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146 results for “Mytilus”
Modeling the metabolic profile of Mytilus edulis reveals molecular signatures linked to gonadal development, sex and environmental site
<p>Metabolomics dataset used in the publication "Modeling the metabolic profile of Mytilus edulis reveals molecular signatures linked to gonadal development, sex and environmental site"</p> <p>Jaanika Kronberg, Jonathan J. Byrne, Jeroen Jansen, Philipp Antczak, Adam Hines, John Bignell, Ioanna Katsiadaki, Mark R. Viant and Francesco Falciani </p> <p>Metabolomics dataset for metabolic bins 1 to 1045 for 376 mussels as used in the publication.</p> <p>Mussel metadata are described in a separate file (spectrum number, sample label, sex, site, species, month, temperature of water, salinity of water, ADG rate, gonadal stage, parasite load)</p> <p>Species 1: Mytilus edulis, species 2: hybrid, species 3: Mytilus galloprovincialis</p>
Annotation and Orthofinder results for three Mytilus species genomes.
<p>Annotations and Orthofinder results for three Mytilus species genomes: accessions JAKGDF000000000 (MgalMED), JAKGDG000000000 (MeduEUS), and JAKGDH000000000 (MeduEUN).</p>
Dataset: Baseline for the Northeast Atlantic (58 – 70° N) intertidal Mytilus species complex (Mytilus spp.) 2021-2022
<p><strong><span>Aim: </span></strong><span>Mussels (<em>Mytilus spp</em>.) are abundant in the North Atlantic, sessile, and sensitive to environmental change, and suitable as sentinels of environment and climate change of costal ecosystems. We aimed to determine the baseline for the Northeast Atlantic (58 – 70° N)<em> Mytilus</em> species complex, and to show the present distribution to surveys conducted 60 years ago. </span></p> <p><strong><span>Location:</span></strong><span> Northeast Atlantic </span></p> <p><strong><span>Methodology: </span></strong><span>Baseline was obtained by investigating a total of 509 stations in the intertidal zone, in four regions comprising the environmental gradient from head of fjord to coast, and distributed over the latitudinal gradient from 58 – 70° N. </span></p> <p><strong><span>Results:</span></strong><span> The baseline shows a range in continuous abundance of mussels from 12 to 36 %, patchy abundance from 26 to 57 % and no or very limited mussel abundance from 26 to 46 % between the four regions. The presence of mussels in the southeast and west region was visualized to previous surveys conducted 60 years ago. The data points to similar past and present presence of mussels in both regions, yet past major mussel fields in the inner section of region southeast was not detected in this study.</span></p> <p><strong><span>Main conclusions:</span></strong></p> <p><span>The baseline of <em>Mytilus spp.</em> in the Northeast Atlantic (58 – 70° N) is now available for future reference. The baseline, plotted to surveys conducted 60 years ago, points to awareness of the population situated in the southeast section of the investigated region. Continued monitoring and modelling are needed to clarify drivers of temporal and spatial variation in the mussel populations along the Northeastern Atlantic coast. </span></p>
mRNA expression data of genes related to mitochondrial quality control in hepatopancreas of the two marine bivalves, Mytilus edulis and Crassostrea gigas, during short-term hypoxia/reoxygenation stress
<p>Coastal environments commonly experience strong oxygen fluctuations. Resulting hypoxia/reoxygenation stress can negatively affect mitochondrial functions, since oxygen deficiency impairs ATP generation, whereas a surge of oxygen causes mitochondrial damage by oxidative stress mechanisms. Marine intertidal bivalves are adapted to fluctuating oxygen conditions, yet the underlying molecular mechanisms that sustain mitochondrial integrity and function during oxygen fluctuations are not yet well understood. We used targeted mRNA expression analysis to determine the potential involvement of the mitochondrial quality control mechanisms in responses to short-term hypoxia (24 h at <0.01% O<sub>2</sub>) and subsequent reoxygenation (1.5 h at 21% O<sub>2</sub>) in two hypoxia-tolerant marine bivalves, the Pacific oysters <em>Crassostrea gigas</em> and the blue mussels <em>Mytilus edulis</em>. To test these hypotheses, We focused on the transcript levels of the following marker genes: for mitochondrial fission and fusion - <em>mfn</em>2 (encoding mitofusin 2), <em>opa</em>1 (mitochondrial dynamin-like 120kDa protein), <em>dnm</em>1<em>l </em>(dynamin-1-like protein), <em>mff</em> (mitochondrial fission factor), <em>fis</em>1 (mitochondrial fission protein 1); for protein and DNA quality control - <em>tsfm</em> (encoding mitochondrial translation elongation factor Ts), <em>lonp</em>1 (mitochondrial Lon protease), <em>spg</em>7 (paraplegin), <em>oma</em>1 (mitochondrial metalloendopeptidase OMA1), <em>clpB</em> (mitochondrial caseinolytic matrix peptidase chaperone subunit B), <em>atp</em>23 (mitochondrial inner membrane protease ATP23), <em>twnk</em> (mitochondrial twinkle mtDNA helicase); and for mitophagy - <em>mieap</em> (encoding mitochondrial eating protein), <em>hyou</em>1 (hypoxia upregulated protein 1), <em>prkn</em> (parkin), <em>pink</em>1 (PTEN- induced kinase 1), and <em>pgam</em>5 (mitochondrial serine/threonine protein phosphatase PGAM5). The revealed species-specific differences in the expression of the mitochondrial quality control pathways shed light on the potentially important mechanisms of mitochondrial protection against H/R-induced damage that might contribute to hypoxia tolerance in marine bivalves. </p>
Data from: Multimodal in situ datalogging quantifies inter-individual variation in thermal experience and persistent origin effects on gaping behavior among intertidal mussels (Mytilus californianus)
In complex habitats, environmental variation over small spatial scales can equal or exceed larger-scale gradients. This small-scale variation may allow motile organisms to mitigate stressful conditions by choosing benign microhabitats, whereas sessile organisms may rely on other behaviors to cope with environmental stresses in these variable environments. We developed a monitoring system to track body temperature, valve gaping behavior, and posture of individual mussels (Mytilus californianus) in field conditions in the rocky intertidal zone. Neighboring mussels' body temperatures varied by up to 14°C during low tides. Valve gaping during low tide and postural adjustments, which could theoretically lower body temperature, were not commonly observed. Rather, gaping behavior followed a tidal rhythm at a warm, high intertidal site; this rhythm shifted to a circadian period at a low intertidal site and for mussels continuously submerged in a tidepool. However, individuals within a site varied considerably in time spent gaping when submerged. This behavioral variation could be attributed in part to persistent effects of mussels' developmental environment. Mussels originating from a wave-protected, warm site gaped more widely, and they remained open for longer periods during high tide than mussels from a wave-exposed, cool site. Variation in behavior was modulated further by recent wave heights and body temperatures during the preceding low tide. These large ranges in body temperatures and durations of valve closure events - which coincide with anaerobic metabolism - support the conclusion that individuals experience "homogeneous" aggregations such as mussel beds in dramatically different fashion, ultimately contributing to physiological variation among neighbors.
Data from: Adaptive genetic variation distinguishes Chilean blue mussels (Mytilus chilensis) from different marine environments
Chilean mussel populations have been thought to be panmictic with limited genetic structure. Genotyping-by-sequencing approaches have enabled investigation of genome-wide variation that may better distinguish populations that have evolved in different environments. We investigated neutral and adaptive genetic variation in Mytilus from six locations in southern Chile with 1,240 SNP obtained with RAD-seq. Differentiation among locations with 891 neutral SNPs was low (FST = 0.005). Higher differentiation was obtained with a panel of 58 putative outlier SNPs (FST = 0.114) indicating the potential for local adaptation. This panel identified clusters of genetically related individuals and demonstrated that much of the differentiation (~92%) could be attributed to the three major regions and environments: extreme conditions in Patagonia, inner bay influenced by aquaculture (Reloncaví́), and outer bay (Chiloé Island). Patagonia samples were most distinct, but additional analysis carried out excluding this collection also revealed adaptive divergence between inner and outer bay samples. The four locations within Reloncaví́ area were most similar with all panels of markers, likely due to similar environments, high gene flow by aquaculture practices and low geographic distance. However, fine scale structure could be detected when analyses included only this zone. Our results and the SNP markers developed will be a powerful tool supporting management and programs of this harvested species.
Рис. 2. Распредение биомассы Mytilus trossulus septentrionalis на литорали дальневоcточных морей России. Здесь и далее на гистограммах по оси абцисс после географических пунктов в скобках укаЗана выборка (число иЗученных проб), по оси ординат – максимальные ЗначениЯ биомассы вида. Под Значением биомассы 0.1 г/м² подраЗумеваютсЯ качественные пробы. СокраЩениЯ (бмп) и (топ) оЗначают соответственно беринговоморское и тихоокеанское побережьЯ Восточной Камчатки. Побережье Зал. Петра Великого от устьЯ р. Туманной к северу до м. Поворотного условно отноcитсЯ к южному Приморью; побережье к северу от м. Поворотного (пос. Преображение, б. СоколовскаЯ) до б. Ольга, включительно, условно относитсЯ к среднему Приморью; побережье к северу от б. Ольга до м. Белкина и материковое побережье Татарского пролива относим к северному Приморью. Fig. 2. The distribution of biomass of Mytilus trossulus septentrionalis in the intertidal zone of the Far Eastern seas of Russia. Here and throughout on histograms, on the abcissa is the number of studied samples (numbers in parentheses following the names geographic localities), on the ordinate is the maximum biomass of species. The number 0.1 g wet wt m-2 means the qualitative samples. Abbreviations (bmp) and (top) mean the Bering Sea coast and the Pacific coast of eastern Kamchatka. The coast of Peter the Great Bay from the mouth of the Tumannaya River to Cape Povorotny is conditionally referred to as southern Primorye; the area north of Cape Povorotny (Preobrazhenie Settlement, Sokolovskaya Bay) to Olga Bay inclusive is conditionally referred to as middle Primorye; north of Olga Bay to Cape Belkin and the mainland coast of the Tatar Strait to as northern Primorye. in Bivalve mollusks of the intertidal zone of the Far Eastern seas of Russia
Рис. 2. Распредение биомассы Mytilus trossulus septentrionalis на литорали дальневоcточных морей России. Здесь и далее на гистограммах по оси абцисс после географических пунктов в скобках укаЗана выборка (число иЗученных проб), по оси ординат – максимальные ЗначениЯ биомассы вида. Под Значением биомассы 0.1 г/м² подраЗумеваютсЯ качественные пробы. СокраЩениЯ (бмп) и (топ) оЗначают соответственно беринговоморское и тихоокеанское побережьЯ Восточной Камчатки. Побережье Зал. Петра Великого от устьЯ р. Туманной к северу до м. Поворотного условно отноcитсЯ к южному Приморью; побережье к северу от м. Поворотного (пос. Преображение, б. СоколовскаЯ) до б. Ольга, включительно, условно относитсЯ к среднему Приморью; побережье к северу от б. Ольга до м. Белкина и материковое побережье Татарского пролива относим к северному Приморью. Fig. 2. The distribution of biomass of Mytilus trossulus septentrionalis in the intertidal zone of the Far Eastern seas of Russia. Here and throughout on histograms, on the abcissa is the number of studied samples (numbers in parentheses following the names geographic localities), on the ordinate is the maximum biomass of species. The number 0.1 g wet wt m-2 means the qualitative samples. Abbreviations (bmp) and (top) mean the Bering Sea coast and the Pacific coast of eastern Kamchatka. The coast of Peter the Great Bay from the mouth of the Tumannaya River to Cape Povorotny is conditionally referred to as southern Primorye; the area north of Cape Povorotny (Preobrazhenie Settlement, Sokolovskaya Bay) to Olga Bay inclusive is conditionally referred to as middle Primorye; north of Olga Bay to Cape Belkin and the mainland coast of the Tatar Strait to as northern Primorye.
Geographical distribution of the Mediterranean mussel Mytilus galloprovincialis Lamarck, 1819 in the Sea of Japan. in The extension of the distributional range of an invasive mussel, Mytilus galloprovincialis (Bivalvia: Mytilidae) in the Sea of Japan
Geographical distribution of the Mediterranean mussel Mytilus galloprovincialis Lamarck, 1819 in the Sea of Japan.
Фототаблица 1 Plate 1 A, B – Arca boucardi (Jousseaume, 1894): СевернаЯ КореЯ, провинциЯ Северный Хамгён, длина 26.3 мм, ЗМ ДВФУ № 38389/Bv-5786; C–F – Glycymeris (Glycymeris) imperialis Kuroda, 1934: СевернаЯ КореЯ, провинциЯ Северный Хамгён, ЁмбудЖин, длина 15.3 мм, ЗМ ДВФУ № 38374/Bv-5780; G, H – G. imperialis: СевернаЯ КореЯ, провинциЯ Северный Хамгён, ЁмбудЖин, длина 20.6 мм, ЗМ ДВФУ № 38375/Bv-5781; I, J – Mytilus (Mytilus) сoruscus Gould, 1861: СевернаЯ КореЯ, провинциЯ Северный Хамгён, ЁмбудЖин, длина 64.0 мм, ЗМ ДВФУ № 38371/Bv-5777; K, L – Modiolus (Modiolus) kurilensis (Bernard, 1983): СевернаЯ КореЯ, провинциЯ Северный Хамгён, длина 28.7 мм, ЗМ ДВФУ № 38373/Bv-5779; M, N – Septifer (Mytilisepta) virgatus (Wiegmann, 1837): СевернаЯ КореЯ, провинциЯ Северный Хамгён, длина 28.6 мм, ЗМ ДВФУ № 38372/Bv-5778; O–R: Mytilus (Mytilus) trossulus A.A Gould, 1850: СевернаЯ КореЯ, провинциЯ Северный Хамгён, Чипсам, длина 20.4 мм, ЗМ ДВФУ № 38617/Bv-5898; S, T – Septifer (Mytilisepta) keenae Nomura, 1936: СевернаЯ КореЯ, провинциЯ Северный Хамгён, Чипсам, длина 18.5 мм, ЗМ ДВФУ № 38615/Bv-5896. A, B – Arca boucardi (Jousseaume, 1894): North Korea, North Hamgyong Province, shell length 26.3 mm, ZMFU no. 38389/Bv-5786; C–F – Glycymeris (Glycymeris) imperialis Kuroda, 1934: North Korea, North Hamgyong Province, Yombunjin, shell length 15.3 mm, ZMFU no. 38374/Bv-5780; G, H – G. imperialis: North Korea, North Hamgyong Province, Yombunjin, shell length 20.6 mm, ZMFU no. 38375/Bv-5781; I, J – Mytilus (Mytilus) сoruscus Gould, 1861: North Korea, North Hamgyong Province, Yombunjin, shell length 64.0 mm, ZMFU no. 38371/Bv-5777; K, L – Modiolus (Modiolus) kurilensis (Bernard, 1983): North Korea, North Hamgyong Province, shell length 28.7 mm, ZMFU no. 38373/Bv-5779; M, N – Septifer (Mytilisepta) virgatus (Wiegmann, 1837): North Korea, North Hamgyong Province, shell length 28.6 mm, ZMFU no. 38372/Bv-5778; O–R: Mytilus (Mytilus) trossulus A.A Gould, 1850: North Korea, North Hamgyong Province, Jipsam, shell length 20.4 mm, ZMFU no. 38617/Bv-5898; S, T – Septifer (Mytilisepta) keenae Nomura, 1936: North Korea, North Hamgyong Province, Jipsam, shell length 18.5 mm, ZMFU no. 38615/Bv-5896. in On the bivalve molluscan fauna of North Hamgyong Province (North Korea)
Фототаблица 1 Plate 1 A, B – Arca boucardi (Jousseaume, 1894): СевернаЯ КореЯ, провинциЯ Северный Хамгён, длина 26.3 мм, ЗМ ДВФУ № 38389/Bv-5786; C–F – Glycymeris (Glycymeris) imperialis Kuroda, 1934: СевернаЯ КореЯ, провинциЯ Северный Хамгён, ЁмбудЖин, длина 15.3 мм, ЗМ ДВФУ № 38374/Bv-5780; G, H – G. imperialis: СевернаЯ КореЯ, провинциЯ Северный Хамгён, ЁмбудЖин, длина 20.6 мм, ЗМ ДВФУ № 38375/Bv-5781; I, J – Mytilus (Mytilus) сoruscus Gould, 1861: СевернаЯ КореЯ, провинциЯ Северный Хамгён, ЁмбудЖин, длина 64.0 мм, ЗМ ДВФУ № 38371/Bv-5777; K, L – Modiolus (Modiolus) kurilensis (Bernard, 1983): СевернаЯ КореЯ, провинциЯ Северный Хамгён, длина 28.7 мм, ЗМ ДВФУ № 38373/Bv-5779; M, N – Septifer (Mytilisepta) virgatus (Wiegmann, 1837): СевернаЯ КореЯ, провинциЯ Северный Хамгён, длина 28.6 мм, ЗМ ДВФУ № 38372/Bv-5778; O–R: Mytilus (Mytilus) trossulus A.A Gould, 1850: СевернаЯ КореЯ, провинциЯ Северный Хамгён, Чипсам, длина 20.4 мм, ЗМ ДВФУ № 38617/Bv-5898; S, T – Septifer (Mytilisepta) keenae Nomura, 1936: СевернаЯ КореЯ, провинциЯ Северный Хамгён, Чипсам, длина 18.5 мм, ЗМ ДВФУ № 38615/Bv-5896. A, B – Arca boucardi (Jousseaume, 1894): North Korea, North Hamgyong Province, shell length 26.3 mm, ZMFU no. 38389/Bv-5786; C–F – Glycymeris (Glycymeris) imperialis Kuroda, 1934: North Korea, North Hamgyong Province, Yombunjin, shell length 15.3 mm, ZMFU no. 38374/Bv-5780; G, H – G. imperialis: North Korea, North Hamgyong Province, Yombunjin, shell length 20.6 mm, ZMFU no. 38375/Bv-5781; I, J – Mytilus (Mytilus) сoruscus Gould, 1861: North Korea, North Hamgyong Province, Yombunjin, shell length 64.0 mm, ZMFU no. 38371/Bv-5777; K, L – Modiolus (Modiolus) kurilensis (Bernard, 1983): North Korea, North Hamgyong Province, shell length 28.7 mm, ZMFU no. 38373/Bv-5779; M, N – Septifer (Mytilisepta) virgatus (Wiegmann, 1837): North Korea, North Hamgyong Province, shell length 28.6 mm, ZMFU no. 38372/Bv-5778; O–R: Mytilus (Mytilus) trossulus A.A Gould, 1850: North Korea, North Hamgyong Province, Jipsam, shell length 20.4 mm, ZMFU no. 38617/Bv-5898; S, T – Septifer (Mytilisepta) keenae Nomura, 1936: North Korea, North Hamgyong Province, Jipsam, shell length 18.5 mm, ZMFU no. 38615/Bv-5896.
Fig. 4 in The dual impact of Ostreopsis cf. ovata on Mytilus galloprovincialis and Paracentrotus lividus: Toxin accumulation and pathological aspects Abstract
Fig. 4: Health status of sea urchins (avg±SDV, n = 4 animals) exposed to Ostreopsis cf. ovata (strain D483) for five days at different cell densities. Health index 1 corresponds to all four sea urchins alive after five days of exposure, 0 to all sea urchins dead in four days, intermediate values to different degrees of damage such as spine folded, partial and total spine loss and death in five days.
Fig. 6 in The dual impact of Ostreopsis cf. ovata on Mytilus galloprovincialis and Paracentrotus lividus: Toxin accumulation and pathological aspects Abstract
Fig. 6: Sea-urchin health status (avg±SDV, n = 4) after exposure to whole Ostreopsis cf. ovata cultures (strain 00APS0810-S1) or toxins extracted from cultures of the same cell density.
Fig. 2 in The dual impact of Ostreopsis cf. ovata on Mytilus galloprovincialis and Paracentrotus lividus: Toxin accumulation and pathological aspects Abstract
Fig. 2: Feeding of Mytilus galloprovincialis on Ostreopsis cf. ovata in a 72 h experiment. Weight-normalised ingested cells (avg±SDV) at different time intervals. Fresh microalgal cultures (2.17±0.23·103 cells ml-1) were provided every 24 h. Of the 10 animals of each replicate, 7-8 died at the beginning of the second day while the survivors were toxic (Table 1).
Fig. 5 in The dual impact of Ostreopsis cf. ovata on Mytilus galloprovincialis and Paracentrotus lividus: Toxin accumulation and pathological aspects Abstract
Fig. 5: Sea urchin health status (avg±SDV, n = 4) upon exposure to entire or sonicated Ostreopsis cf. ovata cultures (strain D483) of the same initial cell density.
Fig. 3 in The dual impact of Ostreopsis cf. ovata on Mytilus galloprovincialis and Paracentrotus lividus: Toxin accumulation and pathological aspects Abstract
Fig. 3: Feeding of Paracentrotus lividus (avg±SDV, n = 15) on Ostreopsis cf. ovata epiphytic on the red alga Asparagopsis taxiformis in five experiments lasting five days each. Experiment 4b was performed with the same animals as 4a, which were given a second stock of seaweeds after a two- day interval. Macroalgae (55-131 g) were completely eaten in all cases. Four additional experiments at low epiphytic cell density (<3.4·103 cells g-1) are not represented. Asterisks indicate the experiments in which sea urchins were weakly toxic at the mouse bioassay (Supplementary Material, Table S2).
Fig. 1 in The dual impact of Ostreopsis cf. ovata on Mytilus galloprovincialis and Paracentrotus lividus: Toxin accumulation and pathological aspects Abstract
Fig. 1: Feeding of Mytilus galloprovincialis in six 24 h experiments with animals of different sizes exposed to different Ostreopsis cf. ovata cell concentrations. A) Mussel wet weight (WW) and O. cf. ovata cell density at the beginning of each experiment (avg±SDV). B) Weight-normalised ingested cells (avg±SDV). The asterisks indicate experiments in which some or all replicates were toxic to the mouse bioassay (Supplementary Material, Table S1).
Рис. 2. Морфотипы Зрелых сперматоЗоидов (СЭМ) у Mytilus trossulus (A–G), Crenomytilus grayanus (H–L) и Mytilus coruscus (M–R): a – акросома; br – basal ring; n – Ядро; m – митохондриЯ; fl – Жгутик. Масштаб линейки – 1 мкм. in Study on sperm heteromorphism in some mussels (Bivalvia: Mytilidae) from the Sea of Japan
Рис. 2. Морфотипы Зрелых сперматоЗоидов (СЭМ) у Mytilus trossulus (A–G), Crenomytilus grayanus (H–L) и Mytilus coruscus (M–R): a – акросома; br – basal ring; n – Ядро; m – митохондриЯ; fl – Жгутик. Масштаб линейки – 1 мкм.
Рис. 2. Схема станΔартных промеров раковины Δвустворчатых моΛΛюсков по А. А. Зютину: L — ΔΛина раковины; H — тоΛщина раковины; D — ширина / выпукΛость Fig. 2. Scheme of bivalve mollusk shell standard measurements: L — shell length; H — shell thickness; D — width / convexity (according to A. A. Zyutin) in Morphometric characteristics of Black Sea mussels Mytilus galloprovincialis Lam. as biomarkers of the anthropogenic impact on the Black Sea coastal biocenoses in tourist destinations
Рис. 2. Схема станΔартных промеров раковины Δвустворчатых моΛΛюсков по А. А. Зютину: L — ΔΛина раковины; H — тоΛщина раковины; D — ширина / выпукΛость Fig. 2. Scheme of bivalve mollusk shell standard measurements: L — shell length; H — shell thickness; D — width / convexity (according to A. A. Zyutin)
Рис. 1. Схема распоΛожения станций отбора проб (сервис ЯнΔекс.Карты) Fig. 1. Location of the sampling stations (source: Yandex.Maps) in Morphometric characteristics of Black Sea mussels Mytilus galloprovincialis Lam. as biomarkers of the anthropogenic impact on the Black Sea coastal biocenoses in tourist destinations
Рис. 1. Схема распоΛожения станций отбора проб (сервис ЯнΔекс.Карты) Fig. 1. Location of the sampling stations (source: Yandex.Maps)
Рис. 3. Ливневый сток, прохоΔящий через территорию муниципаΛьного пΛяжа «Маяк» (фото авторов) Fig. 3. Stormwater runoff passing through the territory of "Mayak" municipal beach (photo by the authors) in Morphometric characteristics of Black Sea mussels Mytilus galloprovincialis Lam. as biomarkers of the anthropogenic impact on the Black Sea coastal biocenoses in tourist destinations
Рис. 3. Ливневый сток, прохоΔящий через территорию муниципаΛьного пΛяжа «Маяк» (фото авторов) Fig. 3. Stormwater runoff passing through the territory of "Mayak" municipal beach (photo by the authors)
FIG. 6 in Морфометрические особенности личинок мидии Mytilus galloprovincialis (Lamarck, 1819) (Bivalvia: Mytilidae) в онтогенеЗе
FIG. 6. Graphs of the correlations: (A) height (H, µm) vs. length (L, µm) of the larval shell, (B) hinge edge length (l, µm) vs. length of Mytilus galloprovincialis larval shells in ontogenesis
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