| Literature DB >> 24594555 |
Jorge A Masso-Silva1, Gill Diamond2.
Abstract
Antimicrobial peptides (AMPs) are found widely distributed through Nature, and participate in the innate host defense of each species. Fish are a great source of these peptides, as they express all of the major classes of AMPs, including defensins, cathelicidins, hepcidins, histone-derived peptides, and a fish-specific class of the cecropin family, called piscidins. As with other species, the fish peptides exhibit broad-spectrum antimicrobial activity, killing both fish and human pathogens. They are also immunomodulatory, and their genes are highly responsive to microbes and innate immuno-stimulatory molecules. Recent research has demonstrated that some of the unique properties of fish peptides, including their ability to act even in very high salt concentrations, make them good potential targets for development as therapeutic antimicrobials. Further, the stimulation of their gene expression by exogenous factors could be useful in preventing pathogenic microbes in aquaculture.Entities:
Year: 2014 PMID: 24594555 PMCID: PMC3978493 DOI: 10.3390/ph7030265
Source DB: PubMed Journal: Pharmaceuticals (Basel) ISSN: 1424-8247
Characterized antimicrobial peptides from fish, by species. Listed is the number of peptides of each family [reference].
| Species | Piscidins | Defensins | Hepcidins | Cathelicidins | Histone-derived | ||
|---|---|---|---|---|---|---|---|
| Common name | Scientific name | Habitat | |||||
| American plaice |
| Marine | 2 [ | ||||
| Antarctic toothfish |
| Marine | 3 [ | ||||
| Atlantic cod |
| Marine and brackish | 2 [ | 1 [ | 1 [ | 1 [ | 1 [ |
| Antarctic eelpout |
| Marine | 2 [ | ||||
| Atlantic hagfish |
| Marine | 3 [ | ||||
| Atlantic salmon |
| Marine, brackish and freshwater | 2 [ | 2 [ | 1 [ | ||
| Ayu |
| Marine, brackish and freshwater | 1 [ | 1 [ | |||
| Barramundi |
| Marine, brackish and freshwater | 2 [ | ||||
| Black porgy |
| Marine and brackish | 7 [ | ||||
| Black rockfish |
| Marine | 2 [ | ||||
| Blotched snakehead |
| Freshwater | 1 [ | ||||
| Blue catfish |
| Freshwater and brackish | 1 [ | ||||
| Blunt snout bream |
| Freshwater | 1 [ | ||||
| Brook trout |
| Marine, brackish and freshwater | 2 [ | ||||
| Brown trout |
| Marine, brackish and freshwater | 1 [ | ||||
| Channel catfish |
| Freshwater | 1 [ | 1 [ | |||
| Chinese loach |
| Freshwater | 1 [ | ||||
| Common carp | Freshwater and brackish | 2 [ | 1 [ | ||||
| European seabass |
| Marine, brackish and freshwater | 1 [ | 1 [ | |||
| Gilthead seabream |
| Marine and brackish | 1 [ | 1 [ | |||
| Grayling |
| Freshwater and brackish | 1 [ | ||||
| Half-smooth tongue sole |
| Marine, brackish and freshwater | 1 [ | ||||
| Atlantic halibut |
| Marine | 1 [ | 1 [ | |||
| Hybrid striped bass |
| Marine, brackish and freshwater | 4 [ | 1 [ | |||
| Icefish |
| Marine | 1 [ | ||||
| Olive flounder |
| Marine | 2 [ | ||||
| Japanese rice fish |
| Freshwater and brackish | 1 [ | ||||
| Japanese pufferfish |
| Marine, brackish and freshwater | 1 [ | ||||
| Japanese seabass |
| Marine, brackish and freshwater | 1 [ | ||||
| Largemouth bass |
| Freshwater | 2 [ | ||||
| Large yellow croaker |
| Marine and brackish | 1 [ | 1 [ | |||
| Mandarin fish |
| Freshwater | 1 [ | 1 [ | |||
| Maori chief |
| Marine | 5 [ | ||||
| Medaka |
| Freshwater and brackish | 1 [ | 2 [ | |||
| Miiuy croaker |
| Marine and brackish | 1 [ | ||||
| Mud dab |
| Marine | 1 [ | ||||
| Mud loach |
| Freshwater | [ | ||||
| Olive flounder |
| Marine | 5 [ | ||||
| Orange-spotted grouper |
| Marine and brackish | 1 [ | 2 [ | 3 [ | ||
| Pacific mutton hamlet |
| Marine | 1 [ | ||||
| Rainbow trout |
| Marine, brackish and freshwater | 4 [ | 2 [ | 3 [ | ||
| Redbanded seabream |
| Marine | 4 [ | ||||
| Red sea bream |
| Marine | 1 [ | 1 [ | |||
| Rockbream |
| Marine | 4 [ | ||||
| Sea bass |
| Marine, brackish and freshwater | 1 [ | ||||
| Seahorse |
| Marine and brackish | 1 [ | ||||
| Smallmouth bass |
| Freshwater | 2 [ | ||||
| Snowtrout |
| Freshwater | 1 [ | ||||
| Spotted-green pufferfish |
| Freshwater and brackish | 2 [ | ||||
| Sunshine bass | Marine, brackish and freshwater | 1 [ | |||||
| Thick-lipped lenok |
| Freshwater | 1 [ | ||||
| Tilapia | Oreochromis mossambicus | Freshwater and brackish | 5 [ | 3 [ | |||
| Turbot |
| Marine and brackish | 2 [ | ||||
| Winter flounder |
| Marine | 6 [ | 5 [ | |||
| Witch flounder |
| Marine | 5 [ | ||||
| Yellowtail flounder |
| Marine | 1 [ | ||||
| Zebrafish |
| Freshwater | 3 [ | 2 [ | |||
Figure 1Alignment of piscidins. Mature peptide sequences were obtained from published data and from the PubMed protein database, and were aligned using MacVector software. The Drosophila cecropin A1 sequences is provided for comparison as a representative member of the cecropin family.
Antimicrobial activity of fish AMPs. Bacteria and fungi included MICs (μM, or μg/mL will be indicated) values, MLCs (μM), vLD90 (virtual 90% lethal dose, mg/mL [mean ± SEM]) or IC50 (μM). If values are not included antimicrobial activity was assessed by inhibitory halo (IH) and size in millimeter was not presented, if so, is indicated. If isoforms were tested, the best performance value was used. For parasites, the minimum protozoacidal concentration (PCmin) or MIC is indicated. Habitat of microorganisms are indicated (freshwater, marine or other).
| Bacteria | β-Defensin | Piscidin | Hepcdin | Cathelicidin | Histone-derived | Pathogenic | Habitat | |
|---|---|---|---|---|---|---|---|---|
| Fish | Human | |||||||
| Gram negative | ||||||||
| 39.0 ± 3.7 (vLD90) [ | 5–10 μM (MIC) [ | 5–10 μM (MIC) [ | <1 μg/mL (MIC) [ | 1 μg/mL(MIC) [ | X | X | Freshwater and others | |
| 11 μM (MIC) [ | X | X | Freshwater | |||||
|
| 12.6 μg/mL (MIC) [ | 22 μM (MIC) [ | 18.8 μM (MIC) [ | X | Other | |||
| 5–10 μM (MIC) [ | >44 μM (MIC) [ | X | Other | |||||
| 5–10 μM (MIC) [ | >44 μM (MIC) [ | X | Other | |||||
| 3.1 μg/mL (MIC) [ | >96 μM (MIC) [ | X | Freshwater and others | |||||
| 2.5–5 μM (MIC) [ | 22 μM (MIC) [ | X | X | Freshwater and others | ||||
|
| 20–40 μM (MIC) [ | X | Freshwater | |||||
|
| >50 μM (MIC) [ | 17.7–35 μM (MIC) [ | >44 μM (MIC) [ | 9.4 μg/mL (MIC)[ | 20 μg/mL (MIC) [ | X | Freshwater and marine | |
|
| 13.4 ± 0.7 [ | 1.05 μg/mL (MIC) [ | 10–20 μM (MIC) [ | X | X | Freshwater and others | ||
|
| 59.4 ± 8.8 [ | 10–20 μM (MIC) [ | 2.5 μM (MIC) [ | X | X | Freshwater and others | ||
|
| 10–20 μM (MIC) [ | X | Freshwater and others | |||||
|
| >50 μM (MIC) [ | 20–40 μM (MIC) [ | 2.92 μM (MIC) [ | 5 μM (MIC) [ | X | Marine | ||
|
| >60 μM (MIC) [ | 25 [ | X | X | Marine | |||
|
| 43.0 ± 10 (vLD90) [ | >96 μM (MIC) [ | 3.1 μg/mL (MIC) [ | X | X | Marine | ||
|
| 12.5 μg/mL (MIC) [ | 20–40 μM (MIC) [ | 6.2 μg/mL (MIC) [ | X | Marine | |||
|
| 0.03 μg/mL (MIC) [ | >60 μM (MIC) [ | X | X | Marine | |||
|
| 0.03 μg/mL (MIC) [ | 20 μM (MIC) [ | X | X | Marine | |||
|
| 2.5–5 μM (MIC) [ | X | X | Freshwater, marine and others | ||||
|
| 48 μM (MIC) [ | X | X | Marine | ||||
|
| 5 μM (MLC) [ | Marine | ||||||
|
| 3.125 μg/mL (MIC) [ | Marine and others | ||||||
|
| >44 μM (MIC) [ | X | X | Marine and freshwater | ||||
|
| 6.25 μg/mL (MIC) [ | 25 μg/mL (MIC) [ | Other | |||||
|
| 44.5 ± 11.8 [ | 0.52 μg/mL (MIC) [ | >44 μM (MIC) [ | 12.5 μg/mL (MIC) [ | X | X | Freshwater, marine and others | |
|
| 10–20 μM (MIC) [ | 24–48 μM (MIC) [ | 20 μM (MIC) [ | X | X | Freshwater and others | ||
|
| <1.5 μM (MIC) [ | X | Other | |||||
|
| 10–20 μM (MIC) [ | >44 μM (MIC) [ | X | X | Freshwater and others | |||
|
| 10–20 μM (MIC) [ | X | Others | |||||
|
| 10–20 μM (MIC) [ | >44 μM (MIC) [ | X | Other | ||||
|
| 10–20 μM (MIC) [ | >44 μM (MIC) [ | X | Other | ||||
|
| 8.8–17.7 μM (MIC) [ | >44 μM (MIC) [ | 2 μM (MIC) [ | X | Other | |||
|
| >35 μM (MIC) [ | >44 μM (MIC) [ | 4 μM (MIC) [ | X | Other | |||
|
| 40–80 μM (MIC) [ | X | Freshwater | |||||
|
| 2.2–4.4 μM (MIC) [ | X | Freshwater | |||||
|
| 2–10 μM (MIC) [ | X | X | Freshwater and others | ||||
|
| 1.5 μg/mL (MIC) [ | X | Marine and freshwater | |||||
|
| 4.4–8.8 μM (MIC) [ | X | Other | |||||
|
| >20 μM (MIC) [ | X | Freshwater and others | |||||
|
| 2.5–5 μM (MIC) [ | X | Other | |||||
| Neisseria gonorrhoeae | >20 μM (MIC) [ | X | Other | |||||
|
| 10 μM (MIC) [ | Marine and others | ||||||
|
| 12 μM (MIC) [ | X | Other | |||||
|
| 15 μM (MIC) [ | X | Other | |||||
|
| ||||||||
|
| 25–50 μM (MIC) [ | 10–20 μM (MIC) [ | >96 μM (MIC) [ | X | Freshwater and others | |||
|
| 358.5 ± 46.5 (vLD90) [ | 0–2 μM (MIC) [ | 1.25–2.5 μM (MIC) [ | 11–45 μM (MIC) [ | 2μM (MIC) [ | X | Other | |
|
| 5–10 μM (MIC) [ | 20–40 μM (MIC) [ | 10 μM (MIC) [ | X | Other | |||
|
| 5–10 μM (MIC) [ | X | Other | |||||
|
| 7.5 μM (MIC) [ | X | Other | |||||
|
| >20 μM (MIC) [ | Other | ||||||
|
| 15 μM (MIC) [ | Other | ||||||
|
| 1.1–2.2 μM (MIC) [ | 5–10 μM (MIC) [ | 11 μg/mL (MIC) [ | Other | ||||
|
| 17.5 ± 4 (vLD90) [ | 0–2 μM (MIC) [ | 40–60 μM (MIC) [ | X | Other | |||
|
| 2.5–5 μM (MIC) [ | Other | ||||||
|
| 0.4–0.8 μM (MIC) [ | 0.08 μg/mL (MIC) [ | Marine | |||||
|
| 8.39 μg/mL (MIC) [ | >44 μM (MIC) [ | X | Other | ||||
|
| 2.5–5 μM (MIC) [ | X | Other | |||||
|
| 0.13 μg/mL (MIC) [ | X | X | Freshwater, marine and others | ||||
|
| 3.1 μg/mL (MIC) [ | X | X | Freshwater, marine and others | ||||
|
| 2.2 μM (MIC) [ | 1 μg/mL (MIC) [ | X | Other | ||||
|
| 8 μg/mL (MIC) [ | X | Other | |||||
|
| 32 μg/mL (MIC) [ | X | Other | |||||
|
| 8 μg/mL (MIC) [ | X | Other | |||||
|
| 1.25–2.5 μM (MIC) [ | X | Other | |||||
|
| 2.5–5 μM (MIC) [ | X | Other | |||||
|
| 1.25–2.5 μM (MIC) [ | X | Other | |||||
|
| 1.25–2.5 μM (MIC) [ | X | Other | |||||
|
| 1.25–2.5 μM (MIC) [ | X | Other | |||||
|
| 3.1 μg/mL (MIC) [ | X | X | Marine and others | ||||
|
| >35 μM (MIC) [ | X | Marine | |||||
|
| 128 μg/mL (MIC) [ | Other | ||||||
|
| 32 μg/mL (MIC) [ | Other | ||||||
|
| 2 μg/mL (MIC) [ | Other | ||||||
|
| 8 μg/mL (MIC) [ | X | Other | |||||
|
| 8 μg/mL (MIC) [ | X | Other | |||||
|
| ||||||||
|
| 50–100 μM (MIC) [ | X | Other | |||||
|
| 48–96 μM (MIC) [ | 20–40 μM (MIC) [ | X | Other | ||||
|
| 20–40 μM (MIC) [ | Other | ||||||
|
| 20–40 μM (MIC) [ | X | Other | |||||
|
| 0.78–1.56 μM (MIC) [ | X | X | Freshwater, marine and others | ||||
|
| 0.39–0.78 [ | Other | ||||||
|
| 15.4 μg/mL (MIC) [ | >60 μM (MIC) [ | 2.3 [ | X | Other | |||
|
| 10–20 μM (MIC) [ | X | Other | |||||
|
| 10–20 μM (MIC) [ | |||||||
|
| 10–20 μM (MIC) [ | X | Other | |||||
| Saccharomyces cerevisiae | 384 μM (MIC) [ | X | Other | |||||
|
| >60 μM (MIC) [ | Other | ||||||
| 12.5–25 μg/mL (MOC) [ | X | Freshwater and others | ||||||
| Neurospora crassa | 1.56–3.12 μM (MIC) [ | Other | ||||||
| Trichosporon beigelii | 2.5 μM (MIC) [ | X | Other | |||||
|
| 6.25 μM (MIC) [ | X | Other | |||||
|
| ||||||||
|
| 12.5 μg/mL (MIC) [ | X | Other | |||||
| Trichodina | 12.5–100 μg/mL (PCmin) [ | X | Freshwater and marine | |||||
|
| 12.5 μg/mL (PCmin) [ | X | Marine | |||||
|
| 6.3 μg/mL (PCmin) [ | X | Marine | |||||
|
| 6.3 μg/mL (PCmin) [ | X | Freshwater | |||||
|
| ||||||||
| VHSV | [ | [ | X | Marine | ||||
| NNV | [ | [ | [ | X | Marine | |||
| IPNV | [ | X | Marine | |||||
| RGV | [ | X | Marine and Freshwater | |||||
| SGIV | [ | [ | X | Marine | ||||
| CCV | [ | X | Freshwater | |||||
| FV3 | [ | Other | ||||||
Figure 2Alignment of β-defensins. Precursor peptide sequences were obtained from published data and from the PubMed protein database, and were aligned using MacVector software. The bovine β-defensin, Tracheal Antimicrobial Peptide (TAP) is shown for comparison. The conserved β-defensin cysteine spacing is shown in the consensus line. The first residue of the mature peptide region (based on the isolated TAP sequence) is denoted with an asterisk.
Figure 3Alignment of hepcidins. Representative precursor peptide sequences were obtained from published data and from the PubMed protein database, and were aligned using MacVector software. Human hepcidin is shown for comparison. The first residue of the mature peptide region is denoted with an asterisk.
Figure 4Alignment of fish cathelicidins. Mature peptide sequences were obtained from published data and from the PubMed protein database, and were aligned using MacVector software. Characteristic cysteine residues found in certain classes of fish cathelicidins are underlined. As, Atlantic salmon; Rt, Rainbow trout; Cs, Chinook salmon; Btr, Brown trout; Ac, Arctic char; Bt, Brook trout; Je, Japanese eel.
Figure 5Alignment of histone-derived peptides. Representative peptide sequences were obtained from published data and from the PubMed protein database, and were aligned using MacVector software. Since the sequences are homolgous to different histone peptide fragments, there is no shared sequence homology.