1. Introduction
To date, the rapid expansion of the aquaculture sector has resulted in a surge in the demand for aquafeeds. Nevertheless, there is a scarcity of top-notch feed resources such as fish meal and fish oil [
1]. To address this issue, both the academic and industrial realms explore diverse technical approaches to increase the feed energy supply ratio. Fish oil, in particular, is highly valuable because of its composition of highly unsaturated fatty acids (HUFAs), such as eicosapentaenoic acid (EPA, 20:5n-3), docosahexaenoic acid (DHA, 22:6n-3) and arachidonic acid (ARA, 20:4n-6), which play pivotal roles in the growth and development of fish [
2,
3]. Fish rely on dietary HUFAs for normal growth and physiological development. Studies show that ARA and EPA competitively regulate key physiological processes in fish [
4,
5]. Extensive research conducted over the past twenty years has unequivocally demonstrated the significant influence of ARA and EPA on the fluidity of cell membranes, as well as their involvement in various physiological processes, including fish growth, oxidative stress, and the regulation of genes related to lipid metabolism [
6,
7,
8].
Numerous studies have confirmed that DHA has a positive effect on the growth performance of marine fish and the health of their liver and intestines [
9,
10,
11]. When DHA levels are adequate, EPA and ARA, along with the ARA/EPA ratio, play a crucial role in the growth and health of fish [
6,
7,
8]. Optimizing the ratios of dietary ARA/EPA is crucial, as diverse species exhibit distinct physiological reactions to such changes. In a recent study, as the dietary ARA content increased from 0.08% to 0.36%, there was a significant increase and subsequent decrease in the final body weight (FW) and specific growth rate (SGR) of juvenile Japanese seabass (
Lateolabrax japonicus). Additionally, the hepatosomatic index (HSI) of fish in the diet group with an ARA content higher than 0.22% was significantly lower than that of the control group (
p < 0.01) [
12]. However, when the diets of juvenile yellow catfish (
Pelteobagrus fulvidraco) were studied, it was found that the survival rate, FCR, liver somatic index (LSI), and visceral index (VSI) were not significantly affected by ARA levels [
13]. Although specific dietary requirements for DHA and EPA in
H. otakii have not yet been formally established, related marine species, such as Japanese seabass [
12,
14] and Japanese eels (
Anguilla japonica) [
12,
14], have shown a clear physiological dependence on adequate provisioning of n-3 HUFA. Consequently, comprehending the roles of individual fatty acids, and their ratios is crucial for developing species-specific nutritional strategies in marine fish aquaculture. The inclusion of different levels of ARA and EPA in the fish diet can affect the antioxidant capacity of the fish. For example, when ARA/EPA ratios of 0.22 and 0.26 were added to the diet, the livers of juvenile yellow catfish presented a greater concentration of malondialdehyde (MDA) than did those of fish fed other diets [
13]. Similarly, compared with feeding other groups of feeds, feeding feed with an ARA/EPA ratio of 3 resulted in a significant increase in SOD specific activity [
14]. Another study conducted on juvenile grass carp (
Ctenopharyngodon idellus) revealed that a relatively high dietary intake of 0.3% ARA reduced MDA concentrations and significantly increased SOD levels [
15]. Dietary fatty acids influence liver fat metabolism and health [
16]. The addition of ARA and EPA at ARA/EPA ratios of 2.04 and 4.01 in feed has been shown to reduce lipid accumulation in the liver of sea bass [
17]. Adequate intake of ARA can also regulate the relative expression levels of genes associated with lipid metabolism in the liver of yellow catfish juveniles. For example, 12.64% ARA intake significantly decreased the relative gene expression of the lipid synthesis-related genes
accα and
evovl5a while increasing the relative gene expression of the lipid decomposition-related genes
atgl and
hslb [
13]. Moreover, LC-PUFAs have been shown to affect various physiological processes in fish, including reproduction, stress resistance, pigmentation, and bone development [
18,
19,
20,
21,
22,
23]. However, most existing studies have concentrated on overall n-3 HUFA levels or the balance between DHA and EPA. In contrast, fewer studies have investigated the specific physiological effects of varying ARA/EPA ratios in contexts where the provision of DHA is deemed sufficient [
24]. Different species have different physiological responses to changes in dietary ARA/EPA ratios, highlighting the need to optimize these ratios for each species.
H. otakii is a bottom-dwelling fish that lives in cold-temperature oceans. This species is distributed mainly in the offshore areas of China, North Korea, Japan, Russia and other regions. Its meat is tender and highly nutritious, and the market demand is strong. It has the prospect and potential for commercial breeding. Owing to the slow growth rate of juvenile H. otakii, investigating the appropriate ARA/EPA ratio and its effects on growth performance, antioxidant capacity, and lipid metabolism-related genes is crucial.
This study hypothesizes that adjusting the ARA/EPA ratio in feed can significantly influence the growth performance, antioxidant capacity and lipid metabolism-related genes in juvenile H. otakii, thereby determining the appropriate ARA/EPA ratio. By adding different proportions of EPA and ARA to the diet of juvenile H. otakii, we hope to determine the most appropriate feed ratio for juvenile H. otakii. This approach can not only reduce the cost of raw feed materials but also ensure the healthy breeding of fish. Moreover, the results of this study can also provide an important theoretical basis for studying the nutritional needs of marine fish and developing feed.
2. Materials and Methods
2.1. Experimental Diets
In this experiment, six types of isonitrogenous (49%) and isolipidic (11%) diets were formulated by modifying the lipid compositions: A (7% fish oil), B (4% fish oil, 3% ARA), C (4% fish oil, 2% ARA, 1% EPA), D (4% fish oil, 1.5% ARA, 1.5% EPA), E (4% fish oil, 1% ARA, 2% EPA), and F (4% fish oil, 3% EPA), the ingredients and proximate composition of the experimental diets are presented in
Table 1. The control group (A) was supplemented with 7% fish oil as the primary fat source, while the experimental groups utilized 4% fish oil as the base fat source, incorporating varying proportions of ARA and EPA to create five diets with distinct ARA/EPA ratios (B 2.66; C 1.34; D 1.01; E 0.47; F 0.19), the dietary fatty acid composition is presented in
Table 2. Fish oil (provided by Dalian Yuelan Biotechnology Co., Ltd., Dalian, China) was added to the control diet, while the other five diets were supplemented with ARA-enriched oil (with approximately 40% ARA relative to the total fatty acid content; sourced from ARA-methyl ester, Hubei Fuxing Biotechnology Co., Ltd., Wuhan, China) or EPA-enriched oil (with approximately 40% EPA relative to the total fatty acid content; obtained from Shanghai McLean Biochemical Technology Co., Ltd., Shanghai, China) to replace the fish oil (obtained from Shandong Provincial Improved Meiweiyuan Biotechnology Co., Qingdao, China) and fulfil the lipid requirements.
The feed was produced in the feed room of the Northern Fish Applied Biology and Breeding Laboratory of Liaoning Province, Dalian Ocean University. The dry ingredients were pulverized via a hammer mill. The pulverized ingredients were subsequently weighed and extensively blended in a Hobart-type mixer after being sifted through an 80-mesh sieve. The resulting mixture was cold-extruded to form floating pellets, which were subsequently cut into uniformly sized strands (2 mm diameter pellets were prepared). The feeding trial utilized dried pellets, which were subjected to forced air at room temperature for 24 h, followed by storage at −20 °C until use.
2.2. Growth Trial
This experiment was conducted in the live breeding room on the first floor of the No. 12 Marine Breeding Building of Dalian Ocean University. At the beginning of the experiment, 540 juvenile H. otakii (purchased from Dalian Bay Commercial Fish Farm, Dalian, China) with an initial mean body weight of 31.4 ± 1.5 g and a body length of 12.8 ± 0.1 cm were randomly distributed into 18 tanks (volume: 100 L; water flow: 600 L/h; rearing temperature: 15 °C; dissolved oxygen: 7 mg/L; salinity: 25; pH: 7.4). Prior to the commencement of the feeding trial, a 24-h fasting period was imposed on the fish, after which their initial body length and weight were measured.
To ensure randomization, each diet was assigned to one of three separate tanks. The fish were manually fed twice daily with the intention of reaching a state of apparent satiation, which occurred at 09.00 and 16.30 h, over a duration of 8 weeks. The fish were allowed to consume food until their feeding activity ceased, and no feed was left in the tank. The amount of feed consumed was meticulously documented.
2.3. Sampling
After 8 weeks of feeding, the fish were fasted for 24 h. Then, the fish were bath anaesthetized with tricaine methane sulfonate (MS-222, 0.08 g/L) within a synchronized time window (9:00–10:00) to minimize diurnal variation interference. The fish were weighed, and their body lengths were measured. Blood was collected from the caudal vein, and serum samples were collected after centrifugation for 10 min (8000 rpm/min, 4 °C) and then stored at −80 °C until analysis. The fish were killed and dissected. After the total visceral weight was measured, the kidney, muscle and intestine were removed. Afterwards, samples of muscle were stored at −20 °C for fatty acid composition analyses; samples of hepatopancreas and intestine were frozen in liquid N2 and then stored at −80 °C for gene expression or enzyme activity measurements; additionally, three samples were stored for histomorphological evaluation in paraformaldehyde.
2.4. Growth Performance
The growth performance was calculated via the following formula.
W
t: Final body weight (g); W
0: Initial body weight (g); W
l: Liver wet weight (g); W
v: Visceral wet weight; W: Body wet weight (g); L: Body length; W
f: Total feed consumption; t: Feeding trial days.
2.5. Proximate Composition and Fatty Acid Composition Analysis
The analysis of the diets and muscles was performed via the standard method to determine their proximate composition. The analytical procedures for this experiment were based on guidelines established by the National Feed Industry Standardization Technical Committee of China. The moisture content was measured by oven drying at a constant temperature of 105 °C until a stable weight was reached, while the ash content was determined after the muffle furnace treatment of the samples at 550 °C for 5 h. Acid digestion followed by the Kjeldahl method was employed to determine the crude protein content. For the determination of crude lipids, extraction was conducted using petroleum ether.
The muscle and feed were hydrolysed with hydrochloric acid, fat was extracted, and potassium hydroxide-methanol was used to saponify and methylate the mixture to obtain fatty acids, which were analysed via gas chromatography. FAMEs were separated via gas–liquid chromatography (GC2010 pro, Fisons, Shimadzu, Kyoto, Japan) via a 30 m × 30 mm × 0.25-μL capillary column (DK802T, Acrichi, Shanghai, China). Individual methyl esters were identified by comparison with the mixed labelling of 37 fatty acid methyl esters from Wuhan Pronets Testing Technology Co., Ltd. (Wuhan, China).
2.6. Intestinal, Liver, and Serum Biochemical Parameter Measurements
The liver and serum metabolic enzymes included superoxide dismutase (SOD, U/mg protein), catalase (CAT, U/mg protein), malondialdehyde (MDA, nmol/g protein), and total antioxidant (T-AOC, U/mg protein); the intestinal digestive enzymes included lipase (U/mg protein), amylase (U/mg protein), and trypsin (U/mg protein), and the enzyme activities were determined through the use of assay kits (Jiancheng Biotech Co., Nanjing, China) following the procedures outlined in the specifications.
2.7. Histological Morphological Evaluation
Servicebio Technology Company (Wuhan, China) cut hepatic sections to for hematoxylin and eosin (HE) staining. The hepatic and intestinal sections were examined under a magnification of ×20. Quantification was carried out via three slides from each group, with five randomly chosen fields on each slide. Photographs were captured, and a scale was included for reference. Villus length was measured via ImageJ software (version 1.53q; National Institutes of Health, Bethesda, MD, USA), while rough results were obtained by observing the number of droplets.
2.8. Real-Time Quantitative PCR
To conduct mRNA level assessments of the liver, three fish were sampled from each tank. TRIzol reagent (Vazyme, Nanjing, China) was utilized for extracting total RNA following the instructions provided by the manufacturer. The quality and quantity of the RNA were subsequently evaluated through 1% agarose gel electrophoresis and Ultra-microphotometer (Biochrom Technologies, Cambridge, UK). The resulting total RNA concentration was adjusted to 0.5 μg/8 μL H
2O. cDNA was produced via an First-Strand cDNA Synthesis Kit (Baisai Biotechnology Co., Shanghai, China). Quantitative real-time PCR (qRT-PCR) analysis was performed using a Roche LightCycler 96 thermal cycler (Basel, Switzerland) with 2× qPCR Master Mix (Tiangen, Beijing, China). The 2
−ΔΔCt method was used for analysis. The relevant genes and primers are listed in
Table 3. The coding DNA sequences (CDS) for the relevant genes were obtained from our laboratory’s complete transcriptome data of
H. otakii. The primers were designed using Primer Premier software (version 5.0), with β-actin as the housekeeping gene.
2.9. Statistical Analysis
The data are presented as the mean ± standard error of the mean. We utilized one-way analysis of variance (ANOVA) to assess and compare the variations among the experimental groups, followed by Duncan’s post hoc tests. For all the statistical analyses, we employed SPSS 18.0 software. A significance level of p < 0.05 was used for all tests.
4. Discussion
ARA and EPA are reported to be involved in the complex and competitive regulation of physiological processes in fish [
26]. In marine fish, competitive inhibition occurs during the synthesis of n-3 and n-6 HUFA. The synthesis of ARA and EPA is subject to competitive inhibition, which prevents their inter-conversion [
3]. ARA represents the final product of the n-6 series fatty acids, while EPA can be readilyconverted into DHA, which serves as the end product of the n-3 series fatty acids [
24]. Consequently, different dietary ARA/EPA ratios may lead to different metabolic patterns in juvenile
H. otakii, potentially affecting physiological functions such as growth performance, oxidative stress, and lipid metabolism-related gene expression. Therefore, determining the appropriate amounts and ratios of ARA and EPA to be incorporated into fish feed is of great significance. The results of this study demonstrated that varying the dietary ARA/EPA ratio influenced the growth performance and feed conversion ratio (FCR) of juvenile
H. otakii. It is important to note that although the study focused on ARA and EPA, DHA was present at baseline levels across all experimental diets, ensuring that essential DHA requirements were not a limiting factor for growth. This context allows for a more reliable interpretation of the specific effects associated with ARA/EPA variation. In a study on juvenile black seabass (
Acanthopagrus schlegelii), researchers added different levels of ARA to the diet along with high levels of EPA and DHA, finding that ARA supplementation in the range of 0–6% significantly enhanced the fish’s growth and survival rates. It was also noted that DHA and EPA can undergo partial interconversion via enzymatic elongation-desaturation pathways, with EPA showing better regulatory capacity than DHA in lipid metabolism and inflammatory responses [
26]. Therefore, the purpose of this study was to investigate the effects of the dietary ARA/EPA ratio on juvenile
H. otakii. The results showed that different ARA/EPA ratios had different effects on the PWG and FCR of juvenile
H. otakii. It should be emphasized that the observed enhancements in PWG and FCR may not be solely attributable to the ARA/EPA ratio itself, but rather to complex interactions among dietary n-3 and n-6 HUFAs, including the underlying presence of DHA.
Previous studies have shown that the growth and feed efficiency of juvenile
H. otakii were optimal when the diet contained 12–17 g/kg of n-3 HUFA, and excessive n-3 HUFA supplementation would impair fish growth [
27]. This finding is similar to the studies on cobia (
Rachycentron canadum) [
28] and the female blue gourami (
Trichopodus trichopterus) [
29]. As the ARA/EPA ratio in cobia feed increased, the PWG and FCR increased. When the ratio was 1.91, the best effect was achieved [
28]. In addition, when the dietary ARA/EPA ratios for fat greenling were 1.34 and 0.19, the FCR and CF were not significantly different from those in the control group, and better results were observed in the other groups (
p < 0.05).However, in studies of juvenile grass carp [
15] and Malabar red snapper (
Lutjanus malabaricus) [
30], the different ratios of ARA and EPA in each experimental group had no statistically significant differences in FCR or CF. Moreover, adding higher contents of ARA and EPA in this experiment caused significant increases in the VSI and HSI (
p < 0.05). Similar conclusions were red for blue gourami [
31] and juvenile yellow catfish [
13]. The varying experimental outcomes observed across different species might be attributed to differences in growth stages and species characteristics. Previous research has shown that adjusting the fatty acid composition of feed can effectively change the fatty acid profile in fish [
32]. Similar results were obtained in this study. Therefore, different ARA/EPA ratios in the diet have an impact on the growth performance of juvenile
H. otakii.
Owing to the high degree of unsaturation of ARA and EPA, they are easily attacked by free radicals, causing lipid peroxidation and damaging the functional integrity and enzyme activity of cell membranes [
26,
33,
34]. SOD, T-AOC, CAT and MDA are important parameters for assessing the antioxidant status of organisms [
35,
36]. SOD is thought to play a key antioxidant role by catalyzing the conversion of O
2− to H
2O
2, which can be removed by the activity of CAT or GSH-Px [
26,
37]. The T-AOC can reflect the defense status of organisms with intracellular antioxidant capacity [
38]. MDA is a useful biomarker of lipid peroxidation [
39]. The fish liver is the metabolic center of the body [
17], and serum biochemistry is an important indicator of body health [
40]. We found that when the feed was supplemented with ARA/EPA at a ratio of 0.47, the MDA content in the liver and serum of juvenile
H. otakii was significantly lower than that in the other groups. The decrease in their content indicates that ARA and EPA have a positive effect on reducing oxidative damage. Moreover, the levels of two important antioxidant enzymes, SOD and CAT, also increased significantly. However, interestingly, the opposite phenomenon was observed in Group B, which may be caused by the difference in the feed ratio. The above results are the same as those for the liver score. The liver score of Group B was significantly lower than that of the other experimental groups, while the scores of Groups D and E were somewhat better (
Figure 1b). Liver histology supported these results: when the dietary ARA/EPA ratios for juvenile
H. otakii was 2.66 showed hepatocyte vacuolization and cell damage, while the dietary ARA/EPA ratios for juvenile
H. otakii were 1.01 and 0.47 showed no obvious pathology. Liver health scores matched these trends. Similarly, intestinal villus length and muscular thickness were improved at moderate ARA/EPA ratios. These findings suggest that appropriate ARA/EPA ratios can help maintain oxidative balance and tissue integrity. However, elevated antioxidant activity may also reflect oxidative stress. Additionally, rising dietary ARA levels altered the overall n-6/n-3 ratio, which may have further influenced oxidative metabolism and warrants deeper investigation. These results are similar to those of Japanese eel (
Anguilla japonica) [
14], juvenile yellow catfish [
13], juvenile turbot (
Scophthalmus maximus L.) [
41], Malabar red snapper fingerlings [
30], juvenile grass carp (
Ctenopharyngodon idellus) [
15] and juvenile Japanese seabass [
12], which suggests that the choice of the ARA/EPA ratio may have an important impact on their effects. Different ratios may have different effects on the antioxidant capacity of juvenile fat greenling.
The intestine plays a crucial role in the absorption and metabolism of dietary lipids, where digestive enzymes break them down into fatty acids and glycerol, which are subsequently absorbed into the blood to engage in diverse physiological functions [
42,
43]. Therefore, the activity and expression levels of intestinal digestive enzymes are important indicators for evaluating feed utilization efficiency [
44,
45]. When the dietary ARA/EPA ratio was 1.01 and 0.47, VL was significantly greater than those in the other experimental groups and the control group A (
p < 0.05). The experimental results of VL were similar to those of turbot [
41]. Compared to the fish oil blank group, VL progressively increased with the addition of ARA concentrate in the diet and with an increase in its concentration. Conversely, the villus width in the low-concentration ARA concentrate group of this experiment was significantly reduced. It might be caused by proinflammatory cytokines [
41]. Longer VL can increase the absorption area, accommodate more digestive enzymes, and facilitate the attachment of immune cells, thus benefiting fish growth [
46]. According to the results of this study, the intestinal lipase and amylase activities reached their highest levels when only ARA was added to the feed. However, indicators such as MH, MW and MT did not show similar results, which may be related to the degree of oxidative stress. When the ARA/EPA ratio was higher or lower than the specific value, the activity of digestive enzymes decreased. Similar results were also observed in
Pangasianodon hypophthalmus juveniles [
47] and juvenile small yellow croaker (
Larimichthys polyactis) [
46]. Numerous studies have revealed that the contents of protein, fat, and other nutrients in feed exert a significant influence on the intestinal health and function of marine fish [
9,
48]. Therefore, further studies of the exact mechanism of HUFA effects on intestinal health are needed to understand their role in fish. However, it’s unclear if these effects directly result from the ARA/EPA ratio or broader metabolic adjustments involving DHA and other n-3 HUFAs. Future studies are needed to clarify the molecular mechanisms linking dietary fatty acid profiles to intestinal health and nutrient assimilation. Previous studies have focused on the respective functions of ARA and EPA and their direct effects on lipid metabolism. However, determining an optimally conducive to the overall metabolic well-being ARA/EPA ratio for juvenile
H. otakii in a broader metabolic context remains a challenging problem. Lipid metabolism is interrelated with multiple physiological processes such as carbohydrate metabolism and protein metabolism, so it is necessary to understand the effect of the ARA/EPA ratio on lipid metabolism from a more comprehensive perspective.
srebp1 is a transcription factor that activates the transcription of key downstream genes involved in de novo fatty acid synthesis [
49]. Current research has shown that
srebp1 regulates the expression of
accα,
fas and
scd1 and affects fat synthesis [
50,
51]. After activation,
srebp1 is cleaved by lyase to form mature
srebp1, which is subsequently transferred to the nucleus by the endoplasmic reticulum to play a regulatory role [
52]. Malonyl-CoA synthesis is catalysed by
accα,
fas catalyses the elongation of malonyl-CoA to synthesize saturated fatty acids, and
scd1 catalyses the oxidative dehydrogenation of saturated fatty acids to synthesize unsaturated fatty acids such as MUFAs [
53,
54]. Studies have shown that triglycerides decompose diacylglycerol (DG) and fatty acids under the action of
atgl, and DG is decomposed from
hsl into MG and fatty acids. Therefore,
atgl and
hsl are the rate-limiting enzymes for the decomposition of TG [
55]. Almost every step in the process of mitochondrial and peroxisomal fatty acid β-oxidation is regulated by
pparα [
56,
57]. Moreover,
pparα can promote the complete oxidative decomposition of acyl-CoA into mitochondria by regulating the expression of
cpt [
58]. The n-3/n-6 fatty acid balance, closely related to the ARA/EPA ratio, is vital in this regard.Prolonged imbalance in this ratio may induce physiological perturbations. Specifically, an elevated n-6/n-3 ratio (more ARA than EPA) upregulates lipid synthesis-related genes such as scd1, accα, and srebp1. This was evidenced by a comparative analysis of dietary groups with ARA/EPA ratios of 1.34 and 0.47, where marked differences in the expression of these genes were observed, potentially driving hepatic lipid deposition and steatosis [
24]. Conversely, an excessively high n-3/n-6 ratio may cause excessive fat oxidation, resulting in slow growth or reduced immunity in fish [
15,
49]. The results of this experiment showed that the addition of ARA and EPA to the diet significantly inhibited the expression of the lipid synthesis-related genes
fas,
scd1,
accα and
srebp1; promoted the expression of the lipid decomposition-related genes
cpt1 and
pparα; and inhibited the expression of
atgl and
hsl. Research on gilthead sea bream has shown that the expression of
fas and
srebp1 tends to first increase and then decrease with decreasing ARA/EPA ratio [
10]. Research on juvenile yellow catfish showed that adding ARA to the diet inhibited the expression of
fas,
accα,
cpt1 and
hsl but had no significant effect on that of
fas. The expression of
srebp1,
atgl and
pparα varied with the amount of ARA added [
13]. The results of these studies on juvenile black seabream are opposite to those on yellow croaker. As the ARA content in the diet increases, the expression level of
accα increases, while the expression of
srebp1 decreases; moreover, the expression levels of the TG decomposition rate-limiting enzymes
atgl and
hsl are inhibited, which is the same as the results of this experiment [
59]. When adjusting the ARA/EPA ratio to influence gene expression, the pros and cons associated with the n-3/n-6 balance must be weighed. The regulatory effects observed in this study may arise from the integrated actions of multiple fatty acids, rather than solely from the ARA/EPA ratios in isolation. Additionally, these effects may reflect broader metabolic adjustments involving DHA and other n-3 HUFAs. Future studies are necessary to elucidate the impact of dietary ARA/EPA/DHA ratios on gene expression related to lipid metabolism and evaluate how gene expression changes, affected by the ARA/EPA and n-3/n-6 ratios, impact fish growth, reproduction, and health, so as to determine the most suitable ARA/EPA ratio for the culture of juvenile
H. otakii.