Next Article in Journal
Investigation of Paraoxonase-1 Genotype and Enzyme-Kinetic Parameters in the Context of Cognitive Impairment in Parkinson’s Disease
Previous Article in Journal
Melatonin as Modulator for Sulfur and Nitrogen Mustard-Induced Inflammation, Oxidative Stress and DNA Damage: Molecular Therapeutics
Previous Article in Special Issue
More Than an Antioxidant: Role of Dietary Astaxanthin on Lipid and Glucose Metabolism in the Liver of Rainbow Trout (Oncorhynchus mykiss)
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Biofloc Technology in Fish Aquaculture: A Review

1
Department of Aquatic Life Medicine, Pukyong National University, Busan 48513, Republic of Korea
2
Department of Aquatic Life and Medical Science, Sun Moon University, Asan-si 31460, Republic of Korea
3
Aquaculture Industry Division, West Sea Fisheries Research Institute, National Institute of Fisheries Science, Incheon 22383, Republic of Korea
*
Author to whom correspondence should be addressed.
These authors contributed equally to this work.
Antioxidants 2023, 12(2), 398; https://doi.org/10.3390/antiox12020398
Submission received: 10 January 2023 / Revised: 30 January 2023 / Accepted: 3 February 2023 / Published: 6 February 2023
(This article belongs to the Special Issue Antioxidants Benefits in Aquaculture)

Abstract

:
The application of biofloc to fish species has several advantages, including the enhancement of production by increasing growth performance and survival rate and the improvement of fish aquaculture physiological activity. There has been a recent increase in biofloc addition to fish culture, and this review examines changes this causes to the survival and growth rate of fish and its economic feasibility. Physiological activity and disease resistance of biofloc-fed fish is being extensively studied. The hematological parameters and antioxidant and immune responses of fish fed biofloc were reviewed in this study, as well as their disease resistance by testing them for major specific diseases. Standards for effectively applying biofloc to fish aquaculture are also suggested.

1. The Necessity of Biofloc Technology in Fish Aquaculture

The rapid growth of the fish farming industry has been caused by the pressure to build intensive aquaculture farms and therefore improve productivity [1,2]. Total global fish production is projected to reach 196 million tons (Mt) by 2025, and within this, aquaculture is estimated to exceed the production of capture fisheries [3]. However, there are several problems associated with this development, such as a decline in animal welfare standards due to breeding in overcrowded conditions and frequent disease occurrence due to poor environmental conditions and a reduction in the disease resistance of fish due to stress [4]. Antibiotics and chemical disinfectants are often used excessively for the prevention and treatment of diseases, but this can lead to drug resistance and the possible evolution of super bacteria due to increased bacterial resistance [5]. Thorough regulation and supervision are therefore needed to avoid these issues, but this is complicated by the fact that regulatory frameworks for the use of antibiotics in fish farming vary widely from country to country, and there are many countries where they are not implemented at all [6]. In fish aquaculture, various environmentally sustainable technologies are being used along with cutting-edge intelligent technologies to build a sustainable aquaculture industry ecosystem [7].
In fish aquaculture production, higher productivity is achieved with greater volumes of feed, resulting in an increase in waste production, which incurs environmental and economic costs. A total of 20–30% of the total nitrogen entering aquaculture ponds remains in the fish biomass, with the remainder becoming a water pollutant, producing high levels of toxic substances such as ammonia and nitrite [8]. Biofloc technology (BFT) is a more environmentally sustainable technology that uses beneficial microorganisms to absorb the ammonia and nitrite produced by feed waste, feces, and urine, which are naturally generated in the metabolic process of aquatic products [9]. This facilitates a self-nitrification process in aquaculture systems without the exchange of stock water and is achieved by stimulating the growth of beneficial microorganisms that can then be utilized as a feed source for aquaculture species and can absorb nitrogenous waste [10]. Innovative aquaculture systems using BFT have been applied to many fish farms due to increasing concern about environmental pollution. The BFT system is an eco-friendly closed system, which has many advantages including no water exchange, improved water quality and fish production, and less contamination by external factors [11]. The BFT system requires strong aeration and carbon sources such as sucrose, glucose, and molasses, and it helps to maintain the water quality by improving the activity of microorganisms and the removal of ammonia [5].
According to FAO statistics, aquaculture production accounted for 47.9% of total fish production in 2019, with common carps and tilapia species accounting for 34.9% and 3.5% of that amount, respectively. Diatin et al. [12] suggest that the majority (62%) of global fish aquaculture production will come from freshwater species such as carp, catfish, and tilapia. Most of these species are suitable for the application of biofloc technology (BFT), as they occupy a high proportion of fish farming and are farmed in ponds [13]. BFT has been successfully applied to intensive aquaculture fish species including common carp (Cyprinus carpio), Nile tilapia (O. niloticus), a polyculture of silver carp (Hypophthalmichthys molitrix), and bighead carp (Aristichtys nobilis) [14]. Efforts are being made to convert land-based systems with flowing-water culture to biofloc systems; however, this is still in the initial stage of research. Biofloc is widely known to improve fish-feed conversion rates and efficiency, liver condition, growth performance, digestive enzyme activity, and the immune competency of fish species, which overall improve fish growth [15]. In addition, biofloc improves biosecurity and feeding management control in fish farming.

2. Survival Rate and Growth Performance of Fish Raised in Biofloc

The useful microorganisms contained in biofloc activate the digestive enzymes of fish and increase feed efficiency, thereby improving growth performance. Biofloc also has a positive effect on survival rate by improving fish immunity [8]; the survival rate of fish species raised in biofloc in fish aquaculture is shown in Table 1. Khanjani et al. [16,17] reported that the survival rate of O. niloticus cultured in biofloc with simple carbon sources such as molasses, starch, barley flour, and corn was significantly improved when compared to the control group, with the starch-treated biofloc having the highest survival rate. The improvement in the survival rate of O. niloticus is likely due to the stress reduction induced by the improvement in the water environment and the addition of the essential amino acids, fatty acids, and nutritional compounds found in biofloc. Ekasari et al. [10] reported that the larval survival rate of O. niloticus broodstock cultured with biofloc was higher than that of the control, indicating that the BFT has a positive effect on larvae in Nile tilapia culture. Fauji et al. [18] reported that the survival rate of African catfish, Clarias gariepinus, raised in biofloc was 96% in the low-density section (4 fish/L), which was higher than that of the control (87%). However, there was a survival rate of 78% in the high-density (8 fish/L) biofloc, which is lower than that of the control group. These results highlight the importance of establishing an optimal density of fish culture using BFT and how vital it is to appreciate that if the density of effective microorganisms exceeds the water purification ability, there may be an adverse effect on the fish. Dauda et al. [19] found that the survival rates of C. gariepinus treated with glycerol and sucrose-treated biofloc were 90.6% and 76.3%, which were significantly higher than that of the control group (60.0%). However, the survival rate in the rice-bran-treated biofloc was found to be significantly lower (27%) than that of the control, which may have been due to the lack of carbon availability in the formation of biofloc. Therefore, it is important to use an appropriate carbon source that is suitable for farm environments and cultured organisms when using biofloc in fish culture. Haridas et al. [20] reported that biofloc significantly improved the survival rate of gray mullet, Mugil cephalus, particularly in the nursery phase. In other studies, it has been reported that both biofloc and control groups showed either 100% survival or no significant difference in the survival rate, which implies that biofloc has an effect on improving the immunity and health of fish but does not always show a significant difference.
The growth performance and feed conversion rate (FCR) of fish species raised in biofloc in fish aquaculture are demonstrated in Table 2. Azim and Little [21] reported that the growth of O. niloticus raised in biofloc increased by 44–46% compared to the control, which explains why biofloc is a suitable food source for fish. The growth performance of O. niloticus cultured with biofloc was increased at salinities of 4 and 8 g/L but decreased at salinities of 12 and 16 g/L, which indicates that growth when cultured with biofloc can vary greatly depending on salinity conditions [22]. Kishawy et al. [23] reported that the increase in the growth performance of O. niloticus cultured with biofloc using glycerol and Mannanoligosaccharides (MOS) as carbon sources was 11.72% and 27.57%, respectively, compared to the control, suggesting that the degree of growth improvement according to carbon source can vary. MOS is a prebiotic unable to be digested by fish enzymes but that can be digested by microbial enzymes. When complex carbohydrates (prebiotics) are added as a carbon source of biofloc, the nutritional content of the biofloc is more improved than that of glycerol. Luo et al. [24] reported that the growth rate of O. niloticus cultured with biofloc was 22% higher than that of O. niloticus cultured with recirculating aquaculture systems (RAS), suggesting that BFT could be a more effective method than RAS, another environmentally sustainable technique. Mirzakhani et al. [25] reported that the growth of O. niloticus cultured with biofloc was between 71.8% and 319.9% higher than that of the control and demonstrated the value of biofloc as a food source. Wang et al. [26] reported an increase in the growth of crucian carp, Carassius auratus, cultured with biofloc; higher increases in growth were observed as the C/N ratio increased. The results of this study confirmed that an appropriate increase in the C/N ratio stimulates the growth of biofloc, thereby increasing the growth of fish. Kim et al. [27] reported an increase in the growth of the olive flounder, Paralichthys olivaceus, of 26.3% when compared to controls, and they suggest that biofloc could improve the immunity and growth capacity of fish. Many authors reported a decrease in FCR with an increase in growth rate, suggesting that the biofloc environment increases the feed efficiency and feed conversion rate of fish. When O. niloticus was cultured with BFT and RAS, it was reported that the FCR of the biofloc was 1.20 ± 0.03, which was 18% higher than the FCR of 1.47 ± 0.02 of the RAS [24].
Table 1. Survival rate of fish species raised in biofloc in fish aquaculture.
Table 1. Survival rate of fish species raised in biofloc in fish aquaculture.
SpeciesCarbon SourceC:N RatioPeriodChange of Survival RateReference
FreshwaterOreochromis niloticusMolasses15:130 days+ [16]
Starch+
Barley flour+
Corn+
Molasses8.4:112 weeks× [22]
Rice bran15:110 weeks× [28]
Wheat-milling by-product×
Sucrose>10:187 days× [25]
Glucose15:18 weeks× [29]
Wheat flour (200 fish/m3)15:190 days× [30]
Wheat flour (250 fish/m3)×
Wheat flour (300 fish/m3)×
Wheat flour (350 fish/m3)×
Molasses10:114 days+ [10]
100% molasses15:1, 20:18 weeks× [26]
100% wheat flour×
75% molasses + 25% wheat flour×
50% molasses + 50% wheat flour×
25% molasses + 75% wheat flour×
Molasses15:137 days+ [17]
Starch+
Barley flour+
Corn+
Molasses (40 fish/m3)15:1112 days× [31]
Molasses (80 fish/m3)×
Cyprinus carpioSugar (6 kg/m3)15:149 days× [32]
Sugar (12 kg/m3)×
Rice bran20:160 days× [33]
Sugarcane molasses-
Rice bran + sugarcane molasses×
Corn starch15:160 days× [34]
Cyprinus carpio L.Sugar beet molasses20:170 days× [35]
Sugar×
Corn starch×
Molasses20:130 days× [36]
Clarias gariepinusTapioca (4 fish/L)10:120 days+ [19]
Tapioca (6 fish/L)-
Tapioca (8 fish/L)-
Glycerol15:18 weeks× [37]
Sucrose15:16 weeks+ [20]
Glycerol+
Rice bran-
Carassius auratusStarch15:1, 20:156 days× [27]
Mugil cephalusSucrose15:160 days+ [21]
Heteropneustes fossilisSugarcane molasses10:1120 days× [38]
Lemon fin barb hybrid (Hypsibarbus wetmorei Antioxidants 12 00398 i001 × Barboides gonionotus Antioxidants 12 00398 i002)Glycerol15:18 weeks× [37]
Lepomis macrochirusCorn starch15:132 days- [39]
Sucrose-sugar-
Labeo rohitaWheat flour10:190 days× [40]
SeawaterOreochromis niloticus sp.Cornmeal + molasses (120 fish/m3)15:17 weeks× [13]
Cornmeal + molasses (240 fish/m3)×
+, increased, - decreased, and × no change in survival rate.
Table 2. Growth performance and FCR of fish species raised in biofloc in fish aquaculture.
Table 2. Growth performance and FCR of fish species raised in biofloc in fish aquaculture.
SpeciesCarbon SourceC:N RatioPeriodResponse C:N RatioResponseReference
Growth performance
FreshwaterOreochromis niloticusMolasses8.4:112 weeks8.4:1+ [23]
Molasses (salinity level 4 g/L)6:170 days6:1+ [23]
Molasses (salinity level 8 g/L)6:1+
Molasses
(salinity level 12 g/L)
6:1-
Molasses
(salinity level 16 g/L)
6:1-
Glycerol15:112 weeks15:1+ [24]
Mannan oligosaccharides15:1+
Glucose (166 organisms/m3)15:1120 days15:1+ [41]
Glucose (333 organisms/m3)15:1+
Glucose (600 organisms/m3)15:1+
Glucose10:1, 15:1, 20:1120 days10:1, 15:1+ [42]
Rice bran and molasses (1:1) (60 fish/m3)15:120 weeks15:1+ [43]
Rice bran and molasses (1:1) (80 fish/m3)15:1+
Molasses15:130 days15:1+ [16]
Starch15:1+
Barley flour15:1+
Corn15:1+
Rice bran15:110 weeks15:1+ [28]
Wheat-milling by-product15:1+
Wheat flour (200 fish/m3)15:190 days15:1+ [30]
Wheat flour (250 fish/m3)15:1+
Wheat flour (300 fish/m3)15:1+
Wheat flour (350 fish/m3)15:1+
Sucrose>10:187 days> 10:1+ [25]
Glucose15:18 weeks15:1+ [29]
Molasses10:114 days-× [18]
100% molasses15:1, 20:18 weeks15:1, 20:1+ [26]
100% wheat flour15:1, 20:1+
75% molasses + 25% wheat flour15:1, 20:1+
50% molasses + 50% wheat flour15:1, 20:1+
25% molasses + 75% wheat flour15:1, 20:1+
Molasses15:137 days15:1+ [17]
Starch15:1+
Barley flour15:1+
Corn15:1+
Molasses (40 fish/m3)15:1112 days15:1+ [31]
Molasses (80 fish/m3)15:1+
Cyprinus carpioSugar (6 kg/m3)15:149 days15:1+ [32]
Sugar (12 kg/m3)15:1+
Glucose20:18 weeks20:1+ [8]
Corn starch15:160 days-× [34]
Rice bran (4.5 kg/m3)20:160 days20:1+ [33]
Sugarcane molasses
(4.5 kg/m3)
-×
Rice bran + sugarcane molasses (4.5 kg/m3)20:1+
Cyprinus carpioSugar beet molasses20:170 days-× [35]
Sugar-×
Corn starch-×
Sugar beet molasses20:110 weeks-× [44]
Sugar-×
Corn starch-×
Molasses20:130 days20:1+ [36]
Clarias gariepinusTapioca (4 fish/L)10:120 days10:1+ [19]
Tapioca (6 fish/L)10:1+
Tapioca (8 fish/L)10:1+
Sucrose15:16 weeks-× [20]
Glycerol-×
Rice bran-×
Glycerol15:18 weeks-× [37]
Carassius auratusStarch15:1, 20:1, 25:156 days20:1, 25:1+ [27]
Carassius auratus gibelioGlucose20:18 weeks20:1+ [8]
Mugil cephalusSucrose15:160 days15:1+ [21]
Heteropneustes fossilisSugarcane molasses10:1120 days10:1+ [29]
Lemon fin barb hybrid (Hypsibarbus wetmorei Antioxidants 12 00398 i001 × Barboides gonionotus Antioxidants 12 00398 i002)Glycerol15:18 weeks15:1+ [37]
Lepomis macrochirusCorn starch15:132 days15:1- [39]
Sucrose-sugar15:1-
Labeo rohitaTapioca15:160 days15:1+ [45]
Wheat15:1+
Corn15:1+
Sugar bagasse15:1+
SeawaterParalichthys olivaceusGlucose<10:14 months10:1+ [27]
Oreochromis niloticus sp.Cornmeal + molasses
120 fish/m3)
15:17 weeks-× [13]
Cornmeal + molasses
(240 fish/m3)
-×
Feed conversion rate (FCR)
FreshwaterOreochromis niloticusMolasses8.4:112 weeks8.4:1- [22]
Molasses (salinity level 4 g/L)6:170 days-× [23]
Molasses (salinity level 8 g/L)-×
Molasses
(salinity level 12 g/L)
-×
Molasses
(salinity level 16 g/L)
6:1+
Glycerol15:112 weeks15:1- [24]
Mannan oligosaccharides15:1-
Glucose (166 organisms/m3)15:1120 days15:1- [41]
Glucose (333 organisms/m3)15:1-
Glucose (600 organisms/m3)15:1-
Glucose10:1, 15:1, 20:1120 days10:1, 15:1+ [42]
Rice bran and molasses (1:1) (60 fish/m3)15:120 weeks15:1- [43]
Rice bran and molasses (1:1) (80 fish/m3)15:1-
Rice bran15:110 weeks15:1- [28]
Wheat-milling by-product15:1-
Sucrose> 10:187 days> 10:1- [25]
Glucose15:18 weeks15:1- [43]
100% molasses15:1, 20:18 weeks15:1, 20:1- [26]
100% wheat flour15:1, 20:1-
75% molasses + 25% wheat flour15:1, 20:1-
50% molasses + 50% wheat flour15:1, 20:1-
25% molasses + 75% wheat flour15:1, 20:1-
Molasses15:137 days15:1+ [17]
Starch15:1+
Barley flour15:1+
Corn15:1+
Molasses (40 fish/m3)15:1112 days15:1+ [33]
Molasses (80 fish/m3)15:1+
Cyprinus carpioSugar (6 kg/m3)15:149 days15:1- [32]
Sugar (12 kg/m3)15:1-
Glucose20:18 weeks20:1- [8]
Corn starch15:160 days15:1- [34]
Rice bran20:160 days20:1- [33]
Sugarcane molasses -×
Rice bran + sugarcane molasses20:1-
Sugar beet molasses20:170 days20:1- [35]
Sugar20:1-
Corn starch20:1-
Sugar beet molasses20:110 weeks20:1- [44]
Sugar20:1-
Corn starch20:1-
Clarias gariepinusTapioca (4 fish/L)10:120 days10:1- [19]
Tapioca (6 fish/L)10:1-
Tapioca (8 fish/L)10:1-
Glycerol15:18 weeks-× [37]
Carassius auratusStarch15:1, 20:1, 25:156 days20:1, 25:1- [27]
Carassius auratus gibelioGlucose20:18 weeks20:1- [8]
Mugil cephalusSucrose15:160 days15:1- [21]
Heteropneustes fossilisSugarcane molasses10:1120 days10:1- [38]
Lemon fin barb hybrid (Hypsibarbus wetmorei Antioxidants 12 00398 i001 × Barboides gonionotus Antioxidants 12 00398 i002)Glycerol15:18 weeks15:1- [37]
Labeo rohitaTapioca15:160 days15:1- [45]
Wheat15:1-
Corn15:1-
Sugar bagasse15:1-
SeawaterOreochromis niloticus sp.Cornmeal + molasses
(120 fish/m3)
15:17 weeks-× [13]
Cornmeal + molasses
(240 fish/m3)
-×
+, increased, - decreased, and × no change in survival rate.

3. Hematological Parameters

Blood in the circulatory system serves several functions in the survival of fish, and hematological parameters are essential indicators for evaluating their physiological state, stress, immune responses, and disease resistance, as well as reflecting the nutritional and environmental conditions, thereby detecting abnormalities connected to fish health status [38]. Biofloc can contribute to the improvement of the health of fish due to both its digestive enzyme activity and physiological activity, and the evaluation of hematological parameters should be a good indicator to confirm its efficacy [18]. Hematological and biochemical parameters of fish species raised in biofloc are demonstrated in Table 3. Erythrocytes are the most abundant cellular components in the circulatory system of fish, playing vital roles in gas exchange and the respiration of cells, as well as performing several functions related to immunity, such as antiviral responses, phagocytosis or cytokine-mediated signaling [46]. Red blood cells (RBCs) can synthesize proteins such as hemoglobin, and an increase in them indicates good health, protecting the fish from stress and disease conditions via non-specific immune responses [38]. Shourbela et al. [47] reported that biofloc made from various carbon sources such as glycerol, molasses, and starch induced a significant increase in RBCs in O. niloticus. Fauji et al. [19] also reported a significant increase in RBCs in C. gariepinus cultured with biofloc, and they go on to suggest that it was therefore healthier than the control group. However, in most studies, there was no significant change in the number of RBCs due to the addition of biofloc to the environment, which suggests that it has little effect on the physiology of fish [29,31,34,35].
While RBCs are responsible for gas exchange, leukocytes (white blood cells: WBCs) are circulating cells of the immune system that are involved in both innate and acquired immune responses by expressing cell-specific immune-related genes [48]. WBCs are associated with the regulation of immune functions, and their number may increase as a protective mechanism during the stress response [49]. Lymphocytes are the most common type of WBCs, and the interaction between lymphocytes B and T is required for an immune response to occur, meaning that the increase in white blood cells is an effective indicator of the stimulation of the fish immune system [50]. Mansour and Esteban [28] reported a significant increase in WBCs in O. niloticus cultured in biofloc, which was caused by an increase in leukocytes due to there being more neutrophils and lymphocytes. This increase was induced by the higher protein levels in the biofloc environment. Other authors have also reported significant increases in WBCs in C. gariepinus and Asian stinging catfish, Heteropneustes fossilis, when cultured in biofloc, suggesting that it causes a higher immune capacity and better health in fish [19,38]. However, many studies showed either no change or a decrease in many fish raised with biofloc, and some suggest that there was no effect on health.
Hematocrit and hemoglobin are both important indicators for evaluating fish health [51,52]. Mansour and Esteban [28] reported a significant increase in hematocrit in O. niloticus cultured with biofloc made from carbon sources of rice bran and wheat-milling by-product, but there was no significant change in biofloc made with glucose as a carbon source. Most of the studies however did not show changes in hematocrit, indicating that the biofloc system did not adversely affect the hematological properties of fish. The main function of hemoglobin is to transport oxygen from the gas exchange organ to peripheral tissues, and a decrease in hemoglobin under stress conditions can be manifested by a decrease in the rate of hemoglobin synthesis, leading to impaired oxygen supply to the tissues and eventually resulting in a decrease in RBCs via hemolysis [53,54]. Shourbela et al. [48] reported a significant increase in the hemoglobin of O. niloticus cultured with biofloc made from various carbon sources such as glycerol, molasses, and starch, indicating an improved health status of fish in this culture. Fauji et al. [19] also reported increased hemoglobin levels in C. gariepinus cultured with biofloc, suggesting that biofloc has a physiologically positive effect on fish [31,38,55].
Blood glucose levels are used by biological systems as an essential fuel to enhance muscle activity, and glucose is an important indicator in assessing acute stress, as glucose levels increase when tissues such as the brain, gills, and muscles increase respiration to cope with the increased energy demands of stress [56]. In a stressful environment, stress hormones such as cortisol and catecholamine are released as a primary reaction in fish, with glucose production being a secondary reaction [57]. Shourbela et al. [47] showed that the plasma glucose of O. niloticus cultured with biofloc made from various carbon sources such as glycerol, molasses, and starch was significantly decreased, meaning that stress levels were lower in the fish in biofloc compared to the control group. Verma et al. [45] also discovered a decrease in plasma glucose levels in Rohu, Labeo rohita, when it was cultured with biofloc made from many carbon sources such as tapioca, wheat, corn, and sugar bagasse, and they suggest that this was due to a decrease in cortisol and glucose caused by the less stressful biofloc environment. Sontakke et al. [58] also reported a significant decrease in plasma glucose in milkfish, Chanos chanos, cultured with biofloc made of various carbon sources such as sorghum, potato, yam, and glucose, and Kim et al. [27] showed a significant decrease in plasma glucose in olive flounder, Paralichthys olivaceus, cultured with biofloc, similarly suggesting that this decrease means that the fish raised with biofloc had less physiological stress than controls. Most studies have reported low plasma glucose levels in fish raised with biofloc, but some studies have reported an increase, suggesting that the biofloc environment may act as a stressor depending on the species and conditions.
Cholesterol is a major component of cell membranes as well as a precursor of all steroid hormones, and it is a major indicator of the health status of fish [59]. Although some studies showed a significant increase or decrease in fish cultured with biofloc, most studies did not show changes in the plasma cholesterol in fish, suggesting that there is no adverse physiological effect [27,33,34,35,60]. Plasma total proteins, including albumin and globulins, are major compounds synthesized in the liver that play an important role in the immune response, meaning that an increase in plasma protein levels is associated with a stronger innate immune response in fish [61,62]. Mansour and Esteban [28] reported a significant increase in the plasma total protein of O. niloticus cultured with biofloc, which implies an improvement in the innate immune response. Verma et al. [45] reported a significant increase in L. rohita plasma glucose in biofloc made from tapioca, but a significant decrease in plasma glucose in biofloc made from wheat, corn, and sugar bagasse, meaning that fish raised in biofloc made from tapioca had a lower immune status compared to when it was made with wheat, corn, and sugar bagasse. Many studies have reported a significant increase in plasma total protein with biofloc in various fish species such as C. carpio, sutchi catfish, Pangasianodon hypophthalmus, and C. chanos [32,33,35,55,58]. However, in some studies, there is no change or a decrease in plasma glucose levels in fish cultured with biofloc, indicating that its efficacy may be limited.
Albumin and globulin are major proteins in the serum. Albumin is a protein carrier involved in the transport of various substances including lipids, hormones, and inorganic ions [63]. Globulin comprises a1, a2, β, and γ-globulin fractions and is a critical component for maintaining a healthy immune system in fish, as an increase in globulin levels is associated with a stronger innate immune response [64]. The ratio of albumin to globulin is a useful indicator for monitoring fish health and immune status. Mansour and Esteban [28] reported a significant increase in plasma albumin in O. niloticus cultured with biofloc. Many authors have reported a similar effect, but also that the change depends on the conditions, implying that there must be an appropriate carbon source and C/N ratio for it to be an immunostimulant [13,26,32,45,47]. Nageswari et al. [55] reported a significant increase in serum albumin in P. hypophthalmus cultured with biofloc made from various carbon sources such as tapioca, sorghum, pearl millet, and finger millet, potentially due to the increase in immunity caused by the bioactive compounds of biofloc. Sontakke et al. [58] also reported a significant increase in serum albumin of C. chanos cultured with biofloc made from various carbon sources such as sorghum, potato, yam, and glucose, and they suggest that this was due to the improved immunity of fish. Many authors have reported significant increases in plasma/serum globulin in various fish species such as O. niloticus, L. rohita, C. carpio, P. hypophthalmus, and C. chanos cultured with biofloc, and this increase means an improved immune status due to interactions with the immune stimulating agent (physiologically active substance) and effective microorganisms present in the biofloc [13,24,26,28,33,45,47,58].
Triglycerides, a provider of cellular energy, are major components of lipoproteins along with cholesterol and phospholipids, and they can be critical biomarkers in evaluating the nutritional status of fish metabolism [65]. Although some studies reported a significant increase in serum/plasma triglyceride in fish cultured with biofloc [20,32], most studies did not show a significant difference in triglyceride levels [33,35].
Aspartate aminotransferase (AST) and alanine aminotransferase (ALT) are responsible for the catalysis of interconversion of non-essential amino acids including glutamate, aspartate, and alanine in fish [66]. Since fish plasma AST and ALT are released into the blood by the increased permeability of damaged hepatocytes due to various environmental stresses and disease infections, the levels of these are important factors in diagnosing liver function and damage [47,67]. Adineh et al. [32] reported that the serum AST and ALT of C. carpio cultured with biofloc were significantly decreased, indicating lower breeding stress. Yu et al. [68] also reported significant reductions in plasma AST and ALT of Kaoping freshwater minnow, Opsariichthys kaopingensis. These suggest that the reduction in AST and ALT of P. olivaceus raised in biofloc creates less stress in the biofloc environment. Alkaline phosphatase (ALP), in addition to the pinocytic vesicle and Golgi complex, is a membrane-bound enzyme found in the bile pole of hepatocytes, which is an important enzyme in fish metabolism that transports metabolites across the membrane [69]. ALP activity plays a role in immune regulation and defense mechanisms in fish, and it is widely used as an indicator of stress-induced tissue damage and physiological responses [70]. Adineh et al. [32] reported a significant increase in serum ALP of C. carpio cultured with biofloc and suggested that the increase in enzymatic activity was due to the stimulated immune activity induced by the biofloc environment. During a stress response, cortisol secretion from interrenal cells in the head kidney is activated by corticotropin-releasing factors via the secretion of adrenocorticotropic hormone from the anterior pituitary, and this is a major indicator of stress in fish [71]. This cortisol increase leads to phagocytic and complement activity suppression in blood and head-kidneys, a decrease in the number of lymphocytes, and an increase in susceptibility to infection [72]. Most of the studies showed a significant decrease in serum cortisol in fish cultured with biofloc, and it was argued that this decrease was the result of proving that biofloc had an effect of relieving stress in fish [30,32,34,47,55,58]. Verma et al. [45] also reported a significant decrease in serum cortisol in L. rohita cultured with biofloc, suggesting that biofloc had an anti-stress effect on fish.
Table 3. Hematological and biochemical parameters of fish species raised in the biofloc in fish aquaculture.
Table 3. Hematological and biochemical parameters of fish species raised in the biofloc in fish aquaculture.
SpeciesCarbon SourceC:N RatioPeriodTarget OrganResponse C/N RatioResponseReference
Red blood cell (RBC)
FreshwaterOreochromis niloticusGlycerol (140 fish/m3)15:198 daysBlood15:1+ [47]
Glycerol (280 fish/m3)15:1+
Molasses (140 fish/m3)15:198 daysBlood15:1+
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysBlood15:1+
Starch (280 fish/m3)15:1+
Glucose15:18 weeksBlood-× [29]
Molasses (40 fish/m3)15:1112 daysBlood-× [31]
Molasses (80 fish/m3)-×
Cyprinus carpioRice bran20:160 daysBlood-× [33]
Sugarcane molasses-×
Rice bran + sugarcane molasses20:1+
Corn starch15:160 daysBlood-× [34]
Corn starch (10% of daily feed deducted)-×
Sugar beet molasses20:110 weeksBlood-× [44]
Sugar-×
corn starch-×
Clarias gariepinusTapioca (4 fish/L)10:120 daysBlood-× [19]
Tapioca (6 fish/L)10:1+
Tapioca (8 fish/L)-×
Heteropneustes fossilisSugarcane molasses10:1120 daysBlood10:1+ [38]
White blood cell (WBC)
FreshwaterOreochromis niloticusRice bran 15:110 weeksBlood15:1+ [28]
Wheat-milling by-product15:1+
Glycerol (140 fish/m3)15:198 daysBlood15:1- [47]
Glycerol (280 fish/m3)15:1-
Molasses (140 fish/m3)15:198 daysBlood15:1-
Molasses (280 fish/m3)15:1-
Starch (140 fish/m3)15:198 daysBlood15:1-
Starch (280 fish/m3)-×
Glucose15:18 weeksBlood-× [29]
Cyprinus carpioRice bran20:160 daysBlood-× [33]
Sugarcane molasses-×
Rice bran + sugarcane molasses-×
Corn starch15:160 daysBlood-× [34]
Sugar beet molasses20:110 weeksBlood-× [44]
Sugar-×
corn starch-×
Clarias gariepinusTapioca (4 fish/L)10:120 daysBlood10:1+ [19]
Tapioca (6 fish/L)10:1+
Tapioca (8 fish/L)10:1+
Heteropneustes fossilisSugarcane molasses10:1120 daysBlood10:1+ [38]
Hematocrit (Ht)
FreshwaterOreochromis niloticusRice bran 15:110 weeksBlood15:1+ [28]
Wheat-milling by-product 15:1+
Glucose15:18 weeksBlood-× [29]
Cyprinus carpioSugar beet molasses20:110 weeksBlood-× [44]
Sugar-×
Corn starch-×
Corn starch15:160 daysBlood-× [34]
Clarias gariepinusTapioca (4 fish/L)10:120 daysBlood-× [19]
Tapioca (6 fish/L)-×
Tapioca (8 fish/L)-×
SeawaterParalichthys olivaceusGlucose<10:14 monthsBlood-× [27]
Hemoglobin (Hb)
FreshwaterOreochromis niloticusGlycerol (140 fish/m3)15:198 daysBlood15:1+ [47]
Glycerol (280 fish/m3)15:1+
Molasses (140 fish/m3)15:198 daysBlood15:1+
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysBlood15:1+
Starch (280 fish/m3)15:1+
Glucose15:18 weeksBlood-× [29]
Molasses (40 fish/m3)15:1112 daysBlood15:1+ [31]
Molasses (80 fish/m3)-×
Cyprinus carpioRice bran (4.5 kg/m3)20:160 daysBlood-× [33]
Sugarcane molasses
(4.5 kg/m3)
20:1-
Rice bran + sugarcane molasses (4.5 kg/m3)-×
Clarias gariepinusTapioca (4 fish/L)10:120 daysBlood10:1+ [19]
Tapioca (6 fish/L)-×
Tapioca (8 fish/L)10:1+
Heteropneustes fossilisSugarcane molasses10:1120 daysBlood10:1+ [38]
Pangasianodon hypophthalmusTapioca15:190 daysBlood15:1+ [54]
Sorghum15:1+
Pearl millet15:1+
Finger millet15:1+
SeawaterParalichthys olivaceusGlucose<10:14 monthsBlood-× [27]
Glucose
FreshwaterOreochromis niloticusGlycerol (140 fish/m3)15:198 daysSerum15:1- [48]
Glycerol (280 fish/m3)15:1-
Molasses (140 fish/m3)15:198 daysSerum15:1-
Molasses (280 fish/m3)15:1-
Starch (140 fish/m3)15:198 daysSerum15:1-
Starch (280 fish/m3)15:1-
Sucrose>10:187 daysSerum-× [25]
Wheat flour
(200 fish/m3)
15:190 daysSerum15:1- [30]
Wheat flour
(250 fish/m3)
15:1-
Wheat flour
(300 fish/m3)
15:1-
Wheat flour
(350 fish/m3)
15:1-
Molasses (40 fish/m3)15:1112 daysPlasma15:1- [31]
Molasses (80 fish/m3)-×
Genetically Improved Farmed TilapiaSpentwash10:1180 daysSerum10:1- [73]
Labeo rohitaTapioca15:120 daysSerum15:1- [45]
40 days15:1-
60 days15:1-
Wheat15:120 daysSerum15:1-
40 days15:1-
60 days15:1-
Corn15:120 daysSerum15:1-
40 days15:1-
60 days-×
Sugar bagasse15:120 daysSerum15:1-
40 days15:1-
60 days15:1-
Molasses15:116 weeksSerum-× [74]
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum15:1- [32]
Sugar (12 kg/m3)15:1-
Rice bran (4.5 kg/m3)20:160 daysSerum-× [33]
Sugarcane molasses
(4.5 kg/m3)
20:1+
Rice bran + Sugarcane molasses (4.5 kg/m3)-×
Sugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
Clarias gariepinusSucrose15:16 weeksPlasma-× [20]
Glycerol-×
Rice bran-×
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1- [55]
Sorghum15:1-
Pearl millet15:1-
Finger millet15:1-
Brackish waterMugil cephalusSucrose15:160 daysSerum-× [30]
Chanos chanosSorghum15:145 daysSerum15:1- [58]
90 days15:1-
Potato15:145 daysSerum15:1-
90 days15:1-
Yam15:145 daysSerum15:1-
90 days15:1-
Glucose15:145 daysSerum15:1-
90 days15:1-
SeawaterParalichthys olivaceusGlucose<10:14 monthsPlasma<10:1- [27]
Oreochromis sp.Cornmeal + molasses (120 fish/m3)15:17 weeksPlasma-× [13]
Cornmeal + molasses (240 fish/m3)-×
Cholesterol
FreshwaterOreochromis niloticusMolasses (40 fish/m3)15:1112 daysPlasma-× [31]
Molasses (80 fish/m3)15:1-
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)15:1+
Rice bran (4.5 kg/m3)20:160 daysSerum-× [33]
Sugarcane molasses
(4.5 kg/m3)
-×
Rice bran + sugarcane molasses (4.5 kg/m3)-×
Corn starch15:160 daysPlasma-× [34]
Sugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
SeawaterParalichthys olivaceusGlucose<10:14 monthsPlasma-× [27]
Oreochromis sp.Cornmeal + molasses (120 fish/m3)15:17 weeksPlasma15:1- [13]
Cornmeal + molasses (240 fish/m3)-×
Total protein
FreshwaterOreochromis niloticusRice bran 15:110 weeksPlasma15:1+ [28]
Wheat-milling by-product15:1+
Glycerol (140 fish/m3)15:198 daysSerum15:1+ [47]
Glycerol (280 fish/m3)-×
Molasses (140 fish/m3)15:198 daysSerum15:1+
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysSerum-×
Starch (280 fish/m3)15:1+
Glucose15:18 weeksSerum-× [29]
Mannan oligosaccharides15:112 weeksSerum15:1+ [24]
Glycerol15:1+
100% molasses15:1, 20:18 weeksSerum15:1, 20:1+ [26]
100% wheat flour15:1, 20:1+
75% molasses + 25% wheat flour15:1, 20:1+
50% molasses + 50 wheat flour15:1, 20:1+
25% molasses + 75% wheat flour15:1, 20:1+
Molasses (40 fish/m3)15:1112 daysPlasma-× [31]
Molasses (80 fish/m3)15:1-
Genetically Improved Farmed TilapiaSpentwash10:1180 daysSerum10:1+ [73]
Labeo rohitaTapioca15:120 daysSerum-× [45]
40 days15:1+
60 days15:1+
Wheat15:120 daysSerum15:1-
40 days-×
60 days-×
Corn15:120 daysSerum15:1-
40 days-×
60 days15:1-
Sugar bagasse15:120 daysSerum15:1-
40 days-×
60 days-×
Molasses15:116 weeksSerum-× [74]
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)15:1+
Rice bran (4.5 kg/m3)20:160 daysSerum-× [33]
Sugarcane molasses
(4.5 kg/m3)
20:1+
Rice bran + sugarcane molasses (4.5 kg/m3)20:1+
Corn starch15:160 daysPlasma-× [34]
Sugar beet molasses20:110 weeksSerum20:1+ [44]
Sugar20:1+
Corn starch20:1+
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1+ [55]
Sorghum15:1+
Pearl millet15:1+
Finger millet15:1+
Brackish waterMugil cephalusSucrose15:160 daysSerum-× [21]
Chanos chanosSorghum15:145 daysSerum15:1+ [58]
90 days15:1+
Potato15:145 daysSerum-×
90 days15:1+
Yam15:145 daysSerum15:1+
90 days15:1+
Glucose15:145 daysSerum15:1+
90 days15:1+
SeawaterParalichthys olivaceusGlucose<10:14 monthsPlasma-× [28]
Oreochromis sp.Cornmeal + molasses (120 fish/m3)15:17 weeksPlasma15:1- [13]
Cornmeal + molasses (240 fish/m3)-×
Albumin
FreshwaterOreochromis niloticusRice bran 15:110 weeksPlasma15:1+ [28]
Wheat-milling by-product 15:1+
Glycerol (140 fish/m3)15:198 daysSerum-× [47]
Glycerol (280 fish/m3)-×
Molasses (140 fish/m3)15:198 daysSerum-×
Molasses (280 fish/m3)-×
Starch (140 fish/m3)15:198 daysSerum-×
Starch (280 fish/m3)15:1+
Mannan oligosaccharides15:112 weeksSerum15:1+ [24]
Glycerol15:1+
100% molasses15:1, 20:18 weeksSerum-× [26]
100% wheat flour15:1, 20:1+
75% molasses + 25% wheat flour-×
50% molasses + 50 wheat flour-×
25% molasses + 75% wheat flour-×
Labeo rohitaTapioca15:120 daysSerum15:1- [45]
40 days15:1+
60 days-×
Wheat15:120 daysSerum15:1-
40 days-×
60 days15:1-
Corn15:120 daysSerum15:1-
40 days15:1+
60 days15:1+
Sugar bagasse15:120 daysSerum15:1-
40 days-×
60 days-×
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum15:1- [32]
Sugar (12 kg/m3)15:1+
Rice bran (4.5 kg/m3)20:160 daysSerum-× [33]
Sugarcane molasses
(4.5 kg/m3)
-×
Rice bran + sugarcane molasses (4.5 kg/m3)-×
Corn starch15:160 daysPlasma-× [34]
Sugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1+ [55]
Sorghum15:1+
Pearl millet15:1+
Finger millet15:1+
Brackish waterMugil cephalusSucrose15:160 daysSerum-× [21]
Chanos chanosSorghum15:145 daysSerum15:1+ [58]
90 days15:1+
Potato15:145 daysSerum15:1+
90 days15:1+
Yam15:145 daysSerum15:1+
90 days15:1+
Glucose15:145 daysSerum15:1+
90 days15:1+
Sea waterOreochromis sp.Cornmeal + molasses (120 fish/m3)15:17 weeksPlasma15:1- [8]
Cornmeal + molasses (240 fish/m3)15:1+
Globulin
FreshwaterOreochromis niloticusRice bran15:110 weeksPlasma-× [28]
Wheat-milling by-product 15:1+
Glycerol (140 fish/m3)15:198 daysSerum15:1+ [47]
Glycerol (280 fish/m3)-×
Molasses (140 fish/m3)15:198 daysSerum15:1+
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysSerum-×
Starch (280 fish/m3)15:1+
Mannan oligosaccharides15:112 weeksSerum15:1+ [24]
Glycerol15:1+
100% molasses15:1, 20:18 weeksSerum-× [26]
100% wheat flour15:1, 20:1+
75% molasses + 25% wheat flour-×
50% molasses + 50% wheat flour15:1+
25% molasses + 75% wheat flour15:1, 20:1+
Labeo rohitaTapioca15:120 daysSerum15:1+ [45]
40 days-×
60 days15:1+
Wheat15:120 daysSerum15:1+
40 days-×
60 days-×
Corn15:120 daysSerum-×
40 days15:1-
60 days-×
Sugar bagasse15:120 daysSerum-×
40 days-×
60 days-×
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)15:1+
Rice bran (4.5 kg/m3)20:160 daysSerum20:1+ [33]
Sugarcane molasses
(4.5 kg/m3)
20:1+
Rice bran + sugarcane molasses (4.5 kg/m3)20:1+
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1+ [55]
Sorghum15:1+
Pearl millet15:1+
Finger millet15:1+
Brackish waterChanos chanosSorghum15:145 daysSerum15:1+ [58]
90 days15:1+
Potato15:145 daysSerum-×
90 days15:1+
Yam15:145 daysSerum15:1+
90 days15:1+
Glucose15:145 daysSerum15:1+
90 days15:1+
Sea waterOreochromis sp.Cornmeal + molasses (120 fish/m3)15:17 weeksPlasma15:1+ [13]
Cornmeal + molasses (240 fish/m3)15:1-
Triglyceride
FreshwaterCyprinus carpioSugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)15:1+
Rice bran (4.5 kg/m3)20:160 daysSerum-× [33]
Sugarcane molasses
(4.5 kg/m3)
-×
Rice bran + sugarcane molasses (4.5 kg/m3)-×
Sugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
Clarias gariepinusSucrose15:16 weeksPlasma-× [20]
Glycerol15:1+
Rice bran-×
Aspartate aminotransferase (AST)
FreshwaterCyprinus carpioSugar (6 kg/m3)15:149 daysSerum15:1- [32]
Sugar (12 kg/m3)15:1-
Clarias gariepinusSucrose15:16 weeksPlasma-× [20]
Glycerol-×
Rice bran-×
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysSerum15:1, 20:1, 25:1- [68]
Sea waterParalichthys olivaceusGlucose<10:14 monthsPlasma<10:1- [28]
Alanine aminotransminase (ALT)
FreshwaterCyprinus carpioSugar (6 kg/m3)15:149 daysSerum15:1- [32]
Sugar (12 kg/m3)15:1-
Clarias gariepinusSucrose15:16 weeksPlasma-× [20]
Glycerol-×
Rice bran-×
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysSerum20:1 - [68]
Sea waterParalichthys olivaceusGlucose<10:14 monthsPlasma<10:1- [28]
Alkaline phosphatase (ALP)
FreshwaterOreochromis niloticusSucrose>10:187 daysSerum-× [25]
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)15:1+
SeawaterParalichthys olivaceusGlucose<10:14 monthsPlasma-× [28]
Cortisol
FreshwaterOreochromis niloticusWheat flour (+35% crude protein)8.4:112 weeksPlasma-× [22]
Glycerol (140 fish/m3)15:198 daysSerum15:1- [31]
Glycerol (280 fish/m3)15:1-
Molasses (140 fish/m3)15:198 daysSerum15:1-
Molasses (280 fish/m3)15:1-
Starch (140 fish/m3)15:198 daysSerum15:1-
Starch (280 fish/m3)15:1-
Wheat flour
(200 fish/m3)
15:190 daysSerum15:1- [63]
Wheat flour
(250 fish/m3)
15:1-
Wheat flour
(300 fish/m3)
15:1-
Wheat flour
(350 fish/m3)
15:1-
Labeo rohitaTapioca15:120 daysSerum15:1- [45]
40 days-×
60 days15:1-
Wheat15:120 daysSerum15:1-
40 days15:1-
60 days15:1-
Corn15:120 daysSerum15:1-
40 days15:1-
60 days15:1+
Sugar bagasse15:120 daysSerum15:1-
40 days-×
60 days15:1-
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)15:1-
Corn starch15:160 daysPlasma15:1- [34]
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1- [55]
Sorghum15:1-
Pearl millet15:1-
Finger millet15:1-
Brackish waterMugil cephalusSucrose15:160 daysSerum-× [21]
Chanos chanosSorghum15:145 daysSerum15:1- [58]
90 days15:1-
Potato15:145 daysSerum15:1-
90 days15:1-
Yam15:145 daysSerum15:1-
90 days15:1-
Glucose15:145 daysSerum15:1-
90 days15:1-
+, increased, - decreased, and × no change in survival rate.

4. Antioxidant Responses

Antioxidant responses in fish, including both enzymatic and non-enzymatic, are closely connected to fish health status, and several types of antioxidant responses are required to control the fish’s complex immune system [75]. Bacterial and viral infections, as well as physical and chemical environmental stress, are the main generators of reactive oxygen species (ROS) in fish, and excessive ROS alters the structural and functional molecules of fish cells, leading to tissue and organ dysfunction by lipid peroxidation [76]. This also induces apoptosis, DNA hydroxylation, protein denaturation, and cell injury [77]. Antioxidant reactions effectively remove the excessively generated ROS as a protection mechanism for the fish, and the excessive ROS exceeding the antioxidant capacity causes oxidative stress [78].
The antioxidant responses of fish species raised in biofloc are shown in Table 4. Total antioxidant capacity (TAC) is an index that measures the antioxidant capacity of all fish, indicating free-radical scavenging ability [68]. Bakhshi et al. [35] reported a significant increase in serum TAC of C. carpio cultured with biofloc made from various carbon sources such as sugar beet molasses, sugar, and corn starch. Yu et al. [68,79] reported a significant increase in TAC in various tissues such as the gills, kidney, brain, liver, gut, and serum of O. kaopingensis and C. auratus cultured with biofloc, and they suggest that antioxidant responses can be increased by bioactive substances such as chlorophyll, polyphenols, carotene, taurine, polysaccharides, phytosterol, and vitamins contained in biofloc, thereby increasing the resistance of fish to environmental stress by lowering the level of lipid peroxidation and inducing a stronger ability in fish to resist free radicals. Yu et al. [80] reported a significant increase in the liver and intestine TAC of Northern snakehead, Channa argus, cultured with biofloc, showing that biofloc strengthened antioxidant enzyme activity and relieved oxidative stress.
Superoxide dismutase (SOD) is a major antioxidant enzyme in fish that converts superoxide anion (O2•−) into hydrogen peroxide to protect fish from damage from reactive oxygen species and maintain the metabolic balance of ROS as a first defense mechanism against oxidative stress [81]. Catalase (CAT) is an enzyme derived from peroxisomes and mitochondria. It establishes a primary antioxidant defense mechanism by converting hydrogen peroxide into water and oxygen with SOD. Mansour and Esteban [28] reported a significant increase in the plasma SOD and CAT activities of O. niloticus cultured with biofloc, and they suggest that these results reflect increased fish well-being and reduced oxidative stress. Shourbela et al. [47] observed an increase in serum SOD and CAT activities in O. niloticus cultured with biofloc, and within this, the biofloc group with low stocking density showed a significant increase in activities compared to biofloc with high stocking density, mirroring the results of [41]. Menaga et al. [73] suggest that biofloc could cause an increase in SOD and CAT activities in fish and that low levels of SOD and CAT activities meant that high levels of free radicals could accumulate in cells, leading to cell damage. Ebrahimi et al. [33] also reported a significant increase in the serum SOD and CAT activities of C. carpio cultured with biofloc, and they suggest that an increase in the antioxidant enzyme that prevents lipid peroxidation improves the antioxidant capacity. Yu et al. [68,79] reported an increase in the SOD and CAT activities of O. kaopingensis and C. auratus cultured with biofloc, which led to lower levels of lipid peroxidation and a stronger ability to resist free radicals in fish. Nageswari et al. [55] reported a significant increase in the SOD and CAT activities of P. hypophthalmus cultured with biofloc, implying that the biofloc environment acts as an effective antioxidant for fish by conferring high resistance to oxidative stress. On the other hand, Haridas et al. [30] reported a decrease in the liver tissue SOD and CAT activities of O. niloticus cultured with biofloc, and they suggest that the presence of bioactive compounds may have reduced the production of SOD and CAT. Sontakke et al. [58] reported that the liver SOD and CAT activities of C. chanos cultured with biofloc were significantly reduced, suggesting that the antioxidant enzymes were less stimulated due to the lower amount of oxidative stress.
Glutathione peroxide (GPx) plays a critical role in converting hydrogen peroxide into water and oxygen along with CAT, detoxifying its active metabolites and maintaining the intracellular redox balance, thereby protecting fish from cell membrane damage [80]. GPx is a family of enzymes displaying peroxidase activity and a broad substrate spectrum. The enzyme uses glutathione (GSH) as an essential cofactor to catalyze hydrogen peroxide, organic hydrogen peroxide, and lipid hydrogen peroxide with water or alcohol to protect fish from oxidative stress, primarily as an intracellular antioxidant enzyme [78]. Long et al. [29] reported a significant increase in serum GPx of O. niloticus cultured with biofloc. Many authors similarly reported a significant increase in GPx in C. carpio cultured with biofloc, and they suggest that this increase in the GPx reflects improved fish health and reduced oxidative stress [33,35,63]. Yu et al. [68,79] reported a significant increase in GPx of O. kaopingensis, C. auratus, and C. argus cultured with biofloc, and they suggest that this increase in the GPx induces a stronger ability to resist free radicals. Glutathione reductase (GR) is a component that plays an important role in non-enzymatic antioxidant defense and is a key component of the apoptosis system, converting GSH to glutathione disulfide (GSSG) and back into GSH to stimulate GPx [82]. Shourbela et al. [47] reported a significant increase in the GR of O. niloticus cultured with biofloc, and they suggest that the increase in the GR was induced by antioxidant response stimulation. GSH is the first and most important non-enzymatic antioxidant defense mechanism against ROS, including singlet oxygen, superoxide, and hydroxyl radicals in addition to playing a critical role in cell protection, protein synthesis, and cell differentiation and death, which is abundant in the cytoplasm and mitochondria of cells [83]. GSH in fish is essential for assessing redox homeostasis and detoxification conditions in cells with respect to their protective role against oxidative and free-radical-mediated cellular damage [84]. Liu et al. [41,42] reported that GSH of O. niloticus cultured with biofloc was significantly increased, which showed that biofloc had an anti-stress effect.
Malondialdehyde (MDA), an important indicator for judging oxidative stress, is the final product of lipid peroxidation produced by the reaction of free radicals with polyunsaturated fatty acids [85]. Liu et al. [41,42] reported a significant decrease in the MDA of O. niloticus cultured with biofloc, indicating that fish raised in biofloc had adequate defense against lipid peroxidation and had improved antioxidant capacity and regulatory mechanisms. In addition, it was found that the MDA of C. carpio cultured with biofloc was significantly increased due to improved fish health and a reduction in oxidative stress [33]. These reductions in MDA were reported in a variety of biofloc-cultured fish species such as O. kaopingensis, C. auratus, and C. argus, and the results suggest that the bioactive substances, such as chlorophyll, carotene, polysaccharides, polyphenols, phytosterol, taurine, and vitamins in biofloc act as antioxidants [68,79,80]. In fish, the generation of ROS due to various stresses stimulates primary antioxidant enzymes such as SOD and CAT, and GSH is converted to GSSG to activate GPx and then back to GSH with the GR enzyme (Figure 1). However, ROS that are not properly removed may produce lipid peroxide in the lipid membrane, and MDA may be a final product. Therefore, the major antioxidant responses in fish indicate health and the improvement of antioxidant ability by biofloc.
Table 4. Antioxidant responses of fish species raised in the biofloc in fish aquaculture.
Table 4. Antioxidant responses of fish species raised in the biofloc in fish aquaculture.
SpeciesCarbon SourceC:N RatioPeriodTarget OrgansResponse C:N RatioResponseReference
Total antioxidant capacity (TAC)
FreshwaterCyprinus carpioSugar beet molasses20:110 weeksSerum20:1+ [44]
Sugar20:1+
Corn starch20:1+
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysGills20:1, 25:1+ [68]
Kidney15:1, 20:1 25:1+
Brain20:1+
Liver20:1+
Gut15:1, 20:1, 25:1+
Serum20:1, 25:1+
Carassius auratusAnhydrous glucose10:1, 15:1, 20:1, 25:18 weeksGut15:1, 20:1, 25:1+ [79]
Kidney10:1, 15:1, 20:1, 25:1+
Liver15:1, 20:1, 25:1+
Channa argusGlucose10:1, 15:1, 20:18 weeksLiver15:1+ [80]
Intestine15:1+
Supero×ide dismutase (SOD)
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksPlasma15:1+ [28]
Rice bran15:1+
Glycerol (140 fish/m3)15:198 daysSerum15:1+ [47]
Glycerol (280 fish/m3)15:1+
Molasses (140 fish/m3)15:198 daysSerum-×
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysSerum-×
Starch (280 fish/m3)-×
Glucose
(166 organisms/m3)
15:1120 daysLiver15:1+ [41]
Glucose
(333 organisms/m3)
15:1+
Glucose
(600 organisms/m3)
-×
Wheat flour
(200 fish/m3)
15:190 daysLiver15:1- [30]
Wheat flour
(250 fish/m3)
15:1-
Wheat flour
(300 fish/m3)
15:1-
Wheat flour
(350 fish/m3)
15:1-
Glucose10:1, 15:1, 20:1120 daysLiver10:1, 15:1+ [42]
20:1-
Spentwash10:1180 daysSerum10:1+ [73]
Molasses14:1, 17:1, 20:162 daysLiver-× [86]
Cyprinus carpioSugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
Sugar (6 kg/m3)15:149 daysSerum-× [32]
Sugar (12 kg/m3)-×
Rice bran20:160 daysSerum-× [33]
Sugarcane molasses20:1+
Rice bran + sugarcane molasses20:1+
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysGills20:1+ [68]
Kidney15:1, 20:1 25:1+
Brain15:1, 20:1+
Liver20:1+
Liver15:1, 25:1-
Gut15:1, 20:1, 25:1+
Serum15:1, 20:1, 25:1+
Carassius auratusAnhydrous glucose10:1, 15:1, 20:1, 25:18 weeksGut10:1, 15:1, 20:1, 25:1+ [79]
Kidney15:1, 20:1, 25:1+
Liver15:1, 20:1, 25:1+
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1+ [55]
Sorghum15:1+
Pearl millet15:1+
Finger millet15:1+
Channa argusGlucose10:1, 15:1, 20:18 weeksLiver15:1, 20:1+ [80]
Intestine10:1, 15:1, 20:1+
Brackish waterChanos chanosSorghum15:145 daysLiver15:1- [58]
90 days-×
Potato15:145 daysLiver-×
90 days-×
Yam15:145 daysLiver15:1-
90 days15:1-
Glucose15:145 daysLiver15:1-
90 days-×
SeawaterOreochromis niloticus sp.Cornmeal + molasses (120 fish/m3)15:17 weeksLiver15:1+ [13]
Cornmeal + molasses (240 fish/m3)-×
Catalase (CAT)
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksPlasma15:1+ [28]
Rice bran15:1+
Glycerol (140 fish/m3)15:198 daysSerum15:1+ [47]
Glycerol (280 fish/m3)15:1+
Molasses (140 fish/m3)15:198 daysSerum-×
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysSerum-×
Starch (280 fish/m3)15:1+
Wheat flour
(200 fish/m3)
15:190 daysLiver15:1- [63]
Wheat flour
(250 fish/m3)
15:1-
Wheat flour
(300 fish/m3)
15:1-
Wheat flour
(350 fish/m3)
15:1-
Spentwash10:1180 daysSerum10:1+ [73]
Molasses14:1, 17:1, 20:162 daysLiver-× [86]
Molasses
(15% food reduction) (500 fish/m3)
15:153 daysSkin mucus-× [87]
Molasses
(30% food reduction) (500 fish/m3)
15:1-
Molasses
(45% food reduction) (500 fish/m3)
15:1-
Molasses
(100% food reduction) (500 fish/m3)
15:1-
Molasses
(15% food reduction) (1000 fish/m3)
15:153 daysSkin mucus-×
Molasses
(30% food reduction) (1000 fish/m3)
15:1-
Molasses
(45% food reduction) (1000 fish/m3)
15:1-
Molasses
(100% food reduction) (1000 fish/m3)
15:1-
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum15:1+ [32]
Sugar (12 kg/m3)15:1-
Rice bran20:160 daysSerum20:1+ [33]
Sugarcane molasses20:1+
Rice bran + sugarcane molasses20:1+
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysGills20:1+ [68]
Kidney20:1, 25:1+
Brain15:1, 20:1, 25:1+
Liver20:1, 25:1+
Gut15:1, 20:1, 25:1+
Serum20:1, 25:1+
Carassius auratusAnhydrous glucose10:1, 15:1, 20:1, 25:18 weeksGut10:1, 15:1, 20:1, 25:1+ [79]
Kidney15:1, 20:1, 25:1+
Liver10:1, 15:1, 20:1, 25:1+
Pangasianodon hypophthalmusTapioca15:190 daysSerum15:1+ [55]
Sorghum15:1+
Pearl millet15:1+
Finger millet15:1+
Channa argusGlucose10:1, 15:1, 20:18 weeksLiver10:1, 15:1, 20:1+ [80]
Intestine15:1, 20:1+
Brackish waterChanos chanosSorghum15:145 daysLiver15:1- [58]
90 days-×
Potato15:145 daysLiver15:1-
90 days-×
Yam15:145 daysLiver15:1-
90 days15:1-
Glucose15:145 daysLiver15:1-
90 days15:1-
SeawaterOreochromis niloticus sp.Cornmeal + molasses (120 fish/m3)15:17 weeksLiver-× [13]
Cornmeal + molasses (240 fish/m3)-×
Glutathione peroxidase (GPx)
FreshwaterOreochromis niloticusGlucose15:18 weeksSerum15:1+ [29]
Cyprinus carpioSugar beet molasses20:110 weeksSerum20:1+ [44]
Sugar20:1-
Corn starch20:1-
Sugar (6 kg/m3)15:149 daysSerum15:1+ [32]
Sugar (12 kg/m3)15:1-
Rice bran20:160 daysSerum-× [33]
Sugarcane molasses-×
Rice bran + sugarcane molasses20:1+
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysGills20:1, 25:1+ [68]
Kidney20:1, 25:1+
Brain15:1, 20:1, 25:1+
Liver20:1+
Gut20:1+
Serum20:1, 25:1+
Carassius auratusAnhydrous glucose10:1, 15:1, 20:1, 25:18 weeksGut10:1, 15:1, 20:1, 25:1+ [79]
Kidney10:1, 15:1, 20:1, 25:1+
Liver15:1, 20:1, 25:1+
Channa argusGlucose10:1, 15:1, 20:18 weeksLiver15:1, + [80]
Intestine10:1, 15:1, 20:1+
SeawaterOreochromis niloticus sp.Cornmeal + molasses (120 fish/m3)15:17 weeksLiver-× [13]
Cornmeal + molasses (240 fish/m3)-×
Glutathione reductase (GR)
FreshwaterOreochromis niloticusGlycerol (140 fish/m3)15:198 daysSerum15:1+ [47]
Glycerol (280 fish/m3)15:1+
Molasses (140 fish/m3)15:198 daysSerum-×
Molasses (280 fish/m3)15:1+
Starch (140 fish/m3)15:198 daysSerum-×
Starch (280 fish/m3)-×
SeawaterOreochromis niloticus sp.Cornmeal + molasses (120 fish/m3)15:17 weeksLiver-× [13]
Cornmeal + molasses (240 fish/m3)-×
Reduced glutathione (GSH)
FreshwaterOreochromis niloticusGlucose
(166 organisms/m3)
15:1120 daysLiver15:1+ [41]
Glucose
(333 organisms/m3)
15:1+
Glucose
(600 organisms/m3)
-×
Glucose10:1, 15:1, 20:1120 daysLiver10:1, 15:1+ [42]
Malondialdehyde (MDA)
FreshwaterOreochromis niloticusGlucose
(166 organisms/m3)
15:1120 daysLiver15:1+ [41]
Glucose
(333 organisms/m3)
15:1+
Glucose
(600 organisms/m3)
-×
Glucose10:1, 15:1, 20:1120 daysLiver10:1, 15:1+ [42]
Cyprinus carpioSugar (6 kg/m3)15:149 daysSerum15:1+ [72]
Sugar (12 kg/m3)15:1-
Rice bran20:160 daysSerum-× [33]
Sugarcane molasses20:1-
Rice bran + sugarcane molasses-×
Clarias gariepinusSucrose15:16 weeksMuscle-× [20]
Glycerol-×
Rice bran-×
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysGills-× [68]
Kidney20:1-
Brain-×
Liver20:1, 25:1-
Gut20:1-
Serum15:1, 20:1, 25:1-
Carassius auratusAnhydrous glucose10:1, 15:1, 20:1, 25:18 weeksGut20:1, 25:1- [79]
Kidney20:1, 25:1-
Liver15:1, 20:1, 25:1-
Channa argusGlucose10:1, 15:1, 20:18 weeksLiver15:1- [80]
Intestine10:1, 15:1, 20:1-
SeawaterOreochromis niloticus sp.Cornmeal + molasses (120 fish/m3)15:17 weeksLiver-× [13]
Cornmeal + molasses (240 fish/m3)-×
+, increased, - decreased, and × no change in survival rate.

5. Immune Responses

The effective microorganisms in biofloc act as immune- and growth-stimulating factors, and the improvement in the immunity of the fish due to biofloc may have a mitigating effect against fatal pathogenic infections [88]. Biofloc carotenoids are known to carry out various bioactive physiological functions including stimulating the fish immune system and providing essential nutrition, and the cell wall components (β-1,3-glucans, LPS, and peptidoglycan) of microorganisms present in biofloc improve the innate immune response of fish [89,90]. Ekasari et al. [10] also found that the consumption of biofloc can induce non-specific immune system stimulation through continuous exposure to microbe-associated molecular patterns (MAMPs) such as β-1,3,-glucans, lipopolysaccharides, and peptidoglycan.
The immune responses of fish raised in the biofloc are demonstrated in Table 5. Macrophages are one of the most primitive phagocytic cells in the non-specific immune system of fish, and macrophage phagocytosis, the process by which a cell engulfs foreign substances (>0.5 μm) into endocytic vesicles named phagosomes, is a major indicator in assessing immune function under various biotic and abiotic factors (including contaminants, pathogens, and genetic variation) [91]. Phagocytic processes include foreign substance detection and recognition, foreign body attachment to phagocytes, foreign particle engulfment or internalization into phagosomes, the fusion of phagosomes with a lysosome, and formation of phagolysosomes (through degranulation of the phagocyte and maturation of compartments through endosomal fusion). Intracellular death and digestion of foreign particles and some phagocyte (dendritic cells and macrophages) uptake and antigen presentation [92] can also occur. Mansour and Esteban [28] reported a significant increase in macrophage phagocytosis of O. niloticus, and this increase indicates an improvement in the innate immune status of fish in biofloc. Fauji et al. [19] also reported a significant increase in phagocytosis in C. gariepinus, and they also suggest that it indicates higher immunity and better health status of fish cultured with biofloc.
Immunoglobulins are major immune molecules that recognize antigens, and they have critical roles in the host destruction of antigens and adaptive immune response responsible for fish immune memory [93]. In addition, immunoglobulins are the main humoral components of specific immunity, and total immunoglobulin concentrations are closely related to fish physiology and pathology [94,95]. Six immunoglobulin isotypes (Ig M, Ig G, Ig A, Ig E, Ig D, and Ig O) have been identified in mammals, but three isotypes (Ig M, Ig D, and Ig T/Z) have been reported so far in teleost [96]. Mansour and Esteban [28] reported a significant increase in total immunoglobulin of O. niloticus cultured with biofloc, and they suggest that this increase was due to the improved immunity provided by the bioactive substances. Verma et al. [45] reported a significant increase in total immunoglobulin in L. rohita, and Bakhshi et al. [35] also reported a significant increase in total immunoglobulin of C. carpio, which was argued to be a result of the components of biofloc having a positive effect on immune parameters by altering the intestinal microbiome, thereby increasing the concentration of immunoglobulins in the serum. Immunoglobulin M (Ig M) is the only component in certain humoral defense systems and plays a critical role in determining and neutralizing foreign antigens such as pathogenic bacteria and viruses [97]. Teleost Ig M is similar to mammalian Ig M in physiological properties, structure, soluble form, and membrane-bound form, and it plays an important role as an immune effector molecule in fish blood as well as fish skin [98]. Kishawy et al. [24] reported a significant increase in Ig M in O. niloticus cultured with biofloc, and the increase was associated with the immunostimulating effect of β-1,3,-glucans, LPS, and peptidoglycans in the cell wall of probiotic bacteria present in biofloc. Ebrahimi et al. [33] reported a significant increase in Ig M in C. carpio cultured with biofloc, which means that the carbon source of biofloc and the energy provided by microbial flocs are effective not only for tissue growth and body maintenance but also for stimulating fish immunity. Yu et al. [80] reported a significant increase in Ig M in C. argus, and Kim et al. [27] also reported a similar significant increase in P. olivaceus, which together indicate that biofloc can act as an immunostimulant.
Lysozyme is an enzyme produced by leukocytes in the blood that lyses bacterial cell walls and stimulates phagocytosis, therefore fighting pathogenic infection and disease [58]. Lysozyme is the first line of defense of fish immunity against various pathogens including bacteria, viruses, and parasites, and its activity in fish can be altered by health, sex, environmental stress, and toxic substances [43]. Mansour and Esteban [28] reported a significant increase in lysozyme in O. niloticus cultured with biofloc, suggesting an improvement in immunity. Many authors have reported this increase, and it has been argued that bioactive compounds that are present in biofloc, such as natural microorganisms, carotenoids, and fat-soluble vitamins, stimulate the fish’s immune response [24,29,30,41,43]. Verma et al. [45] reported a significant increase in lysozyme activity in L. rohita cultured with biofloc, suggesting that breeding fish in a biofloc-based system can induce the enhancement of non-specific immunity. Yu et al. [68,79,80] reported an increase in the activity of lysozyme in many fish species such as O. kaopingensis, C. auratus, and C. argus cultured with biofloc, which means that microbial flocs could be a protein source for the fish immune response.
Myeloperoxidase (MPO), a ferrous lysosomal protein in the myeloid cells of monocytes and neutrophils, is the most abundantly expressed peroxidase in neutrophil granulocytes and liberates hypochlorous acid (HOCl) from hydrogen peroxide (H2O2) and chloride anions (Cl) during the respiratory burst of neutrophils [58]. MPO is widely distributed in the liver, head-kidney, heart, muscle, and intestinal tissues of teleost due to the spread of neutrophil granulocytes, which are highly expressed in head-kidney and spleen tissues [99]. MPO is most abundant in neutrophil primary granules and fuses with phagocyte vesicles to accelerate pathogen destruction, thereby delivering these compounds to invading pathogens. It produces high levels of HOCl to deliver a strong antibacterial response [100]. Many authors reported a significant increase in the MPO of O. niloticus cultured with biofloc, and they suggest that this increase was due to the stimulation or activation of the fish immune system [28,30,73]. Verma et al. [45] found there was an increase in MPO of L. rohita cultured with biofloc, but the degree of stimulation was different depending on the carbon source that produced the biofloc. Although there was a significant decrease in MPO in biofloc made with some carbon sources, other carbon sources showed a significant increase, implying that they have high antibacterial activity through hypochlorous acid production during respiratory bursts. Respiratory burst, a measure of oxygen-dependent defense mechanisms in fish phagocytic cells, is a reaction that occurs in phagocytes to degrade pathogenic bacteria and internalized particles as part of a vital immune response, and the increase in respiratory burst may correlate with increased apoptotic activity against pathogenic bacteria and internalized particles, as the ability of macrophages to kill pathogenic microbes is an important mechanism to protect them against disease in fish [58,101]. Leukocyte respiratory burst activity is measured because phagocytosis was associated with increased oxygen consumption, with the activity also being closely related to inflammatory responses and cytokine release in fish [102]. Mansour and Esteban [28] reported that the respiratory burst activity of O. niloticus cultured with biofloc was significantly increased, which is considered to be due to the stimulation of biofloc-induced fish cell defenses. Haridas et al. [30] reported the same respiratory burst activity and considered it to be a phenomenon of the natural probiotic effect in biofloc. Verma et al. [45] reported an increase in respiratory burst activity of L. rohita cultured with biofloc, and the increase differed depending on the biofloc environment and the carbon source, with the highest respiratory rupture activity being observed in the biofloc made from tapioca. Sontakke et al. [58] reported an increase in respiratory burst activity of C. chanos cultured with biofloc; a result of it acting as an immunostimulant.
This effect is achieved via three pathways, including alternative (independent of the antibody and stimulated directly by bacteria, fungi, viruses, or tumor cells), lectin (stimulated through the binding of ficolins and collectins to carbohydrates present on the surfaces of pathogens) and classical (stimulated when the pattern recognition molecule C1q binds to the CH3 domain(IgM) or CH2 domain(IgG) complexed to antigens). The ACH50 assay (Alternative Complement pathway Hemolytic activity) index is generally used for the analysis of alternative complement activity, and it calculates the volume of serum in sheep or rabbits that is 50% lysed [103,104]. ACH50 is an innate immune system reaction, associated with opsonization, inflammation, and cell membrane attack [105]. Many authors have reported a significant increase in serum ACH50 of O. niloticus and C. carpio cultured with biofloc, meaning that bioactive compounds such as chlorophylls, short-chain fatty acids, amino sugars, phytosterols, bromophenols, carotenoids, and anti-bacterial compounds like poly-β-hydroxybutyrate present in biofloc induce stimulation in fish immunity [28,32,33]. Complement 3 (C3), a critical humoral component in the innate immune response, has a critical function in alerting the host immune system to the presence and clearance of potential pathogens. It is connected to all three pathways that directly lyse pathogenic cells by merging and proceeding through terminal pathways leading to the formation of membrane attack complexes (MAC) [81]. C4 is also a critical humoral component in the innate immune response, and it plays an activating role in the process of MAC formation in the classical and lectin pathway. The covalent tagging of the foreign molecules by C3 or C4 is an important process in complement stimulation, which results in phagocytosis via binding to the complement receptors on phagocytes, or cytolysis via the stimulation of late components [106] Many authors reported a significant increase in C3 in O. niloticus and C. argus cultured with biofloc, and they suggest that this increase indicates an improved immune status in fish [41,42,80].
Table 5. Immune responses of fish species raised in the biofloc in fish aquaculture.
Table 5. Immune responses of fish species raised in the biofloc in fish aquaculture.
SpeciesCarbon SourceC:N RatioPeriodTarget OrgansResponse C:N RatioResponseReference
Phagocytosis
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksMacrophages15:1+ [28]
Rice bran15:1+
Clarias gariepinusTapioca flour
(4 fish/L)
10:120 daysBlood-× [19]
Tapioca flour
(6 fish/L)
-×
Tapioca flour
(8 fish/L)
10:1+
Total immunoglobulin
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksPlasma15:1+ [28]
Rice bran15:1+
Molasses
(15% food reduction) (500 fish/m3)
15:153 daysSkin mucus-× [87]
Molasses
(30% food reduction) (500 fish/m3)
-×
Molasses
(45% food reduction) (500 fish/m3)
-×
Molasses
(100% food reduction)
(500 fish/m3)
15:1-
Molasses
(15% food reduction) (1000 fish/m3)
15:153 daysSkin mucus-×
Molasses
(30% food reduction) (1000 fish/m3)
-×
Molasses
(45% food reduction) (1000 fish/m3)
-×
Molasses
(100% food reduction)
(1000 fish/m3)
-×
Labeo rohitaTapioca15:120 daysPlasma-× [45]
40 days15:1+
60 days15:1+
Wheat15:120 daysPlasma-×
40 days15:1+
60 days15:1+
Corn15:120 daysPlasma-×
40 days15:1+
60 days-×
Sugar bagasse15:120 daysPlasma15:1-
40 days15:1+
60 days-×
Cyprinus carpioSugar beet molasses20:110 weeksSerum20:1+ [44]
Sugar20:1+
Corn starch20:1+
Immunoglobulin M (IgM)
FreshwaterOreochromis niloticusGlycerol15:112 weeksSerum15:1+ [24]
Mannan oligosaccharides15:1+
Cyprinus carpioRice bran20:160 daysSerum20:1+ [33]
Sugarcane molasses20:1+
Rice bran + sugarcane molasses20:1+
Channa argusGlucose10:1, 15:1, 20:18 weeksSerum-× [80]
Kidney15:1, 20:1+
SeawaterParalichthys olivaceusGlucose10:14 monthsPlasma10:1+ [28]
Lysozyme activity
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksPlasma15:1+ [28]
Rice bran15:1+
Sucrose>10:187 daysHepatopancreas-× [25]
Head kidney-×
Serum-×
Glucose15:18 weeksSerum15:1+ [29]
Glucose
(166 organisms/m3)
15:1120 daysLiver15:1+ [41]
Glucose
(333 organisms/m3)
15:1+
Glucose
(600 organisms/m3)
15:1-
Wheat flour
(200 fish/m3)
15:190 daysSerum15:1+ [30]
Wheat flour
(250 fish/m3)
15:1+
Wheat flour
(300 fish/m3)
15:1+
Wheat flour
(350 fish/m3)
15:1+
Glycerol15:112 weeksSerum15:1+ [24]
Mannan oligosaccharides15:1+
Glucose10:1, 15:1, 20:1120 daysLiver10:1, 15:1, 20:1+ [42]
Molasses
(15% food reduction) (500 fish/m3)
15:153 daysSkin mucus-× [87]
Molasses
(30% food reduction) (500 fish/m3)
15:1-
Molasses
(45% food reduction) (500 fish/m3)
15:1-
Molasses
(100% food reduction)
(500 fish/m3)
15:1-
Molasses
(15% food reduction)
(1000 fish/m3)
15:153 daysSkin mucus-×
Molasses
(30% food reduction)
(1000 fish/m3)
-×
Molasses
(45% food reduction) (1000 fish/m3)
15:1-
Molasses
(100% food reduction)
(1000 fish/m3)
15:1-
Labeo rohitaTapioca15:120 daysSerum-× [45]
40 days15:1+
60 days15:1+
Wheat15:120 daysSerum15:1+
40 days15:1+
60 days15:1+
Corn15:120 daysSerum-×
40 days-×
60 days15:1-
Sugar bagasse15:120 daysSerum-×
40 days-×
60 days-×
Cyprinus carpioSugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
Sugar (6 kg/m3)15:149 daysSerum15:1× [32]
Sugar (12 kg/m3)15:1×
Rice bran20:160 daysSerum20:1+ [33]
Sugarcane molasses-×
Rice bran + sugarcane molasses-×
Opsariichthys kaopingensisGlucose15:1, 20:1, 25:128 daysGills20:1+ [68]
Kidney15:1, 20:1 25:1+
Brain20:1+
Liver20:1, 25:1+
Gut15:1, 20:1, 25:1+
Carassius auratusAnhydrous glucose10:1, 15:1, 20:1, 25:18 weeksGut15:1, 20:1, 25:1+ [79]
Kidney15:1, 20:1, 25:1+
Liver20:1, 25:1+
Channa argusGlucose10:1, 15:1, 20:18 weeksSerum10:1, 15:1, 20:1+ [80]
Kidney15:1, 20:1+
Myeloperoxidase (MPO)
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksBlood15:1+ [28]
Rice bran15:1+
Wheat flour
(200 fish/m3)
15:190 daysSerum15:1+ [30]
Wheat flour
(250 fish/m3)
15:1+
Wheat flour
(300 fish/m3)
15:1+
Wheat flour
(350 fish/m3)
-×
Spentwash10:1180 daysSerum10:1+ [73]
Labeo rohitaTapioca15:120 daysSerum15:1- [45]
40 days15:1+
60 days15:1+
Wheat15:120 daysSerum15:1-
40 days-×
60 days15:1+
Corn15:120 daysSerum15:1-
40 days-×
60 days-×
Sugar bagasse15:120 daysSerum15:1-
40 days-×
60 days-×
Respiratory burst activity
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksLeucocytes15:1+ [28]
Rice bran15:1+
Wheat flour
(200 fish/m3)
15:190 daysPhagocytes15:1+ [30]
Wheat flour
(250 fish/m3)
15:1+
Wheat flour
(300 fish/m3)
15:1+
Wheat flour
(350 fish/m3)
15:1+
Labeo rohitaTapioca15:120 daysLeucocytes15:1+ [45]
40 days15:1+
60 days15:1+
Wheat15:120 daysLeucocytes15:1+
40 days15:1+
60 days15:1+
Corn15:120 daysLeucocytes-×
40 days15:1+
60 days15:1+
Sugar bagasse15:120 daysLeucocytes15:1×
40 days15:1+
60 days15:1+
Brackish waterChanos chanosSorghum15:145 daysPhagocytes15:1+ [58]
90 days15:1+
Potato15:145 daysPhagocytes15:1+
90 days15:1+
Yam15:145 daysPhagocytes15:1+
90 days15:1+
Glucose15:145 daysPhagocytes15:1+
90 days15:1+
Alterative complement activity (ACH50)
FreshwaterOreochromis niloticusWheat-milling by-product15:110 weeksPlasma15:1+ [28]
Rice bran15:1+
Cyprinus carpioSugar beet molasses20:110 weeksSerum-× [44]
Sugar-×
Corn starch-×
Sugar (6 kg/m3)15:149 daysSerum15:1× [32]
Sugar (12 kg/m3)15:1+
Rice bran20:160 daysSerum20:1+ [30]
Sugarcane molasses20:1+
Rice bran + sugarcane molasses20:1+
Complement 3 (C3)
FreshwaterOreochromis niloticusGlucose
(166 organisms/m3)
15:1120 daysLiver15:1+ [41]
Glucose
(333 organisms/m3)
15:1+
Glucose
(600 organisms/m3)
15:1-
Glucose10:1, 15:1, 20:1120 daysLiver15:1, 20:1+ [42]
Channa argusGlucose10:1, 15:1, 20:18 weeksSerum10:1, 15:1+ [80]
Kidney15:1+
Complement 4 (C4)
FreshwaterChanna argusGlucose10:1, 15:1, 20:18 weeksSerum10:1, 15:1, 20:1+ [80]
Kidney10:1, 15:1, 20:1+
+, increased, - decreased, and × no change in survival rate.

6. Disease Resistance

In a biofloc environment, various bioactive substances including chlorophyll, polyphenols, carotene, taurine, polysaccharides, phytosterol, and vitamins have unique antagonistic applications against pathogens, thereby suppressing disease outbreaks and improving the immunity of cultured fish [5]. Bacillus, the dominant bacterium in a biofloc environment, is an important probiotic in fish farming, as it enhances the disease resistance and immunity of fish [107]. As effective microorganisms of biofloc compete with pathogenic bacteria, when pathogenic bacteria enter the breeding water, they have limited proliferation when compared to general farms. This is due to competition for dominance with useful microorganisms, thereby reducing damage in fish aquaculture caused by bacterial diseases [73]. These advantages of biofloc mean that antibiotics that affect aquaculture organisms, farm environments, and food hygiene are not used in fish culture using biofloc, and the occurrence of antibiotic-resistant superbacteria caused by the misuse of antibiotics can also be prevented [108]. According to recent studies, biofloc has been proven to have a protective effect against various diseases such as Vibrio harveyi, Aeromonas hydrophila, Edwardsiella tarda, and Streptococcus iniae, all of which cause great damage in fish farms [5,35].
A pathogen challenge test of fish species raised in biofloc in fish aquaculture is shown in Table 6. Liu et al. [41] reported that the survival rate of V. harveyi-infected O. niloticus cultured with biofloc was higher than that of the control group, which is considered to be the result of immune system stimulation. Kishawy et al. [24] suggest that the survival rate of O. niloticus infected with A. hydrophila was higher in the groups cultured with biofloc, and they suggest that using MOS as the carbon source in biofloc improved fish immunity and disease resistance, thereby improving the survival rate. Haridas et al. [30] also reported a high survival rate during aa A. hydrophila infection in O. niloticus cultured with biofloc, which again indicates positive effects on disease resistance. Fauji et al. [19] reported a significant increase in survival rate following infection with A. hydrophila in C. gariepinus cultured with biofloc. Verma et al. [45] reported that the survival rate from an A. hydrophila infection of L. rohita reared with biofloc was higher than that of the control group. Bakhshi et al. [35] similarly reported a high survival rate from an A. hydrophila infection of C. carpio L. cultured with biofloc. Kim et al. [67] reported that the survival rate of P. olivaceus cultured with biofloc with an E. tarda infection was significantly increased, and this was due to the improvement of disease resistance induced by the immunostimulation of biofloc.

7. Conclusions

Fish raised in biofloc can contribute to productivity improvements in the fish culture industry due to the improved growth and high survival rate in fish raised in biofloc. The biofloc-raised fish species demonstrated better physiological indicators and lower stress compared to the control in hematological parameters such as RBC, WBC, Ht, Hb, glucose, cholesterol, total protein, albumin, globulin, triglyceride, AST, ALT, ALP, and cortisol. In antioxidant responses indicated by, e.g., TAC, SOD, CAT, GPx, GR, GSH, and MDA, fish raised in biofloc showed higher antioxidant stimulation, suggesting that they had a stronger ability to remove ROS caused by environmental stress. Immune responses such as phagocytosis, total immunoglobulin, Ig M, lysozyme activity, MPO, respiratory burst activity, ACH50, C3, and C4 were stimulated by a significant amount in various fish species. The fish raised in biofloc had higher disease resistance in challenge tests of major fish diseases such as V. harveyi, A. hydrophila, E. tarda, and S. iniae. In conclusion, various physiological effects and conferred disease resistance of biofloc in fish aquaculture have been confirmed. Our results provide important information in identifying fish health, which is directly related to fish production, and can be used as a standard for applying biofloc to fish aquaculture in the future.

Author Contributions

Conceptualization, Y.-B.Y. and J.-H.C.; methodology, J.-H.K.; validation, J.-H.L. and A.-H.J.; investigation, Y.-B.Y., J.-H.C., J.-H.L. and A.-H.J.; data curation, J.-H.L. and A.-H.J.; writing—original draft preparation, Y.-B.Y. and J.-H.C.; writing—review and editing, J.-H.K.; visualization, A.-H.J.; supervision, J.-H.K. and K.M.L.; funding acquisition, J.-H.K. and K.M.L. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the National Institute of Fisheries Science, Ministry of Oceans and Fisheries, Republic of Korea (R2023041).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The authors appreciate the support of the National Institute of Fisheries Science, Ministry of Oceans and Fisheries, Republic of Korea (R2023041).

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Guerrera, M.C.; Arfuso, F.; Rizzo, M.; Saoca, C.; Fazio, F.; Fortino, G.; Santulli, A.; Piccione, G. Gonadal sexual differentiation of European sea bass (Dicentrarchus labrax, L. 1758) of fingerlings in different size classes. Mar. Freshw. Behav. Physiol. 2016, 49, 347–354. [Google Scholar] [CrossRef]
  2. Arfuso, F.; Guerrera, M.C.; Fortino, G.; Fazio, F.; Santulli, A.; Piccione, G. Water temperature influences growth and gonad differentiation in European sea bass (Dicentrarchus labrax, L. 1758). Theriogenology 2017, 88, 145–151. [Google Scholar] [CrossRef] [PubMed]
  3. Erkinharju, T.; Dalmo, R.A.; Hansen, M.; Seternes, T. Cleaner fish in aquaculture: Review on diseases and vaccination. Rev. Aquac. 2021, 13, 189–237. [Google Scholar] [CrossRef]
  4. Santos, L.; Ramos, F. Antimicrobial resistance in aquaculture: Current knowledge and alternatives to tackle the problem. Int. J. Antimicrob. Agents. 2018, 52, 135–143. [Google Scholar] [CrossRef] [PubMed]
  5. Kim, J.H.; Sohn, S.; Kim, S.K.; Hur, Y.B. Effects on hematological parameters, antioxidant and immune responses, AChE, and stress indicators of olive flounders, Paralichthys olivaceus, raised in bio-floc and seawater challenged by Edwardsiella tarda. Fish Shellfish. Immunol. 2020, 97, 194–203. [Google Scholar] [CrossRef]
  6. Ragasa, C.; Agyakwah, S.K.; Asmah, R.; Mensah, E.T.D.; Amewu, S.; Oyih, M. Accelerating pond aquaculture development and resilience beyond COVID: Ensuring food and jobs in Ghana. Aquaculture 2022, 547, 737476. [Google Scholar] [CrossRef]
  7. Zhao, S.; Zhang, S.; Liu, J.; Wang, H.; Zhu, J.; Li, D.; Zhao, R. Application of machine learning in intelligent fish aquaculture: A review. Aquaculture 2021, 540, 736724. [Google Scholar] [CrossRef]
  8. Liu, H.; Li, H.; Wei, H.; Zhu, X.; Han, D.; Jin, J.; Yang, Y.; Xie, S. Biofloc formation improves water quality and fish yield in a freshwater pond aquaculture system. Aquaculture 2019, 506, 256–269. [Google Scholar] [CrossRef]
  9. Abakari, G.; Luo, G.; Kombat, E.O. Dynamics of nitrogenous compounds and their control in biofloc technology (BFT) systems: A review. Aquacult. Fisheries. 2021, 6, 441–447. [Google Scholar] [CrossRef]
  10. Ekasari, J.; Rivandi, D.R.; Firdausi, A.P.; Surawidjaja, E.H.; Zairin, M., Jr.; Bossier, P.; De Schryver, P. Biofloc technology positively affects Nile tilapia (Oreochromis niloticus) larvae performance. Aquaculture 2015, 441, 72–77. [Google Scholar] [CrossRef]
  11. Kim, J.H.; Kim, S.K.; Hur, Y.B. Temperature-mediated changes in stress responses, acetylcholinesterase, and immune responses of juvenile olive flounder Paralichthys olivaceus in a bio-floc environment. Aquaculture 2019, 506, 453–458. [Google Scholar] [CrossRef]
  12. Diatin, I.; Shafruddin, D.; Hude, N.; Sholihah, M.A.; Mutsmir, I. Production performance and financial feasibility analysis of farming catfish (Clarias gariepinus) utilizing water exchange system, aquaponic, and biofloc technology. J. Saudi Soc. Agric. Sci. 2021, 20, 344–351. [Google Scholar] [CrossRef]
  13. Banuelos-Vargas, I.; de Oca, G.A.R.M.; Martinez-Montano, E.; Perez-Jimenez, A.; Mendoza-Gamboa, O.A.; Estrada-Godínez, J.A.; Hernandez, C. Antioxidant and immune response of juvenile red tilapia (Oreochromis sp.) cultured at different densities in sea water with biofloc plus probiotics. Aquaculture 2021, 544, 737112. [Google Scholar] [CrossRef]
  14. Zhang, M.; Li, Y.; Xu, D.H.; Qiao, G.; Zhang, J.; Qi, Z.; Li, Q. Effect of different water biofloc contents on the growth and immune response of gibel carp cultured in zero water exchange and no feed addition system. Aquac. Res. 2018, 49, 1647–1656. [Google Scholar] [CrossRef]
  15. Deb, S.; Noori, M.T.; Rao, P.S. Application of biofloc technology for Indian major carp culture (polyculture) along with water quality management. Aquac. Eng. 2020, 91, 102106. [Google Scholar] [CrossRef]
  16. Khanjani, M.H.; Alizadeh, M.; Sharifinia, M. Effects of different carbon sources on water quality, biofloc quality, and growth performance of Nile tilapia (Oreochromis niloticus) fingerlings in a heterotrophic culture system. Aquac. Int. 2021, 29, 307–321. [Google Scholar] [CrossRef]
  17. Khanjani, M.H.; Alizadeh, M.; Mohammadi, M.; Sarsangi Aliabad, H. Biofloc system applied to Nile tilapia (Oreochromis niloticus) farming using different carbon sources: Growth performance, carcass analysis, digestive and hepatic enzyme activity. Iran. J. Fish. Sci. 2021, 20, 490–513. [Google Scholar] [CrossRef]
  18. Fauji, H.; Budiardi, T.; Ekasari, J. Growth performance and robustness of African Catfish Clarias gariepinus (Burchell) in biofloc-based nursery production with different stocking densities. Aquac. Res. 2018, 49, 1339–1346. [Google Scholar] [CrossRef]
  19. Dauda, A.B.; Romano, N.; Ebrahimi, M.; Karim, M.; Natrah, I.; Kamarudin, M.S.; Ekasari, J. Different carbon sources affects biofloc volume, water quality and the survival and physiology of African catfish Clarias gariepinus fingerlings reared in an intensive biofloc technology system. Fish. Sci. 2017, 83, 1037–1048. [Google Scholar] [CrossRef]
  20. Haridas, H.; Chadha, N.K.; Sawant, P.B.; Deo, A.D.; Ande, M.P.; Syamala, K.; Sontakke, R.; Lingam, S.S. Growth performance, digestive enzyme activity, non-specific immune response and stress enzyme status in early stages of grey mullet reared in a biofloc system. Aquac. Res. 2021, 52, 4923–4933. [Google Scholar] [CrossRef]
  21. Azim, M.E.; Little, D.C. The biofloc technology (BFT) in indoor tanks: Water quality, biofloc composition, and growth and welfare of Nile tilapia (Oreochromis niloticus). Aquaculture 2008, 283, 29–35. [Google Scholar] [CrossRef]
  22. De Alvarenga, E.R.; Alves, G.F.D.O.; Fernandes, A.F.A.; Costa, G.R.; da Silva, M.A.; Teixeira, E.D.A.; Turra, E.M. Moderate salinities enhance growth performance of Nile tilapia (Oreochromis niloticus) fingerlings in the biofloc system. Aquac. Res. 2018, 49, 2919–2926. [Google Scholar] [CrossRef]
  23. Kishawy, A.T.; Sewid, A.H.; Nada, H.S.; Kamel, M.A.; El-Mandrawy, S.A.; Abdelhakim, T.M.; El-Murr, A.E.I.; Nahhas, E.N.; Hozzein, W.N.; Ibrahim, D. Mannanoligosaccharides as a carbon source in Biofloc boost dietary plant protein and water quality, growth, immunity and Aeromonas hydrophila resistance in Nile tilapia (Oreochromis niloticus). Animals 2020, 10, 1724. [Google Scholar] [CrossRef] [PubMed]
  24. Luo, G.; Gao, Q.; Wang, C.; Liu, W.; Sun, D.; Li, L.; Tan, H. Growth, digestive activity, welfare, and partial cost-effectiveness of genetically improved farmed tilapia (Oreochromis niloticus) cultured in a recirculating aquaculture system and an indoor biofloc system. Aquaculture 2014, 422, 1–7. [Google Scholar] [CrossRef]
  25. Mirzakhani, N.; Ebrahimi, E.; Jalali, S.A.H.; Ekasari, J. Growth performance, intestinal morphology and nonspecific immunity response of Nile tilapia (Oreochromis niloticus) fry cultured in biofloc systems with different carbon sources and input C: N ratios. Aquaculture 2019, 512, 734235. [Google Scholar] [CrossRef]
  26. Wang, G.; Yu, E.; Xie, J.; Yu, D.; Li, Z.; Luo, W.; Qiu, L.; Zheng, Z. Effect of C/N ratio on water quality in zero-water exchange tanks and the biofloc supplementation in feed on the growth performance of crucian carp, Carassius auratus. Aquaculture 2015, 443, 98–104. [Google Scholar] [CrossRef]
  27. Kim, J.H.; Kim, S.K.; Kim, J.H. Bio-floc technology application in flatfish Paralichthys olivaceus culture: Effects on water quality, growth, hematological parameters, and immune responses. Aquaculture 2018, 495, 703–709. [Google Scholar] [CrossRef]
  28. Mansour, A.T.; Esteban, M.Á. Effects of carbon sources and plant protein levels in a biofloc system on growth performance, and the immune and antioxidant status of Nile tilapia (Oreochromis niloticus). Fish Shellfish Immunol. 2017, 64, 202–209. [Google Scholar] [CrossRef]
  29. Long, L.; Yang, J.; Li, Y.; Guan, C.; Wu, F. Effect of biofloc technology on growth, digestive enzyme activity, hematology, and immune response of genetically improved farmed tilapia (Oreochromis niloticus). Aquaculture 2015, 448, 135–141. [Google Scholar] [CrossRef]
  30. Haridas, H.; Verma, A.K.; Rathore, G.; Prakash, C.; Sawant, P.B.; Babitha Rani, A.M. Enhanced growth and immuno-physiological response of Genetically Improved Farmed Tilapia in indoor biofloc units at different stocking densities. Aquac. Res. 2017, 48, 4346–4355. [Google Scholar] [CrossRef]
  31. Klanian, M.G.; Díaz, M.D.; Solís, M.J.S.; Aranda, J.; Moral, P.M. Effect of the content of microbial proteins and the poly-β-hydroxybutyric acid in biofloc on the performance and health of Nile tilapia (Oreochromis niloticus) fingerlings fed on a protein-restricted diet. Aquaculture 2020, 519, 734872. [Google Scholar] [CrossRef]
  32. Adineh, H.; Naderi, M.; Hamidi, M.K.; Harsij, M. Biofloc technology improves growth, innate immune responses, oxidative status, and resistance to acute stress in common carp (Cyprinus carpio) under high stocking density. Fish Shellfish Immunol. 2019, 95, 440–448. [Google Scholar] [CrossRef]
  33. Ebrahimi, A.; Akrami, R.; Najdegerami, E.H.; Ghiasvand, Z.; Koohsari, H. Effects of different protein levels and carbon sources on water quality, antioxidant status and performance of common carp (Cyprinus carpio) juveniles raised in biofloc based system. Aquaculture 2020, 516, 734639. [Google Scholar] [CrossRef]
  34. Tabarrok, M.; Seyfabadi, J.; Salehi Jouzani, G.; Younesi, H. Comparison between recirculating aquaculture and biofloc systems for rearing juvenile common carp (Cyprinus carpio): Growth performance, haemato-immunological indices, water quality and microbial communities. Aquac. Res. 2020, 51, 4881–4892. [Google Scholar] [CrossRef]
  35. Bakhshi, F.; Najdegerami, E.H.; Manaffar, R.; Tukmechi, A.; Farah, K.R. Use of different carbon sources for the biofloc system during the grow-out culture of common carp (Cyprinus carpio L.) fingerlings. Aquaculture 2018, 484, 259–267. [Google Scholar] [CrossRef]
  36. Najdegerami, E.H.; Bakhshi, F.; Lakani, F.B. Effects of biofloc on growth performance, digestive enzyme activities and liver histology of common carp (Cyprinus carpio L.) fingerlings in zero-water exchange system. Fish Physiol. Biochem. 2016, 42, 457–465. [Google Scholar] [CrossRef]
  37. Dauda, A.B.; Romano, N.; Chen, W.W.; Natrah, I.; Kamarudin, M.S. Differences in feeding habits influence the growth performance and feeding efficiencies of African catfish (Clarias gariepinus) and lemon fin barb hybrid (Hypsibarbus wetmorei ♂ × Barboides gonionotus ♀) in a glycerol-based biofloc technology system versus a recirculating system. Aquac. Eng. 2018, 82, 31–37. [Google Scholar] [CrossRef]
  38. Zafar, M.A.; Talha, M.A.; Rana, M.M. Effect of biofloc technology on growth performance, digestive enzyme activity, proximate composition, and hematological parameters of Asian stinging catfish (Heteropneustes fossilis). J. Appl. Aquac. 2021, 34, 1–19. [Google Scholar] [CrossRef]
  39. Fischer, H.; Romano, N.; Renukdas, N.; Egnew, N.; Sinha, A.K.; Ray, A.J. The potential of rearing juveniles of bluegill, Lepomis macrochirus, in a biofloc system. Aquacult. Rep. 2020, 17, 100398. [Google Scholar] [CrossRef]
  40. Mahanand, S.S.; Moulick, S.; Rao, P.S. Optimum formulation of feed for rohu, Labeo rohita (Hamilton), with biofloc as a component. Aquac. Int. 2013, 21, 347–360. [Google Scholar] [CrossRef]
  41. Liu, G.; Ye, Z.; Liu, D.; Zhao, J.; Sivaramasamy, E.; Deng, Y.; Zhu, S. Influence of stocking density on growth, digestive enzyme activities, immune responses, antioxidant of Oreochromis niloticus fingerlings in biofloc systems. Fish Shellfish Immunol. 2018, 81, 416–422. [Google Scholar] [CrossRef] [PubMed]
  42. Liu, G.; Zhu, S.; Liu, D.; Ye, Z. Effect of the C/N ratio on inorganic nitrogen control and the growth and physiological parameters of tilapias fingerlings, Oreochromis niloticus reared in biofloc systems. Aquac. Res. 2018, 49, 2429–2439. [Google Scholar] [CrossRef]
  43. Hwihy, H.; Zeina, A.; Abu Husien, M.; El-Damhougy, K. Impact of Biofloc technology on growth performance and biochemical parameters of Oreochromis niloticus. Egypt. J. Aquat. Biol. Fish. 2021, 25, 761–774. [Google Scholar] [CrossRef]
  44. Bakhshi, F.; Najdegerami, E.H.; Manaffar, R.; Tokmechi, A.; Rahmani Farah, K.; Shalizar Jalali, A. Growth performance, haematology, antioxidant status, immune response and histology of common carp (Cyprinus carpio L.) fed biofloc grown on different carbon sources. Aquac. Res. 2018, 49, 393–403. [Google Scholar] [CrossRef]
  45. Verma, A.K.; Rani, A.B.; Rathore, G.; Saharan, N.; Gora, A.H. Growth, non-specific immunity and disease resistance of Labeo rohita against Aeromonas hydrophila in biofloc systems using different carbon sources. Aquaculture 2016, 457, 61–67. [Google Scholar] [CrossRef]
  46. Puente-Marin, S.; Nombela, I.; Ciordia, S.; Mena, M.C.; Chico, V.; Coll, J.; Ortega-Villaizan, M.D.M. In silico functional networks identified in fish nucleated red blood cells by means of transcriptomic and proteomic profiling. Genes 2018, 9, 202. [Google Scholar] [CrossRef]
  47. Shourbela, R.M.; Khatab, S.A.; Hassan, M.M.; Van Doan, H.; Dawood, M.A. The effect of stocking density and carbon sources on the oxidative status, and nonspecific immunity of Nile tilapia (Oreochromis niloticus) reared under biofloc conditions. Animals 2021, 11, 184. [Google Scholar] [CrossRef]
  48. Shen, Y.; Wang, D.; Zhao, J.; Chen, X. Fish red blood cells express immune genes and responses. Aquac. Fish. 2018, 3, 14–21. [Google Scholar] [CrossRef]
  49. Modesto, K.A.; Martinez, C.B. Effects of Roundup Transorb on fish: Hematology, antioxidant defenses and acetylcholinesterase activity. Chemosphere 2010, 81, 781–787. [Google Scholar] [CrossRef]
  50. Firouzbakhsh, F.; Noori, F.; Khalesi, M.K.; Jani-Khalili, K. Effects of a probiotic, protexin, on the growth performance and hematological parameters in the Oscar (Astronotus ocellatus) fingerlings. Fish Physiol. Biochem. 2011, 37, 833–842. [Google Scholar] [CrossRef]
  51. Kim, J.H.; Kang, J.C. The selenium accumulation and its effect on growth, and haematological parameters in red sea bream, Pagrus major, exposed to waterborne selenium. Ecotox. Environ. Saf. 2014, 104, 96–102. [Google Scholar] [CrossRef]
  52. Kim, J.H.; Kang, J.C. The chromium accumulation and its physiological effects in juvenile rockfish, Sebastes schlegelii, exposed to different levels of dietary chromium (Cr6+) concentrations. Environ. Toxicol. Pharmacol. 2014, 41, 152–158. [Google Scholar] [CrossRef]
  53. Kim, J.H.; Kang, J.C. Changes in hematological parameters, plasma cortisol, and acetylcholinesterase of juvenile rockfish, Sebastes schlegelii supplemented with the dietary ascorbic acid. Aquacult. Rep. 2016, 4, 80–85. [Google Scholar] [CrossRef]
  54. Kim, J.H.; Kang, J.C. Toxic effects on bioaccumulation and hematological parameters of juvenile rockfish Sebastes schlegelii exposed to dietary lead (Pb) and ascorbic acid. Chemosphere 2017, 176, 131–140. [Google Scholar] [CrossRef]
  55. Nageswari, P.; Verma, A.K.; Gupta, S.; Jeyakumari, A.; Mallikarjun Hittinahalli, C. Haematological, serum biochemical and anti-oxidative enzymes responses of sutchi catfish (Pangasianodon hypophthalmus) against Aeromonas hydrophila using various carbon sources in biofloc system. Aquac. Res. 2022, 53, 1851–1861. [Google Scholar] [CrossRef]
  56. Moniruzzaman, M.; Kumar, S.; Das, D.; Sarbajna, A.; Chakraborty, S.B. Enzymatic, non enzymatic antioxidants and glucose metabolism enzymes response differently against metal stress in muscles of three fish species depending on different feeding niche. Ecotox. Environ. Saf. 2020, 202, 110954. [Google Scholar] [CrossRef]
  57. Makaras, T.; Razumienė, J.; Gurevičienė, V.; Šakinytė, I.; Stankevičiūtė, M.; Kazlauskienė, N. A new approach of stress evaluation in fish using β-d-Glucose measurement in fish holding-water. Ecol. Indic. 2020, 109, 105829. [Google Scholar] [CrossRef]
  58. Sontakke, R.; Tiwari, V.K.; Paniprasad, K.; Rani, A.B.; Ande, M.P. Nonspecific immune and antioxidant status of milkfish, Chanos chanos varies with the carbon source used in the biofloc system. J. Exp. Zool. India 2018, 22, 109–118. [Google Scholar]
  59. Kim, J.H.; Kang, J.C. Effects of dietary chromium exposure to rockfish, Sebastes schlegelii are ameliorated by ascorbic acid. Ecotox. Environ. Saf. 2017, 139, 109–115. [Google Scholar] [CrossRef]
  60. Kim, J.H.; Kim, J.Y.; Lim, L.J.; Kim, S.K.; Choi, H.S.; Hur, Y.B. Effects of waterborne nitrite on hematological parameters and stress indicators in olive flounders, Paralichthys olivaceus, raised in bio-floc and seawater. Chemosphere 2018, 209, 28–34. [Google Scholar] [CrossRef]
  61. Kim, J.H.; Kim, S.K.; Hur, Y.B. Hematological parameters and antioxidant responses in olive flounder Paralichthys olivaceus in biofloc depend on water temperature. J. Therm. Biol. 2019, 82, 206–212. [Google Scholar] [CrossRef] [PubMed]
  62. Kim, J.H.; Choi, H.; Sung, G.; Seo, S.A.; Kim, K.I.; Kang, Y.J.; Kang, J.C. Toxic effects on hematological parameters and oxidative stress in juvenile olive flounder, Paralichthys olivaceus exposed to waterborne zinc. Aquacult. Rep. 2019, 15, 100225. [Google Scholar] [CrossRef]
  63. Narra, M.R.; Rajender, K.; Reddy, R.R.; Murty, U.S.; Begum, G. Insecticides induced stress response and recuperation in fish: Biomarkers in blood and tissues related to oxidative damage. Chemosphere 2017, 168, 350–357. [Google Scholar] [CrossRef] [PubMed]
  64. Gholipour Kanani, H.; Nobahar, Z.; Kakoolaki, S.; Jafarian, H. Effect of ginger-and garlic-supplemented diet on growth performance, some hematological parameters and immune responses in juvenile Huso huso. Fish Physiol. Biochem. 2014, 40, 481–490. [Google Scholar] [CrossRef] [PubMed]
  65. Saravanan, M.; Kim, J.Y.; Hur, K.J.; Ramesh, M.; Hur, J.H. Responses of the freshwater fish Cyprinus carpio exposed to different concentrations of butachlor and oxadiazon. Biocatal. Agric. Biotechnol. 2017, 11, 275–281. [Google Scholar] [CrossRef]
  66. Adel, M.; Dawood, M.A.; Shafiei, S.; Sakhaie, F.; Shekarabi, S.P.H. Dietary Polygonum minus extract ameliorated the growth performance, humoral immune parameters, immune-related gene expression and resistance against Yersinia ruckeri in rainbow trout (Oncorhynchus mykiss). Aquaculture 2020, 519, 734738. [Google Scholar] [CrossRef]
  67. Kim, J.H.; Cho, J.H.; Kim, S.R.; Hur, Y.B. Toxic effects of waterborne ammonia exposure on hematological parameters, oxidative stress and stress indicators of juvenile hybrid grouper, Epinephelus lanceolatus ♂ × Epinephelus fuscoguttatus ♀. Environ. Toxicol. Pharmacol. 2020, 80, 103453. [Google Scholar] [CrossRef]
  68. Yu, Z.; Li, L.; Zhu, R.; Li, M.; Wu, L.F. Effects of bioflocs with different C/N ratios on growth, immunological parameters, antioxidants and culture water quality in Opsariichthys kaopingensis Dybowski. Aquac. Res. 2020, 51, 805–815. [Google Scholar] [CrossRef]
  69. Kim, J.H.; Jeong, E.H.; Jeon, Y.H.; Kim, S.K.; Hur, Y.B. Salinity-mediated changes in hematological parameters, stress, antioxidant responses, and acetylcholinesterase of juvenile olive flounders (Paralichthys olivaceus). Environ. Toxicol. Pharmacol. 2021, 83, 103597. [Google Scholar] [CrossRef]
  70. Kim, J.H.; Yu, Y.B.; Choi, J.H. Toxic effects on bioaccumulation, hematological parameters, oxidative stress, immune responses and neurotoxicity in fish exposed to microplastics: A review. J. Hazard. Mater. 2021, 413, 125423. [Google Scholar] [CrossRef]
  71. Kim, J.H.; Kang, J.C. The toxic effects on the stress and immune responses in juvenile rockfish, Sebastes schlegelii exposed to hexavalent chromium. Environ. Toxicol. Pharmacol. 2016, 43, 128–133. [Google Scholar] [CrossRef]
  72. Vargas-Chacoff, L.; Martínez, D.; Oyarzún, R.; Nualart, D.; Olavarría, V.; Yáñez, A.; Bertrán, C.; Ruiz-Jarabo, I.; Mancera, J.M. Combined effects of high stocking density and Piscirickettsia salmonis treatment on the immune system, metabolism and osmoregulatory responses of the Sub-Antarctic Notothenioid fish Eleginops maclovinus. Fish Shellfish Immunol. 2014, 40, 424–434. [Google Scholar] [CrossRef]
  73. Menaga, M.; Felix, S.; Charulatha, M.; Gopalakannan, A.; Panigrahi, A. Effect of in-situ and ex-situ biofloc on immune response of Genetically Improved Farmed Tilapia. Fish Shellfish Immunol. 2019, 92, 698–705. [Google Scholar] [CrossRef]
  74. Kamilya, D.; Debbarma, M.; Pal, P.; Kheti, B.; Sarkar, S.; Singh, S.T. Biofloc technology application in indoor culture of Labeo rohita (Hamilton, 1822) fingerlings: The effects on inorganic nitrogen control, growth and immunity. Chemosphere 2017, 182, 8–14. [Google Scholar] [CrossRef]
  75. Kim, J.H.; Kang, J.C. Oxidative stress, neurotoxicity, and metallothionein (MT) gene expression in juvenile rock fish Sebastes schlegelii under the different levels of dietary chromium (Cr6+) exposure. Ecotox. Environ. Saf. 2016, 125, 78–84. [Google Scholar] [CrossRef]
  76. Kim, J.H.; Kang, J.C. Effects of sub-chronic exposure to lead (Pb) and ascorbic acid in juvenile rockfish: Antioxidant responses, MT gene expression, and neurotransmitters. Chemosphere 2017, 171, 520–527. [Google Scholar] [CrossRef]
  77. Hoseinifar, S.H.; Yousefi, S.; Doan, H.V.; Ashouri, G.; Gioacchini, G.; Maradonna, F.; Carnevali, O. Oxidative stress and antioxidant defense in fish: The implications of probiotic, prebiotic, and synbiotics. Rev. Fish. Sci. Aquac. 2020, 29, 198–217. [Google Scholar] [CrossRef]
  78. Zhang, Y.; Roh, Y.J.; Han, S.J.; Park, I.; Lee, H.M.; Ok, Y.S.; Lee, B.C.; Lee, S.R. Role of selenoproteins in redox regulation of signaling and the antioxidant system: A review. Antioxidants 2020, 9, 383. [Google Scholar] [CrossRef]
  79. Yu, Z.; Li, L.; Zhu, R.; Li, M.; Duan, J.; Wang, J.Y.; Liu, Y.H.; Wu, L.F. Monitoring of growth, digestive enzyme activity, immune response and water quality parameters of Golden crucian carp (Carassius auratus) in zero-water exchange tanks of biofloc systems. Aquacult. Rep. 2020, 16, 100283. [Google Scholar] [CrossRef]
  80. Yu, Z.; Zhao, Y.Y.; Jiang, N.; Zhang, A.Z.; Li, M.Y. Bioflocs attenuates lipopolysaccharide-induced inflammation, immunosuppression and oxidative stress in Channa argus. Fish Shellfish Immunol. 2021, 114, 218–228. [Google Scholar] [CrossRef]
  81. Kim, J.H.; Kang, Y.J.; Kim, K.I.; Kim, S.K.; Kim, J.H. Toxic effects of nitrogenous compounds (ammonia, nitrite, and nitrate) on acute toxicity and antioxidant responses of juvenile olive flounder, Paralichthys olivaceus. Environ. Toxicol. Pharmacol. 2019, 67, 73–78. [Google Scholar] [CrossRef] [PubMed]
  82. Srikanth, K.; Pereira, E.; Duarte, A.C.; Ahmad, I. Glutathione and its dependent enzymes’ modulatory responses to toxic metals and metalloids in fish-a review. Environ. Sci. Pollut. Res. 2013, 20, 2133–2149. [Google Scholar] [CrossRef] [PubMed]
  83. Lee, J.W.; Choi, H.; Hwang, U.K.; Kang, J.C.; Kang, Y.J.; Kim, K.I.; Kim, J.H. Toxic effects of lead exposure on bioaccumulation, oxidative stress, neurotoxicity, and immune responses in fish: A review. Environ. Toxicol. Pharmacol. 2019, 68, 101–108. [Google Scholar] [CrossRef] [PubMed]
  84. Lee, D.C.; Choi, Y.J.; Kim, J.H. Toxic effects of waterborne cadmium exposure on hematological parameters, oxidative stress, neurotoxicity, and heat shock protein 70 in juvenile olive flounder, Paralichthys olivaceus. Fish Shellfish Immunol. 2022, 122, 476–483. [Google Scholar] [CrossRef] [PubMed]
  85. Kim, J.H.; Kang, Y.J.; Lee, K.M. Effects of Nitrite Exposure on the Hematological Properties, Antioxidant and Stress Responses of Juvenile Hybrid Groupers, Epinephelus lanceolatus ♂ × Epinephelus fuscoguttatus ♀. Antioxidants 2022, 11, 545. [Google Scholar] [CrossRef]
  86. Dilmi, A.; Refes, W.; Meknachi, A. Effects of C/N Ratio on Water Quality, Growth Performance, Digestive Enzyme Activity and Antioxidant Status of Nile tilapia Oreochromis niloticus (Linnaeus, 1758) in Biofloc Based Culture System. Turk. J. Fish. Quat. Sci. 2021, 22, TRJFAS19754. [Google Scholar] [CrossRef]
  87. Aliabad, H.S.; Naji, A.; Mortezaei, S.R.S.; Sourinejad, I.; Akbarzadeh, A. Effects of restricted feeding levels and stocking densities on water quality, growth performance, body composition and mucosal innate immunity of Nile tilapia (Oreochromis niloticus) fry in a biofloc system. Aquaculture 2022, 546, 737320. [Google Scholar] [CrossRef]
  88. Doan, H.V.; Lumsangkul, C.; Hoseinifar, S.H.; Tongsiri, S.; Chitmanat, C.; Musthafa, M.S.; El-Haroun, E.; Ringo, E. Modulation of growth, innate immunity, and disease resistance of Nile tilapia (Oreochromis niloticus) culture under biofloc system by supplementing pineapple peel powder and Lactobacillus plantarum. Fish Shellfish Immunol. 2021, 115, 212–220. [Google Scholar] [CrossRef]
  89. Ahmad, I.; Babitha Rani, A.M.; Verma, A.K.; Maqsood, M. Biofloc technology: An emerging avenue in aquatic animal healthcare and nutrition. Aquac. Int. 2017, 25, 1215–1226. [Google Scholar] [CrossRef]
  90. Elayaraja, S.; Mabrok, M.; Algammal, A.; Sabitha, E.; Rajeswari, M.V.; Zágoršek, K.; Ye, Z.; Zhu, S.; Rodkhum, C. Potential influence of jaggery-based biofloc technology at different C:N ratios on water quality, growth performance, innate immunity, immune-related genes expression profiles, and disease resistance against Aeromonas hydrophila in Nile tilapia (Oreochromis niloticus). Fish Shellfish Immunol. 2020, 107, 118–128. [Google Scholar] [CrossRef]
  91. Jensch-Junior, B.E.; Pressinotti, L.N.; Borges, J.C.S.; da Silva, J.R.M.C. Characterization of macrophage phagocytosis of the tropical fish Prochilodus scrofa (Steindachner, 1881). Aquaculture 2006, 251, 509–515. [Google Scholar] [CrossRef]
  92. Esteban, M.Á.; Cuesta, A.; Chaves-Pozo, E.; Meseguer, J. Phagocytosis in teleosts. Implications of the new cells involved. Biology 2015, 4, 907–922. [Google Scholar] [CrossRef]
  93. Fazelan, Z.; Vatnikov, Y.A.; Kulikov, E.V.; Plushikov, V.G.; Yousefi, M. Effects of dietary ginger (Zingiber officinale) administration on growth performance and stress, immunological, and antioxidant responses of common carp (Cyprinus carpio) reared under high stocking density. Aquaculture 2020, 518, 734833. [Google Scholar] [CrossRef]
  94. Kim, J.H.; Kang, J.C. The immune responses in juvenile rockfish, Sebastes schlegelii for the stress by the exposure to the dietary lead (II). Environ. Toxicol. Pharmacol. 2016, 46, 211–216. [Google Scholar] [CrossRef]
  95. Kim, J.H.; Kang, J.C. The immune responses and expression of metallothionein (MT) gene and heat shock protein 70 (HSP 70) in juvenile rockfish, Sebastes schlegelii, exposed to waterborne arsenic (As3+). Environ. Toxicol. Pharmacol. 2016, 47, 136–141. [Google Scholar] [CrossRef]
  96. Teng, Y.; Fu, Q.; Tan, Y.; Ding, Y.; Ding, Y.; Chen, X. Identification and characterization of immunoglobulin T heavy chain in large yellow croaker (Larimichthys crocea). Fishes 2022, 7, 29. [Google Scholar] [CrossRef]
  97. Lee, J.W.; Kim, J.H.; Lee, D.C.; Lim, H.J.; Kang, J.C. Toxic effects on oxidative stress, neurotoxicity, stress, and immune responses in juvenile olive flounder, Paralichthys olivaceus, exposed to waterborne hexavalent chromium. Biology 2022, 11, 766. [Google Scholar] [CrossRef]
  98. Akrami, R.; Gharaei, A.; Mansour, M.R.; Galeshi, A. Effects of dietary onion (Allium cepa) powder on growth, innate immune response and hemato–biochemical parameters of beluga (Huso huso Linnaeus, 1754) juvenile. Fish Shellfish Immunol. 2015, 45, 828–834. [Google Scholar] [CrossRef]
  99. Chen, C.; Yang, B.; Raza, S.H.A.; Zhang, D.; Wu, T.; Zhang, Z.; Ullah, I.; Khan, R.; Yang, G.; Wang, C.; et al. Role of Myeloperoxidase of northern snakehead (Channa argus) in Aeromonas veronii infection. Microb. Pathog. 2019, 135, 103622. [Google Scholar] [CrossRef]
  100. Buchan, K.D.; Prajsnar, T.K.; Ogryzko, N.V.; De Jong, N.W.; Gent, M.V.; Kolata, J.; Foster, S.J.; van Strijp, J.A.G.; Renshaw, S.A. A transgenic zebrafish line for in vivo visualisation of neutrophil myeloperoxidase. PLoS ONE 2019, 14, e0215592. [Google Scholar] [CrossRef]
  101. Kumar, S.; Sahu, N.P.; Pal, A.K.; Choudhury, D.; Yengkokpam, S.; Mukherjee, S.C. Effect of dietary carbohydrate on haematology, respiratory burst activity and histological changes in L. rohita juveniles. Fish Shellfish Immunol. 2005, 19, 331–344. [Google Scholar] [CrossRef] [PubMed]
  102. Biller-Takahashi, J.D.; Takahashi, L.S.; Saita, M.V.; Gimbo, R.Y.; Urbinati, E.C. 2013 Leukocytes respiratory burst activity as indicator of innate immunity of pacu Piaractus mesopotamicus. Braz. J. Biol. 2013, 73, 425–429. [Google Scholar] [CrossRef] [PubMed]
  103. Bavia, L.; Santiesteban-Lores, L.E.; Carneiro, M.C.; Prodocimo, M.M. Advances in the complement system of a teleost fish, Oreochromis niloticus. Fish Shellfish Immunol. 2022, 123, 61–74. [Google Scholar] [CrossRef] [PubMed]
  104. Nayak, S.; Portugal, I.; Zilberg, D. Analyzing complement activity in the serum and body homogenates of different fish species, using rabbit and sheep red blood cells. Vet. Immunol. Immunopathol. 2018, 199, 39–42. [Google Scholar] [CrossRef]
  105. Yousefi, M.; Hoseini, S.M.; Vatnikov, Y.A.; Kulikov, E.V.; Drukovsky, S.G. Rosemary leaf powder improved growth performance, immune and antioxidant parameters, and crowding stress responses in common carp (Cyprinus carpio) fingerlings. Aquaculture 2019, 505, 473–480. [Google Scholar] [CrossRef]
  106. Kuroda, N.; Naruse, K.; Shima, A.; Nonaka, M.; Sasaki, M. Molecular cloning and linkage analysis of complement C3 and C4 genes of the Japanese medaka fish. Immunogenetics 2000, 51, 117–128. [Google Scholar] [CrossRef]
  107. Kim, J.H.; Sohn, S.; Kim, S.K.; Kim, S.R.; Kim, S.K.; Kim, S.M.; Kim, N.Y.; Hur, Y.B. Effects on the survival rates, hematological parameters, and neurotransmitters in olive flounders, Paralichthys olivaceus, reared in bio-floc and seawater by Streptococcus iniae challenge. Fish Shellfish Immunol. 2021, 113, 79–85. [Google Scholar] [CrossRef]
  108. Gutiérrez, S.M.; Dosta, M.D.C.M.; Partida, A.H.; Mejía, J.C.; Rodríguez, G.A.; de Oca, M. Effect of two carbon sources in microbial abundance in a Biofloc culture system with Oreochromis niloticus (Linnaeus, 1758). Int. J. Fish. Aquat. 2016, 4, 421–427. [Google Scholar] [CrossRef]
Figure 1. The mechanisms of antioxidant responses such as SOD, CAT, GPx, GR, GSH in fish (OH : hydroxyl radical, L•: lipid radical, LOOH: lipid hydroperoxide, LPO: lipid peroxidation).
Figure 1. The mechanisms of antioxidant responses such as SOD, CAT, GPx, GR, GSH in fish (OH : hydroxyl radical, L•: lipid radical, LOOH: lipid hydroperoxide, LPO: lipid peroxidation).
Antioxidants 12 00398 g001
Table 6. Pathogen challenge test of fish species raised in the biofloc in fish aquaculture.
Table 6. Pathogen challenge test of fish species raised in the biofloc in fish aquaculture.
SpeciesPathogen (Strain)CFUCarbon SourceC/N RatioPeriodResponse C/N RatioResponseReference
Survival rates
FreshwaterOreochromis niloticusVibrio harveyi4 × 108 CFU/mLGlucose
(166 organisms/m3)
15:114 days15:1+ [41]
Glucose
(333 organisms/m3)
15:1+
Glucose
(600 organisms/m3)
-×
Aeromonas hydrophila (ATCC 7966)3 × 108 CFU/mLMannan oligosaccharides + plant-protein-based diet15:13 days15:1+ [24]
Mannan oligosaccharides + fish-protein-based diet15:1+
Glycerol + plant-protein-based diet15:1+
Glycerol + fish-protein-based diet15:1+
Aeromonas hydrophila (ATCC 7966)3 × 108 CFU/mLMannan oligosaccharides + plant-protein-based diet15:17 days15:1+
Mannan oligosaccharides + fish-protein-based diet15:1+
Glycerol + plant-protein-based diet15:1+
Glycerol + fish-protein-based diet15:1+
Aeromonas hydrophila (ATCC 7966)106 CFU/mLWheat flour
(200 fish/m3)
15:13 days15:1+
(83.33%)
[30]
Wheat flour
(250 fish/m3)
15:1+
(83.33%)
Wheat flour
(300 fish/m3)
15:1+
(75%)
Wheat flour
(350 fish/m3)
15:1+
(62.5%)
Clarias gariepinusAeromonas hydrophila106 CFU/mLTapioca (4 fish/L)10:17 days10:1+ [19]
Tapioca (6 fish/L)10:1+
Tapioca (8 fish/L)10:1+
Labeo rohitaAeromonas hydrophila (ATCC 7966)1.8 × 107 CFU/mLTapioca15:114 days15:1+ [45]
Wheat15:1+
Corn15:1+
Sugar bagasse15:1+
Cyprinus carpioAeromonas hydrophila (ATCC 897)1.1 × 107 CFU/mLSugar beet molasses15:114 days15:1+ [44]
Sugar15:1+
(50%)
Corn starch15:1+
(50%)
SeawaterParalichthys olivaceusEdwardsiella tarda
(FP 5060)
6.61 × 104 CFU/g fish--7 days-× [5]
6.61 × 105 CFU/g fish-+
(100%)
6.61 × 106 CFU/g fish-+
(33%)
6.61 × 107 CFU/g fish-+
(33%)
Streptococcus iniae
(FP 5228)
3.36 × 106 CFU/g fishGlucose10:196 h10:1+
(100%)
[70]
3.36 × 107 CFU/g fish10:1+
(80%)
3.36 × 108 CFU/g fish10:1+
(70%)
3.36 × 109 CFU/g fish10:1×
(20%)
+, increased, - decreased, and × no change in survival rate.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Yu, Y.-B.; Choi, J.-H.; Lee, J.-H.; Jo, A.-H.; Lee, K.M.; Kim, J.-H. Biofloc Technology in Fish Aquaculture: A Review. Antioxidants 2023, 12, 398. https://doi.org/10.3390/antiox12020398

AMA Style

Yu Y-B, Choi J-H, Lee J-H, Jo A-H, Lee KM, Kim J-H. Biofloc Technology in Fish Aquaculture: A Review. Antioxidants. 2023; 12(2):398. https://doi.org/10.3390/antiox12020398

Chicago/Turabian Style

Yu, Young-Bin, Jae-Ho Choi, Ju-Hyeong Lee, A-Hyun Jo, Kyung Mi Lee, and Jun-Hwan Kim. 2023. "Biofloc Technology in Fish Aquaculture: A Review" Antioxidants 12, no. 2: 398. https://doi.org/10.3390/antiox12020398

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop