Eff ects of f lorfenicol exposure on growth, development and antioxidant capacity of f lounder Paralichthys olivaceus larvae at diff erent developmental stages*

GUO Rui , ZHANG Yingqi , ZHANG Xianyu , ZHANG Qian , , CHENG Rui MD MOSTAFIZUR Rahman , LIU Ying

1 College of Marine Science and Environment, Dalian Ocean University, Dalian 116023, China

2 Liaoning Aquacultural Engineering R&D Center, Dalian 116023, China

Abstract Antibiotics are widespread in various environmental media, and may pose a potential threat to aquatic ecosystems and non-target aquatic organisms. Florfenicol (FLO) is one of the most commonly used antibiotics in aquaculture, and extensively used to substitute chloramphenicol with its strong sterilization and low adverse eff ect. In this study, f lounder Paralichthys olivaceus, an important economic f ish species in seawater was used as an experimental subject. Five exposure concentrations of FLO (including environmentrelated concentrations) were set at 0, 0.01, 0.1, 1, and 10 mg/L. Eff ects of FLO exposure for 168 h on growth and development, motor behavior, antioxidant enzyme activity, malondialdehyde (MDA) content,and thyroid hormone level of P. olivaceus larvae were studied in pre-larvae (1 dpf) and post-larvae (20 dpf).The results show that the short-term FLO exposure could promote the larvae growth to some degrees, but inhibit them as the exposure time prolonged. For pre-larvae, FLO at 0.01 mg/L could stimulate the motor nerve system and increase the swimming ability, but inhibited it at 1 mg/L. With the increasing dosage of FLO, the superoxide dismutase (SOD) and MDA contents were elevated, reaching the maximum in the 1 mg/L FLO group. The pre-larvae were more sensitive than the post-larvae to FLO in the environment, and the growth and immune resistance could be damaged with long exposure. Post-larvae were more tolerant to external pollutants, FLO at 1 mg/L could promote the motor behavior and reduce SOD and MDA contents.Therefore, FLO can be used as an antibiotic at a proper concentration but as a drug to prevent disease in a long-term way.

Keyword: f lorfenicol; P aralichthys olivaceus larvae; growth and development; motor behavior; antioxidant capacity

1 INTRODUCTION

Antibiotics have been extensively used in the prevention and treatment of human and animal diseases, and in the feed additives to promote animal growth in husbandry and aquaculture. Due to their pervasive application, antibiotics have been detected in various aquatic environments matrices, with detected concentrations ranging from nanograms per liter to micrograms per liter (Alonso and Camargo, 2009;Bio?i? et al., 2017). Among many antibiotics, f lorfenicol(FLO) is one of the antibiotics approved to be used in aquaculture by the Food and Agriculture Organization(FAO) as the replacement of chloramphenicol (Serrano,2005). FLO may inhibit a variety of aerobic and anaerobic microorganisms and has been commonly used in the treatment of bacterial diseases, such as f ish streptococcosis, bacterial cold-water disease, enteric septicemia etc. In 2016, approximately 1 000 tons of FLO were used in agriculture and medicine in China(Zhang et al., 2015), of which most ended up in the water environment. FLO is pseudo-persistently existed in the aquatic environment because of their physicochemical stability and hard photo-degradation under vis-light (λ=300-800 nm). Reportedly, FLO was detected extensively in a range of 8-937.21 ng/L near f ish farms, and 29.8-11 103 μg/L in the coastal aquacultural area of Dalian, NE China (S?rensen and Elb?k, 2004; Ye et al., 2008).

The long-term existence of antibiotics in aquatic environment may pose a potential threat to the ecosystem, posing toxic eff ects on non-target aquatic organisms, resulting in growth and development abnormality, reproductive dysfunction, physiological function instability, and oxidative stress (Botelho et al., 2015). Many previous studies demonstrated that antibiotics could promote the growth and development of f ish at a low dose, while it may arouse a safety risk to the animals in a long run,especially during the developmental stage.Sulfamethazine at 0.2, 20, and 2 000 mg/L exposed to zebraf ish embryos inhibited the hatching rates and the body length of larvae, and increased the malformation and the heartbeat (Yan et al., 2018).

An acute exposure of FLO was proven toxic to shrimpPenaeusvannameiat diff erent larval stages and juvenile abaloneHaliotisdiscus, i.e., in the LC50of 64 mg/L (24 h) and 100 mg/L (48 h) for nauplius and mysis larvae, and 163 mg/L (96 h) for juvenile abalone. In addition, FLO could inhibit the immune response and antioxidant defense ability; the phagocytosis and lymphocyte proliferation were suppressed in the blood of FLO-fed rainbow trout for 10 days (Lundén et al., 2002; Caipang et al., 2009).

Aquatic animals in early developmental stages are sensitive to environmental contaminants, especially for a f ish in metamorphosis (Hopkins et al., 2006).Japanese f lounder,Paralichthysolivaceus, is an important maricultural f ish (Zhao et al., 2018), and has three developmental stages in post-embryonic period, i.e., pre-larvae, post-larvae, and juveniles.Dramatic morphological changes appear in 20-30 days after hatching (dah), such as right-eye migration,which is closely related to thyroid homeostasis regulated by hypothalamic-pituitary-thyroid (HPT)axis (Yue et al., 2017).

In this study, to elucidate potential eff ects of FLO on the early development of the f ish, pre-larval and post-larval f lounders were used to assess the potential risk of FLO in the aspects of growth and development,motor behavior, and immune resistance, to determine the safe range of FLO application, and to provide a theoretical basis and standard for the scientif ic and rational use of FLO in marine aquaculture.

2 MATERIAL AND METHOD

2.1 Experimental animals

Fertilized eggs of Japanese f lounder (P.olivaceus)were obtained from the Fugu Fish Farm, Dalian,China. Eggs were incubated in aquaria (640 mm×420 mm×355 mm) with sand-f iltered seawater(salinity 32.2±0.05, pH 7.2±0.1). During acclimatization, water temperature and photoperiod were maintained at 17±1°C and 14 h L:10 h D,respectively. Air pump was used to aerate and maintain dissolved oxygen above 6.7±0.05 mg/L.

2.2 Experimental design

The experiment was executed in two diff erent developmental stages of larvae: the pre-larvae (1 day post-fertilization, dpf) and the post-larvae (20 dpf).Five exposure concentrations of FLO (including environment-related concentrations) were set at 0, 0.01,0.1, 1, and 10 mg/L, in triplication for each concentration.Sixty healthyP.olivaceuswere randomly selected and cultured in 220 mm×150 mm×180 mm glass aquarium containing 3-L FLO (purity ＞98%, purchased from Shandong Yakang Pharmaceutical Co., Ltd.) solution at corresponding concentrations. Larvae were reared with rotifers (Brachionusrotundiformis) 3 times a day from 3 dpf, ensuring that the density was maintained at 5-6 rotifers/mL in the culture water. After 15 dpf brine shrimp (Artemianauplii) were added as food and maintained the density above 5-6 shrimps/mL.To keep the constant exposure concentrations, half of the experimental solution in aquaria was renewed daily, and dead individuals were removed every day to maintain water quality.

2.3 Detection of the body length and heart rates

For each group, 9 larvae were selected randomly at 0, 96, and 168 h after FLO exposure at early and late developmental stages. After anesthetization with MS-222, morphological changes of larvae in body length and heart rates were observed with a stereo microscope(Nikon, 745T/SMZ1000). No signif icant deaths were observed in both control and treatment groups.

2.4 Spontaneous behavior analysis

Fig.1 Eff ect of FLO on the growth rate of pre-larvae (a) and post-larvae (b)

The pre- and post- larvae in FLO for 168 h were used for spontaneous behavior analysis. For each experimental group, 9 larvae were randomly selected,and vertically recorded for 30 min in 100-mL culture dishes. A video tracking system (Noldus, EthoVision XT) was used to record the spontaneous behavior trajectory ofP.olivaceusat diff erent development stages. Meanwhile, the swimming distance, movement speed, and activity were analyzed.

2.5 Elisa analysis

Superoxide dismutase (SOD) activity, contents of malondialdehyde (MDA), triiodothyronine (T3), and thyroxine (T4) were detected at 168 h after FLO exposure for both pre- and post- larvae with the commercial kits (Nanjing Jiancheng Bioengineering Institute). As the larvae were too small to collect blood, 30 larvae from each group were stored at -80°C for the use. Later, the larvae were homogenized with physiological saline in a ratio of weight (g)： volume(mL)=1：9 by ultrasonic cell disrupter system (Scientz,JY92-IIN) on ice. The homogenate was centrifuged at 3 000 r/min for 10 min at 4°C to obtain supernatant,then it was detected by microplate reader (Tecan,Inf inite 200 Pro) as per the instruction. Protein concentrations were determined using bicinchoninic acid (BCA) protein kit. The results are presented on a protein basis. SOD activity was calculated by Eq.1,MDA content by Eq.2. The concentrations of T3 and T4 were calculated according to their standard curve equations.

2.6 Statistical analysis

Data were analyzed with SPSS 18.0 software and expressed as mean±standard deviation (SD) (n=3).All data were checked for normality and homoscedasticity before statistical analysis using Kolmogorov-Smirnov test. Comparisons between the control and treatment groups were analyzed by oneway ANOVA, and post hoc comparisons were performed using the least signif icant diff erence (LSD)test (equal variances assumed) or Dunnett’s C test(equal variances not assumed). Probabilities values were considered signif icant whenP＜0.05 and extremely signif icant whenP＜0.01.

3 RESULT

3.1 Eff ects of FLO exposure on growth and development of P. olivaceus

Fig.2 Eff ects of FLO on the heart rates of pre-larvae (a) and post-larvae (b)

After the hatching of fertilized eggs, the initial average body length ofP.olivaceuswas 3.0±0.1 mm.For pre-larvae (1 dpf), the body length signif icantly increased after FLO exposure at diff erent concentrations for 96 h, while it was obviously inhibited after exposure for 168 h. The growth rate in control group (average body length: 3.48±0.21 mm)was signif icantly higher than 1 mg/L and 10 mg/L FLO groups (P＜0.05) (Fig.1a). For post-larvae (20 dpf),the initial average body length was 6.8±0.1 mm. The increase of body length varied at diff erent degrees with an increasing dosage of FLO for 96 h, the growth rate of body length in 10 mg/L FLO group was signif icantly higher than 0.1 mg/L and 1 mg/L FLO groups (P＜0.05), with an increase by 12.4% from the control’s. However, it showed a decline in the body length of larvae in FLO exposure for 168 h compared to the groups for 96 h in control and 10 mg/L FLO groups, by 5.05% and 12.5% drop, respectively (P＜0.05).

3.2 Eff ect of FLO exposure on heart rate of P. olivaceus

As shown in Fig.2, the heart rates of larvae increased with the growth ofP.olivaceus. The heart rate of post-larvae was 160±6 beats/min, which is signif icantly higher than that of pre-larvae of control group (107±8 beats/min). Larvae at early developmental stage was very sensitive to FLO. The heart rate of pre-larvae in exposure to FLO at 1 and 10 mg/L for 96 h was lower than that of control group,while at 0.1, 1, and 10 mg/L for 168 h, and the heart rate was statistically increased by 15.5% in 10 mg/L treated group. The post-larvae exposed to FLO for 96 h and 168 h had no signif icant diff erence in heart rate between treated and the control groups.

3.3 Eff ects of FLO exposure on the spontaneous behavior of P. olivaceus

As shown in Fig.3, the moving distance and moving velocity increased with the growth of larvae.The moving distance and moving velocity of prelarvae and post-larvae in control group increased by 83.04%±6.07% and 85.9%±4.81%, respectively. Prelarvae were sensitive to FLO at low concentrations.The moving distance in the 0.01 mg/L treatment was 41.2% higher than that of control, while no signif icant diff erence was observed in other treatment groups(Fig.3b). Variation in moving velocity was consistent with that in moving distance (Fig.3c). For the postlarvae, no obvious change was shown in the lowconcentration treatment groups in terms of moving distance and moving velocity, while a signif icant increase was found in high concentration treatment groups (1 and 10 mg/L) (Fig.3f, g).

The activity of f ish mobility is measured based on the extent of change in f ish outline to indicate the frequency of change in the swimming posture. The activity was recognized as being highly mobile,mobile, and immobile according to the percentage changes of pixels between current and previous. The changes over than 60% was regarded as being highly mobile, and less than 20% was def ined as being immobile, and the rest, being mobile. As shown in Fig.3d, the percentage of immobile activity of prelarvae was 99.47%, 99.13%, 99.55%, 99.38%, and 99.48% in the control, 0.01, 0.1, 1, and 10 mg/L groups, respectively. The percentage of immobile activity in treatment groups was signif icantly higher than that of high mobile and mobile activity, and that of mobile activity in 0.01 mg/L group was higher than that of other groups. With the growth ofP.olivaceus,average moving distance and moving velocity increased. For post-larvae (Fig.3h), the percentage of mobile activity was 32.44%, 31.51%, 32.53%,35.95%, and 31.97% in the control, 0.01, 0.1, 1, and 10 mg/L groups, respectively. The moving distance and moving velocity of larvae were signif icantly increased in 1 and 10 mg/L groups.

3.4 Eff ects of FLO exposure on antioxidant enzyme activity and MDA level of P. olivaceus

Fig.3 Eff ects of FLO on the motor behavior of pre-larvae and post-larvae

Fig.4 Eff ects of FLO on the SOD activity and MDA content of pre-larvae (a) and post-larvae (b)

Fig.5 Eff ects of FLO on the level of T3 and T4 in P. olivaceus larvae at diff erent developmental stages

Activities of SOD and MDA contents varied in both pre- and post-larvae. As shown in Fig.4, the SOD content in pre-larvae was signif icantly higher than that in post-larvae, and signif icantly increased after FLO exposure in a dose-dependent manner (P＜0.01),with a slight decrease in 10 mg/L group. However,SOD activities were signif icantly inhibited in all the treatment groups of post-larvae (P＜0.01) as FLOdosage increased, and higher in 10 mg/L group than that of 1 mg/L group.

Table 1 Regression analysis of FLO on enzyme activity of pre-larvae and post-larvae

The MDA contents of pre-larvae in treatment groups at all FLO concentrations were accumulated.The increasing trend slightly decreased in 10 mg/L group. On the contrary, FLO posed signif icant repression on MDA contents in post-larvae, with the lowest point in 1 mg/L group, which was 62.1% lower than that of control group.

The MDA content in pre-larvae showed an opposite trend to that of post-larvae in response to FLO exposure, being consistent with the SOD activities,for which we built quadratic polynomials among the SOD activity and MDA content in FLO treated preand post-larvae, and the correlations are signif icant(Table 1).

3.5 Eff ects of FLO exposure on thyroid hormone T3 and T4 of P. olivaceus

Thyroid hormone T3 and T4 in pre- and postlarvae showed high induction after exposure to FLO(Fig.5a, b). For T3 level, it was signif icantly increased in pre-larvae of 10 mg/L group compared with 0.1 mg/L group (P＜0.05), and no statistical changes in other groups. The T4 level in pre-larvae of 10 mg/L group was signif icantly higher than control and 0.01 mg/L groups (P＜0.05). As shown in Fig.5c, T3/T4 ratios in 0.01 mg/L groups was signif icantly higher than those of the other groups (P＜0.05).

4 DISSCUSSION

4.1 Eff ects of FLO exposure on growth and development of P. olivaceus

It remains doubtful whether antibiotics can be added into f ish feed as a growth promoter. Reda et al.(2013) reported that the weight gain of tilapia signif icantly increased with FLO-added feeds(5 mg/kg BW/d) for 12 weeks. Zhang et al. (2015)described phenotypes of developmental delay of zebraf ish embryos, including hatching delay, shorter body length, and uninf lated swim bladder upon exposure to tetracycline. In this study, 1 and 20 dpf f lounder larvae were exposed to diff erent FLO concentrations. FLO exposure for 96 h to pre-larvae promoted signif icantly the body length; however, as the exposure period lasted, the increase of growth rate slowed down.

In early stage of a larva, yolk sac is absorbed completely, develops from endogenous to exogenous nutrition mode, and begins to meet the external environment and becomes more sensitive to outside pollutants. In the f lounder, the post-larvae stage(20 dpf) is the time of intensive changes, including the formation of coronal dorsal f ins, shifting of right eye, and the upturning of end notochord (Brewster,1987). In our study, the growth rate of body length in post-larvae showed a downward trend, which should be related to the upward tilting of notochord and the formation of the tail bone.

During the growth and development of the f lounder,the heart rates of larvae increased gradually, indicating the progress of f ish growth. The heart rates in postlarvae of the control group increased signif icantly compared with those of the pre-larvae in this study. In addition, the heart rates of pre-larvae increased in a dose-dependent manner after FLO exposure for 168 h, which might be related to the stress response and dysfunctional heart function of larvae induced by the long-term FLO exposure. It has been demonstrated that the heart rate of zebraf ish embryos was induced by sulfamethazine at the concentration of 0.2, 20, and 2 000 μg/L for 72 h, which caused arrhythmia and heart dysfunction of f ish (Yan et al., 2018). To our knowledge, the mechanism by which FLO aff ecting the heart rate is not clear yet. It supposed that antibiotics could act as gamma-aminobutyric acid(GABA) agonists for inducing acute neurotoxicity to f ish under the high-dose exposure (Dorman, 2000), or it could act on the cardiac-adrenergic receptors as epinephrine, which resulted in the increase of the heart rate in larval zebraf ish (Milan, 2003; Steele et al., 2011).

4.2 Eff ects of FLO exposure on spontaneous behavior of P. olivaceus

Animal behavior is a sensitive indicator in response to the changes of external environment,and it is an overall ref lection of variations at molecular, biochemical, and physiological levels after being exposed to environmental contaminants.We aimed to analyze the spontaneous movement of larvae by visual tracking software. Flounder larvae in the early life stage showed relative low movement.Distance, velocity, and mobility of swimming changed in an overturned U trend in FLO exposure,which is consistent with previous study on zebraf ish behavior by β-diketone antibiotics exposure. FLO exposure at low concentrations may stimulate the motor nerves of f ish, while high concentrations could do the opposite (Fent and Meier, 1992). The f ish behavior is similar to the change in body length,indicating that FLO at high concentrations may impair the nervous system and aff ect the growth and development of larvae. A high concentration of FLO signif icantly promoted the motility of post-larvae but pre-larvae, which might be related to sensitivity upon the developmental stage as post-larvae were more tolerant to FLO than pre-larvae. As Lin et al.(2014) reported, spontaneous swimming was weakened signif icantly with sulfonamide concentration increase, because sulfonamides may act as GABA (gamma-aminobutyric acid) agonists,causing acute neurotoxical eff ects and damaging the coordination ability.

4.3 Eff ects of FLO exposure on antioxidant enzyme activity and MDA content of P. olivaceus

It had been reported that FLO has immunotoxicity to aquatic animals, especially during the early developmental stages. SOD is an enzyme that can scavenge superoxide anion radicals (O2ˉ) by catalyzing free radicals, which plays a critical role in balancing between oxidation and antioxidant (Shen et al., 2014).We found that pre-larvae in a low concentration of FLO may cause excessive production of O2ˉ. To maintain the dynamic balance of SOD activity and O2ˉ content in larvae, SOD activity increased. However,with the increasing of FLO concentration, SOD is not enough to scavenge the excessive O2ˉ, which may impair the antioxidant capability of the larvae. SOD activity in post-larvae but pre-larvae, was signif icantly decreased, suggesting that SOD may not the main actor in defensing oxidative stress that induced by FLO during the late developmental stage. As larvae grew, antioxidant defense system is gradually matured. Additional to antioxidant enzymes SOD etc., non-enzymatic small-molecule antioxidants were also involved in antioxidant defense system to protect the f ish. These substances include vitamin C,vitamin E, and GSH (glutathione) etc. Studies have reported that vitamin E is an eff ective biological antioxidant that reacts with O2ˉ directly, which inhibit lipid peroxidation in a tissue (Huang and Huang,2004). In addition, GSH is a water-soluble antioxidant found in the cytosol and mitochondria. It also plays an important role in scavenging free radicals and active oxygen species (Yang et al., 2011).

MDA is a byproduct of membrane lipid peroxidation and is frequently used as a marker of cell membrane damage caused by oxidative stress (Mendes et al.,2009). Consistent with the changes of SOD activity,FLO increased the lipid peroxidation. As the exposure concentration of FLO increased, the degree of free radical attacking larvae was signif icantly aggravated.It has been demonstrated that MDA contents were kept at extremely low level under no environmental stress, while it increased after exposing to the external contaminant, which lead to reactive oxygen species accumulation and membrane lipid peroxidation(Khan et al., 2018). FLO showed a dose-dependent decrease in SOD activity and MDA content in postlarvae but pre-larvae, which may be related to the higher tolerance in the late stage of larvae. Research in the antioxidant activity and MDA level in adult and embryonic zebraf ish showed that the adult are more tolerant to sulfonamide than the embryonic (Yan et al., 2018).

4.4 Eff ects of FLO on thyroid hormones T3 and T4 of P. olivaceus

Thyroid hormone includes mainly thyroxine (T4)and triiodothyronine (T3); they play an essential role in physiological processes such as growth and development, reproductive breeding, and energy metabolism (Politis et al., 2018). Miwa and Inui(1987) proposed that dramatic morphological changes of metamorphosis are associated with thyroid hormones levels, and T4 stimulated the metamorphosis of Japanese f lounder larvae. After the hatching, the levels of T3 and T4 stayed at relatively low levels,and gradually increased during the metamorphosis(De Jesus et al., 1991). Moreover, Yue et al. (2017)found that 100 μ g/L semicarbazide exposure shortened the time by 2 days for f lounder larvae to complete metamorphosis as compared to the control group. T4 is the main thyroid hormone produced by hypothalamic-pituitary-thyroid (HPT) axis; T3 is transformed by T4 via three deiodinases and exerts biological activity by binding thyroid hormone receptors. In our study, the post-larvae at 20 dpf exposed to FLO for 7 d was in an important moment of metamorphosis, the ratio of T3/T4 was signif icantly higher than that of the pre-larvae. In addition, we found that the T3/T4 ratio went down with the FLO dosage increase in both pre- and post- larvae,suggesting that FLO may inhibit the conversion from T4 to T3. However, the ratio of T3/T4 in the 0.01 mg/L exposed group did not change, indicating that FLO may promote the growth and development of larvae at a moderate concentration. It is consistent with the result of short-term hexabromocyclododecane exposure on the levels of T3 and T4 in juvenile crimson snapper (Chen et al., 2016).

5 CONCLUSION

The short-term FLO exposure promoted the growth and development of the pre-larvae ofP.olivaceus;however, the long-term one could slow down the body length increase.

Paralichthysolivaceuslarvae showed a diff erent degree of tolerance to FLO in diff erent developmental stages. Post-larvae is more tolerant to external pollutants than pre-larvae, and the spontaneous behavior of pre-larvae can be stimulated by FLO of low concentration. However, for post-larvae, no signif icant eff ect was observed in the spontaneous behavior in a low FLO concentration, while in a high concentration, the behavior was promoted.

The antioxidant activity of pre-larvae declined in high FLO concentration, while the excessive O2ˉ was hard to eliminate. With the aggregation of free radical attacking, the levels of SOD and MDA were raised.

Therefore, an appropriate amount of FLO could promote the growth and development of the larvae,the spontaneous behavior, and the antioxidant capacity. However, in higher concentrations and longer exposure times, these items could be inhibited.The pre-larvae (1 dpf) were more sensitive to FLO residues in the environment than post-larvae (20 dpf).A long-term FLO exposure even at an environmental related level could damage the growth and immune resistance of the f ish. It is not suitable to prevent disease as a drug for long-terms. Controlling the use and emission of FLO and other antibiotics shall be emphasized.

6 DATA AVAILABILITY STATEMENT

All date generated and/or analyzed during this study are available from the corresponding author upon reasonable request.