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Open Access

Peer-reviewed

Research Article

Opportunistic gill infection is associated with TiO2 nanoparticle-induced mortality in zebrafish

  • Chiao-Yi Huang,

    Roles Formal analysis, Investigation

    Affiliation Department of Molecular Biology and Human Genetics, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Wei-Sheng Yu,

    Roles Investigation

    Affiliation Tzu-Chi Senior High School Affiliated with Tzu-Chi University, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Geng-Chia Liu,

    Roles Investigation

    Affiliation Tzu-Chi Senior High School Affiliated with Tzu-Chi University, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Shih-Che Hung,

    Roles Investigation

    Affiliation Institute of Medical Sciences, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Jen-Hsiang Chang,

    Roles Investigation

    Affiliation Department and Graduate School of Computer Science, National Pingtung University, Pingtung, Taiwan

    ⨯
  • Jen-Che Chang,

    Roles Investigation

    Affiliation Stella Maris High School, Hualien, Taiwan

    ⨯
  • Chia-Liang Cheng,

    Roles Investigation

    Affiliation Department of Physics, National Dong Hwa University, Hualien, Taiwan

    ⨯
  • Der-Shan Sun,

    Roles Investigation

    Affiliation Department of Molecular Biology and Human Genetics, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Ming-Der Lin,

    Roles Investigation

    Affiliation Department of Molecular Biology and Human Genetics, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Wen-Ying Lin,

    Roles Investigation

    Affiliation Department of Molecular Biology and Human Genetics, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Yin-Jeh Tzeng ,

    Roles Data curation, Formal analysis, Methodology, Software

    hhchang@mail.tcu.edu.tw (HHC); tzeng@mail.tcu.edu.tw (YJT)

    Affiliation Department of Molecular Biology and Human Genetics, Tzu-Chi University, Hualien, Taiwan

    ⨯
  • Hsin-Hou Chang

    Roles Conceptualization, Formal analysis, Funding acquisition, Project administration, Writing – original draft

    hhchang@mail.tcu.edu.tw (HHC); tzeng@mail.tcu.edu.tw (YJT)

    Affiliations Department of Molecular Biology and Human Genetics, Tzu-Chi University, Hualien, Taiwan, Institute of Medical Sciences, Tzu-Chi University, Hualien, Taiwan

    ⨯

Correction

1 Apr 2024: The PLOS One Staff (2024) Correction: Opportunistic gill infection is associated with TiO2 nanoparticle-induced mortality in zebrafish. PLOS ONE 19(4): e0301783. https://doi.org/10.1371/journal.pone.0301783 View correction

Abstract

The large amounts of engineered titanium dioxide nanoparticles (TiO2NPs) that have been manufactured have inevitably been released into the ecosystem. Reports have suggested that TiO2 is a relatively inert material that has low toxicity to animals. However, as various types of NPs increasingly accumulate in the ocean, their effects on aquatic life-forms remain unclear. In this study, a zebrafish model was used to investigate TiO2NP-induced injury and mortality. We found that the treatment dosages of TiO2NP are positively associated with increased motility of zebrafish and the bacterial counts in the water. Notably, gill but not dorsal fin and caudal fin of the zebrafish displayed considerably increased bacterial load. Metagenomic analysis further revealed that gut microflora, such as phyla Proteobacteria, Bacteroidetes, and Actinobacteria, involving more than 95% of total bacteria counts in the NP-injured zebrafish gill samples. These results collectively suggest that opportunistic bacterial infections are associated with TiO2NP-induced mortality in zebrafish. Infections secondary to TiO2NP-induced injury could be a neglected factor determining the detrimental effects of TiO2NPs on wild fish.

Citation: Huang C-Y, Yu W-S, Liu G-C, Hung S-C, Chang J-H, Chang J-C, et al. (2021) Opportunistic gill infection is associated with TiO2 nanoparticle-induced mortality in zebrafish. PLoS ONE 16(7): e0247859. https://doi.org/10.1371/journal.pone.0247859

Editor: Yogendra Kumar Mishra, University of Southern Denmark, DENMARK

Received: October 21, 2020; Accepted: February 15, 2021; Published: July 20, 2021

Copyright: © 2021 Huang et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

Data Availability: The NGS data are available on the NCBI Sequence Read Archive (SRR14876120).

Funding: This work was supported by research funding from Ministry of Science and Technology, Taiwan (98-2320-B-320-004MY3, 101-2320-B-320-004-MY3, 105-2923-B-320-001-MY3, 107-2311-B-320-002-MY3), Tzu-Chi University (TCIRP95002; TCIRP98001; TCIRP101001) and Tzu-Chi Medical Foundation (TC-NHRI105-02; TCMMP104-06; TCMMP 108-02-02; TCMMP108-04; TCAS-108-01).

Competing interests: The authors have declared that no competing interests exist.

Introduction

Titanium dioxide (TiO2) forms naturally as the well-known minerals rutile, anatase, and brookite phases. Industrial production of TiO2 occurs at a large scale, and an estimated 165,050,000 metric tons of TiO2 were produced worldwide between 1916 and 2011 [1]. Products containing TiO2 nanoparticles (TiO2NPs), such as sunscreen, cosmetics, paints, and semiconductors, are widely manufactured in various industries [2, 3]. For example, upon ultraviolet (UV) irradiation, the photocatalytic properties of TiO2 in the form of anatase enable it to catalyze H2O to release reactive oxygen species [4–6], which can be used in disinfectants and self-cleaning products [4, 5, 7–12]. The UV-shielding property of TiO2 has led to its use in skin-protecting sunscreens and cosmetics [13–15]. Although TiO2 is a vital component of these everyday products, its use means that human-made TiO2NPs will inevitably be released into the ecosystem. Experimental data–based safety guidelines for the release of TiO2NPs into fresh or salt water are not yet available. For example, neither the United States Environmental Protection Agency Aquatic Life Criteria nor the United Kingdom Environmental Quality Standards clearly indicate specific standards for the release of TiO2NPs [2]. Contamination by TiO2NPs has been proven to negatively affect aquatic life-forms, primarily through direct NP-induced toxicity [16, 17], although the other indirect damages remain unclear.

Zebrafish (Danio rerio) are widely used for vertebrate models in the study of diseases and is increasingly being used in preclinical and toxicological studies [16]. As many fundamental cellular pathways involved in the response to toxicants or stresses are highly conserved between the zebrafish and mammals, it has been considered as a ‘gold standard’ for environmental toxicity assessment [18]. More recently, it has been demonstrated to be a useful model for evaluating the environmental health and safety impacts of engineered nanomaterials and nanoscale products, which are increasingly being produced as a result of developments in nanotechnology [17–26]. In addition, benefited by the size and transparent body, zebrafish could be used to observe the impact of NPs on the induction of reactive oxygen species and apoptosis pathways at the cellular level [17, 20, 23, 24, 26, 27]. Furthermore, various analysis methods and high-throughput screening systems have been developed for use in toxicological evaluations [28, 29].

The direct effects of NP-induced toxicity have been revealed by recent studies [19–27, 30–34]. However, the NP-induced collateral damages, such as interactions between injured fish and surrounding microorganisms, have not been considered, and their role remains unclear. We hypothesized that NP-induced injuries are desired conditions for the amplification of those opportunistic infectious bacteria, which may be involved in NP-induced detrimental effects in aquatic life forms. Accordingly, in this study, we investigated the progression of photocatalysis-independent TiO2NP-induced injury using a zebrafish model. We found that TiO2NP-induced opportunistic bacterial gill infections play a critical role in TiO2NP-induced zebrafish death. Potential implications are also discussed.

Materials and methods

Chemicals and TiO2NPs

The chemicals used in this study were purchased from Sigma-Aldrich (St. Louis, MO, USA). To prepare the stock solutions of 1 mg/mL Degussa P25 (Evonik Degussa, Essen, Germany) TiO2NPs (21 ± 5 nm) [4, 8, 35], the NPs were dispersed in distilled deionized water under sonication (50 W/L, 40 kHz) for 20 min. Test TiO2NP solutions were prepared immediately before use through dilution of the stock solutions with distilled deionized water and sonication (50 W/L, 40 kHz) for 20 min. In our studies, the particle size distributions and ζ-potential were estimated using the dynamic light scattering method (DLS) with a Zetasizer Nano ZS (Malvern Instruments, Malvern, UK) [36, 37]. The averaged ζ-potential of the used TiO2NPs in solution was 22.08 ± 0.32 mV, with pH value around 5.35–5.45. The TiO2NPs obtained (from Sigma Aldrich) has an averaged particle size about 20 nm according to company specification, but in medium the particles aggregated and measured to be 100 nm.

Zebrafish maintenance and experimental procedure

Adult wild zebrafish were used in the experiment and were kept in a semistatic system with charcoal-filtered tap water (pH 7.0–7.4) at 28 ± 0.5°C as recommended in a previous study [38], with a 12-h light–12-h dark (12L:12D) photocycle (Classictone incandescent lamp, Philips; Taiwan, without illuminating UV to avoid UV-induced photocatalysis [5, 11, 12, 33, 39, 40]). The fish were fed newly hatched brine shrimp and pellet food (Zeigler Brothers, Gardners, PA, USA) and were kept in 30-L glass tanks with 20 L of water per tank. The zebrafish undergoing testing were exposed to TiO2NPs in well water for 21 days, and the mortality was recorded each day. The Kaplan Meier curves are plotted using the Online Application for the Survival Analysis of Lifespan Assay (http://sbi.postech.ac.kr/oasis) [41–44]. Fish from three of the 3-L tanks were selected for behavior analysis, in which the swimming speed of the zebrafish was analyzed using Kinovea software (version 0.8.24; available at http://www.kinovea.org/) in accordance with methods used in previous studies [45, 46]. After the experiment, the fish were euthanized with an overdose of tricaine methanesulfonate MS-222 (0.03%; Sigma-Aldrich). The gill and fin tissue samples were excised, weighed, cut into small pieces, and homogenized with 100 μL of phosphate-buffered saline at 4°C. Next, the 30-μL tissue homogenates were placed on luria broth (LB) agar plates (BD Difco LB Agar; Becton Dickinson, Taipei, Taiwan), using standard bacterial culture protocols [39, 47]. The bacteria colony–forming unit on the plates was determined at a 24-h incubation period at 37°C according to previously described methods [39]. The zebrafish (AB strain) used in the present study were obtained from the zebrafish facility at the Laboratory Animal center of Tzu Chi University. Institutional Animal Care and Use Committee of Tzu Chi University approved all animal experiments in this study (approval ID: 105060).

Ethics statements

All methods on the collection and analyses of zebrafish samples were performed in accordance with Animal Protection Act, Taiwan, and were approved by the Institutional Animal Care and Use Committee of Tzu-Chi University, Hualien, Taiwan (approval ID: 105060).

Microbiome analysis

DNA preparation.

The bacterial genomic DNA was extracted from the 200-mg frozen gill samples with a QIAamp Fast DNA Stool Mini Kit (Qiagen, Venlo, Netherlands). After isolation, the DNA yield was approximately 1–2 μg. The DNA sample was stored at −20°C before polymerase chain reaction (PCR) amplification.

PCR amplification.

The DNA samples were adjusted to 25 μg/mL. Forward and reverse primers that were complementary upstream and downstream of the V3-V4 region of 16S were designed with Illumina overhang adapters, and used to amplify templates from bacterial genomic DNA. The following 16S amplicon PCR primer sequences were shown: forward, 5’-TCG TCG GCA GCG TCA GAT GTG TAT AAG AGA CAG CCT ACG GGN GGC WGC AG-3’; reverse, 5’-GTC TCG TGG GCT CGG AGA TGT GTA TAA GAG ACA GGA CTA CHV GGG TAT CTA ATC C-3’. The PCR products were then purified with a GenepHlow Gel/PCR purification kit (Geneaid, New Taipei City, Taiwan).

Index PCR and clean up.

The Illumina sequencing adapters and dual indices were attached to the PCR products using the Nextera XT Index Kit (Illumina Inc, San Diego, CA, USA). Next, AMPure XP beads were used to clean up the final libraries, and the expected size on the Bioanalyzer trace of the final libraries was approximately 630 bp.

Normalization and sequencing.

Libraries were normalized and pooled and then sequenced on the MiSeq System using v3.0 reagents (paired-end 250 bp, Illumina Inc).

Data analysis.

Because microbiota profiling using specific hypervariable regions of 16S ribosomal RNA cannot reach taxonomic levels lower than the family or genus level [48], we obtained the results at the family level. The microbiome analysis data is available at NCBI Sequence Read Archive, Accession: SRR14876120.

Statistical analysis.

The mortality of zebrafish was calculated using Online Application for the Survival Analysis of Lifespan Assay (http://sbi.postech.ac.kr/oasis) [41–44]. A t test was used to assess the statistical significance of differences in antimicrobial effects. A P -value of less than 0.05 (P < 0.05) was considered significant. The statistical tests were performed and output to graphs using Microsoft Excel (Microsoft, Taipei, Taiwan) and SigmaPlot (Systat Software, Point Richmond, CA, USA).

Results

Increased TiO2NP levels in water reduced motility and induced mortality in adult zebrafish

Two doses (5 and 40 mg/L) of TiO2NPs were used in the investigation of TiO2NP-induced mortality in adult zebrafish (Fig 1). We found that the 5 and 40 mg/L doses of TiO2NPs induced 100% mortality in adult zebrafish after 20 and 7 days, respectively (Fig 1A experiment outline; Fig 1B).

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Fig 1. Zebrafish mortality is associated with increased TiO2NP levels in the water.

(A) Experiment outline. (B) TiO2NP dose–dependent induction of mortality in zebrafish. (C) Increase in water OD after the addition of TiO2NPs. * P < 0.05, compared with the untreated group; † P < 0.05, compared with the 40 mg/L treatment groups (B); * P < 0.05, compared with the untreated groups; † P < 0.05, compared with the groups at day 0 (C) n = 16.

https://doi.org/10.1371/journal.pone.0247859.g001

Although no mortality had occurred by day 6, the absorbance of water in the zebrafish tanks was considerably increased compared with that of the untreated control groups (Fig 1C, untreated groups vs. groups treated with 5 mg/L TiO2NPs). For this reason, we hypothesized that the zebrafish in the groups treated with 5 mg/L TiO2NPs may have been subject to TiO2NP-induced injury prior to mortality, and the resulting release of blood or tissue fluids would subsequently cause optical-density changes in the water. Consequently, to assess the physical condition of the fish, the motility (Fig 2A–2C, experiment setting; Fig 2D–2F) and body weight (Fig 2G) of the fish in the untreated groups were compared with those of the groups treated with 5 mg/L TiO2NPs prior to mortality (day 6 in the 5 mg/L TiO2NPs groups). We found that when compared with the untreated groups, the groups treated with 5 mg/L TiO2NPs exhibited remarkably reduced motility, as indicated by decreases in both the average swimming speed and spot swimming speed of the zebrafish (Fig 2D–2F). These results indicated that the fish in the groups treated with 5 mg/L TiO2NPs were harmed by the TiO2NPs.

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Fig 2. Analysis of zebrafish motility in water containing TiO2NPs.

(A) Experiment outline and settings. (B, C) Sequential images of zebrafish in tanks with water containing TiO2NPs. (D) 2D plots of zebrafish spot swimming speed versus average swimming speed at day 0 (untreated) and (E) day 6 (with or without TiO2NPs); dashed lines represent the average spot speed and average swimming speed of the groups at day 0. (F) Statistical analysis of zebrafish swimming speed and (G) body weight under various conditions. * P < 0.05, compared with the untreated groups at day 6. n = 7.

https://doi.org/10.1371/journal.pone.0247859.g002

TiO2NP-induced mortality in zebrafish is associated with increased gill bacterial counts

Pure TiO2NPs do not display antibacterial property unless with exposure of UV [4, 10–12, 33, 39, 40, 49]. To maintain zebrafish, incandescent lamps were used as a light source, which does not irradiate UV light to induce photocatalysis, and thus the TiO2NPs will not exert antibacterial effects in this experimental condition [5, 11]. To further investigate whether the increased water optical density (OD) was caused by an overgrowth of bacteria, we analyzed bacteria colonies from the water and the zebrafish tissues by using a plating method (Fig 3 and S1 Fig in S1 Data). We found that the TiO2NP treatments substantially increased the number of bacteria colonies in the water samples. Among the analyzed zebrafish tissues, including those from gills, dorsal fins, and caudal fins, only the gill samples exhibited a significant increase in the number of bacteria colonies (Fig 3; ** P < 0.01, TiO2-treated groups vs. untreated groups). This result indicates that TiO2NP-induced zebrafish injury involves gill infection.

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Fig 3. Analysis of the relative number of bacteria found in the water and zebrafish tissue samples.

(A) Experiment outline and (B) sampling positions for bacterial culture. The culturable bacterial number in (B) the water, (C) zebrafish gill, (D) dorsal fin, and (E) caudal fin after analysis with the plating method. ** P < 0.01, compared with the untreated control groups.

https://doi.org/10.1371/journal.pone.0247859.g003

Because the plating method can only reveal culturable bacteria [50, 51], metagenomic analysis was performed to investigate the entire spectrum of the bacteria population in the infected zebrafish gills. The relative abundance (% relative to the total) of the bacteria populations was analyzed in specific hypervariable regions of 16S ribosomal RNA through new-generation sequencing analyses (Fig 4 and S2 Fig in S1 Data). We found that the phyla Proteobacteria, Bacteroidetes, and Actinobacteria, all of which are bacteria found in normal zebrafish gut microbiomes [52–55], accounted for more than 95% of the total bacteria counts (Fig 4). Because the fish culture conditions did not include pathogens, these results indicate that TiO2NP-induced zebrafish gill injury is associated with opportunistic infection of the gut normal flora.

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Fig 4. Metagenomic analysis of bacterial communities in the gill samples of zebrafish with TiO2NP-induced injury.

(A) Relative abundance (% relative to the total) of the bacteria populations calculated for specific hypervariable regions of 16S ribosomal RNA through new-generation sequencing analyses. (B) Relative abundance (% counts of total) of the top 10 overall bacteria families (listed in the following paragraph). (C) Top 5 bacteria families in the Proteobacteria phylum (most abundant phylum; listed below). (D) Top 4 bacteria families in Bacteroidetes phylum (second abundant phylum; listed below).

https://doi.org/10.1371/journal.pone.0247859.g004

Discussion

Zebrafish have been used to study engineered nanomaterials and NPs in various fields, such as biomedical research [38, 56–58] and studies on environmental health and safety [59, 60]. Most relevant studies have reported that TiO2NPs are toxic and induce mortality in zebrafish embryos but are less toxic and cause less mortality in adult zebrafishes; this finding is likely attributable to the fact that these studies have tended to focus only on observations of acute stimulation [18, 61–64]. In addition, although researchers have concluded that the injury and mortality in the tested zebrafish were attributable to the chemical and physical properties of NPs [18, 61–64], damage caused by secondary infections has yet to be investigated.

In our study, we found that treating adult zebrafish with 1–3 weeks of relatively low doses (5–40 mg/L) of TiO2NPs led to reduced motility, reduced body weight, and increased mortality. Additionally, we also found that the adverse effects of TiO2NPs were associated with gill infection. Accordingly, we postulate a hypothetical model, in which TiO2NPs-induced gill injury the fish at the first stage, while opportunistic gill infection may further exacerbate the injury and then lead to mortality (Fig 5). This suggests that wild fish inhabiting rivers, lakes, and oceans may not immediately die upon exposure to water contaminated by TiO2NPs but that subsequent opportunistic infections determine the survival of aquatic life-forms subject to NP-induced injury.

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Fig 5. A model for putative role of opportunistic gill infection in TiO2NP-induced mortality in zebrafish.

After TiO2NP treatments, the gill of healthy zebrafishes (A) become injured (B). The gill injury further leads to opportunistic infection and increased mortality in zebrafish (C).

https://doi.org/10.1371/journal.pone.0247859.g005

Through metagenomic analysis, we discovered that bacteria found in the gill samples of zebrafish with NP-induced injury, such as the phyla Proteobacteria, Bacteroidetes, and Actinobacteria, accounted for more than 95% of the total bacteria count; these types of bacteria are all found in normal zebrafish gut microflora [52–55]. This result is likely attributable to the fact that the zebrafish in the experiment were kept under pathogen-free conditions; no pathogens other than normal flora were present. However, considering the fact that a larger number of pathogenic microorganisms coexist in the normal habitats of wild aquatic life-forms, TiO2NPs may theoretically be more toxic to wild fish and lead to higher mortality. As an increasing amount of NPs are released into rivers, lakes, and oceans [65, 66], infections in wild fish and other aquatic life-forms as a result of NP-induced injury represent a serious issue worthy of further investigation.

Top 10 bacteria families and abundance (% total counts) in all detections (Fig 4B) (k: Kingdom; P: Phylum; c: Class; o: Order; f: Family)

  1. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Betaproteobacteriales;f__Burkholderiaceae;g__Sphaerotilus.
  2. k__Bacteria;p__Bacteroidetes;c__Bacteroidia;o__Sphingobacteriales;f__env.OPS_17;g__Ambiguous_taxa;s__Ambiguous_taxa
  3. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Aeromonadales;f__Aeromonadaceae;g__Aeromonas.
  4. k__Bacteria;p__Actinobacteria;c__Actinobacteria;o__Corynebacteriales;f__Mycobacteriaceae;g__Mycobacterium.
  5. k__Bacteria;p__Fusobacteria;c__Fusobacteriia;o__Fusobacteriales;f__Fusobacteriaceae;g__Cetobacterium
  6. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Betaproteobacteriales;f__Rhodocyclaceae;g__Methyloversatilis
  7. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Enterobacteriales;f__Enterobacteriaceae;g__Plesiomonas;s__Ambiguous_taxa.
  8. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Betaproteobacteriales;f__Methylophilaceae;g__Methylophilus
  9. k__Bacteria;p__Proteobacteria;c__Alphaproteobacteria;o__Rhizobiales;f__Devosiaceae;g__Devosia.
  10. k__Bacteria;p__Bacteroidetes;c__Bacteroidia;o__Chitinophagales;f__Chitinophagaceae;g__Terrimonas.

Top 5 bacteria families and abundance (% of total counts) in Proteobacteria phylum (Fig 4C)

  1. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Betaproteobacteriales;f__Burkholderiaceae;g__Sphaerotilus.
  2. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Aeromonadales;f__Aeromonadaceae;g__Aeromonas.
  3. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Betaproteobacteriales;f__Rhodocyclaceae;g__Methyloversatilis.
  4. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Enterobacteriales;f__Enterobacteriaceae;g__Plesiomonas;s__Ambiguous_taxa.
  5. k__Bacteria;p__Proteobacteria;c__Gammaproteobacteria;o__Betaproteobacteriales;f__Methylophilaceae;g__Methylophilus.

Top 4 bacteria families and abundance (% of total counts) in Bacteroidetes phylum (Fig 4D)

  1. k__Bacteria;p__Bacteroidetes;c__Bacteroidia;o__Sphingobacteriales;f__env.OPS_17;g__Ambiguous_taxa;s__Ambiguous_taxa.
  2. k__Bacteria;p__Bacteroidetes;c__Bacteroidia;o__Chitinophagales;f__Chitinophagaceae;g__Terrimonas.
  3. k__Bacteria;p__Bacteroidetes;c__Bacteroidia;o__Cytophagales;f__Spirosomaceae;g__Emticicia.
  4. k__Bacteria;p__Bacteroidetes;c__Bacteroidia;o__Chitinophagales;f__Chitinophagaceae;g__Sediminibacterium

Acknowledgments

The authors would like to thank Yi-Jhen Su and Chien-Ying Huang at National Dong Hwa University, Taiwan, for their help in zeta potential and particle size measurements. The authors also wish to thank the Center for Biotechnology, and Bioinformatics & Biostatistics Core Lab, Center of Genomic Medicine, National Taiwan University, for their help on the analyses of microbiome of injured zebrafishes. The authors are grateful to the Core Facility Center, Tzu Chi University for the help on DNA preparation and confocal microscopy analyses.

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