www.fgks.org   »   [go: up one dir, main page]

You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Article Types

Countries / Regions

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Search Results (15,260)

Search Parameters:
Keywords = fish

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
18 pages, 626 KiB  
Article
Practice of Territorial Use Rights in Fisheries in Coastal Fishery Management in China: A Case Study of the Island Reefs Fishery Lease Policy from Shengsi County in Zhejiang Province
by Minsi Xiong and Zuli Wu
Fishes 2024, 9(7), 292; https://doi.org/10.3390/fishes9070292 - 22 Jul 2024
Viewed by 119
Abstract
Coastal fisheries are vital for food supply, employment, and social stability. However, overfishing is a common problem, often attributed to open access. Territorial Use Rights in Fisheries (TURFs) have gained popularity as a tool to improve the sustainability of coastal fisheries, but research [...] Read more.
Coastal fisheries are vital for food supply, employment, and social stability. However, overfishing is a common problem, often attributed to open access. Territorial Use Rights in Fisheries (TURFs) have gained popularity as a tool to improve the sustainability of coastal fisheries, but research on TURFs in China is limited. This paper examines the island reef fishery lease policy implemented in Shengsi County, Zhejiang Province, within the Ma’an Islands National Marine Special Reserve. The policy leases the use of island reefs to a collective, aiming to address overfishing and resource degradation by establishing fishing area boundaries and limiting the number of users and usage time. Technically, it is an application of TURFs, and it represents a shift from traditional fishing licenses to collective compliance. This experience has disrupted the existing top–down fishery governance structure and signifies a transition to a rights-based fishery management system in China. Through a comprehensive investigation and analysis of the policy’s implementation, this research identifies the factors contributing to its flaws. These include the inadequate provision of national and local government policies, insufficient support for policy implementation from fishery management authorities, and the limited involvement of fishermen’s organizations. To enhance coastal fishery management, we propose that the Chinese government should build upon existing foundations by clarifying fishing rights through central and local laws and policies. Additionally, there is a need to strengthen data monitoring of coastal fisheries, conduct multidisciplinary research to improve the allocation mechanism of fishing rights, adopt diverse fishery management approaches to enhance supervision capabilities, establish a collaborative governance mechanism, and foster coordination and cooperation between grassroots fishermen’s organizations and government departments. Full article
Show Figures

Figure 1

Figure 1
<p>Geographical positioning of Shengsi and the Ma’an Islands National Marine Special Reserve (the yellow area is designated as the pilot area for the Island Reefs Fishery Lease Policy).</p>
Full article ">
21 pages, 8929 KiB  
Article
Ecotoxicity Assessment of α-Amino Acid-Derived Polyamidoamines Using Zebrafish as a Vertebrate Model
by Sofia Treccani, Paolo Ferruti, Jenny Alongi, Eugenio Monti, Daniela Zizioli and Elisabetta Ranucci
Polymers 2024, 16(14), 2087; https://doi.org/10.3390/polym16142087 - 22 Jul 2024
Viewed by 190
Abstract
The aquatic ecotoxicity of three α-amino acid-derived polyamidoamines (PAAs) was studied using zebrafish embryos as a viable vertebrate model organism. The PAAs examined were water-soluble amphoteric polyelectrolytes with a primarily negative charge, which were efficient flame retardants for cotton. The fish embryo acute [...] Read more.
The aquatic ecotoxicity of three α-amino acid-derived polyamidoamines (PAAs) was studied using zebrafish embryos as a viable vertebrate model organism. The PAAs examined were water-soluble amphoteric polyelectrolytes with a primarily negative charge, which were efficient flame retardants for cotton. The fish embryo acute toxicity test performed with PAA water solutions using 1.5–500 mg L−1 concentrations showed that toxicity did not statistically differ from the control. The survival rates were indeed >90%, even at the highest concentration; the hatching rates were >80%; and the numbers of morphological defects were comparable to those of the control. Tests using transgenic zebrafish lines indicated that the numbers of microscopic vascular and musculoskeletal defects were comparable to the control, with one random concentration showing doubled alterations. Sensory–motor tests in response to visual and tactile stimuli were also performed. In the presence of PAAs, embryos exposed to alternating light/dark cycles showed an insignificant mobility reduction during the dark phase. Touch-evoked response tests revealed a mild effect of PAAs on the neuromotor system at concentrations > 10 mg L−1. The cystine/glycine copolymer at 100 mg L−1 exhibited the greatest effect. Overall, the studied PAAs showed a minimal impact on aquatic systems and should be further considered as promising ecofriendly materials. Full article
(This article belongs to the Section Polymer Physics and Theory)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Structures of the repeat units of (<b>a</b>) M-GLY and M-GLU and (<b>b</b>) M-GLY<sub>50</sub>-CYSS<sub>50</sub>; (<b>c</b>) synthesis of α-amino acid-derived PAAs.</p>
Full article ">Figure 2
<p>Timeline of the ecotoxicity tests carried out on PAA-exposed zebrafish embryos. Figures in the white frames represent the execution times; hpf stands for hours post-fertilization. From the top: 1st row: tests performed on AB wild-type embryos. In the FET test, developmental toxicity was assessed using different endpoints: survival rate, morphological alterations, and hatching rate. In the light/dark locomotion test, the response of zebrafish embryos’ locomotion activity to a sudden transition from light to darkness was assessed. 2nd row: touch-evoked response test performed on AB wild-type larvae. 3rd row: tests performed on Tg(<span class="html-italic">fli1</span>:EGFP) transgenic embryos expressing enhanced green fluorescent protein. The angiogenetic process was monitored by observing the development of intersegmental vessels. 4th row: tests performed on Tg(<span class="html-italic">Bmp</span>:EGFP) transgenic embryos expressing enhanced green fluorescent protein. The somite-segmentation process was monitored by observing the correct development of somites in a V-shaped pattern.</p>
Full article ">Figure 3
<p>(<b>a</b>) Survival rate of AB wild-type larvae after exposure to different PAA concentrations for 120 hpf. The dotted blue line represents the threshold value for the negative control indicated by the OECD guideline 236 [<a href="#B30-polymers-16-02087" class="html-bibr">30</a>] to assess the test validity; (<b>b</b>) hatching rate of AB wild-type larvae after exposure to different PAA concentrations for 72 hpf; (<b>c</b>) bright-field microscopic image of a hatching zebrafish larva at 72 hpf. In (<b>a</b>,<b>b</b>), controls represent larvae exposed to fish water. For each PAA dose, data were obtained from three independent experiments and expressed as mean ± standard deviation. The dotted red line represents the threshold value for the negative control indicated by the OECD guideline 236 to assess the test validity. The absence of asterisks indicates that no statistically significant differences were observed compared to control (significance level <span class="html-italic">α</span> = 0.05).</p>
Full article ">Figure 4
<p>Representative bright-field microscopic images of morphological alterations by FET test observed in zebrafish larvae after 72 hpf exposure to M-GLU solutions. The dashed green line in the control represents the anterior–posterior A-P axis. (<b>a</b>) Spinal cord malformation (2 mg L<sup>−1</sup>), revealed by the abnormal angle of the head relative to the A-P axis; (<b>b</b>) pericardial edema (25 mg L<sup>−1</sup>), indicated by the red arrow; (<b>c</b>) growth retardation and defects in anterior–posterior axis (2 mg L<sup>−1</sup>), revealed by the abnormal trunk alignment (dashed red line) and tail deformation (blue arrow). All pictures are lateral views with dorsal at the top (magnification 32X).</p>
Full article ">Figure 5
<p>Morphological alterations of zebrafish larvae observed in the FET test at 72 hpf after exposure to (<b>a</b>) M-GLY, (<b>b</b>) M-GLU, and (<b>c</b>) M-GLY<sub>50</sub>-CYSS<sub>50</sub>. For each PAA concentration, the total number of embryos is the sum of embryos tested in three independent experiments. Sub-lethal endpoints are color-coded: green bars represent pericardial edema, red bars growth retardation, and yellow bars spinal distortion. Control represents zebrafish embryos exposed to fish water.</p>
Full article ">Figure 6
<p>Intersegmental vessel (ISV) alteration in PAA-treated Tg(<span class="html-italic">fli1</span>:EGFP) embryos: (<b>a</b>) average number of zebrafish embryos exposed for 30 hpf to 2 and 10 mg L<sup>−1</sup> of M-GLY (yellow), M-GLU (blue), and M-GLY<sub>50</sub>-CYSS<sub>50</sub> (red) with ISV alterations. For each PAA dose, data were obtained from three independent experiments and expressed as mean ± standard deviation. The asterisk indicates significant differences (<span class="html-italic">p</span> &lt; 0.05) compared to control. (<b>b</b>) Representative lateral views of control and PAA-treated embryos with ISV alterations (magnification 63X). ISVs are labeled with a green fluorescent marker. Brightness of images was increased by 40%. DLAV = dorsal longitudinal anastomotic vessel; DA = dorsal aorta.</p>
Full article ">Figure 7
<p>Representative lateral views of control and PAA-treated Tg(<span class="html-italic">Bmp</span>:EGFP) embryos (magnification 40X). Somites are labeled with a green fluorescent marker. Brightness of images was increased by 40%.</p>
Full article ">Figure 8
<p>Results of the locomotion tests performed using AB-wild-type embryos at 120 hpf. Distance moved by zebrafish larvae exposed to different M-GLY (<b>a</b>), M-GLU (<b>b</b>), and M-GLY<sub>50</sub>-CYSS<sub>50</sub> (<b>c</b>) concentrations during dark periods. Data were collected with n = 36 larvae per concentration. Data distribution is represented by the box-and-whisker plot. Asterisks indicate significant differences (<span class="html-italic">p</span> &lt; 0.05) compared to control.</p>
Full article ">Figure 9
<p>Results of the touch-evoked test performed on zebrafish larvae exposed at 4 hpf to different (<b>a</b>) M-GLY, (<b>b</b>) M-GLU, and (<b>c</b>) M-GLY<sub>50</sub>-CYSS<sub>50</sub> concentrations. After 72 hpf, the tail of each single larva placed in the center of a Petri dish was gently touched with a smooth pipette tip, and the touch response was observed and categorized as follows: (1) larvae that did not move, i.e., that remained within the circle with 10 mm diameter; (2) larvae that swam between the circles with 10 and 20 mm diameters; and (3) larvae that swam across the outer circle with 20 mm diameter. Results were derived from three independent experiments performed using 25 embryos.</p>
Full article ">
19 pages, 64166 KiB  
Article
Genome-Wide Identification and Interaction Analysis of Turbot Heat Shock Protein 40 and 70 Families Suggest the Mechanism of Chaperone Proteins Involved in Immune Response after Bacterial Infection
by Yuanwei Geng, Yuxuan Gai, Yanping Zhang, Shengwei Zhao, Anlan Jiang, Xueqing Li, Kaiqing Deng, Fuxuan Zhang, Lingling Tan and Lin Song
Int. J. Mol. Sci. 2024, 25(14), 7963; https://doi.org/10.3390/ijms25147963 (registering DOI) - 21 Jul 2024
Viewed by 225
Abstract
Hsp40–Hsp70 typically function in concert as molecular chaperones, and their roles in post-infection immune responses are increasingly recognized. However, in the economically important fish species Scophthalmus maximus (turbot), there is still a lack in the systematic identification, interaction models, and binding site analysis [...] Read more.
Hsp40–Hsp70 typically function in concert as molecular chaperones, and their roles in post-infection immune responses are increasingly recognized. However, in the economically important fish species Scophthalmus maximus (turbot), there is still a lack in the systematic identification, interaction models, and binding site analysis of these proteins. Herein, 62 Hsp40 genes and 16 Hsp70 genes were identified in the turbot at a genome-wide level and were unevenly distributed on 22 chromosomes through chromosomal distribution analysis. Phylogenetic and syntenic analysis provided strong evidence in supporting the orthologies and paralogies of these HSPs. Protein–protein interaction and expression analysis was conducted to predict the expression profile after challenging with Aeromonas salmonicida. dnajb1b and hspa1a were found to have a co-expression trend under infection stresses. Molecular docking was performed using Auto-Dock Tool and PyMOL for this pair of chaperone proteins. It was discovered that in addition to the interaction sites in the J domain, the carboxyl-terminal domain of Hsp40 also plays a crucial role in its interaction with Hsp70. This is important for the mechanistic understanding of the Hsp40–Hsp70 chaperone system, providing a theoretical basis for turbot disease resistance breeding, and effective value for the prevention of certain diseases in turbot. Full article
(This article belongs to the Section Biochemistry)
Show Figures

Figure 1

Figure 1
<p>The characteristics and domains of Hsp40 and Hsp70 members in <span class="html-italic">S. maximus</span>. (<b>A</b>) Protein sequence length distribution; AA, amino acid; (<b>B</b>) the protein molecular weight distribution; (<b>C</b>) distribution of conserved domains and gene structure on the Hsp40; (<b>D</b>) distribution of conserved domains and gene structure on the Hsp70.</p>
Full article ">Figure 1 Cont.
<p>The characteristics and domains of Hsp40 and Hsp70 members in <span class="html-italic">S. maximus</span>. (<b>A</b>) Protein sequence length distribution; AA, amino acid; (<b>B</b>) the protein molecular weight distribution; (<b>C</b>) distribution of conserved domains and gene structure on the Hsp40; (<b>D</b>) distribution of conserved domains and gene structure on the Hsp70.</p>
Full article ">Figure 2
<p>The genome positions of Hsp40 and Hsp70 members in <span class="html-italic">S. maximus</span>. The Hsp40 genes and the Hsp70 genes are labeled in red and blue respectively.</p>
Full article ">Figure 3
<p>Conserved motif information for Hsp40 and Hsp70 proteins in <span class="html-italic">S. maximus</span>, and each colored rectangular box represents a motif. (<b>A</b>) Motif information in turbot Hsp40 family subfamily A; (<b>B</b>) motif information in turbot Hsp40 family subfamily B; (<b>C</b>) motif information in turbot Hsp40 family subfamily C; (<b>D</b>) motif information in turbot Hsp70 family.</p>
Full article ">Figure 4
<p>The phylogenetic tree constructed from Hsp40 and Hsp70 proteins in <span class="html-italic">S. maximus</span>, <span class="html-italic">C. semilaevis</span>, <span class="html-italic">O. mykiss</span>, <span class="html-italic">D. rerio</span>, <span class="html-italic">X. tropicalis</span>, <span class="html-italic">T. c. triunguis</span>, <span class="html-italic">G. gallus</span>, <span class="html-italic">M. musculus</span>, and <span class="html-italic">H. sapiens</span>. Different colors indicate different groups. The genes for turbot, half-smooth tongue sole, and rainbow trout are labeled with red dots and black and gray triangles, respectively. (<b>A</b>) Phylogenetic tree of subfamily A of the Hsp40 family; (<b>B</b>) phylogenetic tree of subfamily B of the Hsp40 family; (<b>C</b>) phylogenetic tree of dnajc1~dnajc10 in subfamily C of the Hsp40 family; (<b>D</b>) phylogenetic tree of dnajc11~dnajc20 in subfamily C of the Hsp40 family; (<b>E</b>) phylogenetic tree of dnajc21~dnajc30 in subfamily C of the Hsp40 family; (<b>F</b>) phylogenetic tree of Hsp70 family.</p>
Full article ">Figure 5
<p>Duplication event analysis for the Hsp40 and Hsp70 gene families in the turbot genome and the synteny analysis between turbot and other fishes. (<b>A</b>) Number of Hsp40 and Hsp70 genes in six fish species; (<b>B</b>) the paralogues of Hsp40 and Hsp70 in the turbot genome—the blue and red lines indicate the Hsp40 and Hsp70 families members, respectively; (<b>C</b>) sytenic analysis of Hsp40 genes between <span class="html-italic">S. maximus</span>, <span class="html-italic">C. semilaevis</span> and <span class="html-italic">O. mykiss</span>—the blue lines indicate the Hsp40 family members in different species; (<b>D</b>) sytenic analysis of Hsp70 genes between <span class="html-italic">S. maximus</span>, <span class="html-italic">C. semilaevis</span>, and <span class="html-italic">O. mykiss</span>—the violet lines indicate the Hsp70 family members in different species.</p>
Full article ">Figure 6
<p>PPI network of the Hsp40 and Hsp70 proteins.</p>
Full article ">Figure 7
<p>Expression analysis of differentially expressed genes of Hsp40 and Hsp70 families after infection with <span class="html-italic">A. salmonicida</span> in turbot.</p>
Full article ">Figure 8
<p>Dnajb1b and Hspa1a protein molecular docking model. Surface diagram of the docking model and their interfacing residues between Dnajb1b and Hspa1a protein (Dnajb1b, yellow; Hspa1a, blue; hydrogen bond interaction, dotted line).</p>
Full article ">Figure 9
<p>Dnajb1b and Hspa1a protein molecular docking model combined with motif analysis (Dnajb1b, yellow; Hspa1a, blue; hydrogen bonding interactions, dashed lines). (<b>A</b>) Molecular structure of the JD of Dnajb1b interacting with the NBD of Hspa1a; (<b>B</b>) molecular structure of the GF-rich regions of Dnajb1b interacting with the NBD of Hspa1a; (<b>C</b>) molecular structure of the CTD of Dnajb1b interacting with the NBD of Hspa1a; (<b>D</b>) molecular structure of the CTD of Dnajb1b interacting with both the SBD and the CTD of Hspa1a; (<b>E</b>) domain interactions between Dnajb1b and Hspa1a and the motif where the interactions amino acid sites are located.</p>
Full article ">
18 pages, 6753 KiB  
Article
Effect of Pond-Based Rice Floating Bed on the Microbial Community Structure and Quality of Water in Pond of Mandarin Fish Fed Using Artificial Diet
by Lijin Jiang, Mengmeng Yi, Zhiyong Jiang, Yuli Wu, Jianmeng Cao, Zhigang Liu, Zhang Wang, Maixin Lu, Xiaoli Ke and Miao Wang
Biology 2024, 13(7), 549; https://doi.org/10.3390/biology13070549 (registering DOI) - 21 Jul 2024
Viewed by 263
Abstract
The culture of mandarin fish using artificial feed has been gaining increasing attention in China. Ensuring good water quality in the ponds is crucial for successful aquaculture. Recently, the trial of pond-based rice floating beds (PRFBs) in aquaculture ponds has shown promising results. [...] Read more.
The culture of mandarin fish using artificial feed has been gaining increasing attention in China. Ensuring good water quality in the ponds is crucial for successful aquaculture. Recently, the trial of pond-based rice floating beds (PRFBs) in aquaculture ponds has shown promising results. This research assessed the impact of PRFBs on the microbial community structure and overall quality of the aquaculture pond, thereby enhancing our understanding of its functions. The results revealed that the PRFB group exhibited lower levels of NH4+-N, NO2-N, NO3-N, TN, TP, and Alk in pond water compared to the control group. The microbial diversity indices in the PRFB group showed a declining trend, while these indices were increasing in the control group. At the phylum level, there was a considerable increase in Proteobacteria abundance in the PRFB group throughout the culture period, suggesting that PRFBs may promote the proliferation of Proteobacteria. In the PRFB group, there was a remarkable decrease in bacterial populations related to carbon, nitrogen, and phosphorus metabolism, including genera Rhodobacter, Rhizorhapis, Dinghuibacter, Candidatus Aquiluna, and Chryseomicrobium as well as the CL500_29_marine_group. Overall, the research findings will provide a basis for the application of aquaculture of mandarin fish fed an artificial diet and rice floating beds. Full article
(This article belongs to the Special Issue The Relationship between Water Quality and Aquatic Organisms)
Show Figures

Figure 1

Figure 1
<p>(<b>A</b>) The sampling location; (<b>B</b>) the control pond; (<b>C</b>) the PRFB pond. The black dot indicates the sampling location.</p>
Full article ">Figure 2
<p>Changes in water quality in different groups. Note: Control I, Control II, and Control III represent the sample numbers in the control group for periods I, II, and III respectively. PRFB I, PRFB II, and PRFB III represent the sample numbers in the PRFB group for periods I, II, and III, respectively.</p>
Full article ">Figure 3
<p>Rarefaction curve. Note: C represents the sample number in the control group. P represents the sample number in the PRFB group.</p>
Full article ">Figure 4
<p>α- Diversity index analysis. Note: Control I, Control II, and Control III represent the sample numbers in the control group for periods I, II, and III respectively. PRFB I, PRFB II, and PRFB III represent the sample numbers in the PRFB group for periods I, II, and III, respectively.</p>
Full article ">Figure 5
<p>PLSDA analysis between different groups.</p>
Full article ">Figure 6
<p>Spearman correlation analysis between water quality parameters and microbial communities at the genus level. Note: * represents <span class="html-italic">p</span> &lt; 0.05, ** represents <span class="html-italic">p</span> &lt; 0.01, and the correlation coefficient R &gt; 0.3.</p>
Full article ">Figure 7
<p>Relative abundance of microbiota at the phylum level. Note: Control I, Control II, and Control III represent the sample numbers in the control group for periods I, II, and III, respectively. PRFB I, PRFB II, and PRFB III represent the sample numbers in the PRFB group for periods I, II, and III, respectively.</p>
Full article ">Figure 8
<p>Relative abundance of microbiota at the genus level. Note: Control I, Control II, and Control III represent the sample numbers in the control group for periods I, II, and III, respectively. PRFB I, PRFB II, and PRFB III represent the sample numbers in the PRFB group for periods I, II, and III, respectively.</p>
Full article ">Figure 9
<p>LefSe analysis of microbial communities. Note: Control III and PRFB III represent the sample numbers for the control group and PRFB group, respectively, during the third sampling period; LDA discriminant analysis score threshold is 3, <span class="html-italic">p</span> &lt; 0.05.</p>
Full article ">Figure 10
<p>Correlation network analysis of water microbiota based on genus level: (<b>A</b>) control group (nodes  =  181, edges  =  507) and (<b>B</b>) PRFB group (nodes  =  124, edge  =  277). Spearman’s R  &gt;  0.6; <span class="html-italic">p</span>  &lt;  0.05.</p>
Full article ">Figure 11
<p>FAPROTAX analysis of the water microbiota. (<b>A</b>) The relative abundance of top 10 functions; (<b>B</b>) LefSe analysis of functional composition of the water microbiota based on FAPROTAX. * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01.</p>
Full article ">
21 pages, 3790 KiB  
Article
Xenotransplantation of European Eel (Anguilla anguilla) Spermatogonia in Zebrafish (Danio rerio) and European Sea Bass (Dicentrarchus labrax)
by Marta Blanes-García, Zoran Marinović, Marina Morini, Alain Vergnet, Ákos Horváth and Juan F. Asturiano
Fishes 2024, 9(7), 290; https://doi.org/10.3390/fishes9070290 - 21 Jul 2024
Viewed by 289
Abstract
The European eel encounters challenges in achieving sexual maturation in captivity, which has been a concern for researchers. This study explores surrogate broodstock technology as an alternative approach for eel production. The present study aimed to evaluate zebrafish and European sea bass as [...] Read more.
The European eel encounters challenges in achieving sexual maturation in captivity, which has been a concern for researchers. This study explores surrogate broodstock technology as an alternative approach for eel production. The present study aimed to evaluate zebrafish and European sea bass as potential recipients for European eel spermatogonia transplantation, given the abundance of eel type A spermatogonia (SPGA). Immature European eel testes were dissected and maintained at 4 °C or cryopreserved. SPGA were obtained by dissociation of fresh or post-thawed tissue, employing an enzymatic solution, and then labelled with fluorescent membrane marker PKH26. SPGA from fresh tissue were transplanted into wild-type zebrafish larvae and triploid European sea bass larvae, while SPGA from cryopreserved testis were transplanted into vasa::egfp transgenic zebrafish larvae. One-and-a-half months post-transplantation (mpt), fluorescent donor cells were not detected in the gonads of zebrafish or European sea bass. Molecular qPCR analyses at 1.5 or 6 mpt did not reveal European eel-specific gene expression in the gonads of any transplanted fish. The findings suggest that the gonadal microenvironments of zebrafish and European sea bass are unsuitable for the development of European eel spermatogonia, highlighting distinctive spermatogonial stem cell migration mechanisms within teleost species Full article
(This article belongs to the Section Physiology and Biochemistry)
Show Figures

Figure 1

Figure 1
<p>Experimental design of European eel spermatogonial transplantation. Testis from immature eels (1) were dissected (2) and kept in cold storage for less than 30 min (3a) or cryopreserved for storage of more than 2 months (3b). The same dissociation protocol was applied for both groups of preserved testis (4a and 4b). After the spermatogonia isolation and dyeing via the use of fluorescent linker-dye PKH26 (5), the SPG obtained were utilized for the xenotransplantation into recipient larvae (6). Eel SPG from fresh testis was transplanted into triploid European sea bass or TU zebrafish larvae (6a). Eel SPG from thawed testis was transplanted into transgenic <span class="html-italic">vasa::egfp</span> zebrafish larvae (6b).</p>
Full article ">Figure 2
<p>Testicular cell suspensions from immature European eel labelled with PKH-26 under phase contrast (<b>A</b>) and under a fluorescent filter (<b>B</b>). Arrows indicate spermatogonia. Scale bar: 50 µm.</p>
Full article ">Figure 3
<p>Detailed pictures of the injection point (<b>A</b>) in European sea bass 24 h after the xenotransplantation: control group (<b>B</b>,<b>E</b>), high cell-concentration group (<b>C</b>,<b>F</b>,<b>H</b>) and low cell-concentration group (<b>D</b>,<b>G</b>,<b>I</b>). The dashed rectangle in A indicates the enlarged area (<b>B</b>–<b>D</b>). The swim bladder position is illustrated with dashed lines (<b>E</b>–<b>G</b>). The dotted circles in F and G indicate the enlarged area, within which the injected eel cells are shown (<b>H</b>,<b>I</b>). Scale bars: (<b>B</b>–<b>G</b>): 200 µm; (<b>H</b>,<b>I</b>): 50 µm.</p>
Full article ">Figure 4
<p>European sea bass gonads 1.5 months post-xenotransplantation from the control group (<b>A</b>,<b>D</b>,<b>G</b>), high cell-concentration group (HC: (<b>B</b>,<b>E</b>,<b>H</b>)) and low cell-concentration group (LC: (<b>C</b>,<b>F</b>,<b>I</b>)). The gonads’ positions are shown with dashed lines. Scale bars: (<b>A</b>–<b>C</b>): 200 µm; (<b>D</b>–<b>I</b>): 50 µm.</p>
Full article ">Figure 5
<p>Detailed pictures of the area around the injection point (<b>A</b>) in zebrafish 7 days after the xenotransplantation: control group (<b>B</b>,<b>D</b>,<b>F</b>) and xenotransplanted group (<b>C</b>,<b>E</b>,<b>G</b>). Fluorescence can be observed next to the swim bladder in the xenotransplanted fish. The arrow indicates the injection point. The dashed rectangle in (<b>A</b>) indicates the enlarged area (<b>B</b>–<b>G</b>). Scale bars: 200 µm.</p>
Full article ">Figure 6
<p>Zebrafish gonads 1.5 months post-transplantation in both experiments: control group (experiment 1: (<b>A</b>,<b>C</b>); experiment 2: (<b>E</b>,<b>G</b>)) and transplanted group (experiment 1: (<b>B</b>,<b>D</b>); experiment 2: (<b>F</b>,<b>H</b>)). Expression of the <span class="html-italic">vasa</span> gene in the gonads from transgenic <span class="html-italic">vasa::egfp</span>: control (<b>E</b>) and xenotransplanted (<b>F</b>) zebrafish. Red fluorescent-labelled cells were not observed in the control or xenotransplanted groups from either experiment (<b>C</b>,<b>D</b>,<b>G</b>,<b>H</b>). The swim bladder position is shown with dashed lines. Scale bars: 100 µm.</p>
Full article ">Figure 7
<p>Absolute expression of the <span class="html-italic">vasa</span> and <span class="html-italic">dnd1</span> genes in European sea bass (<b>A</b>) in the mid-body segment, from control and 1.5 month-post-transplant larvae, and (<b>B</b>) in the gonad and muscle, from control and 6 month-post-transplant larvae, with high or low concentrations of cells. Values are presented as the mean ± SEM. Asterisks indicate significantly higher expression levels of both genes in the gonads, independently of the experimental group (control or transplanted). SB: European sea bass.</p>
Full article ">Figure 8
<p>Absolute expression of the <span class="html-italic">vasa</span> and <span class="html-italic">dnd1</span> genes in zebrafish in the gonad and muscle from control and 1.5 month-post-transplant larvae from (<b>A</b>) experiment 1, using fresh European eel spermatogonia, and (<b>B</b>) experiment 2, using thawed European eel spermatogonia. Values are presented as the mean ± SEM. Different upper-case letters indicate significantly different expression levels between <span class="html-italic">vasa</span> and <span class="html-italic">dnd1</span>. Asterisks indicate significantly higher expression of vasa in the gonads, independently of the experimental group (control or transplanted). ZF: Zebrafish.</p>
Full article ">
14 pages, 1889 KiB  
Article
Fishing Eco-Efficiency of Ports in Northwest Spain
by Luis T. Antelo and Amaya Franco-Uría
J. Mar. Sci. Eng. 2024, 12(7), 1227; https://doi.org/10.3390/jmse12071227 - 21 Jul 2024
Viewed by 261
Abstract
Fishing is an essential economic activity and source of livelihood for millions of people worldwide. However, overfishing and unsustainable practices have led to a decline in fish populations and the degradation of marine ecosystems. Moreover, fishing activities can contribute to climate change through [...] Read more.
Fishing is an essential economic activity and source of livelihood for millions of people worldwide. However, overfishing and unsustainable practices have led to a decline in fish populations and the degradation of marine ecosystems. Moreover, fishing activities can contribute to climate change through the emission of greenhouse gases (e.g., carbon dioxide and methane) from fishing vessels and seafood transportation. To mitigate the environmental impacts of fishing activities, sustainable fishing practices must be implemented to minimize the negative impacts of fishing on the environment while maintaining the productivity and diversity of fish populations and ecosystems. These practices include using selective fishing gear, avoiding fishing in vulnerable habitats, implementing fishery management plans, and reducing the carbon footprint of the fishing industry. To this end, and as a first step in defining efficient and effective measures towards the sustainability of capture fishing activity, an analysis of the environmental sustainability of the Galician fishing sector, one of the main European regions in this field, is presented in this work. An ecosystem-based indicator (ecological footprint, calculated by adding the so-called fishing ground footprint and the carbon footprint) was employed to quantify the main impacts of capture fishing during extractive activity. The catch composition and fuel consumption of the fleet based on the vessels’ power, and economic benefits, were the parameters used in this analysis. The results showed that ports with larger vessels and fleets seem to be more eco-efficient than those concentrating smaller vessels in targeting lower trophic level species. Full article
(This article belongs to the Section Marine Environmental Science)
Show Figures

Figure 1

Figure 1
<p>Location of the different ports studied in this work: Burela (43°39′42″ N/7°21′24″ W); Celeiro (43°40′43″ N/7°35′40″ W); A Coruña (43°21′52″ N/8°23′38″ W); Ribeira (2°33′39″ N/8°59′24″ W); and Vigo (42°14′13″ N/8°43′59″ W).</p>
Full article ">Figure 2
<p>Total ecological footprint (EF) of the analyzed ports by species (hake <span style="color:#002060">■</span>, black-bellied angler <span style="color:#0070C0">■</span>, megrim <span style="color:#00B0F0">■</span>, angler <span style="color:#00B050">■</span>, blue whiting <span style="color:#92D050">■</span>, Atlantic horse mackerel <span style="color:#FFC000">■</span>, Atlantic mackerel <span style="color:red">■</span>).</p>
Full article ">Figure 3
<p>Carbon footprint (CF) of the analyzed ports by employed fishing gear.</p>
Full article ">Figure 4
<p>Catch of main species as a function of their EF intensity (gha/t of fish) and economic benefit (millions of euros) in the analyzed ports: (<b>a</b>) Celeiro; (<b>b</b>) Burela; (<b>c</b>) Vigo; (<b>d</b>) A Coruña; (<b>e</b>) Ribeira. Graph (<b>f</b>) shows a comparison of the calculated <span class="html-italic">eco-efficiency</span> of the different ports.</p>
Full article ">
19 pages, 1923 KiB  
Article
Effects of Substituting Tenebrio molitor and Elodea nuttallii as Feed on Growth, Flesh Quality and Intestinal Microbiota of Red Swamp Crayfish (Procambarus clarkii)
by Muyan Li, Weiwei Lv, Yifan Zhao, Weiwei Huang, Quan Yuan, Hang Yang, Aimin Wang, Wenzong Zhou and Mingyou Li
Foods 2024, 13(14), 2292; https://doi.org/10.3390/foods13142292 - 20 Jul 2024
Viewed by 318
Abstract
This study aimed to evaluate the impact of substituting a portion of feed with Tenebrio molitor (TM) and Elodea nuttallii (EN) on crayfish culture. A total of 270 crayfish (5.1 ± 0.4 g) were fed three different diet combinations (A: 100% feed; B: [...] Read more.
This study aimed to evaluate the impact of substituting a portion of feed with Tenebrio molitor (TM) and Elodea nuttallii (EN) on crayfish culture. A total of 270 crayfish (5.1 ± 0.4 g) were fed three different diet combinations (A: 100% feed; B: 80% feed + 10% TM + 10% EN; C: 75% feed + 15% TM + 10% EN) for 12 weeks. The findings demonstrated that group C had an important beneficial impact on the growth performance of crayfish. This was evidenced by a rise in digestive enzyme activity (trypsin, lipase, and cellulase) in the intestinal and hepatopancreas, as well as an upregulation in the expression of growth-related genes (ghsr, igfbp7, mhc, mlc1, mef2, and pax7) in the muscle. Furthermore, the assessment of the flesh quality of crayfish muscle in group C was conducted. The findings indicated a significant increase (p < 0.05) in the energy value (moisture, crude protein, and crude lipid) within the muscle. The levels of delicious amino acids (Glu, Ala, Ser, Gly, and Tyr) and polyunsaturated fatty acids (ARA, DHA) were enhanced, resulting in an improved nutritional profile and flavor of the muscle while maintaining the Σn-3/Σn-6 ratio. The remodeling of the intestinal microbiota (abundance of Proteobacteria and ratio of Firmicutes/Bacteroidota bacteria) also revealed improved growth performance. Additional research is necessary to ascertain whether excessive use of TM or EN feed substitution can have negative effects on crayfish culture. Full article
(This article belongs to the Section Foods of Marine Origin)
Show Figures

Figure 1

Figure 1
<p>Effects of three different diet combinations on intestinal digestive enzyme activity levels of <span class="html-italic">P. clarkii after</span> 12 weeks (n = 9). Different lowercase letters indicate significant differences among the groups (<span class="html-italic">p</span> &lt; 0.05). (<b>A</b>–<b>D</b>) Amylase, trypsin, lipase, and cellulase activity levels in the intestinal.</p>
Full article ">Figure 2
<p>Effects of three different diet combinations on hepatopancreas digestive enzyme activity levels of <span class="html-italic">P. clarkii</span> after 12 weeks (n = 9). Different lowercase letters indicate significant differences among the groups (<span class="html-italic">p</span> &lt; 0.05). (<b>A</b>–<b>D</b>) Amylase, trypsin, lipase, and cellulase activity levels in the hepatopancreas.</p>
Full article ">Figure 3
<p>Effects of three different diet combinations on muscle mRNA expression levels of <span class="html-italic">P. clarkii</span> after 12 weeks (n = 9). Different lowercase letters indicate significant differences among the groups (<span class="html-italic">p</span> &lt; 0.05). (<b>A</b>–<b>F</b>) <span class="html-italic">ghsr</span>, <span class="html-italic">igfbp7</span>, <span class="html-italic">mhc</span>, <span class="html-italic">mlc1</span>, <span class="html-italic">mef2</span>, and <span class="html-italic">pax7</span> mRNA expression levels in the muscle.</p>
Full article ">Figure 4
<p>Effects of three different diet combinations on the composition of the intestinal microbiota in <span class="html-italic">P. clarkii</span> after 12 weeks (n = 6). (<b>A</b>) Principal coordinates analysis (PCoA) results. (<b>B</b>) Average relative abundances at the phylum level. (<b>C</b>) Average relative abundances at the genus level.</p>
Full article ">
23 pages, 337 KiB  
Article
Does Adaptation to Saltwater Intrusion Improve the Livelihoods of Farmers? Evidence for the Central Coastal Region of Vietnam
by Thi Dieu Linh Nguyen, Bart Defloor, Stijn Speelman and Brent Bleys
Sustainability 2024, 16(14), 6216; https://doi.org/10.3390/su16146216 (registering DOI) - 20 Jul 2024
Viewed by 403
Abstract
Saltwater intrusion poses severe threats to rice farming in Vietnam. Farmers can adapt by producing other crops or switching to other production models. This study evaluates the impact of implementing different saltwater-intrusion-adaptation strategies on farmers’ livelihoods by applying propensity score matching to cross-sectional [...] Read more.
Saltwater intrusion poses severe threats to rice farming in Vietnam. Farmers can adapt by producing other crops or switching to other production models. This study evaluates the impact of implementing different saltwater-intrusion-adaptation strategies on farmers’ livelihoods by applying propensity score matching to cross-sectional survey data for 414 farmers in the Central Coastal region of Vietnam. We consider both economic and social indicators and find that there is considerable heterogeneity in the outcomes. With the exception of switching to new rice varieties, all adaptation strategies considered in the study significantly increase saline-land productivity, mainly as a result of higher revenues. Moreover, for these strategies, food security is found to be significantly higher, whereas life satisfaction is only higher for those farm households that cultivate vegetables, shrimp, or lotus-fish. Adopting new rice varieties is found to significantly decrease saline-land productivity, whereas the social impacts are not significant. Full article
24 pages, 4039 KiB  
Review
Bayesian Meta-Analysis: Impacts of Eating Habits and Habitats on Omega-3 Long-Chain Polyunsaturated Fatty Acid Composition and Growth in Cultured Fish
by Yuanbing Wu, Ania Rashidpour and Isidoro Metón
Animals 2024, 14(14), 2118; https://doi.org/10.3390/ani14142118 - 20 Jul 2024
Viewed by 396
Abstract
Omega-3 long-chain polyunsaturated fatty acids (n-3 LC-PUFAs) such as eicosapentaenoic acid (20:5n-3, EPA) and docosahexaenoic acid (22:6n-3, DHA) offer protective benefits against various pathological conditions, including atherosclerosis, obesity, inflammation, and autoimmune diseases. Marine fish and seafood are [...] Read more.
Omega-3 long-chain polyunsaturated fatty acids (n-3 LC-PUFAs) such as eicosapentaenoic acid (20:5n-3, EPA) and docosahexaenoic acid (22:6n-3, DHA) offer protective benefits against various pathological conditions, including atherosclerosis, obesity, inflammation, and autoimmune diseases. Marine fish and seafood are the primary sources of n-3 LC-PUFAs in the human diet. However, the inclusion of fish oil in aquafeeds is declining due to limited availability, fluctuating prices, sustainability concerns, and replacement with vegetable oils. While comprehensive narrative reviews on the impact of substituting fish oil with vegetable oil in aquafeeds exist, quantitative studies are relatively scarce and mainly focused on comparing the source of vegetable oils. Herein, we employed, for the first time, a Bayesian meta-analysis approach, collecting research data from 81 articles to quantitatively analyze the effects of dietary n-3 LC-PUFA levels on the n-3 LC-PUFA composition and growth performance in cultured fish. Our findings indicate that with the exception of herbivorous fish, dietary n-3 LC-PUFA levels significantly affect the EPA and DHA levels in the livers and muscles of carnivorous, omnivorous, freshwater, and marine fish. Additionally, the growths of freshwater and herbivorous fish were less affected by changes in dietary n-3 LC-PUFA levels compared to that of carnivorous and marine fish. Full article
Show Figures

Figure 1

Figure 1
<p>Flow diagram for study search and selection according to Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) [<a href="#B7-animals-14-02118" class="html-bibr">7</a>].</p>
Full article ">Figure 2
<p>Distribution of studies included in this article based on country, publication date, and the feeding habits, habitats, and taxonomic orders of the studied fish. (<b>A</b>) Cumulative number of publications included in this article across different countries. (<b>B</b>) Cumulative number of publications included in this article from 2010 to 2023. (<b>C</b>) Cumulative number of publications related to the fish species studied in this article, categorized by habitat and feeding habit. (<b>D</b>) Cumulative number of publications related to the fish species studied in this article, categorized by taxonomic classification at the order rank.</p>
Full article ">Figure 3
<p>Percentages of various fatty acids in the feeds used in the research reports covered in this study. The control group refers to the group in a specific study with the highest <span class="html-italic">n</span>-3 LC-PUFA content in the feed. 0 &lt; RL ≤ 25, 25 &lt; RL ≤ 50, 50 &lt; RL ≤ 75, and 75 &lt; RL ≤ 100 denote the percentages of <span class="html-italic">n</span>-3 LC-PUFAs in the feed of a particular group in a study relative to its highest content group, falling within the ranges of 0–25%, 25–50%, 50–75%, and 75–100%, respectively. SFA, saturated fatty acid; MUFA, monounsaturated fatty acid; <span class="html-italic">n</span>-3, <span class="html-italic">n</span>-3 polyunsaturated fatty acids; <span class="html-italic">n</span>-6, <span class="html-italic">n</span>-6 polyunsaturated fatty acids; EPA, eicosapentaenoic acid; DHA, docosahexaenoic acid; <span class="html-italic">n</span>-3 LC-PUFA, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acid; RL, replacement level.</p>
Full article ">Figure 4
<p>The impact of dietary <span class="html-italic">n</span>-3 LC-PUFA levels on the FBWs of carnivorous, omnivorous, herbivorous, marine, and freshwater fish. The blue curve represents the posterior distribution of the SMD for the pooled effect size of the FBW. The black dot and black line below each blue curve indicate the median and 95% CrI of the posterior distribution, respectively. These values are also numerically displayed to the bottom right of each blue curve. The numerical values to the left of the brackets represent medians, and the values inside the brackets represent the 95% CrI. An SMD &lt; 0 indicates that the increase in the FBW is attributed to lower dietary <span class="html-italic">n</span>-3 LC-PUFAs, while an SMD &gt; 0 indicates that the increase in FBW is attributed to higher dietary <span class="html-italic">n</span>-3 LC-PUFAs. In general, an interval within the brackets containing 0 suggests that changes in dietary <span class="html-italic">n</span>-3 LC-PUFAs have no significant effect on FBW, while not containing 0 indicates a significant effect. RL, replacement level; FBW, final body weight; SMD, standardized mean difference; CrI, credible interval; <span class="html-italic">n</span>-3 LC-PUFAs, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acids.</p>
Full article ">Figure 5
<p>The impact of dietary <span class="html-italic">n</span>-3 LC-PUFA levels on the SGRs of carnivorous, omnivorous, herbivorous, marine, and freshwater fish. The blue curve represents the posterior distribution of the SMD for the pooled effect size of the SGR. The black dot and black line below each blue curve indicate the median and 95% CrI of the posterior distribution, respectively. These values are also numerically displayed to the bottom right of each blue curve. The numerical values to the left of the brackets represent medians, and the values inside the brackets represent the 95% CrI. An SMD &lt; 0 indicates that the increase in SGR is attributed to lower dietary <span class="html-italic">n</span>-3 LC-PUFAs, while an SMD &gt; 0 indicates that the increase in SGR is attributed to higher dietary <span class="html-italic">n</span>-3 LC-PUFAs. In general, an interval within the brackets containing 0 suggests that changes in dietary <span class="html-italic">n</span>-3 LC-PUFAs have no significant effect on SGR, while not containing 0 indicates a significant effect. RL, replacement level; SGR, specific growth rate; SMD, standardized mean difference; CrI, credible interval; <span class="html-italic">n</span>-3 LC-PUFAs, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acids.</p>
Full article ">Figure 6
<p>The impact of dietary <span class="html-italic">n</span>-3 LC-PUFA levels on liver EPA of carnivorous, omnivorous, herbivorous, marine, and freshwater fish. The blue curve represents the posterior distribution of the SMD for the pooled effect size of liver EPA. The black dot and black line below each blue curve indicate the median and 95% CrI of the posterior distribution, respectively. These values are also numerically displayed to the bottom right of each blue curve. The numerical values to the left of the brackets represent medians, and the values inside the brackets represent the 95% CrI. An SMD &lt; 0 indicates that the increase in liver EPA is attributed to lower dietary <span class="html-italic">n</span>-3 LC-PUFAs, while an SMD &gt; 0 indicates that the increase in liver EPA is attributed to higher dietary <span class="html-italic">n</span>-3 LC-PUFAs. In general, an interval within the brackets containing 0 suggests that changes in dietary <span class="html-italic">n</span>-3 LC-PUFAs have no significant effect on liver EPA, while not containing 0 indicates a significant effect. RL, replacement level; EPA, eicosapentaenoic acid; SMD, standardized mean difference; CrI, credible interval; <span class="html-italic">n</span>-3 LC-PUFAs, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acids.</p>
Full article ">Figure 7
<p>The impact of dietary <span class="html-italic">n</span>-3 LC-PUFA levels on liver DHA of carnivorous, omnivorous, herbivorous, marine, and freshwater fish. The blue curve represents the posterior distribution of the SMD for the pooled effect size of liver DHA. The black dot and black line below each blue curve indicate the median and 95% CrI of the posterior distribution, respectively. These values are also numerically displayed to the bottom right of each blue curve. The numerical values to the left of the brackets represent medians, and the values inside the brackets represent the 95% CrI. An SMD &lt; 0 indicates that the increase in liver DHA is attributed to lower dietary <span class="html-italic">n</span>-3 LC-PUFAs, while an SMD &gt; 0 indicates that the increase in liver DHA is attributed to higher dietary <span class="html-italic">n</span>-3 LC-PUFAs. In general, an interval within the brackets containing 0 suggests that changes in dietary <span class="html-italic">n</span>-3 LC-PUFAs have no significant effect on liver DHA, while not containing 0 indicates a significant effect. RL, replacement level; DHA, docosahexaenoic acid; SMD, standardized mean difference; CrI, credible interval; <span class="html-italic">n</span>-3 LC-PUFAs, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acids.</p>
Full article ">Figure 8
<p>The impact of dietary <span class="html-italic">n</span>-3 LC-PUFA levels on muscle EPA of carnivorous, omnivorous, herbivorous, marine, and freshwater fish. The blue curve represents the posterior distribution of the SMD for the pooled effect size of muscle EPA. The black dot and black line below each blue curve indicate the median and 95% CrI of the posterior distribution, respectively. These values are also numerically displayed to the bottom right of each blue curve. The numerical values to the left of the brackets represent medians, and the values inside the brackets represent the 95% CrI. An SMD &lt; 0 indicates that the increase in muscle EPA is attributed to lower dietary <span class="html-italic">n</span>-3 LC-PUFAs, while an SMD &gt; 0 indicates that the increase in muscle EPA is attributed to higher dietary <span class="html-italic">n</span>-3 LC-PUFAs. In general, an interval within the brackets containing 0 suggests that changes in dietary <span class="html-italic">n</span>-3 LC-PUFAs have no significant effect on muscle EPA, while not containing 0 indicates a significant effect. RL, replacement level; EPA, eicosapentaenoic acid; SMD, standardized mean difference; CrI, credible interval; <span class="html-italic">n</span>-3 LC-PUFAs, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acids.</p>
Full article ">Figure 9
<p>The impact of dietary <span class="html-italic">n</span>-3 LC-PUFA levels on muscle DHA of carnivorous, omnivorous, herbivorous, marine, and freshwater fish. The blue curve represents the posterior distribution of the SMD for the pooled effect size of muscle DHA. The black dot and black line below each blue curve indicate the median and 95% CrI of the posterior distribution, respectively. These values are also numerically displayed to the bottom right of each blue curve. The numerical values to the left of the brackets represent medians, and the values inside the brackets represent the 95% CrI. An SMD &lt; 0 indicates that the increase in muscle DHA is attributed to lower dietary <span class="html-italic">n</span>-3 LC-PUFAs, while an SMD &gt; 0 indicates that the increase in muscle DHA is attributed to higher dietary <span class="html-italic">n</span>-3 LC-PUFAs. In general, an interval within the brackets containing 0 suggests that changes in dietary <span class="html-italic">n</span>-3 LC-PUFAs have no significant effect on muscle DHA, while not containing 0 indicates a significant effect. RL, replacement level; DHA, docosahexaenoic acid; SMD, standardized mean difference; CrI, credible interval; <span class="html-italic">n</span>-3 LC-PUFAs, <span class="html-italic">n</span>-3 long-chain polyunsaturated fatty acids.</p>
Full article ">
12 pages, 547 KiB  
Article
Assessing Movements between Freshwater and Saltwater by Brown Trout (Salmo trutta L.) Based on Otolith Microchemistry
by Magdalena Andersson, Bror Jonsson, Olle Calles and Larry Greenberg
Animals 2024, 14(14), 2116; https://doi.org/10.3390/ani14142116 - 20 Jul 2024
Viewed by 151
Abstract
By analyzing otolith microchemistry, we examined the use of freshwater and marine environments by brown trout Salmo trutta L. that spawn in the Swedish River Emån and migrate to the Baltic Sea. We estimated the time juveniles spent in freshwater and the number [...] Read more.
By analyzing otolith microchemistry, we examined the use of freshwater and marine environments by brown trout Salmo trutta L. that spawn in the Swedish River Emån and migrate to the Baltic Sea. We estimated the time juveniles spent in freshwater and the number of times the fish returned to freshwater, presumably to spawn. Twenty-six percent of the fish migrated to sea by 1 year of age. However, 13% spent less than one year in the river. Most brown trout (48%) migrated to the sea between 1 and 2 years of age. On average, brown trout, which averaged 4.4 years in age (range 3–6 years), returned to freshwater 2.3 times, and there was an inverse relationship between time spent in freshwater after hatching and the number of visits to freshwater. Our results do not support the classical life history pattern, where brown trout spend one or more years in freshwater before migrating to the sea. Here, we found evidence that part of the population leaves freshwater during their first year. While the cause for precocial migration in the River Emån is not known, our results from this permanently flowing river do not support the idea proposed for other Baltic Sea populations, where the risk of drought has been suggested to be the cause. Full article
(This article belongs to the Section Aquatic Animals)
21 pages, 4007 KiB  
Article
Juvenile/Peripubertal Exposure to Omega-3 and Environmental Enrichment Differentially Affects CORT Secretion and Adulthood Stress Coping, Sociability, and CA3 Glucocorticoid Receptor Expression in Male and Female Rats
by Julie Raymond, Alexandre Morin, Meenakshie Bradley-Garcia and Hélène Plamondon
Nutrients 2024, 16(14), 2350; https://doi.org/10.3390/nu16142350 - 20 Jul 2024
Viewed by 368
Abstract
In adult rats, omega-3 supplementation through fish oil (FO) and environmental enrichment (EE) have shown beneficial effects on cognition and stress regulation. This study assessed sex-specific effects of FO and EE during adolescence, a period critical for brain maturation, on adulthood coping mechanisms, [...] Read more.
In adult rats, omega-3 supplementation through fish oil (FO) and environmental enrichment (EE) have shown beneficial effects on cognition and stress regulation. This study assessed sex-specific effects of FO and EE during adolescence, a period critical for brain maturation, on adulthood coping mechanisms, sociability, and glucocorticoid regulation. An amount of 64 Wistar rats [n = 32/sex; postnatal day (PND) 23] were assigned to supplementation of control soybean oil (CSO) or menhaden fish oil (FO; 0.3 mL/100 g) from PND28 to 47 and exposed to EE or regular cage (RC) housing from PND28 to 58, with their blood corticosterone (CORT) levels being assessed weekly. As adults, exposure to repeated forced swim tests (FSTs; PND90–91) enabled analysis of coping responses, while socioemotional and memory responses were evaluated using the OFT, EPM, SIT, and Y maze tests (PND92–94). Immunohistochemistry determined hippocampal CA1/CA3 glucocorticoid receptor (GR) expression (PND95). CORT secretion gradually increased as the supplementation period elapsed in female rats, while changes were minimal in males. Coping strategies in the FST differed between sexes, particularly in FO-fed rats, where females and males, respectively, favoured floating and tail support to minimise energy consumption and maintain immobility. In the SIT, FO/EE promoted sociability in females, while a CSO diet favoured social recognition in males. Reduced CA3 GR-ir expression was found in FO/RC and CSO/EE rat groups, supporting stress resilience and memory consolidation. Our findings support environment and dietary conditions to exert a sex-specific impact on biobehavioural responses. Full article
Show Figures

Figure 1

Figure 1
<p>Timeline of the experiment. Wistar rats (male and female, <span class="html-italic">N</span> = 64) arrived at the facility at PND23. Dietary supplementation [FO or CSO] was provided daily from PND28 to 47, and rats were exposed to EE or RC from PND28 to 59. Four conditions were tested: CSO/RC, CSO/EE, FO/RC, and FO/EE. Following the FST (PND90–91), rats were exposed to the OFT, EPM, SIT and Y-Maze (PND92–94). Brain tissue was collected on PND95. <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: environmental enrichment; RC: regular cage; CORT: corticosterone; FST: forced swim test; OFT: open field test; EPM: elevated-plus maze; SIT: social interaction test; GR-ir: glucocorticoid receptors</span>.</p>
Full article ">Figure 2
<p>Effect of supplementation, sex, and environment in the forced swim test (FST) on time spent climbing (<b>A</b>), swimming (<b>B</b>), immobility by floating (<b>C</b>), and immobility by tail support (<b>D</b>). Increased climbing was observed for CSO/RC males compared to all groups (<span class="html-italic">p</span> &lt; 0.001; #). FO Females climbed more than CSO regardless of the environment (<span class="html-italic">p</span> &lt; 0.001; *; (<b>A</b>)). Swimming was enhanced in CSO-fed females compared to male counterparts in both RC and EE (<span class="html-italic">p</span> &lt; 0.001; &amp;). Male CSO/RC rats show reduced swim compared to all groups (<span class="html-italic">p</span> &lt; 0.01, #; (<b>B</b>)). Immobility was increased in FO/RC females compared to all groups (<span class="html-italic">p</span> &lt; 0.001; #; (<b>C</b>)). Male rats fed FO used tail support to maintain immobility (<span class="html-italic">p</span> = 0.001; &amp;), while female counterparts preferred floating (<span class="html-italic">p</span> &lt; 0.001; #; (<b>D</b>)). Data are presented as mean ± S.E.M. * and # indicate significant differences between groups at <span class="html-italic">p</span> &lt; 0.05. * indicates significant impact of supplementation only (<span class="html-italic">p</span> &lt; 0.05). <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: enriched environment; RC: regular cage</span>.</p>
Full article ">Figure 3
<p>Effect of supplementation, sex, and environment in the Open Field Test (OFT) for time spent in the centre (<b>A</b>), time spent in the periphery (<b>B</b>), frequency to centre (<b>C</b>), and frequency to periphery (<b>D</b>). Male rodents spent more time in the centre zone compared to females (<span class="html-italic">p</span> &lt; 0.05; #). CSO/EE males spent increased time in the centre zone (<b>A</b>), while females in the same condition spent increased time in the periphery ((<b>B</b>); <span class="html-italic">p</span> &lt; 0.05; *). Rats in the FO/RC and CSO/EE group also entered more frequently the centre (<b>C</b>) and peripheral zone (<b>D</b>) compared to the FO/EE condition (<span class="html-italic">p</span> &lt; 0.05; &amp;). Data are presented as mean ± S.E.M. * and # indicate a statistically significant difference between groups (<span class="html-italic">p</span> &lt; 0.05). * indicates significant impact of the condition (supplementation and housing only) with no effect of sex (<span class="html-italic">p</span> &lt; 0.05). <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: enriched environment; RC: regular cage</span>.</p>
Full article ">Figure 4
<p>Effect of supplementation, sex, and environment in the Elevated Plus Maze (EPM) for frequency in the open arm (<b>A</b>) and closed arm (<b>B</b>). FO-supplemented rats entered the open (<b>A</b>) and closed arms (<b>B</b>) less frequently than CSO-supplemented rats (<span class="html-italic">p</span> &lt; 0.001; &amp;). Data are presented as mean ± S.E.M. &amp; indicates a significant impact of the condition (supplementation only) without an influence of sex or housing at <span class="html-italic">p</span> &lt; 0.05. <span class="html-italic">FO: menhaden fish oil; CSO: control Soybean oil; EE: enriched environment; RC: regular cage</span>.</p>
Full article ">Figure 5
<p>Effect of supplementation, sex, and environment in the Social Interaction Test (SIT) for exploration in session 1 (<b>A</b>) and session 2 (<b>B</b>). FO/EE females spent more time interacting with S1 than the empty cup compared to CSO/EE counterparts (<span class="html-italic">p</span> &lt; 0.05; *), supporting increased sociability (<b>A</b>). FO supplementation in males reduced social recognition through reduced interaction time with S2 compared to CSO-fed counterparts (<span class="html-italic">p</span> &lt; 0.05; *), notwithstanding housing conditions (<b>B</b>). Data are presented as mean ± S.E.M. * indicates a statistically significant difference between groups at <span class="html-italic">p</span> &lt; 0.05. <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: enriched environment; RC: regular cage</span>.</p>
Full article ">Figure 6
<p>Effect of supplementation, sex, and environment for latency to arm re-entry (<b>A</b>) and Risk assessment behaviour (<b>B</b>) in the Y-maze passive avoidance test. In general, males CSO/RC and FO/EE took more time to re-enter the aversive arm compared to females in the same condition (<span class="html-italic">p</span> &lt; 0.05; *; (<b>A</b>)). In males, CSO/EE and FO/EE showed reduced assessments compared to the CSO/RC condition (<span class="html-italic">p</span> &lt; 0.05; *). Females underwent fewer risk assessments compared to males (<span class="html-italic">p</span> &lt; 0.05; #; (<b>B</b>)). Data are presented as mean ± S.E.M. * and # indicate a statistically significant difference between groups at <span class="html-italic">p</span> &lt; 0.05. <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: enriched environment; RC: regular cage</span>.</p>
Full article ">Figure 7
<p>Corticosterone levels (pg/mL) assessed on experimental DAY1, 7, 14, 21. Statistical increases in CORT were observed for all females compared to males on DAY21 (<span class="html-italic">p</span> &lt; 0.001) as well as between females from DAY1, 7, and 14 (<span class="html-italic">p</span> &lt; 0.001 for each day). Data are presented as mean ± S.E.M. * indicates a statistically significant difference between groups at <span class="html-italic">p</span> &lt; 0.05. <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: enriched environment; RC: regular cage</span>.</p>
Full article ">Figure 8
<p>GR-ir at the CA3 region of the hippocampus. Figure shows representative photomicrographs of GR-ir in the CA3 for each experimental condition (<b>A</b>) as well as specificity of GR antibody through superposition on Hoechst adenine–thymine-binding dye (<b>B</b>). Reduced GR-ir was observed in CSO/EE and FO/RC groups compared to CSO/RC rats (<span class="html-italic">p</span> = 0.019 and <span class="html-italic">p</span> = 0.005, respectively; (<b>C</b>)). Data are presented as mean ± S.E.M. &amp; indicates effects of supplementation and housing without effects of sex (<span class="html-italic">p</span> &lt; 0.05). <span class="html-italic">FO: menhaden fish oil; CSO: control soybean oil; EE: enriched environment; RC: regular cage; GR: glucocorticoid receptors</span>.</p>
Full article ">
24 pages, 2732 KiB  
Review
Tracking Biomarkers for the Health and Welfare of Aquaculture Fish
by Joana Oliveira, Aires Oliva-Teles and Ana Couto
Fishes 2024, 9(7), 289; https://doi.org/10.3390/fishes9070289 - 19 Jul 2024
Viewed by 428
Abstract
Aquaculture production has been growing consistently over the last few decades to meet the increasing animal protein demand of the human population. However, increased production and rearing intensities raise the challenges of guaranteeing fish health and welfare, which is essential to avoid losses [...] Read more.
Aquaculture production has been growing consistently over the last few decades to meet the increasing animal protein demand of the human population. However, increased production and rearing intensities raise the challenges of guaranteeing fish health and welfare, which is essential to avoid losses and ensure product quality. Biomarkers can provide insights into the fish’s nutritional, physiological, and health status, and aid in the evaluation of early nutritional and physiological imbalances, distress conditions, and pathological diagnosis. The discovery and validation of biomarkers rely mostly on the use of information provided by different parameters, including biochemical, metabolic, or immunologic, as well as several omics, from genomics and transcriptomics to proteomics and metabolomics. In this review, a summary of the main biomarkers used in aquaculture is provided along with an overview of the main omics technologies available for further biomarker research. This review also highlights the need to develop non-lethal biomarkers that can easily and quickly be measured to provide a prompt response to producers. Full article
Show Figures

Figure 1

Figure 1
<p>Ideal qualities of biomarkers. Adapted from [<a href="#B11-fishes-09-00289" class="html-bibr">11</a>,<a href="#B15-fishes-09-00289" class="html-bibr">15</a>].</p>
Full article ">Figure 2
<p>Overview of the main digestive and intermediary metabolism enzymes in fish commonly used as biomarkers. ALP (Alkaline phosphatase); ALT (Alanine aminotransferase); AST (Aspartate aminotransferase); GDH (Glutamate dehydrogenase); ME (Malic enzyme); HOAD (β-hydroxyacyl-CoA dehydrogenase). It is possible to categorize these enzymes according to the substrate they act on. Adapted from [<a href="#B16-fishes-09-00289" class="html-bibr">16</a>,<a href="#B17-fishes-09-00289" class="html-bibr">17</a>,<a href="#B18-fishes-09-00289" class="html-bibr">18</a>,<a href="#B25-fishes-09-00289" class="html-bibr">25</a>,<a href="#B26-fishes-09-00289" class="html-bibr">26</a>,<a href="#B27-fishes-09-00289" class="html-bibr">27</a>,<a href="#B28-fishes-09-00289" class="html-bibr">28</a>,<a href="#B29-fishes-09-00289" class="html-bibr">29</a>,<a href="#B30-fishes-09-00289" class="html-bibr">30</a>,<a href="#B31-fishes-09-00289" class="html-bibr">31</a>].</p>
Full article ">Figure 3
<p>Overview of oxidative stress defense mechanisms in fish. Reactive oxygen species (ROS) are a natural product of oxygen metabolism which can have a deleterious effect on the organism, particularly when present in excess. Therefore, most organisms have mechanisms to help break down ROS. In fish, similarly to other animals, various enzymes have a crucial role in the defense against ROS. Adapted from [<a href="#B34-fishes-09-00289" class="html-bibr">34</a>,<a href="#B36-fishes-09-00289" class="html-bibr">36</a>,<a href="#B37-fishes-09-00289" class="html-bibr">37</a>,<a href="#B38-fishes-09-00289" class="html-bibr">38</a>].</p>
Full article ">Figure 4
<p>Overview of extracellular vesicles (EV). Extracellular vesicles can be produced by various types of normal cells and are commonly divided into three types. Exosomes are smaller than microvesicles but both vesicles share similar cargo, which can consist of proteins, lipids, and nucleic acids. Apoptotic bodies, on the other hand, are Evs that are produced by dying cells and typically contain intact organelles, chromatin, and glycosylated proteins. Adapted from [<a href="#B63-fishes-09-00289" class="html-bibr">63</a>,<a href="#B64-fishes-09-00289" class="html-bibr">64</a>].</p>
Full article ">
14 pages, 5104 KiB  
Article
Feed Components and Timing to Improve the Feed Conversion Ratio for Sustainable Aquaculture Using Starch
by Hideaki Shima, Taiga Asakura, Kenji Sakata, Masahiko Koiso and Jun Kikuchi
Int. J. Mol. Sci. 2024, 25(14), 7921; https://doi.org/10.3390/ijms25147921 - 19 Jul 2024
Viewed by 251
Abstract
Aquaculture contributes to the sustainable development of food security, marine resource conservation, and economy. Shifting aquaculture feed from fish meal and oil to terrestrial plant derivatives may result in cost savings. However, many carnivorous fish cannot be sustained on plant-derived materials, necessitating the [...] Read more.
Aquaculture contributes to the sustainable development of food security, marine resource conservation, and economy. Shifting aquaculture feed from fish meal and oil to terrestrial plant derivatives may result in cost savings. However, many carnivorous fish cannot be sustained on plant-derived materials, necessitating the need for the identification of important factors for farmed fish growth and the identification of whether components derived from terrestrial plants can be used in feed. Herein, we focused on the carnivorous fish leopard coral grouper (P. leopardus) to identify the essential growth factors and clarify their intake timing from feeds. Furthermore, we evaluated the functionality of starch, which are easily produced by terrestrial plants. Results reveal that carbohydrates, which are not considered essential for carnivorous fish, can be introduced as a major part of an artificial diet. The development of artificial feed using starch offers the possibility of increasing the growth of carnivorous fish in aquaculture. Full article
(This article belongs to the Section Molecular Biophysics)
Show Figures

Figure 1

Figure 1
<p>Differences based on feed type using distance information and the corresponding heatmap. (<b>a</b>) Nonmetric Multidimensional Scaling. Each circle shows distance data of feed similarity. Distance information was calculated as the Euclidean distance. (<b>b</b>) The ratio of signal intensities measured by nuclear magnetic resonance spectroscopy between feed types. Data are sorted by metabolite similarity (Ward method, arranged by similarity). A normalization step was performed for each metabolite.</p>
Full article ">Figure 2
<p>Heatmap of the components in the muscles of <span class="html-italic">P. leopardus</span> sorted by time (days) after hatching. Fish are arranged in descending order from top to bottom, with natural ocean fish at the bottom. Left, number of days since hatching; right, main feed type. Circles, squares, and triangles indicate brachionus, artemia, and artificial bait, respectively. The graph is sorted by metabolite similarity (Ward method, arranged by similarity). A normalization step was performed for each metabolite.</p>
Full article ">Figure 3
<p>Distribution of common relevant factors to time fluctuations for separating high- and low-growth by machine learning. Relevant factors for classifying fish into high- and low-growth groups on each sampling day were calculated using the random forest method. It was repeated 20 times, and each Gini impurity was used as an importance score, with high implied importance. The x-axis represents the values on the right. In the list on the right, numbers next to names indicate multiple signals measured from the same component. Conversely, a signal with multiple names indicates overlapping signals. The horizontal black line indicates the average, and the vertical bar indicates one standard deviation.</p>
Full article ">Figure 4
<p>Probabilistic network for large and small fish based on important growth factors. Components that were used were extracted from random forest regression and from those that suggested a relationship between taurine and glycine. Part (<b>a</b>) was drawn using Large sample data (largest five individuals on each sampling day), and part (<b>b</b>) was drawn using Small sample data (smallest five individuals on each sampling day). The arrows indicate the probabilistic direction, and the line width indicates the strength of the connection. Red borders indicate important factors for growth (objective variables for regression), green indicates amino acids, yellow indicates glucose and blue indicates other components.</p>
Full article ">Figure 5
<p>Time-series heatmap of growth-related components for fish groups with large and small body sizes. Growth-related components were extracted and used to depict the Bayesian network. Fish growth increases from left to right. The top half shows large fish, and the bottom shows the small fish. Scaling was performed in the time direction. The main feed type is shown at the bottom. Circles, squares, and triangles indicate brachionus, artemia, and artificial bait, respectively.</p>
Full article ">Figure 6
<p><sup>1</sup>H–<sup>13</sup>C HSQC spectra of water-soluble metabolites in <span class="html-italic">P. leopardus</span> muscle tissue. (<b>a</b>) Coupling constants between carbon atoms shown in Hz and indicated by arrows. Carbon atoms of the amino acids are successively numbered from the carboxyl carbon next to those carrying the amino group. Colored signals are <sup>13</sup>C-labeled metabolites derived from <sup>13</sup>C-labeled starch in the feed. Green, glyceraldehyde-3-phosphate (G3P); red, glycine; blue, lactate; light green, alanine. (<b>b</b>) Illustration of the metabolism of <sup>13</sup>C-labeled starch into other compounds based on visual inspection of NMR data.</p>
Full article ">Figure 7
<p><sup>1</sup>H–<sup>13</sup>C correlation and <sup>1</sup>H–<sup>1</sup>H <span class="html-italic">J</span>-resolved (2D-<span class="html-italic">J</span>res) NMR spectrum of muscle tissue. (<b>a</b>,<b>b</b>) Two-dimensional HSQC spectrum. (<b>c</b>) Two-dimensional 2D-<span class="html-italic">J</span>res spectrum. (<b>d</b>) Skyline plot of (<b>c</b>). The color indicates intensity. When blue is one, green is twice as strong, yellow is four times as strong, and red is eight times as strong (<a href="#app1-ijms-25-07921" class="html-app">Supplementary Table S1</a>).</p>
Full article ">Figure 8
<p>Histogram showing original growth distribution of <span class="html-italic">P. leopardus</span> and simulation results of aquaculture using starch effectively. Red histogram indicates length of <span class="html-italic">P. leopardus</span> at 52 days after hatching, and blue histogram indicates the simulated result. The simulation was scaled such that the average improvement was 30% and deviation was 10%.</p>
Full article ">
11 pages, 893 KiB  
Article
Hepatopancreas Transcriptome Analysis of Spinibarbus sinensis to Reveal Different Growth-Related Genes
by Bo Zhou, Leyan Ling, Bin Wang, Fei Yang, Mengdan Hou, Fan Liu, Yu Li, Hui Luo, Wenping He and Hua Ye
Genes 2024, 15(7), 949; https://doi.org/10.3390/genes15070949 - 19 Jul 2024
Viewed by 221
Abstract
Spinibarbus sinensis, also known as Qingbo, is an important economic fish in China. However, the detailed mechanisms underlying its growth are still unknown. To excavate the genes and signaling pathways related to its growth, we compared the transcriptome profiles of the hepatopancreas [...] Read more.
Spinibarbus sinensis, also known as Qingbo, is an important economic fish in China. However, the detailed mechanisms underlying its growth are still unknown. To excavate the genes and signaling pathways related to its growth, we compared the transcriptome profiles of the hepatopancreas tissues of S. sinensis, with two groups of growth rate for evaluation. An average of 66,304,909 and 68,739,585 clean reads were obtained in the fast growth (FG) and slow growth (SG) group, respectively. The differential gene expression analysis results showed that 272 differentially expressed genes (DEGs) were screened between the FG and SG groups, including 101 up-regulated genes and 171 down-regulated genes. Gene Ontology (GO) and Kyoto Encyclopedia of Genes and Genomes (KEGG) enrichment analysis results showed that GO terms related to metabolic process, organic substance metabolic process, and catalytic activity were enriched, pathway signals related to steroid biosynthesis and protein digestion and absorption were also detected. Meanwhile, the potential key regulatory genes sst2, fndc4, and cckra related to the growth of S. sinensis were screened. Reverse transcript fluorescence quantitative PCR (RT-qPCR) validation of 18 DEGs associated with growth differences showed that the RT-qPCR results were consistent with RNA-seq analysis, and nine genes, stk31, gpr149, angptl1, fstl1, sik1, ror2, nlrc3, pdlim2, and nav2 were significantly expressed in the FG group. bmp1, stc1, gpatch8, sstrt2, s100a1, ktf6, cckar6, sync1, bhlha15, a total of nine genes were significantly expressed in the SG group. This study provides basic information for improving the growth characteristics of S. sinensis and the functional research of candidate genes. Full article
(This article belongs to the Section Animal Genetics and Genomics)
9 pages, 3859 KiB  
Article
First Record of the Invasive Alien Species Rugulopteryx okamurae (Phaeophyceae, Dictyotales) along the Eastern Coast of Sicily (Italy, Mediterranean Sea): Is It Ready to Expand into the Ionian Sea?
by Giuliana Marletta, Andrea Lombardo and Donatella Serio
Diversity 2024, 16(7), 424; https://doi.org/10.3390/d16070424 - 19 Jul 2024
Viewed by 214
Abstract
The Mediterranean Sea is a hotspot for the introduction of non-indigenous species. Among them, invasive alien species can seriously affect the areas they colonize, not only by altering the marine food webs and community structure, but also by harming certain economic activities, such [...] Read more.
The Mediterranean Sea is a hotspot for the introduction of non-indigenous species. Among them, invasive alien species can seriously affect the areas they colonize, not only by altering the marine food webs and community structure, but also by harming certain economic activities, such as fishing, tourism, aquaculture and marine infrastructure. Rugulopteryx okamurae is a brown macroalga considered the fourth most harmful species among the 10 most invasive species reported in the Mediterranean; in fact, it has recently been included in the list of invasive alien species of Union concern due to its serious impact on biodiversity and socioeconomic implications. This species was reported for the first time in the Mediterranean in 2002 in Thau Lagoon (France), introduced by the aquaculture of the Japanese oyster Magallana gigas. Since then, this species has spread in both the Mediterranean and Atlantic Ocean with a strong invasive behavior, particularly along the Strait of Gibraltar. Rugulopteryx okamurae was also recently reported for the first time in Italian waters, in the Gulf of Palermo (Sicily). In this study, we report a record of this species further to the east, in the Ionian Sea, where it has not previously been recorded, and provide possible explanations of the spreading and arrival routes in this area. The rapid expansion of R. okamurae is raising concerns; thus, in order to safeguard native communities, it is crucial to keep monitoring this invasive species so that it is possible to regularly update its distribution and follow up on its spread dynamics in the Mediterranean basin. Full article
(This article belongs to the Special Issue Biodiversity in Italy: Past and Future Perspectives)
Show Figures

Figure 1

Figure 1
<p>Map showing the distribution of <span class="html-italic">Rugulopteryx okamurae</span> in the Mediterranean Sea. In red squares. the related bibliographic reference: Bellissimo et al., 2023 = [<a href="#B8-diversity-16-00424" class="html-bibr">8</a>]; Verlaque et al., 2009 = [<a href="#B11-diversity-16-00424" class="html-bibr">11</a>]; Lauret and Verlaque, 2013 = [<a href="#B12-diversity-16-00424" class="html-bibr">12</a>]; Ocaña et al., 2016 = [<a href="#B13-diversity-16-00424" class="html-bibr">13</a>]; Altamirano et al., 2016 = [<a href="#B14-diversity-16-00424" class="html-bibr">14</a>]; Terradas-Fernández et al., 2023 = [<a href="#B16-diversity-16-00424" class="html-bibr">16</a>]; El Aamari et al., 2018 = [<a href="#B17-diversity-16-00424" class="html-bibr">17</a>]; Ruitton et al., 2021 = [<a href="#B18-diversity-16-00424" class="html-bibr">18</a>]; Tursi et al., 2023 = [<a href="#B19-diversity-16-00424" class="html-bibr">19</a>]. p.s. = present study.</p>
Full article ">Figure 2
<p><span class="html-italic">Rugulopteryx okamurae</span> from the Ionian Sea. (<b>A</b>) Thallus in natural habitat at 30 m depth observed in May 2024 (CAT 2248). (<b>B</b>) Thallus of a specimen collected in March 2024 (CAT 2247). Scale bar = 2 cm (black arrows indicate swollen frond margins).</p>
Full article ">Figure 3
<p><span class="html-italic">Rugulopteryx okamurae</span> from the Ionian Sea. Specimen collected in March 2024 (CAT 2247). (<b>A</b>) Basal portion of thallus with multicellular rhizoids. Scale bar = 200 µm. (<b>B</b>) Apical portion of the thallus. Scale bar = 200 µm. (<b>C</b>) Detail of an initial dichotomy showing the two apical cells. Scale bar = 50 µm. (<b>D</b>) Detail of transverse section of subapical part of the thallus showing one layer of medullary cells centrally and two layers marginally. Scale bar = 100 µm. (<b>E</b>) Detail of transverse section of middle part of the thallus showing four layers of medullary cells marginally. Scale bar = 100 µm. (<b>F</b>) Detail of transverse section of basal part of the thallus showing a multilayered medulla. Scale bar = 100 µm.</p>
Full article ">
Back to TopTop