Background
There are over 100 different species of puffers in the world (Bai et al. 1999). Among them, tiger puffer, Takifugu rubripes, and river puffer, Takifugu obscurus, are the main culture species. River puffer is distributed in the south-western and the south-eastern seawaters of Korea and China, respectively (Kato et al. 2005). River puffer moves from sea to river for reproduction during the spawning season of May to June in Korea. Therefore, it has typical anadromous life history (Yang and Chen 2004). River puffer is one of the promising cultured fish species in South Korea because of its desirable taste and high market price (Ministry of Oceans and Fisheries 2013).
The current commercial culture practice involves the growing of fingerlings with a size of 2–5 g using floating net cages along the coast or indoor recirculating aquaculture system (RAS). River puffer takes 30 months to grow to marketable size, 400 g. One of the most serious problems in the aquaculture of river puffer is the extremely low productivity that is linked with high mortalities from outbreaks of parasitic diseases as shown in tiger puffer (Kikuchi et al. 2006). Survival through the production period is estimated to be less than 50 %, and prospects for developing methods for the prevention and treatment of diseases remain as a major challenge faced by aquaculture enterprise. Nevertheless, the river puffer is a promising candidate for aquaculture production because of its high market price being more than four times that of olive flounder and rock fish (Ministry of Oceans and Fisheries 2013).
In recent years, a new production technology, based on mixed biofloc communities, has been implemented in shrimp and tilapia production because they feature high production yield, water quality control, and feed protein recycling simultaneously in the same culture unit (Avnimelech 2006; Crab et al. 2007; Little et al. 2008). Such units are known as intensive zero-exchange systems (BFT), and they utilize direct carbon inputs (sugar or molasses) to promote the growth of biofloc communities (McIntosh 2001; Burford et al. 2004). Mixed biofloc communities remove ammonia-nitrogen from the water and assimilate it directly into bacterial biomass. Containing as much as 34 % crude protein (Tacon et al. 2002), this bacterial biomass has been shown to contribute substantially to fish nutrition, thereby potentially deducing feed costs, lowering production costs, and improving the overall economics of the system (Moss 2002; Samocha et al. 2004; Azim and Little 2008). This also reduces equipment and energy costs for the production system by eliminating the need for external components such as biofiltration, disinfection through ultraviolet light or ozonation, and possibly solid filtration.
Key biological parameters, such as nitrogenous waste levels, effects of water temperature, and impacts of stocking density on growth, and proper feed composition need to be determined for a specific species in order to develop a profitable production system (Kikuchi et al. 2006). Previous investigations on the river puffer, however, have focused mainly on the development of larvae and juvenile, reproductive physiology, and seed production (Jang et al. 1996; Park et al. 1997; Son et al. 2001; Yang and Chen 2004; Kato et al. 2005; Yang and Chen 2006). We confirmed that BFT tank (217 %) showed a higher weight gain than the running seawater tank (164 %) in a preliminary study where 5-g-size river puffers were carried out in BFT tank and running seawater tank for 8 weeks (unpublished data). However, information for developing a cost-effective, zero-exchange system for this species is still scarce. Therefore, the objective of the present study was to evaluate the effects of feeding frequency, water temperature, and stocking density on the growth of river puffer in non-exchange water mixed biofloc community systems.
Methods
River puffers produced by Chungcheongnam-do Fishery Research Institute were reared with commercial diet (Woosong, Daejeon, South Korea) at 20 °C until the start of the experiments. The experiments were conducted in six circular concrete tanks (two tanks have an inner diameter of 6 m and height of 1 m, and four tanks have an inner diameter of 3 m and height of 0.8 m) illuminated by 100-lx fluorescent light during the day (07:00–19:00). Each tank was filled with 20-psu seawater and was aerated and agitated continuously using pipe diffusers connected to an air pump. Fish (average weight of 13 ± 4.8 g) were stocked in each tank with an initial stocking density of approximately 2 kg/m3. Fish were grown without intentional water exchange until the end of feeding trials and were fed twice daily at 09:00 and 17:00 with floating commercial feed containing 45 % crude protein (Woosong, Daejeon, South Korea) at 2 % of total fish weight per day. Molasses (44 % C) was added in each tank as an external carbon source to be the estimated C:N ratio of 15 (Avnimelech 2007). The pH was maintained between 7 and 8, and alkalinity was kept between 100 and 150 mg/L CaCO3 by periodic addition of NaHCO3. Dissolved oxygen concentration was maintained greater than 4.0 mg/L. After 50 days of rearing experiments, feeding trials were conducted by installing plastic cages in each rearing tank. A tight net of 10 cm was lined inside the plastic cages to prevent feed loss through the wall and bottom of the cages.
The effect of temperature on the rate of the physiological processes is generally expressed as Q10, where
R1 and R2 are specific growth rate (SGR) at a higher and lower temperature, respectively, and T1 and T2 are the higher and lower temperatures, respectively.
Throughout the experimental period, water temperature, salinity, dissolved oxygen (DO), and pH were measured daily at 08:00–10:00 h using YSI 556 (YSI, Inc., Yellow Springs, USA). Water samples (50 mL) were collected twice a week at 14:00 h from each tank. Half of the water sample was analyzed spectrophotometrically for total ammonia-nitrogen (TAN) and nitrite nitrogen (NO2–N) following the Standard methods for the examination of water and wastewater (APHA 1998); the remaining half was filtered under vacuum pressure through predried and preweighed GF/C filter paper. The filter paper containing suspended materials was dried at 105 °C in an oven until constant weight, and the dried sample was weighed to 0.01 mg. The weight difference and the total suspended solids (TSS) were calculated. Alkalinity was determined twice a week by titration (Hach digital titrator, Hach, Loveland, CO, USA).
All data were subjected to one-way ANOVA using SPSS for Windows (release 14.0). When a significant treatment effect was observed, Duncan’s multiple range test was used to compare means. Treatment effects were considered significant at P ≤ 0.05.
The effect of feeding frequency on the growth of river puffer was examined with fish of 10 and 40 g in initial body weight. Thirty and 20 fish with average body weight of 10 and 40 g, respectively, were stocked in plastic cages. Plastic cages (0.5 × 0.4 × 0.3 m) were placed in a tank (inner diameter of 6 m, height of 1 m). Fish were fed floating commercial pellet feed one, two, three, and five meals per day to apparent satiation by hand. Each feeding group was triplicated, and the experiment lasted for a period of 8 weeks. Any uneaten food was collected, and feed intake was calculated for each meal as feed provided minus feed waste. Feeding was conducted between 07:30 and 08:00 for the once daily feeding; 07:30 and 08:00 and 17:30 and 18:00 for the twice daily feeding; 07:30 and 08:00, 12:30 and 13:00, and 17:30 and 18:00 for the three times feeding; and 07:30 and 08:00, 10:00 and 10:30, 12:30 and 13:00, 15:00 and 15:30, and 17:30 and 18:00 for the five times feeding. Water temperature was maintained at 25 ± 1 °C.
The effect of water temperature on the growth of river puffer was examined with fish of 10 and 40 g in initial body weight. Fish were stocked in plastic cages (0.5 × 0.4 × 0.3 m) in four rearing experiment tanks (inner diameter of 3 m, height of 0.8 m), and water temperature of rearing tanks was controlled using a heat pump at 15 ± 1, 20 ± 1, 25 ± 1, and 30 ± 1 °C. Thirty fish of 10-g size and 20 fish of 40-g size were distributed randomly to each plastic cage and were fed floating commercial pellet feed in triplicate groups at twice a day to apparent satiation each by hand for 8 weeks. Prior to the rearing experiment, fish were acclimated to each experimental temperature during a week.
The effect of stocking density on the growth of river puffer was studied using two size groups, 10 and 40 g. Fish averaging 10 g were randomly distributed to floating plastic cages 0.4 × 0.17 × 0.3 m in a group of 8, 16, 24, and 40 at a density of 4, 8, 12, and 20 kg/m3, respectively. Fish in the second size group with average weight of 40 g were distributed to floating plastic cages of 0.6 × 0.45 × 0.3 m in a group of 6, 12, 18, and 30 fish at a density of 3, 6, 9, and 15 kg/m3, respectively. The plastic cages were randomly assigned to triplicate groups of each stocking density in the experimental tank (inner diameter of 6 m, height of 1 m). Fish in both size groups were fed floating commercial feed twice a day to apparent satiation for 8 and 12 weeks, respectively. Water temperature was kept at 25 ± 1 °C.
Results
Water quality parameters of different experimental groups are shown in Table 1. The biofloc development was observed in terms of total suspended solids (TSS). The TSS gradually increased during the experiment. Bioflocs were observed as brown in color and were composed of suspended organic particles in the form of flocculated aggregates, which were colonized by a number of heterotrophic bacteria, microalgae, and protozoa. All the water quality parameters in the six experimental tanks were found within suitable ranges for river puffer culture throughout the experimental period.
Means and standard deviations of triplicate for each experimental group
The growth of river puffer reared at different daily feeding frequencies is shown in Table 2. In both the 10- and 40-g size groups, the final body weight, daily feed consumption, and weight gain of fish fed one meal per day were significantly lower than those of fish fed five meals per day (P < 0.05). However, there were no significant differences in the final body weight, daily feed consumption, and weight gain among fish fed two, three, and five meals per day. Feed efficiency of the 10-g-size fish fed one meal per day was significantly lower than that of similar-sized fish fed two, three, and five meals per day (P < 0.05). However, there was no significant difference in feed efficiency among treatments for the 40-g size group. There was no significant difference in survival among treatments for both the 10- and 40-g size groups.
Means and standard deviations of triplicate for each experimental group. For each body weight group, values in the same column having the same superscript are not significantly different (P < 0.05)
1DFC = daily feed consumption: (final body weight − initial body weight)/[(final body weight + initial body weight)/2 × feeding days] × 100
2Feed efficiency: (weight gain/feed intake) × 100
Table 3 shows the average feed consumption for the 10-g-size river puffer in response to the number of daily feedings during the 8-week feeding experiment. Total feed consumption increased with increasing daily feeding frequency. However, it did not differ among the groups that were fed two, three, and five meals per day. Feed consumption at the first feeding (07:30 to 08:00) for groups that were fed three and five meals per day was almost equal and was much smaller than that for the one and two meals per day feeding groups. For the groups that were fed three and five meals per day, feed consumption on and after the second feeding was much smaller than that of the first and was almost constant at each of the other feeding times, about 125 g for the group fed three meals per day and 78 g for the group fed five meals per day. Similar trends were observed for the remainder of the experimental period for the 10-g size group as well as the 40-g size group.
Data are the total feed consumption of each cage during the 8-week feeding experiment. Means and standard deviations of triplicate for each experimental group. Values in the same column having the same superscript are not significantly different (P < 0.05)
The effects of water temperature on the growth of river puffer are shown in Table 4. The final body weight, weight gain, specific growth rate, and feed efficiency increased with raising water temperature up to 25 °C and drastically decreased at 30 °C for both fish sizes. Survival rate was observed to be lower in fish reared at 20 and 30 °C. However, the mortalities were apparently not the result of parasites or of a bacterial disease. The observed Q10 of SGR decreased with raising water temperature from 5.04 (temperature interval, 15–20 °C) to 0.66 (25–30 °C) for the 10-g-size fish and from 4.98 to 0.31 for the 40-g-size fish.
Means and standard deviations of triplicate for each experimental group. For each body weight group, values in the same column having the same superscript are not significantly different (P < 0.05)
1Specific growth rate: [(ln final wt. − ln initial wt.)/days] × 100
2Refer to Table 1
The effects of stocking density on the growth of river puffer are shown in Table 5. The final body weight for initial stocking densities of 4, 8, and 12 kg/m3 was significantly higher than that of 20 kg/m3 for the 10-g-size fish, and the final stocking density reached 10.1, 19.2, 28.7, and 39.9 kg/m3, respectively. For the 40-g-size fish, the final body weight for initial stocking densities of 3 and 6 kg/m3 was significantly higher than that of 9 and 15 kg/m3 and the final stocking density reached 7.38, 13.5, 17.1, and 27.5 kg/m3, respectively (P < 0.05). In both groups, weight gain tended to decrease with increasing stocking density and survival showed no significant difference among groups.
For each body weight group, values in the same column having the same superscript are not significantly different (P < 0.05)
1Refer to Table 1
Discussion
The results of this study indicated that the growth rate and feed consumption of the river puffer, T. obscurus (between 10 and 40 g), fed daily multiple diets seem to be higher than those of fish provided with a single meal. Numerous experiments have been carried out on feeding frequency in several kinds of aquaculture species (Kikuchi et al. 2006; Flood et al. 2012; Zhao et al. 2014; Kousoulaki et al. 2015), but it is difficult to make general conclusions on optimal feeding frequencies as each study has different conditions, species, and life stages of fish (Kousoulaki et al. 2015). High feeding frequency has been reported to obtain high growth by increasing feed consumption in most species (Schnaittacher et al. 2005; Seo and Lee 2008; Zhao et al. 2014). The present study was also consistent with this opinion. Different results have also reported that the highest feeding frequency did not gain the most weight in yellowtail flounder, a species with small stomachs and relatively long intestines, due to the short interval between meals (Dwyer et al. 2002). When the interval between meals is short, the food passes through the digestive tract more quickly, resulting in a less effective digestion (Zhao et al. 2014).
The effects of water temperature on the growth of fish have been examined with several kinds of fish such as the olive flounder (Fonds et al. 1995), channel catfish (Buentello et al. 2000), sea bass (Ruyet et al. 2004), parrot fish (Kim et al. 2008), and turbot (Ham et al. 2003). Generally, the growth of fish increases with raising water temperature up to a certain level and then decreases at higher temperatures as was observed in the current study and reported for other fishes (Jobling 1994a). It has also been reported that the optimum temperature for growth tended to decrease with the age of the fish (Björnsson et al. 2001; Kikuchi et al. 2006). In the current study, the optimum temperature for the growth of river puffer less than 50 g in body weight is around 25 °C. Further research will be required with larger size fish in order to determine the effective temperature regimen needed for the production of river puffer because the commercial size of river puffer at harvest is more than 400 g in Korea.
The Q10 of SGR obtained in the current study tended to decrease with raising water temperature and was consistent with what was reported by Jobling (1994b). The values in the same temperature range were similar for fish between 10- and 40-g initial body weight and were not largely affected by the fish size, although SGR was considerably different.
In the effects of stocking density, the numbers of fish were held constant for the duration of the experiment, and so stocking density was allowed to increase with time because of the growth of fish. Judging from the final biomass per cage, the maximum stocking densities of river puffer with BFT tanks are estimated to be more than 28 kg/m3 for fish of 24-g body weight and decreased to about 13 kg/m3 for the 90-g-size fish. The growth of river puffer in our study was affected by stocking density. Similar results have been European sea bass (Papoutsoglou et al. 1998), rock fish (Oh et al. 2013), and Amur sturgeon (Ni et al. 2014). Kikuchi et al. (2006) reported that the relationship between stocking density and growth of fish may not be uniformly positively or negatively linear for a given species. In our study, mortality showed no significant difference among different stocking densities in both the 10- and 40-g size groups. Similarly, many studies have not found any significant effects of density on survival (Gomes et al. 2006; Rafatnezhad et al. 2008; Ni et al. 2014). Kikuchi et al. (2006) reported that injuring of caudal fin was observed at high stocking densities of 8, 20, and 10 kg/m3 for 8-, 13-, and 100-g-size tiger puffers, respectively. In our study, no injury was observed in both size groups. It may be for the reason that tiger puffer has more interspecific aggression than river puffer. Meanwhile, previous studies have reported that stocking density affected skeletal anomalies (Boglione et al. 2009), metamorphosis (Hosfeld et al. 2009), sex ratios (Saillant et al. 2003), gonad development Claudia et al. 2004, egg production (Peck and Holste 2006), skin pigmentation (Doolan et al. 2008), and survival (Tagawa et al. 2004) on various fishes.
Conclusions
In the present study, the effects of feeding frequency, water temperature, and stocking density on the growth of river puffer were examined by the use of fingerlings of 10 and 40 g with the objective of developing effective techniques for producing river puffer in zero-exchange mixed biofloc community systems. The results of the current study showed that keeping water temperature around 25 °C, stocking density less than 15 kg/m3, and feeding frequency of three meals per day are suitable conditions for the production of river puffer when starting with fish that are between 10 and 90 g in body weight. These parameters, however, still require additional work as the suitable market size for river puffer in Korea is about 400 g, and the results obtained in this study did not cover the full size range for commercial-scale production. The results of the current study are a major first step in defining the culture parameters that are needed to establish rearing conditions of river puffer in zero-exchange mixed biofloc community systems. Further research will be necessary to understand the influence of growth on water quality control and other size classes of river puffer.
