Aquaculture is the fastest growing source of animal protein for humans. However, as this industry continues to develop, several inherent challenges will arise. Foremost is the need for increased production of suitable and sustainable feeds. Aquaculture has long been criticized for ‘‘using fish protein to make fish protein’’ (Naylor et al., 2009). This ‘‘fishmeal trap’’ (New & Wijkström, 2002) caused the industry to prioritize improving feed conversion ratios and finding alternative protein sources (Naylor et al., 2009). While soy is the most common terrestrial plant protein used in fishmeal substitution to date, many environmental concerns surround the land-use and fertilizer run-off requirements associated with soy production. Additionally, palatability and anti-nutritional factors, as well as unintended biological consequences (e.g., gastroenteritis in salmon, Romarheim et al., 2011), limit the immediate and broad application of unmodified soy and other plant proteins.
Alternatively, single cell proteins (SCP), mainly yeast, algae, and bacteria, show much promise for aquaculture (Naylor et al., 2009). SCP has historical roots in Germany when, during the First World War, approximately 50% of imported protein was offset by yeast (Suman et al., 2015). Today, spent yeast cells from corn ethanol fermentation processes are commonly blended with dried distiller’s grains and solubles in terrestrial animal feeds (Kim & Dale, 2004). However, the high fiber content of this blend limits its use in aquaculture (Gatlin et al., 2007). Similarly, algae are grown commercially in ponds or bioreactors for use in food, cosmetics, oil and nutritional supplements. To date, the large scale application of algae as an alternative protein source is limited by high production costs and technical challenges (Spolaore et al., 2006).
Bacterial biomass, while currently the least developed SCP, has potentially great applicability as a protein replacement for aquaculture. Here we test the applicability of Methylobacterium extorquens, an abundant leaf symbiont that can grow rapidly and to high densities on the non-food, single-carbon (C1) feedstock methanol (Schrader et al., 2008). Given the large production levels of natural gas-derived methanol, this has driven a new wave of research into C1 biotechnology, much of which has been with M. extorquens (Ochsner et al., 2015). M. extorquens has attracted this attention as the premier model organism for growth on C1 compounds because of its relative metabolic versatility, the large suite of genetic tools developed for it, and the availability of full genome sequences for multiple strains (Vuilleumier et al., 2009; Marx et al., 2012). Being produced through a fermentation process, this SCP is immune to seasonality or other undue climate influences (e.g., extreme temperatures, droughts, floods). One particular endogenous trait that provides advantage is that M. extorquens contains a suite of naturally occurring anti-oxidant carotenoid compounds that have been associated with both imparting color and enhancing immunity (Osawa et al., 2015; Van Dien et al., 2003). Carotenoid compounds, such as astaxanthin and canthaxanthin, are commonly added to aquaculture feeds to provide aquacultured product with the color of wild counterparts (Tlusty & Hyland, 2005). Carotenoid compounds often represent one of the most expensive ingredients in feed. Also, some carotenoids are precursors of vitamin A and many have antioxidant properties important to immune systems. The principal method for the manufacturing of pigments to serve the aquaculture industry is often by chemical synthesis, which is restricted for use in certain jurisdictions (e.g., European Union). These natural traits of M. extorquens offer a uniquely powerful opportunity to rapidly advance and tailor SCP for specific nutritional benefits.
Before the full potential of SCP for aquaculture can be realized, a number of interdisciplinary first principles must be established (Engle, 2016; Rhodes, Johnson & Myers, 2016). These include demonstrating that diets containing SCP (1) are accepted by the species in question, (2) result in equivalent survival and growth as individuals raised with traditional feeds, (3) do not cause illness or other maladies, (4) result in an organoleptically suitable product, and (5) are cost effective to manufacture and feed.
Here, we describe the production and use of KnipBio Meal (KBM), a novel high-yielding platform biocatalyst using Methylobacterium extorquens, as an effective protein source for aquafeeds. We tested this SCP as a potential feed item in two species of commercial aquaculture value (Pacific white shrimp, Litopenaeus vannamei, and, Atlantic salmon, Salmo salar) and one of ornamental aquaculture value (smallmouth grunt, Haemulon chrysargyreum, Tlusty et al., 2017). Specifically, we conducted feeding trials using Pacific white shrimp and smallmouth grunt to determine the effect of KBM (up to 30% or 100% fishmeal inclusion rates, depending on species) on animal growth, health, and survival. Additionally, we conducted a trial using Atlantic salmon to determine the digestibility of the KBM compared to a commercially available reference diet. Together, these data represent the initial trials for the feasibility of KBM as a suitable SCP for use in aquafeeds.
Single cell protein biomass and feed pellet formulation
Methylobacterium extorquens (strain KB203) was produced via standard aerobic fermentation processes (BØlanger et al., 2004) and de-watered to form a flour referred to as KnipBio Meal (KBM). KB203 was incubated at 30 C at 200 RPM on CHOI4 liquid medium (Supplemental Table 1) with 0.5% methanol for 24 hr in 50 mL liquid medium (in a 250 mL baffled flask). To determine purity, the suspension was streaked onto tryptic soy agar and incubated at 30 C for 96 hr. Only colonies of a single morphology were considered pure and fit for further use in scale-up.
CHOI4-defined medium and trace metals stock solution recipes were used for growing M. extorquens to high cell densities. The trace metals solution was prepared separately as a concentrate and autoclaved for 30 min at 121 C. A 30 mL trace metals solution was added to the medium before sterilization. Although precipitation is often observed in these solutions, they have been used repeatedly with success for growing M. extorquens to high cell densities (BØlanger et al., 2004).
A 20 L fermenter (equipped with two Rushton-type impellers; Chemap, Uster, Switzerland) was used for growing the inoculum for the main fermenter. Two pH probes (Mettler, Toledo), two pO2probes (Ingold) and one methanol probe (volatile organic compound (VOC) probe; NRC, Montreal, Canada) were prepared and fit into the 20L fermenter before sterilization. Ten liters of CHOI4 medium was prepared and sterilized in the fermenter for 45 min. After cooling to room temperature, a two-point calibration was conducted on the methanol probe by aseptically adding two defined volumes of methanol to reach a final concentration of 0.18% in the fermenter (2 9 mL). Sterile ammonium hydroxide and methanol were connected to the fermenter to control pH (at 7.0) and methanol concentration. The pO2 and methanol probes were calibrated under standard minimal positive pressure (0.05 bar). Final fermentation occurred in a 1500 L fermenter (equipped with three Rushton-type impellers and a mechanical foam breaker; Chemap, Uster, Switzerland) with similar specifications to seed fermentation, prepared with two pH probes (Mettler Toledo, Columbus, OH, USA), two pO2 probes (Ingold and Hamilton, Reno, NV, USA) and two methanol probes (NRC, Montreal, Canada). The probes were prepared and fit into the fermenter before sterilization.
For bench top fermentations, biomass was collected through centrifugation (Beckman-Coulter, Indianapolis, IN, USA) and freeze dried for 48 hr at 80 C, and moisture content was verified to be below 10% (New Jersey Feed Labs, Ewing Township, NJ, USA). At larger scale, the biomass was harvested by cooling to 20 C and pressure was increased to 0.8 bar before feeding to the BTPX 205 disc stack centrifuge (Alfa-Laval, Lund, Sweden) at 100L/hr (discharged every 2 min). The slurry was sent directly into 50 L polypropylene carboys and stored at 4 C until further treatment. After approximately 24 hr, the slurry was spray dried at 182 C/70 C (inlet/outlet).
Experimental diets used for all animal trials were produced using commercial manufacturing methods. Specifically, for both Pacific white shrimp (Litopenaeus vannamei, Table 1) and Atlantic salmon (Salmo salar, Table 2) trials, ingredients were ground to a particle size of <200 mm using an air-swept pulverizer (Model 18H; Jacobsen, Minneapolis, MN, USA). The diets were processed using a twin-screw cooking extruder (DNDL-44, Buhler AG, Uzwil, Switzerland) with a 25 sec exposure to 127 C in the extruder barrel (average across five sections). Pellets were dried with a pulse bed drier (Buhler AG, Uzwil, Switzerland) for 20 min at 102 C with a 10 min cooling period, resulting in final moisture levels less than 10%. All oil was top-coated after the pellets were cooled using a vacuum-coater (AJ Mixing, Ontario, CA, USA). Yttrium oxide was added to the reference diet at 0.1% of dry weight to serve as an inert, indigestible marker and was diluted to 0.07% when the test ingredients were added. Diets were stored in polypropylene plastic bags at room temperature until fed. All diets were fed within four months of manufacture.
For smallmouth grunt (Haemulon chrysargyreum) trials (Table 3), all dry ingredients were mixed using a feed mixer (Model KSMS, Kitchen Aid Inc.; St. Joseph, Michigan, USA). Pollock liver oil and lecithin were added to the mixture followed by about 45% distilled water to aid the pelleting process via meat chopper (Royal, Tokyo, Japan, type 22VR-1500). After pelleting, all diets were dried at 70 C in a constant temperature oven (DK 400; Yamato Scientific Co., Ltd., Tokyo, Japan). The dried pellets were steamed at 100 C for 1 min in a cylindrical steamer to improve water stability. Pellets were stored in plastics bags at 30 C until used. All diets were fed within four months of manufacture.
The effect of KBM on growth, survival, and feed efficiency of the Pacific white shrimp
Hatchery-raised Pacific white shrimp (Litopenaeus vannamei) were acquired from SKY8 Shrimp Farm, LLC (Stoughton, MA, USA) and stocked at 60 shrimp/tank (shrimp average weight was 4.52 0.21 g (1.S.D.)) into twelve 110 L glass aquaria (0.228 m3) comprising a 1,675 L single clear water recirculating saltwater aquaculture system with mechanical and biological filtration. Experimental systems were maintained at 27.5 28.5 C, and 29.5 32.5 ppt salinity, and ammonia, nitrite, and nitrate were maintained at 0.25, 0.25, and 80.00 ppm, respectively. This density was greater for the initial stocking given that destructive sampling would take place. The final stocking density is on par with those practices by intensive land-based systems. Animal care and procedures used in this trial were approved by Roger Williams University Animal Care and Use Committee (IACUC protocol R-13-12-20).
To determine the effect of KBM on shrimp growth and survival, three diets of varying KBM inclusion were formulated (Table 1). Each of the 12 experimental tanks was randomly assigned one of the three diets, totaling four replicates per treatment. Each tank was fed to apparent satiation four times/day (800, 1100, 1400, 1600 hours). Uneaten food from the previous feed, as well as any excrement or molts, was manually siphoned from each tank prior to the next feeding. Water chemistry was tested and corrected daily throughout the duration of the experiment.
The gross wet weight (g) of all shrimp per tank was measured at days 0, 60, and 150. All shrimp were measured on day 0 (n D 60), and day 60 (n D 45 55, depending on survivorship). At day 60, 20 shrimp from each tank (n D 80 per treatment) were randomly selected and returned to their original tank (a density of 87 m 2) and maintained according to the above experimental design for an additional 90 days, as which point each individual was enumerated for wet weight (g) and carapace length (mm). The shrimp not selected for the second 90-day trial (n D 25 35, depending on tank) were euthanized, placed on ice, and wet weight (g), and carapace length (mm) were measured for each individual.
A blind taste test was conducted immediately following the conclusion of the second 90-day trial. After final data were collected, the shrimp were grouped by treatment, placed on ice, and transported to JR Bean Saloon in Bristol, RI, USA for preparation for human consumption. Shrimp were aggregated by treatment and were subsequently shelled, de-veined, boiled, and immediately served to 39 test participants. Diet treatment identity was concealed from test participants using colored plastic forks, one color per treatment. To randomize the order of shrimp consumption per participant, each fork was randomly labeled with a number (1, 2, or 3), indicating the order in which each participant should consume his/her shrimps. Upon completing the tasting, each participant ranked the three shrimp based on overall taste from 1 3 by placing the corresponding fork from each shrimp into one of three buckets. Participants were given the option to vote for a ‘‘tie’’, however, these votes only accounted for 5% of total votes, and were not included in the analysis.
The effect of KBM on smallmouth grunt growth, proximate composition, and gut microbiome
Hatchery-raised smallmouth grunts (Haemulon chrysargyreum; N D 120; 1.37 0.27 g wet wt) were stocked at 10 fish/tank into twelve 110 L glass aquaria (0.113 m3) comprising a 1,675 L recirculating saltwater aquaculture system with mechanical and biological filtration. Each of the 12 experimental tanks was randomly assigned one of four experimental diets, totaling three replicates per treatment (Table 2). Each tank was fed until apparent satiation four times/day (800, 1100, 1400, 1600 hours). Uneaten food from the previous feed, as well as any excrement, was manually siphoned from each tank prior to the next feeding. Water chemistry was tested and corrected daily throughout the duration of the experiment. Experimental systems were maintained at 27.5 28.7 C, 31.0 33.8 ppt salinity. Ammonia, nitrite, and nitrate were maintained at 0.25, 0.25, and 80.00 ppm, respectively. Animal care and procedures used in this trial were approved by Roger Williams University Animal Care and Use Committee (IACUC protocol R-13-12-20).
Wet weight (g) and standard length (mm) was determined for each fish on day 0 and 41 (N D 120 and 112, respectively). Fish were individually collected using a dip net and blotted dry with a towel prior to measurements. Wet weight was measured by placing each fish on the center of a digital balance, and standard length per fish was measured from photographs of each individual using ImageJ digital imaging software (Schneider, Rasband & Eliceiri, 2012). Specific growth rate (SGR as g 1) was calculated as ((lnWf lnWi 100)=t ) where lnWf D the natural logarithm of the final weight, lnWi D the natural logarithm of the initial weight, and t D time (days) between the two measures.
On day 41, three fish were randomly selected from each treatment (N D 12 total), freeze-dried for 48 hr, homogenized using a mortar and pestle, and stored in borosilicate vials. Processed samples were then shipped to the New Jersey Feed Laboratory for whole body proximate, amino acid, and fatty acid analyses (% composition).
The foregut of three additional fish from each treatment (N D 12 total) was removed via dissection and immediately frozen on dry ice for gut microbial DNA analysis. DNA was extracted from the entire foregut of each animal using MoBio PowerSoil R DNA Isolation Kits (Carlsbad, CA, USA). DNA was amplified using nested PCR, with initial amplification using primers 27F and 1525R that targeted the V1 V6 section of the 16S rRNA gene (Coates et al., 1999). A second amplification using uniquely barcoded primers 515F and 808R (Caporaso et al., 2012) were used to generate final amplicons for sequencing. The amplicons were gel purified using the Qiagen QIAquick R Gel Extraction Kit following the manufacturer’s instructions (Valencia, CA, USA), and then were sequenced using an Illumina MiSeq high throughput DNA sequencer. The resulting sequences were quality filtered and analyzed in QIIME using default parameters (Caporaso et al., 2010).
Digestibility of KBM using Atlantic salmon
Atlantic salmon (Salmo salar; N D 96; 635 97 g wet wt) were stocked at 16 fish/tank into six 417 L fiberglass tanks (0.265 m3) comprising a 7,500 L flow-through recirculating system with a drum filter, bio-filter, and 1200 L sump. Brackish well water ( 2 ppt salinity) was supplied to the system (19 L min 1) and water quality was monitored weekly to ensure that a healthy environment was maintained during the trial. Dissolved oxygen (90 125%) and temperature (11.5 12.2 C) were monitored daily. Animal care and procedures used in this trial were approved per USDA-ARS Animal Care and Use Committee (IACUC FY2014-001).
To determine the digestibility of KBM, a reference diet was formulated and then KBM was added in a standard 70%/30% (Table 3). Each of the six experimental tanks was randomly assigned to one experimental treatment, totaling three replicates per treatment. All tanks were fed the control diet (C; Table 3) for 7-days prior to initiating the experimental treatments. The basal diet contained 40% protein and 25% lipid with an estimated digestible energy of 19.6 kJ g 1. Fish were fed three times/day; at 800 and 1200 hours using automatic feeders (Arvo-Tec Oy, Huutokoski, Finland) and at 1600 hours by hand to apparent satiation. The feeding software was developed from experimental growth models validated from commercial data and different genetic stocks (From & Rasmussen, 1984; Ruohonen & Mäkinen, 1992; Ursin, 1967).
Fecal material was collected from each tank 18 hr post feeding on day 2 and day 4 by manual stripping (Austreng, 1978; Hajen et al., 1993). All fish in each tank were sedated with tricaine methylsulfonate (MS 222, 0.1 g L 1) and physically restrained. Pressure was applied to the abdomen to initiate defecation into clean stainless steel pans. Fish were returned to their respective tanks and allowed to recover from handling. Fecal samples collected from all fish (N D 6) in each tank were pooled as one composite sample/tank, averaging 5 g of dried feces. The fecal material was dried at 60 C for 24 hr, placed into plastic bags and stored at 20 C until analysis.
The methods of Cho, Slinger & Bayley (1982); Cho, Slinger & Bayley (1982)) and Bureau, Harris & Cho (1999) were used to estimate apparent digestibility coefficients. Yttrium oxide served as the inert maker.
The diets and fecal material were analyzed for organic matter by drying the samples at 120 C for 2 hr and ashing the dried samples at 550 C for 3 hr (AOAC, 1990). Organic matter was calculated as 100 minus ash content. The diets and fecal material were analyzed for lipid content by ether extraction using an Ankom lipid extraction instrument (XT-10; Ankom Technologies, Macedon, NY, USA). Crude protein was determined by the Dumas method (Ebeling, 1968) using a Leco Nitrogen Determinator (FP 528; Leco Corporation, St. Joseph, MI, USA). Energy was determined by using a Parr Instruments calorimeter (Model 1281; Moline, IL, USA). Yttrium oxide determination was by inductively coupled plasma atomic emission spectroscopy (University of Idaho Analytical Laboratory, Moscow, ID, USA). Amino acid analysis was performed using a Beckman 7300 Amino Acid Analyzer (University of Missouri Analytical Lab, Columbia, MO, USA).
Apparent digestibility coefficients of each nutrient in the experimental diets were calculated according to the following equations (Kleiber, 1961; Forster, 1999):
ADCNdiet D 100 100f%Yd X Nfg=f%Yf in feces X Ndg
ADCNingredient D f(a Cb)X ADCNt (a X ADCNr)gb 1
where, ADCN D apparent digestibility coefficient of nutrient; Yd D % Yttrium oxide in diet; Nf D % nutrient in feces; Yf D % Yttrium oxide in feces; Nd D % nutrient in diet; p D proportion of test ingredient in the test diet; a D (1 p) nutrient content of the reference diet; b D p nutrient content of the test ingredient; t D apparent digestibility coefficients of the nutrient in the test diets; r D apparent digestibility coefficients of the nutrient in the reference diet.
Statistical analyses were conducted using JMP 8.0, SAS, Inc. (Cary, NC, USA). The effect of experimental diets on shrimp growth rate and feed conversion ratio, and the effect of experimental diets on animal growth rate, was assessed using a one-factor analytical design. Normal data (indicated by a Jarque-Barre (JB) test for normality; Zaiontz, 2015) were tested with a one-way analysis of variance (ANOVA). If the JB test indicated non-normal data, the analyses were conducted nonparametrically using a Kruskal-Wallis test. Post-hoc comparisons of normal data were made and post hoc comparisons of orthogonal contrasts from ANOVA tests were examined using the Real Statistics Resource Pack software (Release 4.9, Zaiontz, 2015). The effect of experimental diet on shrimp taste was determined using a two-factor (treatment and order of preference) chi-square goodness-of-fit test. The effect of experimental diets on grunt microbiome was determined using adonis, a permutational multivariate analysis of variance, (PERMANOVA) implemented in R, and the similarities among treatments were calculated using the Bray-Curtis similarity metric and were visualized using a principal coordinates analysis in QIIME (Caporaso et al., 2012). The significance level for all analyses was set at P 0:05. All values are presented as mean standard error.
Pacific white shrimp
Diet had no effect on shrimp survival (one-way ANOVA, F2;9 D 2:4, p > 0:1, combined average D 84:7 5:6%); however, diet did influence shrimp growth (one-way ANOVA, % weight gain, F2;9 D 5:4, p < 0:05; SGR, F2;9 D 8:6 g d 1, p < 0:01). Shrimp fed diet with 100% FM replacement (SHR-KH) grew less than those fed the control diet (SHR-C), and shrimp fed diet with 50% FM replacement (SHR-KL) showed growth intermediate to, and not statistically different from either SHR-C or SHR-KH (Table 4). Diet influenced shrimp feed efficiency (one-way ANOVA, F2;9 D 5:27, p < 0:05, Table 4). The food conversion ratio (FCR) of shrimp fed diets containing KBM (SHR-KL and SHR-KH) were not statistically different than those fed the control diet (SHR-C, 1:70 0:12, orthogonal contrast, Q Test D 0:99, p > 0:7). The shrimp fed the SHR-KH had a statistically greater FCR than those fed SHR-KL (orthogonal contrast, Q Test D 4:48, p < 0:05).
In the consumer taste trial, diet did influence shrimp preference (df D 4, 2 D 9:8, p < 0:05). This was largely because shrimp fed diet SHR-C received more votes as ‘‘most preferred’’ (50% of all first place votes). The shrimp fed diets SHR-KL and SHR-KH each received 25% of the ‘‘most preferred’’ votes. However, there was no diet difference in the shrimp that was voted ‘‘least favorite’’; each diet received 1/3 of the last place votes.
Diet had no effect on grunt mortality, length, weight, condition factor, or specific growth rate (SGR) (for all variables, one-way ANOVA F3;8 > 2:85). Only 12 of the 120 grunts died during the experiment, and no more than one fish was lost per tank. For all fish, the average weight increase was 353:2 45:9%, length increase was 48:4 6:2%, condition factor was 2:3 0:2, and SGR was 3:8 0:3 g d 1. Average feed conversion ratio (FCR) per treatment ranged from 1.09 1.24. Diet did affect fish proximate composition (one-way ANOVA F3;8 D 4:3, p < 0:05), where fish fed the control diet (GRU-C1) had the greatest protein content (dry matter, 56:3 1:9%), while those fed diet with 50% FM replacement (GRU-KH) had the lowest (52:93 1:2), while the control diet with pigment (GRU-C2) and the diet with 10% FM replacement (GRU-KL) were intermediate and not statistically different from the extremes (R30: 53:6 1:0%; CC: 53:76 1:1%. The percent fat on a dry matter basis, while not significant, exhibited the opposite trend to protein with the fish fed GRU-C having 22:9 2:2% fat, while those fed diet GRU-KL had 27:3 1:3% fat.
Diet did not significantly affect grunt gut microbial community (adonis, p > 0.05). Regardless of diet, ∼60% of the fish gut microbiome was composed of three types of bacteria: Halomonas, Oxalobacteracaea, and Shewanella. The composition of the remaining microbial community varied among individuals, but differences in the total number of operational taxonomic units among treatments was not statistically significant (Fig. 1), and there was no clear treatment grouping on the principal coordinates analysis.
For salmon, KBM inclusion had no measurable effect on the Apparent Digestibility Coefficient (ADC) value. The ADC for protein was slightly greater for the animals fed the control diet compared to the 30% inclusion KBM diet (67.8±2.8 and 63.0±3.1 (averages ±1 S.D.) respectively). Diet did have a positive although insignificant influence amino acid digestibility, as the KBM diet (SAL-K) resulted in better digestibility for seven of the eight essential amino acids and six of the 11 non-essential amino acids (Table 5) than the control (SAL-C) diet (for all amino acids, binomial probability, Π = 0.5p < 0.08).
Ultimately, innovative sources of protein are required to meet the feed needs of aquaculture (Naylor et al., 2009) if aquaculture will meet its projected doubling by 2030 (Kobayashi et al., 2015). The production of single cell proteins (SCP) is one potential high quality protein alternative to fishmeal, and has the potential to stabilize the rising aquafeed input costs and address the over-harvesting of pelagic fisheries for use in fishmeal. This will ultimately lead to a more resilient and sustainable global food supply.
Here we demonstrated the broad applicability of KnipBio Meal, made from Methylobacterium extorquens, as a viable protein source for use in aquafeeds. When fed to fishes it resulted in equivalent performance in growth for grunts, and ADC for salmon as trials using traditionally formulated diets containing fishmeal. The salmon demonstrated higher digestibility for amino acids in the KBM diets. The FCR of shrimp was best when there was 50% substitution with KBM, yet growth (weight gain and SGR) was greatest in the control diets. Overall, this suite of results is encouraging given that there was no engineering, selection, or tuning of the bacteria to be more suitable as an aquaculture feed or to achieve advanced feed formulation considerations. These results also suggest that KBM contains no anti-nutritional properties, a common hurdle to overcome in the adoption of plant-derived alternate feed ingredients (Francis, Makkar & Becker, 2001; Refstie et al., 2005). The anti-nutritional properties may be a reason that prior studies on plant-based feed substitution have reported changes in the intestinal microbiome, with associated decreased health outcomes (Desai et al., 2012; Green, Smullen & Barnes, 2013; Ingerslev et al., 2014; Rhodes, Johnson & Myers, 2016). This diet-based gut microbiome modulation (Estruch et al., 2015) can help indicate inadequate diets. Thus, our observed lack of treatment related difference in the gut microbiome of the smallmouth grunts in this study should be considered significant in that it suggests M. extorquens is of sufficient quality in this early stage testing to garner support as a SCP feed additive.
Diet apparent digestibility coefficient (ADC) values for protein were slightly lower for the KBM diet compared to fishmeal (73.2%–69.1%), a result consistent with prior findings (Skrede et al., 1998; Storebakken et al., 2004). Amino acids can drive ADC values, and the relative proportion of lysine, methionine and histidine could influence the greater ADC in the fishmeal.
While the initial tests with KBM in aquaculture feed are promising, further development is still required, particularly in two areas. First, a diet treatment difference was observed that resulted in a minor difference in shrimp taste. Often, studies involving protein substitution in aquaculture will result in a less palatable product (De Francesco et al., 2004). Within this study, while the shrimp fed the control diets were the most preferred, it is noted that all treatments were represented equally within the third-ranked (least-preferred) category. Thus, none of the treatments had an unpalatable flavor or texture, and, in the words of Tamar Haspel, writer for The Plate, the shrimp fed the KBM diets ‘‘tasted like shrimp’’ (Haspel, 2015). A second issue associated with sub-scale pellet manufacturing was the inclusion of air bubbles in the shrimp diet SHR-KH (100% KBM replacement) that did not sink as well as the other two diets (SHR-LK and SHR-C). While all pellets were consumed by shrimps, those fed SHR-HK did need to swim in the water column to retrieve some of the pellets, while those fed SHR-LK and SHR-C mostly fed off the tank floor. Additionally, diet SHR-KH seemed to be less palatable as the shrimps had a lower feed efficiency of this than the other diets. Whether this is an absence of an attractant not replaced in SHR-KH or the absence of a critical nutritional component like methionine (DA Davis, pers. comm., 2015) in the diet, the exact cause is unknown at this time. While minor adjustments to the diet formulation will be necessary, they likely will not be onerous, and this work gives promise for M. extorquens as a SCP in aquafeeds.
In early stage technology development, sub-optimal bioprocessing volumes, feed pellet manufacturing and other related operation scales can magnify negative results. As such, the cost effectiveness of KBM production has not yet been validated and was beyond the scope of this study. However, one immense potential efficiency advantage of SCP as a protein source is to small amount of space required for production. An estimated 40.5 ha SCP facility can match the protein production of a 4047 ha soy operation, dramatically reducing the environmental footprint of production. The ability to make a fishmeal alternative, combined with vital ingredients like anti-oxidant carotenoids, both simplifies and diversifies the raw ingredients available to feed manufacturers while avoiding the exploitation of marine resources. Continued work to scale up KBM and other SCP solutions is required to create a cost effective near-term solution for alternate protein sources for aquafeeds. Based on this research, we believe KBM can be used as a dietary component, and upon further investigation, could serve as a complete fishmeal substitution for aquafeeds without compromising feed performance. The use of this SCP will ensure future food security by creating novel resources to grow larger volumes of aquatic protein that does not complete with humans and terrestrial livestock for limited resources.
We thank D Cerino, A Davis, T Baskin, F Greco, L Hardy, M Levi, L Riley, A Campbell, and T Gerson for assistance with shrimp and grunt husbandry and data collection. We also thank S Feinman, P Kearns, R Cost and J Falcone of the University of Massachusetts at Boston for the microbiome work, and P Swanson for preparing inoculum for the early studies. Funding for the microbiome work was provided in part by the Civic Engagement Scholars Initiative at the University of Massachusetts at Boston. R Barrows and DA Davis assisted with shrimp diet formulation, and W Watanabe and S Alam from UNCW assisted with grunt diet formulation. B Wolters conducted the technical work for the salmon digestibility trials. C Rosas and one anonymous reviewer provided comments on a draft manuscript. Finally, thanks to Chef R Ross and JR Bean Saloon for preparing the shrimp and hosting the taste test.
This article was originally published in PeerJ 5:e3170; DOI 10.7717/peerj.3170. This is an Open Access article distributed under Creative Commons Public Domain Dedication.