Source: WARD AQUAFARMS LLC submitted to
INCREASING DOMESTIC SALMONID PRODUCTION IN AN ECONOMICALLY AND ENVIRONMENTALLY SUSTAINABLE SYSTEM
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
1019751
Grant No.
2019-33610-29816
Cumulative Award Amt.
$99,101.00
Proposal No.
2019-00777
Multistate No.
(N/A)
Project Start Date
Aug 1, 2019
Project End Date
Mar 31, 2020
Grant Year
2019
Program Code
[8.12]- Small and Mid-Size Farms
Recipient Organization
WARD AQUAFARMS LLC
51 N FALMOUTH HWY
NORTH FALMOUTH,MA 02556
Performing Department
(N/A)
Non Technical Summary
The east coast of the United States has a prospering and growing shellfish aquaculture industry with over 1,000 small farms producing $45 million annually in dockside revenue. However, there are currently no marine finfish aquaculture operations outside of limited salmon operations in the state of Maine. This is partially due to difficulty in securing permits for finfish operations, and partially due to the difficulty in growing a fish in New England waters year round. With coastal water temperatures that can fluctuate in excess of 20 degrees Celsius, there are very few options in terms of species of fish to grow, and places to grow them. The future expansion of the Massachusetts aquaculture industry is dependent on developing alternative strategies to diversify farms within a highly developed marine ecosystem. This project will demonstrate the economic and environmental viability of a novel grow-out strategy for farming steelhead trout, by utilizing existing marina infrastructure in the winter offseason, from October to May. This will yield farmers a high-valued, off-season crop for aquaculture operations, increasing the profitability and production of the farm. Netpens are less likely to receive negative stakeholder feedback if sited in commercially established marina locations in the winter offseason. The netpens will be surrounded by eastern oysters and bay scallops in lantern nets, and lines of sugar kelp to incorporate an integrated multi-trophic design. The addition of filter feeding shellfish and nutrient retaining kelp will decrease the environmental impacts, while increasing the economic viability of the system by adding new crops to the farm.
Animal Health Component
100%
Research Effort Categories
Basic
0%
Applied
100%
Developmental
0%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
30708101060100%
Knowledge Area
307 - Animal Management Systems;

Subject Of Investigation
0810 - Finfish;

Field Of Science
1060 - Biology (whole systems);
Goals / Objectives
The goal of this project is to produce steelhead trout, eastern oysters, bay scallops and sugar kelp in an integrated multi-trophic production system within existing marina infrastructure. Specific objectives include:Investigate optimal multi-trophic production techniques for steelhead trout, eastern oysters, bay scallops and sugar kelp within an integrated system.Evaluate environmental impact through comprehensive water quality and benthic sampling.Evaluate the economic viability of two intermediate grow-out strategies; direct from the hatchery vs. intermediate growout in a recirculation system.Evaluate the market potential given three different sales strategies: whole fish (1 lb. fish), live sales (2 lb. fish) and fillets (3 lb. fish).
Project Methods
Objective 1: Investigate optimal multi-trophic production techniques for steelhead trout, eastern oysters, bay scallops and sugar kelp within an integrated system.Two netpens will be installed into two identical slips at Fiddler's Cove Marina, North Falmouth, MA (Fig. 1) in October of 2019. Ward Aquafarms already utilizes two other slips for float storage from October-May, and boat use throughout the year. Marinas are frequently used by shellfish farms for nursery and boat operations. By placing the net pens adjacent to an existing shellfish farm operation, additional labor costs will be reduced, and integration into standard farm operations will be more efficient. The two identical surface net pens (4m x 6m x 3m; custom nets from Reidar's Nets, New Bedford, MA), will be hung from existing finger piers, utilizing existing flotation and cleats. Young-of-the-year Steelhead trout will be purchased from a local hatchery (12 months old, approximately 400g, 20-25 cm), stocked into each net pen in late fall (October-November), when summer water temperatures have declined below 20°C.Oysters and bay scallops will be stocked at 2 locations in October 2019: 1) directly adjacent to the trout netpens in the same or adjacent slip; and 2) in outer Megansett at the farm growout site. In October, approximately 10,000 oysters (< 2") will be stocked into replicate 5-level, 21 mm monofilament lantern nets at commonly accepted commercial levels (1/3 surface area), and 10,000 bay scallops (< 2") will be stocked into replicate lantern nets, at 20 per ft2. Half of the animals will be deployed directly adjacent to the netpens, and half of the animals will be deployed on the Megansett growout site. Sugar kelp seed string will be purchased from one of the locally available seed string suppliers (Greenwave, CT; Walrus and Carpenter, RI; Cottage City Oysters, MA; Springtide Seaweed ME) in October of 2019. Five, identical 20' lines of sugar kelp will be installed adjacent to the trout netpens, and five identical lines will also be installed at the current Megansett Harbor oyster farm. For this objective we will evaluate fish, shellfish and algae growth between the two treatments. Net production, effort and cost will also be evaluated. A one-way analysis of variance (ANOVA) will be employed to evaluate the effect of different treatments on the above variables. Tukey's HSD test will be employed for comparison of various treatments for the significance of difference at P < 0.05.Objective 2: Evaluate environmental impact through comprehensive water quality and benthic sampling.First in October (prior to adding fish), in again in May (after all fish have been removed). Sediment grab samples will be taken from the top 5 cm of sediment from identical locations as the water samples, at the same sampling times as noted above. All water samples will be assayed for the following parameters by Envirotech Labs, Sandwich, MA: ammonia, nitrate, nitrite, total nitrogen, organic nitrogen, total phosphorus, organic phosphorus, pH and suspended solids. All sediment samples will be assayed for the same parameters, except suspended solids in the sediment samples. At the same environmental sampling intervals, identical samples will be taken from four randomly assigned locations within the 10 acre grow-out site, ½ nm west of the netpen site, and will be assayed for the same parameters. All data will be analyzed, evaluated for changes in water and sediment quality and submitted to the required regulatory agencies.Objective 3: Evaluate the economic viability of two intermediate grow-out strategies; direct from the hatchery vs. intermediate growout in a recirculation system.In the Phase I project, the logistical and economic impacts of two different initial stocking densities and harvest strategies will be investigated. Based on the results from Phase I, the best method will be employed in the Phase II trial, and the variable to be investigated will be the financial impact of differential fish size at stocking. Spring water feeding the hatcheries in the southern New England region is approximately 10° C, which results in a 20-25 cm, 400-500 g fish in October (12 months post-hatch), which typically sells for $6.00 per fish. However, fish from the same cohort can be purchased in May-July at 10-15 cm, and 140-150 g, for $2.00 per fish. When the rainbow trout are raised at 17° C instead of 10° C for 3 months, the same fish can grow to 1 kg when stocked into the net pens at 12 months as opposed to 400-500g. If the feed conversion ratio (FCR) can be kept low, and the install cost of a recirculating system can be minimized, the difference in stocking size could lead to a significant difference in harvest value, and subsequently economic viability of the enterprise, given the short growing window in New England. The design, build and installation costs are variable and specific to each farm, and therefore will not be evaluated in this project. The intent of this objective is to study the economic impact of "pre-growing" the rainbow trout in recirculating tanks, aside from initial installation consideration. Collaborating with Mr. Rillahan at the University of Massachusetts is ideal, as the school recently constructed a new recirculating seawater facility, which will be utilized for this objective.Objective 4: Evaluate the market potential given three different sales strategies: whole fish (1 lb. fish), live sales (2 lb. fish) and fillets (3 lb. fish).While quantifying the biological impacts on the environment, and the viability of the culture technique are the main objectives of the project, marketability of the final products and maintaining economic viability are just as important to the success of the entire project in the long term. The trout raised will be marketed in 3 ways: 1) live market through Boston, 2) seafood restaurants in Cape Cod, and, 3) fresh fillets. Live market prices can often be much higher per pound as compared to filleted or fresh product. In 2017, gutted trout were purchased at $7.00/lb for min. 500 g fish (Michael Chambers, per comm.). All trout, shellfish and seaweeds on both the control site as well as the netpen site will be sold for human consumption. In addition to the high-price live-market, the high quality flesh may be ideal to sell to markets in and around Cape Cod, and to restaurants in the Cape Cod area. The above possibilities for trout sales will be explored in this project, as well as combination strategies for oyster, fish and seaweed combination sales. All expenditures will be tracked throughout the project to best evaluate the economic viability of the multi-trophic system as described in this proposal. It is important to evaluate survival in the culture location, growth rates as they compare to theoretical and measured in the lab, and market acceptability of the finished product. The end analysis of the above factors, combined with the tracked expenditures throughout the project will allow for comparison following the conclusion to determine expected revenue from a farm of this size, under these conditions. Most likely to justify the expenditures of refrigeration, materials, etc. that are associated with expansion into finfish culture, it may be that multiple cages of this magnitude are built, and the associated costs are shared by multiple farmers.

Progress 08/01/19 to 03/31/20

Outputs
Target Audience:The main target audience of this project was aquaculture operations and/or institutions/organizations conducting aquaculture research in the northeastern United States. Many of which the target audience of aquaculture operations in the northeastern United States exist in coastal communities where income is seasonal and the need for more year round jobs will help boost local economies and the wellbeing of the individuals within those coastal communities. However, none of the results from this project have been conveyed to the intended audiences due to Covid-19. Once the threat of Covid-19 has passed, results will be conveyed via presentations at scientific and aquaculture focused conferences in the northeastern United States. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?This study provided an opportunity for multiple employees to gain experience in finfish farming. The employees (i.e. not the Primary Investigators) involved in this experiment had an aquaculture research background of primarily shellfish. Their involvement improved their knowledge of finfish aquaculture. Furthermore, they represented the target audience of individuals who have shellfish experience in the northeastern United States, but have limited experience in finfish aquaculture. Thus, they provided an example of how this project could be replicated by other aquaculturists in the northeastern United States. Outside of the individuals involved directly with the experiment, no other individuals have been reached yet. The lack of the information obtained from this study being conveyed to larger audience is due to social distancing restrictions caused by Covid-19. How have the results been disseminated to communities of interest?The results have yet to be disseminated to communities of interest due to social distancing restrictions in placed in regards to Covid-19. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? This study investigated methods to promote small scale finfish aquaculture operations in New England with a focus on promoting year-round revenue for current and future aquaculture operations. The first portion of the study was to investigate the use of a recirculating aquaculture system to raise steelhead trout at a water temperature and feeding rate that optimized growth rates and promoted healthy livestock. The use of the recirculating system was to identify if artificially maintained temperatures can increase biomass production in steelhead trout culturing compared trout pond culturing. The studied also investigate the use of an integrated multi-trophic aquaculture approach (IMTA), which permitted the culturing of different species at different trophic levels. The intention of investigating IMTA was to assess its ability to increase the revenue of small shellfish farms by diversifying the livestock species cultivated while mitigating any negative side effects associated with finfish culture. In New England, growers primarily grow and sell oysters. However, oysters in New England don't grow for about four months a year once water temperatures drop below 10oC. Diversifying the species cultured by aquaculture operations in New England states could provide year round revenue and jobs. During the recirculating aquaculture system phase of the study, average monthly growth rates (grams/day) increased linearly (R2 = 0.9643) at a rate of 1.68% total body weight per day. The Fulton's condition factor (K) of the trout in the recirculating system also increased linearly (R2 = 0.9999). Once the trout from the recirculating aquaculture system were transferred to net pens in December, daily growth rates in weight significantly decreased and the average Fulton's condition factor of the population fluctuated resulting in a minimal decrease from the initial condition factor of the population by the end of the four month net pen experiment. Shellfish in the IMTA portion exhibited no differences in growth rates between the control site and the site adjacent to the net pens. High kelp growth rates were observed adjacent to the net pens, but the high growth may have been due preexisting water environmental conditions in cove were the net pens were located. Overall, the study illustrated the use of a recirculating aquaculture system at optimal temperatures (20oC) results in high gains in biomass and promotes a healthy population of trout for stocking in net pens in winter months when shellfish sales are minimal or nonexistent. However, with no significant growth and increases in health to be expected from the net pen phase, increasing biomass and health beyond that observed in this experiment must be achieved prior to net pen deployment. Thus, an extension in the duration in which the trout are housed in the recirculating aquaculture system would promote a larger more viable market sized trout for sale during winter months when shellfish sales are minimal. Objective I: Investigate optimal multi-trophic production techniques for steelhead trout, eastern oysters, bay scallops and sugar kelp within an integrated system. 1) Major activities completed / experiments conducted Two netpens were installed by Ward Aquafarms into two identical slips at Fiddler's Cove Marina, North Falmouth, MA (Figure 1) in December of 2019. Ward Aquafarms already utilizes two other slips for float storage from October-May, and boat use throughout the year. By placing the net pens adjacent to an existing shellfish farm operation, additional labor costs were be reduced, and integration into standard farm operations was easily established. The two identical surface net pens (4m x 6m x 3m; custom nets from Reidar's Nets, New Bedford, MA), were hung from existing finger piers, utilizing existing flotation and cleats. Figure 1: Cape Cod, Massachusetts. Red inset illustrates the project location at Fiddler's Cove Marina, which is adjacent to Megansett Harbor, where Ward Aquafarms' commercial growout sites are located. Prior to netpen stocking, two different grow-out strategies were implemented. The two different methods of stocking which were evaluated: 1) direct from the hatchery, or 2) pre-growing in recirculating aquaculture system tanks (R.A.S.) (Objective 3). In December of 2019 one net pen was stocked with 1,000 steelhead trout 187.4 grams (SD±34.8) from the recirculating tanks and one netpen was stocked with 1,000 steelhead trout 189.6 grams (SD±34.1) from the hatchery. Once fish were transferred to the netpens, they were fed until satiation over a ten minute period (~0.5% total biomass weight) twice a day. Oysters and bay scallops were stocked at two locations in December 2019: 1) directly adjacent to the trout netpens in the same slip; and 2) in outer Megansett at the farm growout site. In December, 2019, approximately 10,000 oysters (< 100 mm) were be stocked into replicate 5-level, 21 mm monofilament lantern nets at commonly accepted commercial levels (1/3 surface area), and 10,000 bay scallops (< 50 mm) were be stocked into replicate lantern nets, at 20 per ft2. Half of the animals were deployed directly adjacent to the netpens and half of the animals were deployed on the Megansett Harbor growout site (Figure 1). Sugar kelp seed string was purchased from one of the locally available seed string suppliers (Greenwave, CT; Walrus and Carpenter, RI; Cottage City Oysters, MA; Springtide Seaweed ME) in December of 2019. Three, identical 20' lines of sugar kelp were installed adjacent to both the trout netpens, and three identical lines were also installed at the current Megansett Harbor oyster farm. The lines were installed starting at the northwest corner, leading from north to south, spaced 25' apart. The line was then sunk to 7' at all locations. 2) Data collected Total weight and total length measurements were sampled monthly from January through April of 2020 to evaluate growth. All net pens were inspected for holes and mortalities daily, and all mortalities were removed, tallied and disposed of. From January through April of 2020, thirty oysters and thirty bay scallops were sampled from three randomly selected bags or lantern nets monthly. For each organism during each sampling, percent survival and shell height were measured to investigate differences between sites. Sugar kelp lines were checked monthly and adjusted as necessary to remain at 7' depth. In addition to the monthly trout and oyster measurements, all kelp longlines were brought to the surface monthly from initial set (December, 2019) through final harvest (April, 2020) to check for biofouling. During the routine inspection for biofouling, once per month each line was sampled to quantify growth. Three locations were randomly chosen on each of the three lines, and 10 random plants within each 12" section will be measured for total length. When estimating the health of trout, Fulton's condition factor (K) was used (Froese, 2006; Shabani et al., 2018). Fulton's condition factor is a widely accepted metric for estimating the health of fish, such as rainbow trout, and can be an indicator of stress, reproductive status, nutrition and age (Sharma and Bhat, 2015; Dekic et al., 2016; Shabani et al., 2018). The equation used to calculate Fulton's condition factor (K) was: K = ((W)/(L*3))*100 (Froese, 2006; Tasaduq et al., 2011; Sharma and Bhat, 2015; Dekic et al., 2016). The use of Fulton's condition factor (K) allows for health comparisons to other studies involving rainbow trout culturing and health. Percent body weight increase was calculated using the equation: G = ((W2 - W1)/(0.5 x (W1 + W2) x t)) x 100 to allow for comparisons to other steelhead and rainbow trout growth rate studies (Holm et al., 1990; Myrick and Cech, 2005).

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