Introduction
⌅It is expected that aquaculture will supply the future demand for aquatic foodstuffs due to the combination of a stagnated capture fisheries production and an increase in human consumption as a result of increases in both global population and per capita aquatic food products consumption (FAO, 2022FAO, 2022. The State of World Fisheries and Aquaculture2022. Food and Agriculture Organization of the United Nations, Rome. 236 pp.). Moreover, it has been emphasized that to provide for this through conventional semi-intensive and intensive systems, such as those employing earthen ponds and water renewal, could create conflicts with other uses of land and water resources, particularly in the coast where human population is concentrated (Avnimelech, 2008Avnimelech Y, Verdegem M, Kurup M, Keshavanath P, 2008. Sustainable land-based aquaculture: rational utilization of water, land and feed resources. Med Aquacult J1: 45-54. 10.21608/maj.2008.2663), in addition to coastal aquaculture already being heavily criticized by environmental movements due to the destruction of mangroves (Lacerda et al., 2021Lacerda LD, Ward RD, Godoy MDP, de Andrade Meireles AJ, Borges R, Ferreira AC, 2021. 20-Years cumulative impact from shrimp farming on mangroves of northeast Brazil. Front For Glob Change4: 653096. 10.3389/ffgc.2021.653096).
In this regard, super-intensive closed systems can be an alternative to increase aquaculture production with greater efficiency in the use of water and land, through techniques such as biofloc technology and recirculating aquaculture systems (Sun et al., 2023Sun Y, Hou H, Dong D, Zhang J, Yang X, Li X, et al., 2023. Comparative life cycle assessment of whiteleg shrimp (Penaeus vannamei) cultured in recirculating aquaculture systems (RAS), biofloc technology (BFT) and higher-place ponds (HPP) farming systems in China. Aquaculture574: 739625. 10.1016/j.aquaculture.2023.739625). Biofloc technology (BFT), in particular, has been studied extensively for the culture of whiteleg shrimp [Penaeus (Litopenaeus) vannamei] (Samocha, 2019Samocha TM, 2019. Sustainable biofloc systems for marine shrimp. Academic Press: Elsevier, London; San Diego, CA. 431 pp.10.1016/B978-0-12-818040-2.00003-4; Emerenciano et al., 2022Emerenciano MGC, Rombenso AN, Vieira FN, Martins MA, Coman GJ, Truong HH, et al., 2022. Intensification of penaeid shrimp culture: An applied review of advances in production systems, nutrition and breeding. Animals12: 236. 10.3390/ani12030236; Khanjani et al., 2023Khanjani MH, Mozanzadeh MT, Sharifinia M, Emerenciano MGC, 2023. Broodstock and seed production in biofloc technology (BFT): an updated review focused on fish and penaeid shrimp. Aquaculture, 740278. 10.1016/j.aquaculture.2023.740278), the most produced crustacean worldwide (FAO, 2022FAO, 2022. The State of World Fisheries and Aquaculture2022. Food and Agriculture Organization of the United Nations, Rome. 236 pp.). However, a problem faced in aquatic animal production ‒ particularly in more intensive systems in comparison with extensive ones that rely on natural productivity ‒ is the fact that cultured animals assimilate a low percentage of the feed nutrients provided to them, about 39.1% of nitrogen and 35.0% of phosphorus in the case of marine shrimp (Silva et al., 2013Silva KR, Wasielesky Jr W, Abreu PC, 2013. Nitrogen and phosphorus dynamics in the biofloc production of the pacific white shrimp, Litopenaeus vannamei. J World Aquacult Soc44: 30-41. 10.1111/jwas.12009), with the rest being converted into wastes that can damage both the cultured animals and the environment. The integration of additional species with different feeding habits to a main fed species receives the name of integrated multitrophic aquaculture (IMTA) and can help alleviate this problem (Khanjani et al., 2022Khanjani MH, Zahedi S, Mohammadi A, 2022. Integrated multitrophic aquaculture (IMTA) as an environmentally friendly system for sustainable aquaculture: functionality, species, and application of biofloc technology (BFT). Environ Sci Pollut Res29: 67513-67531. 10.1007/s11356-022-22371-8). In this strategy, organic extractive (e.g. bivalves and fish) and inorganic extractive (e.g. macroalgae and terrestrial plants) use the wasted nutrients from the main species to grow, allowing for a greater and diversified overall production (Chopin et al., 2008Chopin T, Robinson SMC, Troell M, Neori A, Buschmann AH, Fang J, 2008. Multitrophic integration for sustainable marine aquaculture. In: Encyclopedia of Ecology. Elsevier, pp. 2463-2475. 10.1016/B978-008045405-4.00065-3).
The application of integrated cultures to shrimp rearing using BFT has been evaluated with different species, e.g. Nile tilapia (Oreochromis niloticus) and lebranche mullet (Mugil liza) (Poli et al., 2019Poli MA, Legarda EC, de Lorenzo MA, Martins MA, do Nascimento Vieira F, 2019. Pacific white shrimp and Nile tilapia integrated in a biofloc system under different fish-stocking densities. Aquaculture498: 83-89. 10.1016/j.aquaculture.2018.08.045; Legarda et al., 2021Legarda EC, da Silva D, Miranda CS, Pereira PKM, Martins MA, Machado C, et al., 2021. Sea lettuce integrated with Pacific white shrimp and mullet cultivation in biofloc impact system performance and the sea lettuce nutritional composition. Aquaculture534: 736265. 10.1016/j.aquaculture.2020.736265), and different system configurations, e.g. both species in the same tank or in separate ones (Holanda et al., 2020Holanda M, Santana G, Furtado P, Rodrigues RV, Cerqueira VR, Sampaio LA, et al., 2020. Evidence of total suspended solids control by Mugil liza reared in an integrated system with pacific white shrimp Litopenaeus vannamei using biofloc technology. Aquacult Rep18: 100479. 10.1016/j.aqrep.2020.100479, 2022Holanda M, Wasielesky W, de Lara GR, Poersch LH, 2022. Production of marine shrimp integrated with tilapia at high densities and in a biofloc system: Choosing the best spatial configuration. Fishes7: 283. 10.3390/fishes7050283). One aspect of such system relates to how the secondary species, whose aim is to consume the wastes of the primary one, is to be fed. In fish monoculture, different feeding strategies, such as underfeeding, have been employed as a means to optimize feed use as regards it effects on animal growth performance and waste production (Ali et al., 2010Ali M, Hayward RS, Bajer PG, Whitledge GW, 2010. Maintenance/submaximum feeding schedules for reducing solid wastes and improving feed conversion in aquaculture. J World Aquacult Soc41: 319-331. 10.1111/j.1749-7345.2010.00374.x; Cavalcante et al., 2017Cavalcante DDH, Lima FRS, Rebouças VT, Sá MVC, 2017. Nile tilapia culture under feeding restriction in bioflocs and bioflocs plus periphyton tanks. Acta Sci Anim Sci39: 223-228. 10.4025/actascianimsci.v39i3.33574). In integrated cultures, considering that the role of the added species is to take advantage of the greatest amount of waste as possible, rates of supplementary feeding can affect the performance of the fish and, consequentially the overall system performance (Silva et al., 2022Silva VF, Pereira PKM, Martins MA, Lorenzo MA, Cella H, Lopes RG, et al., 2022. Effects of microalgae addition and fish feed supplementation in the integrated rearing of Pacific white shrimp and Nile tilapia using biofloc technology. Animals12: 1527. 10.3390/ani12121527). For instance, when Nile tilapia was integrated to whiteleg shrimp culture using biofloc technology, the use of supplementary feeding for the fish allowed for higher fish and system yields without affecting water microbiology and sludge production (Silva et al., 2022Silva VF, Pereira PKM, Martins MA, Lorenzo MA, Cella H, Lopes RG, et al., 2022. Effects of microalgae addition and fish feed supplementation in the integrated rearing of Pacific white shrimp and Nile tilapia using biofloc technology. Animals12: 1527. 10.3390/ani12121527), whereas, to the best of our knowledge, such evaluation of feeding rates when mullet was integrated has not been published so far. Therefore, the aim of this study was to evaluate the effects of different fish feeding rate levels when lebranche mullet was cultured in integration with whiteleg shrimp in biofloc technology as regards animal and overall system productive performance, water quality and water microbiology.
Material and methods
⌅The experimental work lasted 46 days and was carried out at the Marine Shrimp Laboratory, of the Federal University of Santa Catarina (UFSC), located in Barra da Lagoa, in Florianópolis, Santa Catarina. This study was approved by the Ethics Committee on the Use of Animals of UFSC, through the protocol number 5718250220.
Biological material
⌅Shrimp (Penaeus vannamei) post-larvae, acquired from the commercial laboratory AQUATEC Ltda., located in Rio Grande do Norte, were used. The shrimp were kept in a biofloc system in the Marine Shrimp Laboratory until the beginning of the experiment.
Fish of the species Mugil liza, from the Marine Fish Farming Laboratory of UFSC, located in Barra da Lagoa, in Florianópolis, Santa Catarina, were used. The fish were kept in a biofloc system in the Marine Shrimp Laboratory and, for the initial stocking in the experimental units, a pre-selection of fish size was made.
Experimental design and system management
⌅Four experimental groups consisting of different fish feeding rates were evaluated with four replicates in a completely randomized design: 0%, 1%, 2% and 3% of fish biomass. The shrimp feeding was unchanged in between treatments.
The experimental units were composed of a tank with a useful volume of 800 L, in which the shrimps were stocked, connected by recirculation to a tank with a useful volume of 90 L, used for the stocking of the mullets (Fig. 1). The water was pumped from the shrimp tank to the fish tank by a Sarlo-Better 650 L hour-1 pump, returning to the shrimp tank by gravity, keeping the system in recirculation 24 hours a day. Each 800 L tank was equipped with a central aeration ring, while the 90 L tanks each contained four porous stones connected to an aeration system, in order to keep dissolved oxygen levels within the appropriate range for the species and prevent sedimentation of solids in the tanks. The tanks were located in a greenhouse with natural photoperiod.
Shrimp (2.36 ± 0.02 g) were stocked under a density of 375 animals m-3 (300 animals tank-1), whereas fish (7.06 ± 0.65 g) were stocked under a density of 167 animals m-3 (15 animals tank-1).
In each experimental unit, 800 L of mature biofloc water (0.47 mg L-1 TAN, 0.16 mg L-1 N-NO2-, alkalinity 226 mg CaCO3 L-1, 9.44 mg L-1 N-NO3-, 9.6 mg L-1 P-PO43-) from a shrimp culture of the Marine Shrimp Laboratory, and 90 L of seawater, pumped from Barra da Lagoa beach, totalling 89.89% of inoculum in each experimental unit. In addition, the 800 L tanks were equipped with four artificial substrates composed of Needlona®, oriented vertically, corresponding to 80% of the tank surface area. To maintain the adequate water temperature for the culture of both species, each experimental unit was equipped with an 800 W titanium heater, located in the shrimp tanks.
The shrimp were fed four times a day (8:30 a.m., 11:30 a.m., 2:00 p.m. and 5:30 p.m.), initially with the Guabitech feed (1 mm), with 45% crude protein, until the morning of the seventh day of experiment, when they started to be fed with the Guabi Poti Guaçu feed (1.6 mm), which contains 35% crude protein. In treatments 1%, 2% and 3%, the mullets were fed twice a day (11:30 a.m. and 4:00 p.m.) with Nutripiscis starter 0.8 mm, which contains 40% crude protein. In these treatments, 1, 2 and 3% of the fish biomass of feed were offered. Fish from treatment 0% were not fed. The adjustment of the amount of shrimp feed was made according to the feeding table developed by Van Wyk (1999Van Wyk P, 1999. Nutrition and feeding of Litopenaeus vannamei in intensive culture systems. In: Farming marine shrimp in recirculating freshwater systems; Van Wyk P et al. (Eds.). Department of Agriculture and Consumer Services, Tallahassee, pp. 125-139.) through weekly biometrics, and fortnightly for fish.
Alkalinity was corrected with calcium hydroxide when the measured values were below 120 mg L-1 (Furtado et al., 2011Furtado PS,Poersch LH, Wasielesky W, 2011. Effect of calcium hydroxide, carbonate and sodium bicarbonate on water quality and zootechnical performance of shrimp Litopenaeus vannamei reared in bio-flocs technology (BFT) systems. Aquaculture321: 130-135. 10.1016/j.aquaculture.2011.08.034). The amount of calcium hydroxide was calculated using 5 to 20% of the amount of feed supplied to the experimental unit on the previous day.
Water quality
⌅Temperature and dissolved oxygen were measured twice a day (morning and afternoon), with a YSI pro20 oximeter both in the shrimp tanks as well as in the fish tanks, while the remaining variables were measured in the shrimp tanks only. Twice a week, pH was measured with a Thermo Scientific Orion Star A211 pHmeter. Salinity was measured twice a week with the Ecosense EC300A digital conductivity meter. Alkalinity was measured twice a week using the titrimetric method. Total ammonia nitrogen (Grasshoff et al., 1983Grasshoff K, Ehrhardt M, Kremling K, 1983. Methods of seawater analysis, 2nd Ed. Verlag Chemie Weinhein, New York.) and nitrite-N (Strickland & Parsons, 1972Strickland JDH, Parsons TR, 1972. A practical handbook of seawater analysis, 2nd ed. Fisheries Research Board of Canada, Ottawa.) were measured twice a week. Nitrate-N was measured at the beginning, middle and end of the experiment, according to the method of Strickland & Parsons (1972Strickland JDH, Parsons TR, 1972. A practical handbook of seawater analysis, 2nd ed. Fisheries Research Board of Canada, Ottawa.). Total suspended solids (TSS) were measured twice a week (APHA et al., 2005APHA (American Public Health Association), Water Works Association, Water Environment Federation, 2005. Standard methods for the examination of water and wastewater, 21 ed. American Public Health Association, Washington, DC.).
Dissolved oxygen (shrimp tank: 5.34±0.47 mg L-1; fish tank: 5.05±0.60 mg L-1), temperature (shrimp tank: 29.5±1.3°C; fish tank: 29.6±1.4°C) and salinity (33.9±1.4 gL-1) remained within ranges commonly used to successfully rear whiteleg shrimp (Van Wyk & Scarpa, 1999Van Wyk P, Scarpa J, 1999. Water quality management. In: Farming marine shrimp in recirculating freshwater systems; Van Wyk P et al. (Eds.). Department of Agriculture and Consumer Services, Tallahassee, pp. 141-161.) and Mugil spp. (Legarda et al., 2019Legarda EC, Poli MA, Martins MA, Pereira SA, Martins ML, Machado C, et al., 2019. Integrated recirculating aquaculture system for mullet and shrimp using biofloc technology. Aquaculture512: 734308. 10.1016/j.aquaculture.2019.734308, 2021Legarda EC, da Silva D, Miranda CS, Pereira PKM, Martins MA, Machado C, et al., 2021. Sea lettuce integrated with Pacific white shrimp and mullet cultivation in biofloc impact system performance and the sea lettuce nutritional composition. Aquaculture534: 736265. 10.1016/j.aquaculture.2020.736265).
Productive performance
⌅At the end of the experiment, the final population of shrimps and mullets was counted and weighted. The following variables were calculated with the resulting values:
where s denotes variables used in the case of shrimp, f those in the case of fish and i those in the case of the integrated system as a whole. Wi and Wf denote the initial and final individual weights, respectively.
Water microbiology
⌅For the quantification of total heterotrophic bacteria and Vibrio spp., 10-mL water samples from each tank were collected at the beginning and end of the experiment using sterile assay tubes with screw caps. A serial dilution using 1-mL samples was performed using tubes filled with 9 mL of sterile saline solution (3% NaCl), after which 100 µL aliquots of the homogenized contents were seeded in Petri dishes containing trypticase soy agar (TSA) and thiosulfate-citrate-bile salts-sucrose agar (TCBS) for viable heterotrophic bacteria and Vibrio spp., respectively. The seeded Petri dishes were incubated in a bacteriological stove at 30oC for 24 h and the colonies counted through colony forming units (CFU mL-1) plate counting.
Statistical analysis
⌅Data on water quality and zootechnical performance of organisms were tested for homoscedasticity and normality through Levene and Shapiro-Wilk tests, respectively, for subsequent application of ANOVA. When significant differences were found, the Tukey test was used to compare the means between treatments. When the data did not meet the assumptions for application of ANOVA, the Kruskal-Wallis nonparametric test was used. Linear regressions were also performed on the productive performance variables. The analyses were carried out with the software Statistica (TIBCO) and jamovi (The jamovi project, 2022The jamovi project, 2022. jamovi. (version 2.3) [Computer Software]. https://www.jamovi.org) at a significance level of 5%.
Results
⌅Water quality
⌅Water quality variables are presented in Table 1, with no significant differences found between the experimental groups (p>0.05). The treatments had pH values ranging from 7.3 to 8.5, with a mean value higher than 7.9 in all treatments. Mean total ammonia nitrogen values remained below 0.1 mg L-1, and mean nitrite-N values below 1 mg L-1. Alkalinity remained around 150 mg CaCO3 L-1 (92‒200 mg CaCO3 L-1) in all treatments. The mean values of total suspended solids remained between 500 mg L-1 and 600 mg L-1 in all treatments. The mean nitrate-N values remained between 16 mg L-1 and 20 mg L-1, increasing from an overall mean of 11.61 ± 3.22 mg L-1 at the beginning to 23.34 ± 4.33 mg L-1 at the end of the experiment.
| Variable1 | Fish feeding rate | p-value2 | |||
|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | ||
| pH | 7.98 ± 0.34 | 7.92 ± 0.35 | 7.92 ± 0.34 | 7.94 ± 0.36 | 0.775 |
| TAN (mg L-1) | 0.07 ± 0.10 | 0.05 ± 0.07 | 0.07 ± 0.10 | 0.04 ± 0.06 | 0.174 |
| Nitrite-N (mg L-1) | 0.73 ± 0.73 | 0.88 ± 1.00 | 0.75 ± 0.80 | 0.81 ± 0.77 | 0.743 |
| Nitrate-N (mg L-1) | 18.18 ± 6.21 | 19.21 ± 5.77 | 16.74 ± 6.66 | 18.34 ± 5.38 | 0.793 |
| Alkalinity (mg CaCO3L-1) | 149.25 ± 17.88 | 147.64 ± 17.75 | 150.68 ± 19.28 | 142.57 ± 19.79 | 0.114 |
| TSS (mg L-1) | 521.98 ± 171.05 | 561.95 ± 188.73 | 575.98 ± 189.49 | 552.91 ± 162.70 | 0.487 |
Productive performance
⌅Table 2 shows the productive performance of both species and the system as a whole. For the shrimp performance, no significant differences between treatments were found (p>0.05). The mean final weight of the shrimp was above 12.0 g. The final shrimp biomass presented mean values above 3.0 kg. Shrimp grew an average of around 1.5 g per week in all treatments. Mean daily growth coefficient values around 2.1 % day-1 were observed in all cases. The feed conversion ratio had a mean value close to 1.6. All treatments showed mean survival above 82% and mean yield around 3.9 kg m-3.
| Variable | Fish feeding rate1 | p-value2 | |||
|---|---|---|---|---|---|
| 0% | 1% | 2% | 3% | ||
| Shrimp | |||||
| Final mean weight (g) | 12.63 ± 0.07 | 12.70 ± 0.49 | 12.48 ± 0.37 | 12.27 ± 0.50 | 0.472 |
| Final biomass (kg) | 3.14 ± 0.07 | 3.12 ± 0.08 | 3.15 ± 0.09 | 3.08 ± 0.12 | 0.710 |
| Weekly weight gain (g week-1) | 1.57 ± 0.01 | 1.57 ± 0.07 | 1.54 ± 0.05 | 1.51 ± 0.07 | 0.419 |
| Daily growth coefficient (% day-1) | 2.17 ± 0.01 | 2.18 ± 0.06 | 2.15 ± 0.04 | 2.12 ± 0.06 | 0.302 |
| Survival (%) | 83.00 ± 2.33 | 82.00 ± 4.77 | 84.25 ± 3.66 | 83.75 ± 3.20 | 0.824 |
| Feed conversion ratio | 1.63 ± 0.05 | 1.65 ± 0.06 | 1.63 ± 0.07 | 1.68 ± 0.08 | 0.654 |
| Yield (kg m-3) | 3.93 ± 0.09 | 3.90 ± 0.10 | 3.94 ± 0.12 | 3.85 ± 0.15 | 0.710 |
| Fish | |||||
| Final mean weight (g) | 19.72a ± 1.07 | 25.06b ± 1.50 | 31.20c ± 2.54 | 38.02d ± 1.46 | <0.001 |
| Final biomass (kg) | 0.29a ± 0.01 | 0.36b ± 0.02 | 0.47c ± 0.04 | 0.57d ± 0.02 | <0.001 |
| Daily growth coefficient (% day-1) | 0.34a ± 0.09 | 0.76b ± 0.12 | 1.19c ± 0.18 | 1.70d ± 0.10 | <0.001 |
| Survival (%) | 98.33 ± 3.33 | 96.67 ± 3.85 | 100 ± 0.00 | 100 ± 0.00 | 0.2383 |
| Feed conversion ratio | - | 1.34 ± 0.45 | 1.34 ± 0.25 | 1.40 ± 0.13 | 0.942 |
| Yield (kg m-3) | 3.23a ± 0.09 | 4.03b ± 0.21 | 5.20c ± 0.42 | 6.34d ± 0.24 | <0.001 |
| Integrated system | |||||
| Final biomass (kg) | 3.44a ± 0.07 | 3.48ab ± 0.08 | 3.62bc ± 0.06 | 3.65c ± 0.11 | 0.007 |
| Feed conversion ratio | 1.61 ± 0.04 | 1.63 ± 0.05 | 1.60 ± 0.04 | 1.64 ± 0.06 | 0.576 |
| Yield (kg m-3) | 3.86a ± 0.07 | 3.91ab ± 0.09 | 4.07bc ± 0.07 | 4.10c ± 0.12 | 0.007 |
For the fish, significant differences were found for final mean weight, final biomass, daily growth coefficient and yield (p>0.05), with each increase in the fish feeding rate resulting in a significant increase in the assessed variable (Table 2). Survival was above 95% in all cases and mean feed conversion ratio mean values in the treatments that received feed ranged between 1.34 and 1.40.
As regards the system performance, similar to the case with the fish, significant increase in final biomass and yield were observed as the fish feeding rate increased (p<0.05) (Table 2), with the 3% feeding rate treatment presenting the highest value in comparison with both the 0% and 1% treatments. The system mean feed conversion ratio remained around 1.6 in all experimental groups.
Significant linear regression models were found for some of the fish and system performance variables (p<0.05) (Table 3), i.e. fish final mean weight, final biomass, daily growth coefficient and yield, in addition to system final biomass and yield. Fish final mean weight, daily growth coefficient and yield regression models presented R2 values higher than 0.9 (Fig. 2).
| Variable | Regression equation | R² (adjusted R²) | p-value1 |
|---|---|---|---|
| Fish | |||
| Final mean weight (g) | y = 6.12x + 19.33 | 0.952 (0.949) | <0.001 |
| Final biomass (kg) | y = 0.09x + 0.29 | 0.853 (0.842) | <0.001 |
| Daily growth coefficient (% day-1) | y = 0.465x + 0.302 | 0.944 (0.940) | <0.001 |
| Survival (%) | - | - | 0.173 |
| Feed conversion ratio | - | - | 0.736 |
| Yield (kg m-3) | y = 1.05x + 3.12 | 0.957 (0.954) | <0.001 |
| Integrated system | |||
| Final biomass (kg) | y = 0.0875x + 3.425 | 0.640 (0.614) | <0.001 |
| Feed conversion ratio | - | - | 0.503 |
| Yield (kg m-3) | y = 0.0825x + 3.87 | 0.546 (0.513) | 0.001 |
Water microbiology
⌅There were no significant differences between treatments for the counts of total heterotrophic bacteria and Vibrio spp. (p>0.05) (Fig. 3). The overall values were: total heterotrophic bacteria 5.0 ± 0.7 CFU mL-1 (log) and Vibrio spp. 3.2 ± 0.6 CFU mL-1 (log).
Discussion
⌅Water quality
⌅The increasing input of feed did not have deleterious effects on water quality, with the values of pH, TAN, nitrite-N, nitrate-N and alkalinity remaining within appropriate ranges for shrimp (Van Wyk & Scarpa, 1999Van Wyk P, Scarpa J, 1999. Water quality management. In: Farming marine shrimp in recirculating freshwater systems; Van Wyk P et al. (Eds.). Department of Agriculture and Consumer Services, Tallahassee, pp. 141-161.; Lin & Chen, 2001Lin YC, Chen JC, 2001. Acute toxicity of ammonia on Litopenaeus vannamei Boone juveniles at different salinity levels. J Exp Mar Biol Ecol259(1): 109-119. 10.1016/S0022-0981(01)00227-1) and within values previously employed to successfully rear mullets in BFT (Legarda et al., 2019Legarda EC, Poli MA, Martins MA, Pereira SA, Martins ML, Machado C, et al., 2019. Integrated recirculating aquaculture system for mullet and shrimp using biofloc technology. Aquaculture512: 734308. 10.1016/j.aquaculture.2019.734308; Chamorro-Legarda et al., 2020Chamorro Legarda E, Aranha Martins M, Moreira Pereira PK, Siqueira Carneiro RF, Pinheiro IC, Seiffert WQ, et al., 2020. Shrimp rearing in biofloc integrated with different mullet stocking densities. Aquacult Res51: 3571-3581. 10.1111/are.14694; Holanda et al., 2020Holanda M, Santana G, Furtado P, Rodrigues RV, Cerqueira VR, Sampaio LA, et al., 2020. Evidence of total suspended solids control by Mugil liza reared in an integrated system with pacific white shrimp Litopenaeus vannamei using biofloc technology. Aquacult Rep18: 100479. 10.1016/j.aqrep.2020.100479; Legarda et al., 2021Legarda EC, da Silva D, Miranda CS, Pereira PKM, Martins MA, Machado C, et al., 2021. Sea lettuce integrated with Pacific white shrimp and mullet cultivation in biofloc impact system performance and the sea lettuce nutritional composition. Aquaculture534: 736265. 10.1016/j.aquaculture.2020.736265).
There are studies evaluating the optimal TSS concentration for different species in BFT, such as shrimp P. vannamei (400 to 600 mg L-1; Schveitzer et al., 2013Schveitzer R, Arantes R, Costódio PFS, do Espírito Santo CM, Arana LV, Seiffert WQ, et al., 2013. Effect of different biofloc levels on microbial activity, water quality and performance of Litopenaeus vannamei in a tank system operated with no water exchange. Aquacult Eng56: 59-70. 10.1016/j.aquaeng.2013.04.006), South American catfish (Rhamdia quelen) larvae (200 mg L-1; Poli et al., 2015Poli MA, Schveitzer R, de Oliveira Nuñer AP, 2015. The use of biofloc technology in a South American catfish (Rhamdia quelen) hatchery: Effect of suspended solids in the performance of larvae. Aquacult Eng66: 17-21. 10.1016/j.aquaeng.2015.01.004) and pacu (Piaractus mesopotamicus) juveniles (>250 mg L-1; Pellegrin et al., 2022Pellegrin L, Nitz LF, Pinto DSB, Copatti CE, Wasielesky W, Garcia L, 2022. Effects of suspended solids in the survival and haematological parameters of pacu juveniles (Piaractus mesopotamicus) in a biofloc technology culture system. Aquacult Res53: 276-284. 10.1111/are.15575). For lebranche mullets (M. liza), no such study has been published, but previous studies have successfully cultivated Mugil spp. under mean TSS concentrations varying from values as low as 89.79 ± 18.32 mg L-1 (Holanda et al., 2020Holanda M, Santana G, Furtado P, Rodrigues RV, Cerqueira VR, Sampaio LA, et al., 2020. Evidence of total suspended solids control by Mugil liza reared in an integrated system with pacific white shrimp Litopenaeus vannamei using biofloc technology. Aquacult Rep18: 100479. 10.1016/j.aqrep.2020.100479), intermediate values between 300 mg L1 and 600 mg L-1 (Legarda et al., 2019Legarda EC, Poli MA, Martins MA, Pereira SA, Martins ML, Machado C, et al., 2019. Integrated recirculating aquaculture system for mullet and shrimp using biofloc technology. Aquaculture512: 734308. 10.1016/j.aquaculture.2019.734308; Chamorro-Legarda et al., 2020Chamorro Legarda E, Aranha Martins M, Moreira Pereira PK, Siqueira Carneiro RF, Pinheiro IC, Seiffert WQ, et al., 2020. Shrimp rearing in biofloc integrated with different mullet stocking densities. Aquacult Res51: 3571-3581. 10.1111/are.14694; Legarda et al., 2021Legarda EC, da Silva D, Miranda CS, Pereira PKM, Martins MA, Machado C, et al., 2021. Sea lettuce integrated with Pacific white shrimp and mullet cultivation in biofloc impact system performance and the sea lettuce nutritional composition. Aquaculture534: 736265. 10.1016/j.aquaculture.2020.736265) and as high as 706.52 ± 252.13 mg L-1 (Borges et al., 2020Borges BAA, Rocha JL, Pinto PHO, Zacheu T, Chede AC, Magnotti CCF, et al., 2020. Integrated culture of white shrimp Litopenaeus vannamei and mullet Mugil liza on biofloc technology: Zootechnical performance, sludge generation, and Vibrio spp. reduction. Aquaculture524: 735234. 10.1016/j.aquaculture.2020.735234). In the current study, the fish exhibited high survival (above 96% in all treatments) in a situation where the mean TSS concentration varied from 521.98 ± 171.05 mg L-1 to 575.98 ± 189.49 mg L-1, suggesting the feasibility of cultivating mullets under these concentrations.
Strategies employed to manage biofloc systems vary, from using different organic carbon sources to stimulate the immobilization of ammonia, to using tactics to hasten the establishment of a nitrifying community (Ebeling et al., 2006Ebeling JM, Timmons MB, Bisogni JJ, 2006. Engineering analysis of the stoichiometry of photoautotrophic, autotrophic, and heterotrophic removal of ammonia-nitrogen in aquaculture systems. Aquaculture257: 346-358. 10.1016/j.aquaculture.2006.03.019). In the case of this study, the use of an inoculum of mature bioflocs, i.e. water from a tank in which nitrification is already occurring, allowed for the maintenance of low concentrations of the most toxic nitrogenous compounds, TAN and nitrite-N, throughout the entire experiment. It can also be highlighted that the nitrate-N concentration increased at the end of the experiment in comparison with the inoculum (from 11.61 ± 3.22 mg L-1 to 23.34 ± 4.33 mg L-1), although remaining in concentrations that are not harmful to the cultured animals, where concentrations as high as 177 mg L-1 having been reported as acceptable for rearing P. vannamei under a salinity of 23 g L-1 (Furtado et al., 2015Furtado PS, Campos BR, Serra FP, Klosterhoff M, Romano LA, Wasielesky W, 2015. Effects of nitrate toxicity in the Pacific white shrimp, Litopenaeus vannamei, reared with biofloc technology (BFT). Aquacult Int23: 315-327. 10.1007/s10499-014-9817-z). These two observations, the low concentrations of TAN and nitrite-N, along with the increasing nitrate-N concentration, suggest that the system was characterized as being a mature biofloc system, as expected from the management employed.
Productive performance
⌅Regarding the shrimp, the lack of significant effects of the fish feeding rates on its performance was likely a result of the increased rates not deteriorating water quality. A similar phenomenon was also observed when P. vannamei was cultured in integration with Nile tilapia in a study evaluating different feeding rates for the fish (Silva et al., 2022Silva VF, Pereira PKM, Martins MA, Lorenzo MA, Cella H, Lopes RG, et al., 2022. Effects of microalgae addition and fish feed supplementation in the integrated rearing of Pacific white shrimp and Nile tilapia using biofloc technology. Animals12: 1527. 10.3390/ani12121527). The authors also observed no significant effects of the fish feeding rates on the shrimp performance.
In contrast, the significant effects observed on the fish performance variables indicate that mullet growth and productivity were influenced by the feeding rates. As the feeding rate increased, there was an incremental improvement in fish final mean weight, final biomass, daily growth coefficient, and yield. This suggests that a higher feeding rate provides a greater availability of feed resources for the fish, leading to enhanced growth and productivity. The positive relationship between feeding rate and fish performance aligns with previous studies that have reported similar findings for aquatic animals reared in BFT, such as Nile tilapia (Oliveira et al., (Oliveira et al., 2021Oliveira LK, Pilz L, Furtado PS, Ballester ELC, Bicudo ÁJA, 2021. Growth, nutritional efficiency, and profitability of juvenile GIFT strain of Nile tilapia (Oreochromis niloticus) reared in biofloc system on graded feeding rates. Aquaculture541: 736830. 10.1016/j.aquaculture.2021.736830; Silva et al., 2022Silva VF, Pereira PKM, Martins MA, Lorenzo MA, Cella H, Lopes RG, et al., 2022. Effects of microalgae addition and fish feed supplementation in the integrated rearing of Pacific white shrimp and Nile tilapia using biofloc technology. Animals12: 1527. 10.3390/ani12121527) and whiteleg shrimp (Khanjani et al., 2016Khanjani MH, Sajjadi MM, Alizadeh M, Sourinejad I, 2016. Study on nursery growth performance of Pacific white shrimp (Litopenaeus vannamei Boone, 1931) under different feeding levels in zero water exchange system. Iran J Fish Sci15(4): 1465-1484.) under different feeding levels.
The observed significant effects on the overall system productive performance further support the influence of feeding rates on the integrated culture system. Specifically, there were significant effects on the final biomass and yield of the system. As the feeding rate increased, both the final biomass and yield of the system increased accordingly. This indicates that a higher feeding rate promotes a higher overall production output, highlighting the importance of feed availability for system productivity. Silva et al. (2022Silva VF, Pereira PKM, Martins MA, Lorenzo MA, Cella H, Lopes RG, et al., 2022. Effects of microalgae addition and fish feed supplementation in the integrated rearing of Pacific white shrimp and Nile tilapia using biofloc technology. Animals12: 1527. 10.3390/ani12121527) also reported higher system productive performance when Nile tilapia were fed at 1% of their biomass in the integrated culture with whiteleg shrimp, when compared to a treatment in which the fish were not fed at all.
The results of this study have practical implications for the optimization of feeding strategies in the integrated culture of marine shrimp and mullets using biofloc technology. The findings suggest that increasing the fish feeding rate can positively impact fish growth and system productivity without negatively affecting shrimp performance. However, it is important to note that there may be limits to the positive effects of increasing feeding rates. Beyond a certain point, excessive feeding rates may lead to diminishing returns or potential negative impacts, such as deteriorating water quality and poor growth performance (Oliveira et al., 2021Oliveira LK, Pilz L, Furtado PS, Ballester ELC, Bicudo ÁJA, 2021. Growth, nutritional efficiency, and profitability of juvenile GIFT strain of Nile tilapia (Oreochromis niloticus) reared in biofloc system on graded feeding rates. Aquaculture541: 736830. 10.1016/j.aquaculture.2021.736830).
Water microbiology
⌅The counts of total heterotrophic bacteria and Vibrio spp. in the water were measured to assess the impact of different fish feeding rates on water microbiology in the integrated culture of whiteleg shrimp and lebranche mullet using biofloc technology. The results showed no statistically significant effects of the fish feeding rate on water microbiology. This suggests that the microbial communities associated with biofloc formation and maintenance remained resilient and stable, unaffected by the feeding rates tested. This was also observed in a study evaluating the effect of fish feeding rate on the integrated culture of Nile tilapia and whiteleg shrimp, in which no statistical significance was found for Vibrio spp. and total heterotrophic bacteria when different fish feeding rates were used (Silva et al., 2022Silva VF, Pereira PKM, Martins MA, Lorenzo MA, Cella H, Lopes RG, et al., 2022. Effects of microalgae addition and fish feed supplementation in the integrated rearing of Pacific white shrimp and Nile tilapia using biofloc technology. Animals12: 1527. 10.3390/ani12121527)
The lack of significant effects could be related to the fact that the fish feeding represented a small percentage of the overall feed input, due to the greater shrimp biomass in the system. A support for this hypothesis is a study that evaluated the effects of different feeding rates and species configurations in the integrated culture of Tilapia hornorum and P. monodon (Tendencia et al., 2006Tendencia EA, dela Peña MR, ChorescaJr. CH, 2006. Effect of shrimp biomass and feeding on the anti-Vibrio harveyi activity of Tilapia sp. in a simulated shrimp-tilapia polyculture system, 2006. Aquaculture253: 154-162. 10.1016/j.aquaculture.2005.08.004). The system that employed shrimp and fish with both being fed resulted in statistically higher values of total bacterial count when compared with a system in which the fish were not fed. However, the proportion of biomasses differed from the ones used in the current study. For example, Tendencia et al. (2006Tendencia EA, dela Peña MR, ChorescaJr. CH, 2006. Effect of shrimp biomass and feeding on the anti-Vibrio harveyi activity of Tilapia sp. in a simulated shrimp-tilapia polyculture system, 2006. Aquaculture253: 154-162. 10.1016/j.aquaculture.2005.08.004) used 0.5 kg m-3 of fish and only 0.080 kg m-3 of shrimp, compared to the current study where the mean final biomasses were at most 0.64 kg of fish m-3 and 3.54 kg of shrimp m-3 when considering the whole volume of the system.
These findings indicate the robustness of the microbial ecosystem in biofloc-based systems and highlight the potential for adjusting feeding rates within a reasonable range without significant disruptions to the microbial balance. Future research should investigate the long-term effects of feeding rates on water microbiology and explore the functional roles of specific microbial taxa in biofloc systems for a comprehensive understanding of their contributions to system performance and sustainability.
Conclusion
⌅TThis study demonstrated that different fish feeding rates in the integrated culture of marine shrimp and mullets using biofloc technology significantly influenced fish growth and system productivity, without negatively impacting shrimp performance. Water quality variables remained stable and unaffected by the feeding rates. Additionally, the counts of Vibrio spp. and total heterotrophic bacteria in the water were not significantly influenced by the feeding rates. These findings provide valuable insights for optimizing feeding strategies and management practices in bioflocbased integrated culture systems, enhancing efficiency, and minimizing environmental impacts. Future research should focus on comprehensive economic analyses to determine the cost-effectiveness and profitability of different feeding rates.