1. Introduction
Aquaculture has become very important in increasing global access to fish [
1,
2], improving nutrition to the deprived populations of the world [
3]. However, burden of infectious diseases has been identified as the greatest of all setbacks in the quest to sustainable global aquaculture growth [
4,
5], with losses exceeding 6 billion USD per annum [
6]. More than 50 % of the most common devastating infectious diseases of fish are caused by bacteria [
7,
8].
In response, frequent and indiscriminate use of antibiotics have characterized aquaculture in many countries [
9,
10,
11]. The consequences have been antibiotic resistance in several bacteria strains resulting in high numbers of diverse bacteria in aquacultural systems [
12]. As a result, treatments for some common fish bacterial diseases become less successful as it is reported for furunculosis and edwardsiellosis, increasing losses to these diseases. Also, some fish bacterial pathogens including
Streptococcus iniae, and
Photobacterium damselae, which are zoonotic, carry antimicrobial resistant genes like the extended-spectrum beta-lactamases. These bacteria, hence, the resistant genes are transferrable to humans through contact and food [
13]. Due to these, some countries have strict regulations completely prohibiting the use of some and overall reduction in the application of chemotherapeutic drugs in aquaculture [
14,
15]. Vaccines and probiotics are considered safer alternatives in preventing diseases in aquaculture but there remain difficulties [
16,
17]. The use of nanoparticles of high antimicrobial ability is considered the most modern, advanced, and promising approach to fish disease control in aquaculture [
18]. Several metal nanoparticles have been found to exhibit strong antibacterial properties [
19]. However, bioaccumulation in fish flesh, gene toxicity and induction of oxidative to fish have raised serious concerns about their use in aquaculture [
20,
21,
22]. Preference is growing for nanoparticles which are biodegradable, easy to prepare and with no or very minimal toxicity threats [
23]. Poly (alkyl cyanoacrylate) (PACA) have been used in medicine as adhesives and its nanoparticles as drug carriers for several decades [
24,
25,
26]. However, antibacterial property and hence suitability of cyanoacrylate nanoparticles as antibiotic agents are recent discoveries [
27]. Their advantages, including easy fabrication and functionalization, biocompatibility, and biodegradability, make them promising candidates for disease control including fish disease management in the aquaculture industry [
26,
28]. Cyanoacrylate nanoparticles have high affinity for the glycopeptides that make up the cell walls of bacteria. They attach to the cell walls, induce distortion of cell wall synthesis, leading to autolysis and lysis by mechanisms detailed by Shirotake [
23]. Widyaningrum et al. [
29] also reported a similar interaction between isobutyl cyanoacrylate nanoparticles, iBCA-NPs, and algae. Thus, unlike antibiotics, iBCA-NPs, like other nanoparticles, employ physical action against pathogens, hence, it is believed that the possibility of emergence of resistant bacteria is reduced. The antibacterial activity of cyanoacrylate nanoparticles remains a new research area. As much as we know, the application of cyanoacrylate nanoparticles in disease control in the field of fisheries has not yet been considered by anyone else. In this study, we investigated the in vitro antimicrobial activity of two iBCA-NPs (NP30 and D60) against twelve prominent fish disease pathogens. We also assessed the selection preference and safety of D60 and NP30 for the land-based aquacultural production of rainbow trout, [
Onchorhyncus mykiss (Walbaum, 1792)], an important aquaculture species, when administered through feed.
4. Discussion
The characteristics of the cyanoacrylate nanoparticles, iBCA-NPs, (D60 and NP30) were very similar to iBCA-NPs (25 nm and 180 nm), respectively, described by Widyanigrum et al. [
29]. This is because, in both instances, the monomers used were the same, and reagents and methods of formulation were very similar.
From the results of the antibacterial and bactericidal activity examined in this study, the isobutyl iBCA-NPs we studied demonstrated strong antibacterial activity against all the bacterial pathogens we examined (
Table 1). NP30 was bactericidal against 100 % of the pathogens while D60 was bacteriostatic against most of them (
Table 1). Shirotake, [
27] reported high affinity of iBCA-NPs for glycoproteins and junctioning between iBCA-NPs and Gram-positive bacteria resulting in bacterial wall autolysis. The dispersant types played very important roles in differentiating between the sizes of the two iBCA-NPs and in preventing their agglomeration consistent with Guzman et al., [
49]. However, the dispersants did not interfere with the antimicrobial effect of our iBCA-NPs, as none showed significant antibacterial against the bacterial strains. That is, from our results, the iBCA-NPs, not the dispersants, were the source of the antibacterial activities observed (
Figure 2 & S1). Widyaningrum et al. [
29] reported a similar finding, where the dispersants had no effects on algal cell walls. The massive global aquacultural losses to these bacteria species are well documented [
50,
51,
52,
53,
54,
55,
56,
57,
58]. The cost of using antibiotics to control these aquacultural pathogens is enormous [
11] and it will require several different types of vaccines to combat them. The importance of the efficacy of a single safer antimicrobial agent, iBCA-NP, to manage several bacterial strains cannot be overemphasized.
The comparatively higher antimicrobial activity of NP30 might be due to its minute particle size (mean size = 30 nm), increasing the surface area for attachment to the bacterial pathogens. This assertion agreed with Widyaningrum et al. [
29] who found an inverse relationship between iBCA-NPs size and algal cell mortality at any given concentration. D60 particles were larger (mean size = 180 nm) resulting in a more viscous colloid (
Figure 1b). The superior performance of NP30 might also be explained by the negative electrical charge effect between NP30 particles induced by its anionic dispersant. This effect is thought to keep particles uniformly distributed in solution and in constant motion, increasing contact with bacteria cells. The nanoparticle-size-antibacterial activity relationship has been widely studied. Consistent with our results, generally, the smaller the size, the higher the activity [
59,
60,
61].
The presence of a lipopolysaccharide outer membrane and chromosomally encoded drug efflux mechanisms in Gram-negative bacilli is considered to confer comparative higher antibacterial resistance on them than on Gram-positive bacteria [
62,
63,
64]. Consistent with this, Gram-negative bacteria were more resistant to our iBCA-NPs (
Table 1). Importantly, although susceptibility of several Gram-positive bacteria, including multiple antibiotic resistant bacteria, to iBCA-NPs has been reported, all previous work reported no antibacterial activity of iBCA-NPs on Gram-negative baccilli [
27,
65]. The extreme sensitivity of
P. damselae, and
T. maritimus and indeed the susceptibility of other Gram-negative bacilli we tested was thus an interesting result. It is possible that differences in the iBCA-NPs preparation method and bacterial strains used accounted for the variations in results as it is known that differences in structure and composition between N-acetylglucosamine and N-acetylmuraminic acid may account for differences in antimicrobial resistance among Gram-negative bacteria [
66,
67]. The antimicrobial resistance of
Aeromonas spp. and
Vibrio spp., consistent with our results, are well documented [
31,
68,
69,
70,
71,
72,
73]. On the other hand, although differences have been demonstrated in the mechanism of virulence and pathogenicity of the typical and atypical
E. tarda strains [
33,
34], their antimicrobial susceptibility and resistance to both iBCA-NPs were very similar (
Table 1). Their structural indistinguishability and molecular closeness might have accounted for the observation [
74,
75].
We observed increasing GI % with decreasing concentration for NP30 against
T. maritimum (
Figure 5 c) which we initially thought to be the display of the Eagle effect [
38]. Divya et al., [
76] reported similar results, where lower, rather than higher, concentrations of some of their chitosan nanoparticles showed higher growth inhibition. However, bactericidal properties were observed at both the higher NP30 concentrations (500 µl) and lower concentrations (until 31.25 µl).
T. maritimum is a filamentous bacterium and possesses rhizoids with which gliding colonies adhere one-to-another creating a huge network of bacteria mass [
54]. On the other hand, the iBCA-NPs assay transparency increased (decreasing OD
620 value) by dilution. The effect of bacteria lysis and assay transparency on OD reading was suspected to have accounted for the inconsistency observed. As much as we know, this study presents the lowest concentrations of iBCA-NPs at which antibacterial activities have been observed [
65]. If the in vitro efficacy of our iBCA-NPs is replicated
in vivo, their relevance in the disease-burdened aquacultural industry may be enormous.
Growth performance and safety evaluation in rainbow trout: The treatments did not have adverse effects on water quality parameters [
77] throughout the period of the study.
In vitro, as well as
in vivo, medium molecular weight cyanoacrylate nanoparticles like iBCA-NPs significantly degrade in 24 hours [
24,
25,
28]. This, coupled with high rate of water exchange (85.5 % h
-1) might have played a role in maintaining stable water quality parameters despite the heavy feed ration.
The growth test lasted for twelve weeks; a duration we considered long enough to reveal any effects the iBCA-NPs might have on rainbow trout. During this duration, rainbow trout were consistently fed with iBCA-NPs-supplemented feed at the highest possible concentration (3,571.4 mg/kg feed). At high concentrations, several metallic nanoparticles have been found to be toxic to fish, killing fish [
47]. Growth inhibition was also reported in
Cyprinus carpio by copper nanoparticles after thirty days of exposure [
78]. On the contrary, growth performance was excellent in the iBCA-NPs groups as in the control and sometimes slightly better, but not significantly higher (
P > 0.05), than the latter. The comparatively significant decline in gain rate (
Figure 7a) after the first four weeks was consistent with documented growth trends of rainbow trout. Feed conversion efficiency is reportedly lower in older rainbow trout [
79] which hypothesis was consistent with our results (results not shown). Fish condition factor, K, hepatosomatic and viscerosomatic indices (HIS & VSI respectively) are important indicators of fish health, metabolism and of energy reserves in fish [
43,
44,
45]. The K, HSI and VSI values we obtained in this study are similar to the values reported for healthy fish in similar studies [
80,
81]. Therefore, like the growth performance parameters, these indices also suggested no toxic effects of the iBCA-NPs (
Table 2).
Both the complement system and lysozymes are important components of the first barrier of fish against disease pathogens and are also important growth inhibition factors of bacterial agents. They also possess lytic activity against viruses and both Gram-positive and Gram-negative bacteria [
82,
83,
84,
85]. In addition, the complement system of fish is critical in the modulation of the adaptive immune response and has chemotaxic, opsonization, and pro-inflammatory functions, making it one of the most important factors of fish innate immune system [
82,
83,
86]. Increased alternative complement hemolysis of foreign objects like sheep erythrocytes are indicative of improved immune response [
82]. While the relationship between the level of lysozyme activity and immunity in fish remains unclear, generally, long term exposure to toxins and immunosupressants have decreasing effects on it. On the other hand, immunostimulants and dietary supplements like prebiotics are known to be associated with increasing lysozyme levels and fish complement titer, conferring protection against a variety of fish diseases [
83,
84,
85]. In this study, lysozyme activity was significantly higher (
P < 0.05) in the twelfth week than fourth week (
Figure 7b). Similarly, complement titer was significantly higher in the eighth week than the fourth week (
Figure 7c). Generally, the immune indicators increased with age suggesting improved immunity of rainbow trout with age, irrespective of treatment. This agrees with Sauer et al. [
87] that age improves, not decline, fish health. Considering both indicators therefore, iBCA-NPs had no adverse effects on rainbow trout in this study.
The major concerns about nanoparticle use in aquaculture include, among others, oxidative damage to fish and impairment of many biomarkers. Metallic nanoparticle-induced oxidative stress has been reported by several publications [
22,
47,
88,
89,
90,
91]. Similar damages in fish have been reported in the use of carbon-based and green synthesized cadmium nanoparticles [
92,
93]. These damages have been proven to correlate with increased acute stress, signified by increased concentrations of blood cortisol and glucose in the Nile tilapia and the African catfish [
47,
93]. Toxic effects are fought off by fish by increased rates of glycolysis, resulting in increased glucose concentration [
93]. In the current study, glucose concentration for all groups was consistently optimal (mean = 60.02 ± 0.76 mg/dl) [
46,
47,
93] which meant that at 3,571.4 mg(iBCA-NP)/kg feed, the iBCA-NPs did not induce stress in rainbow trout. Compared to the liver, blood plasma estimates of oxidative stress are more accurate because the former has high activity of antioxidant enzymes to adapt to, and cope with oxidative stress [
90]. Persistent or high oxidative stress may cause notable damages to proteins, decreasing SOD activity [
90]. On the contrary, plasma SOD activity also confirmed that the SOD antioxidant defense systems of iBCA-NPs treated rainbow trout were as good as fish in the control group (
Figure 7d).
A couple of pathways have been predicted for orally administered poly (alkyl cyanoacrylate), nanoparticles, PACA-NPs. According to Vauthier et al. [
26] translocation via the Peyer’s patches in the ileum is the major pathway for drug-carrier PACA-NPs. Catalyzed by esterases from serum, lysosomes, and pancreatic juice, they are eliminated from the body by the kidneys in the forms of alkyl alcohol and poly-cyanoacrylic acid. Unlike shorter-chain derivatives, butyl derivatives and higher homologs of PACA are considered non-toxic to tissues [
25] and safer than any other antimicrobial substances [
27]. In agreement, from results of the current study, at 3,571.4 mg(iBCA-NP)/kg feed, iBCA-NPs produced excellent growth and innate immunity of rainbow trout was not compromised.
Author Contributions
Conceptualization, M.G.A., K.M., M.H., K.I., F.B. and S-I.O; Methodology, M.G.A., K.M., M.H., K.I., F.B. and S-I.O; Software, M.G.A., K.I. and F.B.; Validation, M.G.A., K.M., M.H., K.I., F.B. and S-I.O; Formal Analysis, M.G.A., K.M., and M.H.; Investigation, M.G.A., K.M., M.H. and S-I.O.; Resources, M.G.A., K.I., F.B. and S-I.O; Data Curation, M.G.A., K.M., M.H. and S-I.O.; Writing – Original Draft Preparation, MGA.; Writing – Review & Editing, M.G.A., K.M., M.H. and S-I.O.; Supervision, S-I.O.; Project Administration, M.G.A., K.M., M.H., K.I., F.B. and S-I.O.; Funding Acquisition, M.G.A., K.I., F.B. and S-I.O.