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Hoyle, I., Oidtmann, B., Ellis, T., Turnbull, J., North, B., Nikolaidis, J., Knowles, T.G.,

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Hoyle, I., Oidtmann, B., Ellis, T., Turnbull, J., North, B., Nikolaidis, J., Knowles, T.G.,

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  1. An Economic Analysis of a New High Density Polyethylene Aquaculture TankDaniel Miller, Dr. Gerard D’Souza - Davis College of Agriculture Forestry and Consumer Sciences - West Virginia UniversityCharles Conklin - Big Brown Fish Hatchery Financial support: USDA-CSREES via Northeast Regional Aquaculture Center (NRAC) and Eastern Associated Coal Co. Objectives The goal of this research was to compare the cost of purchasing, installing and operating a new plastic “U” shaped raceway (fish tank) to the traditional concrete flat-bottomed raceways used in many federal, state, and private fish hatcheries. Potential benefits of this new design include lower fixed (purchase and installation) costs, ease of mobility due to its light weight, reduced operational cost, due to the rapid cleaning process that the “U” shape allows, and the simplicity with which modifications can be made to the tank to suit the operation. 1) To determine if a plastic (high density polyethylene, HDPE) “U”shaped raceway can reduce the cost of production for small and medium sized (< 100,000 lbs. yr.) fish producers. 2) To measure the labor savings required for solids removal in terms of time and money, by modifying the quiescent zone with a ventral manifold pipe. 3) To compare the fixed and variable costs of traditional concrete raceways to plastic (HDPE) raceways. 4) To determine the fin condition of trout grown in the plastic tanks, and compare them to trout grown in concrete raceways. Results Critical water quality parameters remained stable at both sites for the most of this study. Water temperatures remained between 11 and 15 degrees Celsius at both sites. Water analysis from both sites showed that all measured parameters were within the tolerance range of trout. The water quality monitoring that was done at each site showed that the concrete tank had one low oxygen event during the last week in May, which resulted in the precautionary removal of 400 trout (40%) from the system. The plastic tanks had two low oxygen events in the lower tanks, one in May and one in June, due to the intrusion of a bear which managed to divert the water from the lower tanks. The upper two tanks were unaffected by this diversion of water. Growth, fin condition, and mortality data presented here is based on the average in top two plastic tanks compared to the concrete tank. At the end of the demonstration (31 weeks) average fish weight was based on a random sample of at least 50 fish from the approximately 1000 fish stocked in each tank. The trout in the concrete tank showed better growth and higher mortality than those in the plastic tanks (Table 1). A one way ANOVA was performed on the fin condition data using total fin condition scores. When the trout from the two plastic tanks were compared to the trout in the concrete tank, the ANOVA procedure showed there was no significant difference (α < 0.05) of fin erosion comparing the two trout populations. Table 1. Growth, fin condition, and mortality from concrete and plastic tank system. Tank Weight Growth Fin Culture Volume Gain Score Mortality Period (m3) (g) (g/day) (%) (days) Concrete 7.84 484 2.20 7.93 5.62 220 Plastic 7.57 382 1.75 8.08 3.96 219 Annual Maintenance / Cleaning costs: Assuming labor costs at $10 per hr. and cleaning occurs every 5 days (73 times per year), an average of 5 cleanings during the study resulted in 3.4 hours per tank per year for cleaning or $34 per tank per year. The average cleaning time for the concrete tank required 6.75 minutes. This translates into 8.2 hours per tank per year or $82 per tank per year (Table 2). Table 2. Cost comparison for concrete and plastic tanks (10 tanks) Cost Install Cleaning Total precast $ $ $ $ % Concrete precast 45,850 6,000 820 52,670 100% Concrete poured 33,110 4,000 820 37,930 72% HDPE plastic 24,507 3,000 340 27,847 53% Based on the enterprise budget the Net Present Value is relatively large. This assumes a 10-year planning horizon and 20,000 lb./ year harvest. Cost of CapitalNet Present Value 7% $103,005 10% $82,980 13% $66,614 The internal rate of return over a 10 year period is 36%. Measuring fin condition • Conclusions • The plastic tanks used in this demonstration appear to be suitable for quarantine, fingerlings, and growout, with flow-through or recirculating systems. Development of improved screens and crowding systems is warranted. • These plastic tanks are presently limited to a maximum diameter of 60 inches. Concrete tanks can be made nearly any size or shape. Although extremely resilient, the plastic tanks should be partially set into the ground ( 20” – 24” ) for stability. Had this been done in this demonstration, we expect the damage done by bears would have been minimal. If used indoors, cross-braces or some other support will be required for the plastic tanks. • Total cost of the plastic tank system is was estimated to be approximately 53% of a precast concrete system and 74% of a poured concrete system for similar production volume. Net present value and the internal rate of return are favorable for the plastic tanks based on our analysis. • The equipment and skills used to install the plastic tanks are more commonly available than for concrete tanks. It is conceivable that the grower can install them himself. The modular nature and durability of the tanks should allow them to be moved and reset if necessary. • The time required to clean the plastic tanks was 41% of the labor required to clean the flat bottomed concrete tanks. This is attributed to the design of the quiescent zone. Labor savings were estimated to be $9,600 over the expected 20 year life span of a ten tank system. • There was no significant difference between the concrete and plastic tanks regarding fin condition of the trout. • WVU has received a provisional patent on this tank design (docket number 349) and will license a U. S. based manufacturer to make the low cost tank. High Density Polyethylene (HDPE) tank system Methods In November of 2006 one group of 4 inch rainbow trout fingerlings were stocked into a series of 2,000 gallon “U” shaped plastic tanks at a density of about 4 fish per cubic foot. The plastic tanks were located in a remote area of southern West Virginia that had a reliable high quality mine water discharge. A chain link fence surrounded the tanks and three electrified wires around the fence were used to deter predators. Fingerlings from the same cohort and from the same hatchery, were stocked at the same densities into a blank gallon flat bottomed concrete at a commercial trout hatchery in Pennsylvania. Facilities at each locations had a history of supporting normal trout growth. Fish were fed (daily?) a 42% protein 16% fat commercial trout diet during the 31 week production cycle. Demand feeders were used at both sites. Nylon netting was used to deter aerial predators. Average weight was measured at six week intervals. A random sample of at least 50 fish were weighed with an Ohaus bench scale. As the trout approached marketable size, fin condition was recorded using a scale from 0 (perfect) to 5 (> 90% missing or eroded) for each of the 7 rayed fins. Each fish had a potential score between 0 and 35. A photographic key for each of the fins, developed by Hoyle (2007), was used as a reference during the fin condition data collection. Water quality data was monitored in the plastic tanks using a YSI 600XLM sonde. Temperature, pH, oxygen and conductivity were recorded hourly. In the concrete system, a hand held YSI oxygen meter was used to measure temperature and dissolved oxygen. Water samples from each site were analyzed by a certified analytical laboratory for blank, blank and blank (how often?). The cost of purchasing, installing, and cleaning the custom plastic tanks during the study were compared to the estimated cost of purchasing, installing, and cleaning precast concrete tanks as well as poured concrete tanks. Businesses that specialize in building concrete tanks provided recent quotes for this cost estimate. The labor cost for cleaning the plastic and concrete tanks was measured on five occasions during the last five months of the study. Annual labor demands for this task were estimated with this data. Introduction West Virginia has many free flowing groundwater sources from coal mines that can be used for small scale fish production. Economies of scale usually result in a higher cost of production for smaller producers, making it difficult to compete with larger operations. This study uses a small mine water discharge to determine if there is a way for producers to reduce their costs by using a new “U” shaped plastic tank for fish production. The potential advantages of this new tank include lower purchase and installation costs, easy modifications, transportability, which allows for resale value, and reduced labor for cleaning. The costs of the new tank are compared to precast concrete and poured concrete raceway systems, the material most commonly use for producing trout. Hoyle, I., Oidtmann, B., Ellis, T., Turnbull, J., North, B., Nikolaidis, J., Knowles, T.G., A Validated Macroscopic Key to Assess Fin Damage in Farmed Rainbow Trout (Oncorhynchus mykiss), Aquaculture (2007), doi:10.1016/j.aquaculture.2007.03.037 Plastic (HDPE) tank installation

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