1. Introduction
The biggest difference between fish oil (FO) and edible vegetable oil (VO) is that the former is rich in n-3 long-chain polyunsaturated fatty acids (n-3 LC-PUFA), such as docosahexaenoic acid (DHA) and eicosapentaenoic acid (EPA), which can provide essential EFA for marine aquaculture fish [
1]. Fish oil also contains some flavor components that can improve the palatability of feed and the ingestion of fish [
2]. Therefore, FO has become the preferred oil ingredient for feed formulations of marine aquaculture fish [
3]. However, the fast development of the global aquaculture industry, represented by China, has contributed to a sharp increase in FO consumption. This leads to a constant shortage in FO supplies, which in turn has kept prices high, thereby increasing the cost of aquatic feed [
4]. Therefore, finding candidates to replace FO has become one of the major issues in the aquafeed sector. Edible VOs are widely used as a potential alternative to FO in aquafeeds due to their wide sources, huge production, and relatively low prices. So far, the application of VOs in commercial feed formulations for fish farming has made great progress [
5,
6,
7,
8,
9,
10]. Several results show that the effects of replacing FO with edible VOs differ due to the different fatty acid (FA) compositions of different VOs and the synergistic effects of FAs through the blending of FO and VOs [
11,
12,
13,
14,
15].
Coconut oil (CO) is a VO extracted from coconut meat. It is mainly produced in Southeast Asian and South Asian countries such as Philippines, Indonesia, and India, and South American countries such as Brazil and Colombia [
16]. Unlike other VOs, CO is rich in saturated fatty acids (SFAs), accounting for about 80–90% of total FAs, which makes CO a firm texture at room temperatures, which is less prone to oxidation and rancidity [
17]. Medium chain fatty acids (MCFAs) are the predominant FA type of CO, mainly including lauric acid, decanoic acid, and octanoic acid, accounting for about 60% of the total FAs, with the lauric acid content being as high as 50–53% [
18]. MCFAs can be quickly absorbed after digestion and immediately used as energy in the liver [
19,
20]. With the abundant presence of MCFAs, CO exhibits many health benefits, mainly including rapid energy supply, lipid-lowering, antiviral, antibacterial, and antioxidant properties [
20,
21,
22,
23,
24,
25]. Although there is a concern about the risk of cardiovascular disease caused by SFAs [
26], any direct significant relationship between mortalities of cardiovascular disease and intakes of total fats, SFAs, MUFAs, and PUFAs has not yet been confirmed and is highly controversial [
27,
28,
29]. In fish, there is limited research on the potential use of CO in aquafeeds as an alternative to FO. However, these limited studies have yielded inconsistent results. Some studies reported that CO can completely replace FO without affecting the growth of fish [
11,
30,
31,
32,
33] and that a synergistic effect of a CO and FO blend on promoting growth was also observed [
11,
12], while others have reported that excessive CO substitution for FO can have adverse effects on fish growth [
34,
35,
36,
37,
38]. This may be due to differences in fish species, feed composition, and dietary CO inclusion levels. Therefore, it is necessary to further study the role of CO in growth promotion and lipid metabolism when CO is used as a FO alternative in aquafeeds in an attempt to promote the development of sustainable aquaculture.
The grouper, an important marine carnivorous fish species, is favored by people in Southeast Asian coastal countries including China due to its high market price and benefits for intensive farming [
39]. China has boosted its overall development, with an aquaculture output of 205,800 tons in 2022 [
40]. There was still limited research on the potential use of VOs as an alternative to FO in feed for the fish species, and their influences on lipid metabolism were reported by our research team [
10,
14] and previous studies [
38,
41,
42]. These results indicate that FO could be replaced partially or completely by VOs without affecting growth. Furthermore, feeding a 50% palm oil (PO) substitution diet resulted in maximum growth, possibly due to the synergistic effect of FO and PO when mixed in an appropriate proportion [
14]. We also assume that CO and FO mixing in an appropriate proportion may have a synergistic effect, as CO is rich in well-known MCFAs and other SFAs. The orange-spotted grouper (
Epinephelus coioides) is one of the major species of farmed grouper. In view of this, we conducted an experiment to investigate the effects of replacing dietary FO with CO on growth performance, plasma biochemical components, tissue FA composition, and the expression levels of genes related to lipid metabolism in orange-spotted grouper, attempting to determine whether dietary CO affects the growth and feed utilization and whether it directly activated the gene expressions associated with lipid metabolism in the fish species.
2. Materials and Methods
2.1. Test Feed
A basal diet was formulated to contain 50% crude protein and 12% crude lipids using a defatted fish meal, wheat gluten, soybean meal, shrimp meal, gelatin, and casein as the protein sources, and FO, CO, and soy lecithin as the main lipid sources (
Table 1). The FO was replaced by CO at 0%, 25%, 50%, 75%, and 100% increments in the basal diets to prepare 5 experimental diets (0% CO, 25% CO, 50% CO, 75% CO, and 100% CO, respectively). The five experimental diets were made according to the feed preparation procedure of our previous study [
14]. The pellets were dried in a ventilated oven at 65 °C for 24 h until the moisture was reduced to below 10%, and were then sealed in plastic bags and stored at −20 °C for the subsequent growth trial. The FA profiles of the test diets are presented in
Table 2.
2.2. Feeding Management
The feeding trial was carried out at Fujian Dabeinong Fisheries Technology Company (Zhaoan County, Zhangzhou City, China). The orange-spotted grouper juveniles were maintained in a concrete pond and fed with the basal diet for 2-week acclimatization prior to the start of the trial. Groupers initially weighing 22.35 g/fish (n = 25 fish) were randomly allotted into five groups, each with triplicate tanks (500 L/tank), at a density of twenty-five fish per tank within a circulating aquaculture system equipped with a temperature control device. Groups of fish were hand-fed one of the five diets to apparent satiation twice daily (7:00 and 17:00) under a natural photoperiod across an eight-week feeding period. Uneaten feed was collected and then feces were removed via siphoning 30 min after each meal. The collected feed was then dried at 65 °C and weighed to calculate the amount of feed intake. Dissolved oxygen and water temperature were measured daily at 15:00 h and nitrite—N was monitored twice a week using a multi-parameter photome (HI83200, Hanna Instruments, Woonsocket, Rhode Island). The water temperature was kept at 29 ± 0.5 °C, the dissolved oxygen content ranged from 6.93 ± 0.65 mg/L, and ammonia nitrogen was below 0.21 mg/L throughout the feeding period.
2.3. Sample Collection
At the end of the experiment, fish in each tank were captured and anesthetized with 100 mg/L of MS-222 (tricaine methane sulfonate, Sigma-Aldrich Shanghai Trading Co., Ltd., Shanghai, China), then batch-weighed and counted to determine the percentages of weight gain (WG), the specific growth rate (SGR), the daily feed intake (DFI), the feed conversation rate (FCR), and survival. Fifteen fish per treatment (five fish per tank) were randomly captured and anesthetized with MS 222 (100 mg/L) and weighted individually, followed by a blood draw using a 2 mL syringe through the caudal vein. Blood samples were placed at 4 °C for 12 h before serum separation via centrifugation at 1027× g at 4 °C for 10 min. Serum samples were pooled by tank, and then stored in 1.5 mL Eppendorf tubes at −80 °C for the subsequent analysis of biochemical parameters. After completing the blood draw, the same batch of five fish per tank were then dissected to aseptically remove the liver and viscera in order to calculate the hepatosomatic index (HSI) and condition factor (CF), followed by the excision of dorsal muscles. For liver histological observations, 1 mm3 of liver (one fish per tank) was cut and fixed in 4% polyformaldehyde solution. Liver and dorsal muscles were then, respectively, pooled by tank and stored at −80 °C for the analysis of lipids, fatty acids, and gene expression. Another four fish in each tank were randomly caught and pooled in plastic bags and stored at −20 °C for the determination of the proximate composition.
2.4. Proximate Composition Analysis
The proximate composition of ingredients, diets, fish samples, liver, and samples were determined according to the method of the Association of Official Analytical Chemists [
43]. Dry matter was measured via drying in an oven at 105 °C to a constant weight. Crude protein was measured via the Kjeldahl method using a Kjeltec System (Foss Tecator AB, Hoganas, Sweden). Crude lipid was assayed with the Soxtec extraction method using Soxtec Avanti 2050 (Foss Tecator AB). Ash was measured with a muffle furnace at 550 °C for 8 h. Before the proximate composition determination, the fish samples were autoclaved at 121 °C for 20 min, followed by homogenization, and then dried at 65 °C for 24 h.
2.5. Serum Components Analysis
The contents of total cholesterol (TC), triglycerides (TG), high-density lipoprotein cholesterol (HDL-C), and low-density lipoprotein cholesterol (LDL-C), as well as the activities of alanine aminotransferase (ALT) and aspartate aminotransferase (AST) in the serum, were assayed via the use of their respective kits produced by Jiancheng Bioengineering Institute (Nanjing, China) following the manufacturer’s instructions. The TC and TG content were measured through the COD-PAP method using the multifunctional enzyme marker (Infinite 200pro, Tecan Austria GimbH, Shanghai, China); the HDL-C and LDL-C content were measured via the peroxidase colorimetric method using the multifunctional enzyme marker (Infinite 200pro); ALT and AST were measured via the Reitman-Frankel method using a visible light spectrophotometer (V-1100D, MAPADA, Shanghai, China).
2.6. Fatty Acid Analysis
The total lipids of muscle, liver, and diet samples were extracted via homogenization in a chloroform/methanol (2:1, vol/vol) solution according to [
44], and were determined gravimetrically after drying a 5 mL aliquot under nitrogen. The freeze-dried lipid samples (~100 mg) were added into a 25 mL volumetric screwed glass tube with a plastic lid, followed by the addition of 3 mL 2% KOH methanol solution, and were then incubated in a water bath at 75 °C for 20 min. After cooling, the 25 mL glass tube was added with 3 mL 14% boron trifluoride methanol solution, mixed thoroughly, and then the procedure was performed with a water bath at 85 °C for another 20 min. After completing the FA methylation treatment, the resultant solution was transferred to a 10 mL centrifuge tube, followed by the addition of 2 mL double distilled water and 2 mL n-hexane in sequence. The mixture was then shaken vigorously for 1 min, and allowed to separate into 2 layers. The upper layer containing FA methyl esters was separated for subsequent GC analysis.
Fatty acids were determined using gas chromatography (Agilent 7890B-GC, Fairborn Precision Instruments Co., Ltd., Shanghai, China) equipped with a flame ionization detector (FID) and a CD-2560 capillary column (100 m × 0.25 mm × 0.2 μm). When performing measurements, 1 μL of the methylated sample was injected in the split mode at a 50:1 ratio. The column carrier gas was nitrogen, applied at a constant flow rate of 1.25 mL/min. The injector temperature and the FID temperature were set at 250 °C and 270 °C, respectively. The oven temperature was programmed from an initial temperature of 50 °C for 2 min, followed by increments of 5 °C/min until reaching a final temperature of 270 °C for 2 min. The FA component was estimated according to the retention time of standard FAs, and the data were collected via peak area normalization with C19 alkanoic acid (Sigma-Aldrich Shanghai Trading Co., Ltd., Shanghai, China) used as an internal standard.
2.7. RNA Extraction and Expression Analysis
The total RNA extraction of individual livers was performed using SYBR Premix Ex Taq Kit (Takara, Dalian, China), followed by the quantification for the total RNA concentration and purity via spectrophotometry, and the quality check through the use of agarose gel electrophoresis. The reverse transcription was completed with one microgram of total RNA using a reverse transcription kit (Thermo). The targeted genes were expressed via quantitative real-time PCR (qRT-PCR) under an ABI 7500 real-time PCR Detection system (Applied Biosystems, Foster City, CA, USA) using SYBR Green Real-time PCR Master Mix (Toyobo, Shanghai, China). The primers for the amplification of gene-specific PCR products were designed through the Primer-BLAST (
https://www.ncbi.nlm.nih.gov/tools/primer-blast/, accessed on 7 December 2023); the information of primers for qRT-PCR are shown in
Table 3. All primers were commercially provided by Integrated DNA Technologies (Hunan Accurate biological engineering Co., Ltd., Changsha, China). The real-time PCR procedure included a pre-denaturation step at 95 °C for 30 s, 40 cycles at 95 °C for 5 s, annealing and extension temperatures at 60 °C for 30 s, and the final dissociation. The final step was performed to ensure a single product was amplified. The qRT-PCR efficiency (E) was achieved with the equation E = 10
(−1/slope). Only after the primers were verified with an efficiency of approximately 100% through amplification can the gene expression results be analyzed using the 2
−ΔΔCt method [
45]; the data for all treatments were compared to the control group. β-actin was used as the internal reference, and its expression maintains relatively stable in the study.
2.8. Calculations
Weight gain (WG, %) = 100 × (final body weight (g/fish) − initial body weight (g/fish))/initial body weight (g/fish)
Specific growth rate (SGR, %/d) = 100 × (ln (finial body weight (g/fish)) − ln (initial body weight(g/fish)))/feeding duration (days)
Daily feed intake (DFI, %/d) = 100 × (feed intake (g/fish)/((final body weight (g/fish) + initial body weight (g/fish))/2 × days))
Feed efficiency (FE) = 100 × ((final body weight (g/fish) − initial body weight (g/fish))/feed intake (g/fish))
Survival (%) = 100 × (final number of fish)/(initial number of fish)
Hepatosomatic index (HSI, %) = 100 × (liver weight (g/fish)/body weight of sample fish (g/fish))
Condition factor (CF, g/cm3) = 100 × (body weight of sample fish (g/fish)/(body length (cm/fish))3)
Intraperitoneal fat rate (IPF, %) = 100 × (intraperitoneal fat weight (g/fish)/body weight of sample fish (g/fish)).
2.9. Statistical Analysis
The data were subjected to analysis of variance (ANOVA) to determine if significant differences occurred among treatments of CO replacing FO after the confirmation of the normality and homogeneity of variance through the Kolmogorov–Smirnov test and Levene’s test in SPSS Statistics 22.0 (SPSS, Michigan Avenue, Chicago, IL, USA). Data presented in percentages or ratios were subjected to data transformation before statistical analysis. The significance of linear or quadratic models were analyzed using orthogonal polynomial contrasts in order to describe the response of the dependent variable to CO inclusion levels. The results were given as the mean and standard deviation (SD). p values < 0.05 were considered statistically significant.
4. Discussion
The results of our study indicate that groupers fed diets with up to 100% CO had a comparable growth performance with those being fed the control diet, which was consistent with the observations that mostly or completely replacing FO with CO did not affect the growth performance in other studies with fish [
30,
32,
33,
46,
47]. In this study, the DHA and EPA contents in the 100% CO diet came entirely from a 30% fish meal containing 6% FO in this feed. This means that 1.8% FO in a 100% CO diet may meet low levels of the EFA requirements of groupers [
48]. The findings suggest that diets with high or 100% CO replacement can provide a low level of the EFA demand (such as DHA and EPA) for the growth of juvenile groupers under the current feeding regime, which further explained why groupers achieved a reasonable growth performance when given high CO feed. Recent studies have showed that the inclusion level of EPA + DHA to support the optimal health of fish, such as Atlantic salmon, is much higher than the level of the EFA requirement [
49]. From the perspective of the entire production cycle, further verification is needed to determine whether the low level of EPA + DHA can keep the normal growth and health levels of fish at the finishing stage. When EFAs meet the growth requirements, it is natural for VOs containing a large amount of non-EFAs to replace FO in a large proportion [
1,
50]. The findings are in accordance with the results of previous studies on other fish that were fed high CO diets [
30,
33]. Moreover, the percent of WG showed a quadratic response and peaked with the 25% CO diet, being significantly higher than that of the control diet, as observed with a peak for the 50% CO replacement diets in previous studies in large yellow croaker [
11] and Nile tilapia [
34] species, indicating a synergistic effect on growth. In other studies with golden pompano [
12] and gibel carp [
51], 100% CO diets also exhibited superior growth performance when compared to the FO diet. The enhanced feed utilization and/or feed intake may contribute to growth promotion, as observed in our current study and a previous study [
34], a result of the enhanced protein and energy metabolism of fish that consume a certain amount of SFAs [
52,
53] due to the preferential utilization of SFAs and MUFAs over PUFAs in fish [
15,
54,
55]. However, there are some studies reporting a decrease in fish growth when fish were fed diets with high CO [
35,
37,
38,
56,
57].
It is clear that MCFAs, rather than LC-PUFAs, are preferentially utilized as substrates for FA β-oxidation to provide more fuel for fish [
58]. However, higher levels of MCFAs did not further promote the β-oxidation of FAs for energy supply [
19]. Therefore, liver and intraperitoneal lipid accumulation occurred and exhibited an increasing trend with increasing levels of CO replacing FO in this study. This dose-dependent relationship has also been observed in previous studies with other fish species [
11,
12], indicating that dietary high CO inclusion may be the cause of increased lipid deposition in the liver and other visceral adipose tissues. This may partly explain why suitable levels of SFAs in feed promotes fish growth, while excessive SFAs intake causes inferior growth and/or an increase in lipid deposition in the body [
59,
60], as evidenced by an elevation in the HSI or/and lipid contents of the whole body and liver, as well as the IPF in this study and previous studies when fish were fed high CO diets [
11,
12,
34].
The results of our current study showed that the proximate compositions of both the whole body and muscle were not influenced by CO replacing FO, which was supported by what has been reported in previous studies [
11,
32,
34,
47,
51,
61]. Inconsistent with the aforementioned, the whole-body lipid content was elevated [
12,
21,
33], but was reduced [
37] in CO inclusion diets vs. FO diets. The inconsistency may be attributed to differences in ingredients, fish species, dietary lipid levels, and FA profiles.
Blood biochemical components are metabolic intermediates of nutrients and are usually used to measure the nutritional status of fish [
62]. In this study, we observed that both the serum LDL-C and TC had linear and quadratic responses, reaching a peak at the 25% CO inclusion level, while the serum HDL-C followed the similar trend with a peak being found at the 100% CO inclusion level, with increasing levels of CO replacing FO. The aforementioned changes were paralleled with the growth of orange-spotted groupers, reflecting two different states of lipid metabolism of fish fed diets with optimal CO levels and high CO levels. Inconsistent with our observations, the plasma TC was not affected by CO replacing FO in Nile tilapia [
21,
33] and gibel carp [
51]. We also observed an increasing trend of serum ALT activity with increasing levels of CO replacing FO, which disagreed with studies with golden pompano [
12] and Nile tilapia [
34], whose ALT values were not affected when replacing FO with CO. The elevated serum ALT activity may be attributed to high CO inclusion in higher dietary lipid levels in our current study (12% feed lipid) when compared to the latter (7% and 5.8% feed lipid for golden pompano and Nile tilapia, respectively). This means that the restricted growth performance of orange-spotted groupers was associated with the enhanced serum ALT activity, accompanied by a significant increase in liver lipid deposition caused by dietary 75% and 100% CO inclusion, suggesting the reflection of liver lipid metabolic disturbance [
63], potentially as a result of some lipid imbalance between lipid synthesis, β-oxidation, and transport in the liver [
49,
64,
65].
It is clear that the FA compositions in the liver and fillet of fish are influenced by the FA composition in the feed in previous studies [
66,
67,
68,
69,
70,
71,
72] and studies from our research team [
10,
14]. Interestingly, the n-3/n-6 PUFA ratios in the liver and dorsal muscle were positively correlated with those in the feeds and displayed a declining trend with response to the incremental CO level in the feed, reflecting the FA profile of the diet, as evidenced by our previous studies [
10,
14]. As mentioned above, a lower n-3/n-6 PUFA ratio in the feed promotes the transportation of MCFAs, linoleic acid, and linolenic acid into intermediate metabolism for energy production, but triggers DHA deposition in the liver and muscle [
15,
55,
58,
73]. Therefore, it is understandable that the lower n-3/n-6 PUFA ratio in the diets with above 75% CO enhanced a significant lipid accumulation in the liver [
11,
32], accompanied with the increased enrichment of SFAs and the decreased enrichment of LC-PUFAs in our current research and previous research on PO substitution for FO [
14]. Thus, it can be seen that a high CO inclusion level in feeds will compromise the nutritional value of fish flesh. In addition, there were identical DHA/EPA ratios in the tested feeds, and the liver DHA/EPA ratios did not alter across the dietary treatments, but the DHA/EPA ratios in the muscle showed a decreasing trend with increasing CO levels in feed. This indicates that the DHA and EPA contents in the muscle are more susceptible to the influence of dietary CO levels than in the liver [
66], reflecting the different utilization and deposition of DHA and EPA by fish [
15].
The homeostasis of lipid metabolism in cells of vertebrates mainly involves two important processes: lipid synthesis and decomposition [
64]. The key enzymes that regulate FA synthesis include fas, acc, and g6pd, while the key enzymes involved in lipid degradation include lpl, atgl, and hsl [
64,
65]. The cpt 1 transports LC-PUFAs into mitochondria for β-oxidation [
52]. The induction of lipolytic gene expression activates cpt 1 activity, thereby promoting FA β-oxidation [
74,
75]. The
srebp regulates metabolic enzyme genes including the
acc,
fas, and
scd involved in FA biosynthesis in vertebrate cells [
76]. On the contrary, the
pparα activation by n-3 LC-PUFA induces lipolytic gene expression and subsequently increases cpt-1 activity, thus enhancing FA β-oxidation [
74,
75]. In this study, with high levels of FO being replaced with CO, the significant elevation of the SFA content was at the expense of the significant decline of the LC-PUFA content, accompanied with up-regulating the expression of
fas,
acc,
g6pd, and
srebp-1c genes. Similarly, the enhanced expression of
fas,
acc, and/or
g6pd genes occurred for fish consuming a diet with high or complete levels of CO replacing FO [
11,
12,
32,
33,
37]. It is clear that high levels of n-3 LC-PUFAs (DHA or/and EPA) down-regulate
fas,
acc, and/or
srebp-1c in gilthead sea bream [
77], Atlantic salmon [
78], black seabream [
37,
79], and rainbow trout [
80], while low n-3 LC-PUFA levels up-regulate the expression of FA synthesis genes in black seabream [
79] as a result of inhibitory FA synthesis genes originating from PUFAs rather than SFAs [
81]. Therefore, an enhanced lipogenesis is induced via the up-regulation of the abovementioned genes due to the decrease in the dietary n-3 LC-PUFA levels [
79]. On the other hand, although the mRNA level of
pparα was not determined in this study, the expression level of the
cpt 1 gene was up-regulated with the 25–50% CO levels and down-regulated with the 75–100% CO levels. Similarly, a down-regulated expression of
pparα and
cpt-1 was observed in large yellow croakers fed a 100% CO substitution diet [
37], indicating decreased lipolysis. These findings show a declined β-oxidation, resulting in a reduction in liver lipid consumption in fish fed higher CO diets, eventually promoting an enhanced lipid accumulation in the hepatocytes [
82]. However, the expression of the
lpl gene remained unchanged, which means that the gene does not influence FA uptake by tissues [
65]. Meanwhile, the expression levels of the
atgl and
hsl genes were down-regulated with the high levels of CO replacing FO in this study and in previous studies [
37], but the opposite results occurred in large yellow croakers [
11] and largemouth bass [
33] when fed high CO diets. The discrepancy may be attributed to the varied degrees of β-oxidation in tissues due to the different FA compositions [
79].
The delta-6 fatty acyl desaturases (δfads) and elongases of very long-chain fatty acids (elovls) mediate the LC-PUFA synthesis [
83,
84]. The former converts LA and LNA into LC-PUFA, and the latter acts as the first step of the FA elongation process [
85,
86]. In the present study, we observed an up-regulated expression of the
δ6fad gene and the down-regulated expression of the
elovl 4 and
elovl 5 genes in orange-spotted groupers who were fed high CO diets, which was in accordance with our recently published results concerning FO being replaced with soybean oil or PO in the same fish species [
10,
14], as well as previous studies where CO replaced FO in black seabream [
37]. However, the up-regulated expression of
elovl 5 genes was observed in black seabream when 100% of the FO was replaced with soybean oil or PO [
37], Atlantic cod when 100% of the FO was replaced with camelina oil [
87,
88], and Atlantic salmon when FO was replaced with PO [
66]. The conflicting results indicate that the fish species and VO source may determine the extent to which different fish species biosynthesize LC-PUFAs from LA and LNA. In addition, the expression levels of the
δ6fad gene were positively correlated with, and the expression levels of the
elovl 4 and
elovl 5 genes were negatively correlated with the levels of CO replacing FO in this study, but the LC-PUFA contents were not promoted significantly, reflecting the weak ability of marine or carnivorous fish to synthesize LC-PUFAs.