Outflow) Discounted Cash Flow Analysis 10 years Net Present Value (dollars 000's) at 10% 232 Internal Rate of Return (percent) 15.09% 'Percentage of total operating cost. 9 Table 3. Projected Annual Income Statement for Operating Years Three Through Ten, and Discounted Cash Flow Analysis in the Base Scenario for a Hypothetical Penaeus setiferus Shrimp Farm in South Carolina. Item Value or Cost Percent' (in Thousands) Proiected Annual Sales $ 810 (171,226 kilograms at $4.73/kg) Proiected Annual ExRenses Juveniles 192 27 Feed 192 27 Energy 80 12 Lease Rent 60 8 Labor 59 8 Salaried Personnel 83 12 Contingency 7 1 Other 33 5 TOTAL OPERATING COST $706 100 Projected Depreciation 129 Total Operating Costs with Depreciation 837 Projected Taxable Income -28 (Sales Minus Total Operating Costs) Taxes (Federal and Local) -6 Income After Taxes -22 (Taxable Income Minus Taxes) Total Annual Cash Outflow 702 (Total Operating Costs plus Taxes) Net Cash Flow 107 (Sales Minus Annual Cash Outflow) Discounted Cash Flow An@ftsis 10 years Net Present Value (dollars 000's) at 10% -568 Internal rate of return (percent) -4.93% 'Percentage of total operating cost 10 18 % greater than the break even price. That farnis of similar sizes. The estimated IRR's is, prices of P. vannamei can drop approxi- range from 0. 75 % by Hanson, et al. (1985) mately 18% and the producers will continue to for a 40 ha facility to 4.5 % by Griffin, et al. make a positive NPV. (1984). The IRR of 9.06% estimated by Hollin and Griffin (1985) is with a survival rate of 50 %, less than that assumed in this study. Alternative Scenarios The estimated IRR for P. setiferus is less P. setiferus is unprofitable (i.e. a negative than the assumed discount rate for the base NPV) in all the alternative scenarios consid- scenario. Therefore, this operation fails to ered in this analysis (Table 4). The profitabili- generate a positive return on equity. The ty of P. vannamei is sensitive to changes in negative NPV may be improved if better prices, stocking densities and survival rates. growth can be achieved and/or by developing a specialty market for P. setiferus. Relatively In scenario S4, 5 % of the shrimp are live high growth rates have been recorded for this marketed. Discounted cash flow analysis for species in the wild or at relatively low densi- P. vannamei and P. setiferus with 5 % of ties in ponds (Sandifer, et al. 1993 and WMC production for live market sales and the re- unpublished data). Achievement of these maining 95 % of production for final market growth rates in intensive pond culture will sales were generated (Table 4). For P. vanna- depend on improved diets and/or rearing mei, the ten-year IRR is 16.9%, which is procedures for P. setiferus. Live shrimp greater than the base scenario after-tax dis- market segments for fishing bait are limited to count rate of 10%. NPV in ten years is native species. Although wholesale bait $321,000. The higher IRR and NPV in Sce- shrimp prices may be somewhat higher, there nario S4, as compared to the base scenario is a potential risk of "flooding" this relatively where 100% of the shrimp are for normal limited market. In addition, the lack of cost market sales, indicates the potential higher effective storage facilities may hinder entrance profitability of selling shrimp to "live-haulers". to these markets. For P. setifew, IRR is 2.2 %, but the NPV is still a negative -$320,000. Relative to the base The projected IRR for P. vannamei, scenario, live harvesting does improve the 15. 1 %, is greater than the assumed base sce- financial viability of a P. setiferus shrimp nario discount rate of 10%. The positive NPV farm. However, the negative NPV still indi- for P. vannamei indicates that commercial cates that this operation would not generate a shrimp farm in S.C. could have a positive positive return on equity even if 5 % of the return to equity assuming specific pathogen shrimps are used for live market sales. free PL are used. Hollin and Griffin (1985) estimated an IRR of 22.5 % for a 40 acre farm DISCUSSION with an 80% survival rate, a survival rate 10% points higher than used in the base scenario in Sandifer, et al. (1993) evaluated produc- this analysis. The NPV for both species may tion data from Waddell Mariculture Center be improved by operating larger facilities, (WMC) and concluded that P. setiferus may be integrating a nursery "headstart" operation a viable alternative to P. vannamei for inten- with the farm or if price increases. sive cultivation in the continental U.S. when P. vannamei are unavailable. They recom- The profitability of Pacific white shrimp, mended further evaluation of this potential. P. vannamei and the negative NPV of indige- The preliminary financial analysis presented in nous P. setifenis have implications on regula- this report suggests that a P. setifenis commer- tions that might affect the import of PL from cial shrimp farm operation would only gener- out-of-state. Regulations that exclude P. ate a negative IRR. This is less than the range vannamei as the target species could severely of IRR estimated by other researchers for 11 Table 4. Discounted Cash Flow Analysis for the Alternative Scenarios for Hypothetical Penaeus setiferus and Penaeus vannamei Shrimp Farm in South Carolina, 1993. Scenarios P. setiferus P. vannamei NPV IRR (0/,) NPV IRR Scenario S -$416,000 -0.40% $232,000* 15.09%* Scenario SIA -$843,000 -14.92% -$275,000 3.40% Scenario SIB -$166,000 6.11% $516,000 20.84% Scenario S2A -$568,000* 4.93%* $87,000 11-95% Scenario S2B -$201,000 5.26% $438,000 19-31% Scenario S3A -$600,000 -5.96% $55,000 11-25% Scenario S3B -$236,000 4.40% $402,000 18-60% Scenario S4 -$320,000 2.22% $321,000 16.94% *BASE SCENARIO Scenario S Stocking density of 80 PL/meter', aggregate survival rate of 70%, price of $4.95 / kg. Scenario SIA Stocking density of 60 PL/meter, aggregate survival rate of 70%, price of $4.95 / kg for P. vannamei and $4.73 / kg for P. setiferus Scenario SIB Stocking density of 100 PL/meter, aggregate survival rate of 70%, price of $4.95 / kg for P. vannamei and $4.73 / kg for P. setiferus Scenario S2A Stocking density of 80 PL/meter, aggregate survival rate of 70%, price of $4.73 / kg. Scenario S2B Stocking density of 80 PL/meter2, aggregate survival rate of 70%, price of $5.28 / kg. Scenario S3A Stocking density of 80 PL/meter2, aggregate survival rate of 65%, price of $4.95 / kg. Scenario S2B Stocking density of 80 PL/meter, aggregate survival rate of 75%, price of $4.95 / kg. Scenario S4 Stocking density of 80 PL/meter, aggregate survival rate of 70%, continuous live market sales of 5% and "normal" market sales of 95%. NPV = Net present value after taxes. IRR = Internal rate of return after taxes. After-tax discount rate is 10%. 12 constrain the profitability of shrimp farming Griffin, W.L., W.E. Grant, R.W. Brick, and using the techniques outlined in this analysis. J.S. Hanson. 1984. A bio-econornic model of shrimp maricultaral systems Continuous live market sales have positive in the U.S.A. Ecological Modelling, effects on net cash flows for P. setiferus and 25(2):47-68. P. vannamei. A 1993 survey conducted by Rhodes, et al. (1994) suggests that opportuni- Griffin, W.L., and J.A.D. Lambregts. 1993. ties for selling live shrimp probably exist The impact of aquaculture pond throughout the major metropolitan areas of engineering design on the returns to continental U.S., especially in the Northeastern shrimp farms. Journal of the World states, but the lack of cost effective storage Aquaculture Society 24(l):23-30. facilities may hinder entrance to these markets. In addition, the live shrimp market for S.C. Hanson, J.S., W.L. Griffin, J.W. Richardson producers seems relatively small. Unless addi- and C.J. Nixon. 1985. Economic tional markets are identified, live harvesting of feasibility of shrimp farming in Texas: large quantities of shrimps can have a negative An investment analysis for semi-inten- impact on prices. Therefore, because the live sive pond grow-out. Journal of the shrimp market is relatively small, it is irnpor- World Mariculture Society. 16:129- tant that producers remain alert for potential 150. "oversupply" conditions that might signal a major reduction in prices, particularly for live Hollin, D. and W.L. Griffin. 1985. Prelimi- market sales. nary economics of shrimp mariculture in Texas. Presented at Texas Shrimp This study confirms the findings in Farming Workshop, Corpus Christi, Rhodes, et al. (1987) that the profitability of Texas. S.C. marine shrimp operations is strongly influenced by survival rates, stocking densities, Leung, P.S. and L.W. Rowland. 1989. Finan- etc. The effects of these variables on the cial analysis of shrimp production: An financial viability of producing P. setiferus and electronic spreadsheet model. Com- P. vannamei were examined by developing puters and Electronics in Agriculture alternative scenarios. The models used in this 3:287-304. study are based on several simplifying assump- tions, e.g., the land is leased. Nevertheless, McGovern-Hopkins, K., C.L. Browdy, J.D. in general, the model did demonstrate potential Holloway and J.S. Hopkins. 1991. species effects on the direction of changes in Penaeid shrimp hatchery system de- profits, and to a lesser extent, the magnitude velopment for South Carolina. (Ab- of such profits. Therefore, it may be fruitful stract) World Aquaculture Society for prospective shrimp aquaculturists, inves- 22nd Annual Conf. & Expo., San tors, and perhaps lending institutions and Juan, Puerto Rico, June 16-20, 1991. policy makers to be aware of these findings. Pardy, C.R., W. L. Griffin, M.A. Johns, and A.L. Lawrence. 1983. A preliminary LITERATURE CITED economic analysis of stocking strate- gies for penaeid shrimp culture. Adams, C. M., W.L. Griffin, J.P. Nichols Journal of the World Mariculture and R.E. Brick. 1980. Application of a Society, 14:49-63. bio-economic-engineering model for shrimp mariculture systems. Southern Journal of Agricultural Economics, 12(l):135-142. 13 Rhodes, R.J., P.A. Sandifer and J.M. Whet- Wyban, James A., J. S. Swingle, J. N. stone. 1987. A preliminary financial Sweeny, and G. D. Pruder. 1992. analysis of semi-intensive penaeid Development and commercial perfor- shrimp farming in South Carolina. mance of high health shrimp using S.C. Marine Res. Ctr., Tech. Rpt. No. specific pathogen free (SPF) brood- 64. stock Penaeus vannamei. In: J.A. Wyban (Editor), Proceedings of the Rhodes, R.J. 1991. Economics of Aqua- Special Session on Shrimp Farming, culture production: Financial Feasibil- World Aquaculture Society, Baton ity. In: J.A. Hargreaves and D.A. Rouge, LA. Alston (Editors), Status and Potential of Aquaculture in the Caribbean. Wyban, James A., J. S. Swingle, J.N. World Aquaculture Society, Baton Sweeney, and G. D. Pruder. 1993. Rouge, LA. Specific pathogen free Penaeus vanna- mei. World Aquaculture 24(l):39-45. Rhodes, R.J., K. McGovern-Hopkins, and C.L. Browdy. 1992. Preliminary financial feasibility analysis of an inde- APPENDIX 1 pendent marine shrimp hatchery locat- ed in South Carolina. S.C. Marine SHRIMP HARVEST WEIGHT MODEL Res. Ctr., Tech. Rpt. No. 80. The empirical specification of the model is: Rhodes, R.J., A. Johnson, C.L. Browdy, P.A. Sandifer. 1994. Analyzing Live LWeight = bo + b, 4Age + b2 LDensity + Seafood Marketing Opportunities in the b3 Species + b4 Disease + b. Year 87 + b6 United States: The South Carolina Year88 + b7 Year89 + b8 Year9O + bg Experience with Live Shrimp. (Poster) Year9l blo Year92 + e . Annual meetings of the World Aqua- culture Society, New Orleans, LA, Where, LWeight = Log of average harvest January 1994. weight in grams per week, LAge =Log of the number of growout days in weeks; Disease Rosenberry, B. 1993. (Editor) World Shrimp binary variable, equal to I if signs of viral Farming: Special Report, Shrimp Far- infection were observed during the growout ming In The United States. Aqua- cycle (0 otherwise); Species = binary variable, culture Digest, San Diego, CA 92131. equal to one if species is P. vamamei (0 other- wise); and LDensity = Log of stocking Sandifer, P.A., J.S. Hopkins, A.D. Stokes density, number stocked/m@ Year87,...,Year92 and C.L. Browdy. 1993. Preliminary = binary variable, equal to one for that year, comparisons of the native P. setiferus (0 otherwise). and pacific P. vannamei white shrimp for pond culture in South Carolina, There were a total of 100 observations USA. Journal of the World Aqua- (ponds) in the data collected at Waddell Maric- culture Society, 24(3):295-303. ulture Center during shrimp culture experi- ments conducted from 1984 to 1992. Each observation had 18 variables (Pond, year, stock date, harvest date, crop length, stock weight, harvest weight, growth rate, pond size, species, stock source, disease status, stocking density, number stocked, number harvested, estimated survival rate, production, and experimental comparison). The biweekly sampling data were excluded from the 14 analysis. Among the 100 observations 45 Binary variables, one for each year ponds satisfied the criteria similar to the best from 1987 to 1992 were included as a proxy management practices recommended for S.C. for water temperature. To avoid problems commercial shrimp farms. with multicollinearity, the year 1986 is omitted and its effects are captured by the intercept. The selected criteria are: a) survival All the YEAR variables shift the intercept by rate greater than 60%; b) density between 20 the amount of the estimated coefficient. and 100 per square meter; c) ponds were stocked before June 1; d) ponds were harvest- ed late September or October; e) all aeration rates were included; f) all exchange rates were included; g) ponds in which shellfish were cul- tured with shrimps were included. The estimated regression coefficients are presented in Table 5. Significance of the estimated coefficients were tested at 0.05 and 0. 1 levels. Three criterion were used to ex- amine the overall "goodness" of fit of the regression models. The high F-value rejects the null hypothesis that all the regression coefficients for the explanatory variables are simultaneously equal to zero. The W and the adjusted RI indicate that a large percentage of the variation in the dependent variable are explained by the independent variables includ- ed in the model - The adjusted W takes into account the number of explanatory variables in relation to the number of observations. There- fore, in a multiple regression model, the ad- justed W is preferred to R. As expected, age and species have a positive effect on the final harvest weight of shrimps. A 1 % increase in age will increase the harvest weight by 0.52 %. Species, a binary variable, with a value of 1 for P. vann- amei and 0 otherwise, increases the intercept for the regression model for P. vannamei. Density and disease have a negative regression coefficient. That is, as expected, at higher densities the average harvest weight would be smaller. The results show that a 1 % increase in density will decrease the harvest weight by 0. 16 % Disease, a binary variable, with a value of 1 for post larvae with disease and 0 otherwise, will reduce the intercept for the model P. vannamei with disease by the estimated coefficient. 15 Table 5. Regression Coefficients for the Harvest Weight Model',' Variable Coefficients Name Intercept 0.62* Age 0.52* Density -0. 16* Species 0.13* Disease -0.07** Year87 -0.05 Year88 0.07 Year89 0.18 Year9O 0. 15* Year9l 0. 12* Year92 0.01 Variables significant at 0.05 level Variables significant at 0.10 level 'Harvest weight model adjusted for commercial grow-out experience in Penaeus vannamei: Lweight = 0. 85 + 0.52 LAge - 0. 16 L Density. bPenaeus setiferus: Lweight 0. 75 + 0.52 LAge - 0. 16 L Density. @er low 411 Aaft -2w mo-iiia , W_ 2@1 4i* Aw 3 6668 00003 6451