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Chamelea gallina reproductive biology and Minimum Conservation Reference Size: implications for fishery management in the Adriatic Sea



The striped venus clam Chamelea gallina is an economically important species in Adriatic Sea fisheries. The use of hydraulic dredging for its catch has a long history in Italy and its management faced several stages of development in the last 40 years. A great effort has been made in the past two decades to move from poorly or weakly managed fisheries to a well-structured co-management system to improve the sustainability of this fishery. However, a prerequisite for appropriate resource management is a sound knowledge of the biology and reproductive strategy of the species.


We investigated three major biological features– the gametogenic cycle, size at sexual maturity and partial fecundity – by microscopic, histological and video analysis techniques. We demonstrated that its breeding season is driven by rises in seawater temperature and chlorophyll-a concentration and that its spawning period lasted from March to September. Size at sexual maturity was reached very early in the life cycle. As regards partial fecundity – the number of mature oocytes potentially released by females with ripe gonads in a single release event – varied in relation to size. Nevertheless, the reduction on the Minimum Conservation Reference Size (MCRS) from 25 to 22 mm (Delegated Regulation (EU) 2020/2237) lead to a 40% reduction in the number of emitted eggs.


We suggest that the ability of Adriatic clam stocks to withstand the strong fishing pressure of the past 40 years and the present one is due to their high reproductive potential and multiple spawning events combined with the effect of management measures (closed areas/seasons, quota, MCRS) and technical constraints on the gear and the sieve on board. Moreover, since the reduced MCRS for Venus shells is still larger than the size at maturity, it will probably not be detrimental to the reproductive capacity of the stock.


The striped venus clam (Chamelea gallina Linnaeus, 1758) is an economically important species in the Mediterranean Sea, where it thrives at depths of 2–12 m [1, 2] in the coastal biocenosis of well-sorted fine sands described by Pérès and Picard [3], although it can even reach greater depths up to 20 m [4, 5]. In Italy, the fleet targeting C. gallina consists of 635 active hydraulic dredges, 601 of which are concentrated along the Adriatic coasts [6]. Hydraulic dredges harvesting C. gallina operate in a narrow strip between 0.3 and 2 nautical miles (NM) off the coast (depth range 3–15 m), and along 1400 km of the 8000 km of the Italian coastline. In the early 1970’s, the transition from hand-operated to hydraulic dredges resulted in an immediate and steep yield increase of up to 80,000–100,000 tons/year that was followed by a progressive decline due to overexploitation and poor management [7]. In the past two decades, considerable effort has been made to move to a well-structured co-management system, to improve the sustainability of this fishery [8]. In recent years, annual production has been around 19,000 tons (~ €51.4 million), accounting for 11% of fishery production in Italy in weight and for 6% in revenues [6]. However, the declining landings do not accurately reflect the status of the resource at sea, which is influenced by factors such as natural population fluctuations; the variable catch quota, which is set on the basis of market demand; and the wide range of restrictions that have been adopted over time to promote the sustainability and responsiveness of the fishery. The C. gallina fishery is managed through technical measures that:

  1. a)

    set dredge dimensions (maximum width, 3 m; maximum weight, 600 kg; Ministerial Decree 22/12/2000 [9]);

  2. b)

    regulate the fishing effort through closed areas (dredging is banned within 0.3 NM of the coast; Regulation (EC) 1967/2006 [10]);

  3. c)

    ban fishing activities in some periods (dredging is forbidden for 2 months between April and October [6]);

  4. d)

    limit the catch of juveniles through constraints on the technical features of the dredge and the mechanical sieve on board (Ministerial Decree 22/12/2000) [9];

  5. e)

    establish the Minimum Conservation Reference Size (MCRS), which is currently 22 mm (Delegated Regulation (EC) 2016/2376, Regulation (EC) 2020/3, and Delegated Regulation (EC) 2020/2237 [11,12,13]) by way of derogation from the previous 25 mm (Annex III to Regulation (EC) 1967/2006 [10]).

A prerequisite for appropriate resource management is a sound knowledge of its biology and reproductive strategy. The reproductive cycle of C. gallina in the Adriatic has been reported to span from March to September [14,15,16]. However, there is disagreement on its size at sexual maturity (TL50), which has been described to range from 11 to 18 mm [4, 17, 18]. A thorough knowledge of this parameter is crucial to evaluate the spawning fraction and fecundity of the population that has not been harvested, which contributes to its reproductive output [19].

Chamelea gallina reproduction has been the subject of several qualitative studies in the Adriatic Sea and elsewhere [20,21,22,23,24]. On the other hand, there is only one quantitative study investigating the potential number of emitted eggs per females in a single spawning event in relation to shell size [19]. The disproportion is due to the diffusion of gonad tissue in the visceral mass, which hampers the study of reproductive output and investment in all bivalves [25] except Pectinidae, whose gonad is a discrete organ. Quantitative reproduction data, like gonad biomass and fecundity, are critical to understand the life history of marine bivalves and to manage them successfully, i.e. to define the MCRS [26,27,28].

Various semi-quantitative and quantitative methods have been applied to estimate bivalve fecundity also in relation to their reproductive strategy and ovary structure, even though quantitative investigations are still much fewer than qualitative studies [29]. For example, the reproductive investment has been assessed in live specimens by inducing spawning through thermal shock or chemical injection, to count the number of eggs released [30,31,32] or by weighing them before and after spawning [33]. Dead specimens can be analysed indirectly by strip spawning [34, 35], volumetric reconstruction [36,37,38] and histological [39] and immunological methods [40]. However, all of them underestimate the reproductive output, since incomplete spawning is not infrequent and spawning events of different intensity may occur several times during the reproductive season [41]. This is the case of C. gallina, a multiple partial spawner with intraindividual asynchronous ovary development [42]. Bivalve fecundity is closely related to size and age [7, 38], although it can also be influenced by phylogeny and environmental conditions [25, 43,44,45].

Altogether, the information on the reproductive biology of C. gallina in the Adriatic Sea is dated and limited, which has the potential to undermine stock management and conservation efforts. The aim of this study is to provide new and updated information on the reproductive cycle of C. gallina: i) by investigating the gametogenic cycle using histological techniques and evaluating its relationships with temperature and chlorophyll-a (Chl-a); ii) by estimating TL50 by microscopic observation; and iii) by assessing partial fecundity (PF) by means of histological and image analysis approaches. Since in Italian territorial waters the MCRS has temporarily been reduced from 25 mm to 22 mm total length (TL) we also describe how the reduction affects clam fecundity. The study findings provide insights for fishery management, such as the MCRS and the time of the year when fishing should be closed.


Environmental parameters

The mean monthly BST and Chl-a values exhibited a seasonal trend (Fig. 1). BST was 16.6 ± 1.4 °C in November, dropping to 10.7 ± 0.5 °C until March with a minimum at 8.8 ± 1.1 °C in January. It gradually rose from January, and in June it approached the values recorded in November (16.4 ± 1.0 °C). From July to October, BST ranged from 20.6 ± 2.2 to 25.8 ± 1.5 °C, peaking in August. Chl-a fell steeply from 7.8 ± 4.3 mg/m3 in November to ~ 2.2 ± 0.8 mg/m3 in December–April, it increased in May–July with a peak in June (4.6 ± 1.9 mg/m3) and fell again from August to October (1.6 ± 0.4 mg/m3).

Fig. 1
figure 1

Mean monthly bottom seawater temperature and chlorophyll-a concentrations recorded between November 2018 and October 2019. Grey area: standard deviation


Altogether 213 females, 205 males and 64 indeterminate individuals were subjected to histological analysis. The progress of maturity stages over the months is reported in Fig. 2. During the 12-month sampling, the 64 indeterminate individuals were recorded only in November, December and October. At this stage sexes were not distinguishable, therefore the inactive stage is hereafter reported as F1/M1. The inactive stage was characterized by abundant connective tissue occupying the whole visceral mass without follicles/acini or gametes; only indeterminate cells were present and the sexes were indistinguishable (Figs. 3 and 4a).

Fig. 2
figure 2

Ridge plots showing the progress of maturity stages over the months in a females and b males. The curves illustrate the percentage of individuals in each maturity stage. The sum of the areas defined by the curves corresponds to the total monthly observations

Fig. 3
figure 3

Histomorphological maturity stages in C. gallina females: a inactive stage, M1/F1; b early active stage, F2; c late active stage, F3; d ripe stage, F4A; e partial emission stage, F4B; f regressing stage, F5. Abbreviations: ic: immature cells; Oo: oogonia; Pv: previtellogenic oocyte; Po: pedunculated oocyte; Vo: vitellogenic oocyte; L: lumen; ro: residual oocyte, mt: muscle tissue

Fig. 4
figure 4

Histomorphological maturity stages in C. gallina males: a inactive stage, M1/F1; b early active stage, M2; c late active stage, M3; d ripe stage, M4A; e partial emission stage, M4B; f regressing stage, M5. Abbreviations. ic: immature cells; Sg: spermatogonia, Sc: spermatocytes; St: spermatids; Sz: spermatozoa; pe: partial emission; te: total emission; L: lumen

In November gametogenesis had already resumed, as 56.5 and 76.7% of females and males were respectively in stage F2 and M2 (early gametogenesis). The gonads of F2 females showed fully developed follicles and oogonia (diameter, 5–6 μm) together with some small previtellogenic oocytes in early stage of development (diameter, 15–20 μm) around the follicle wall; only vesicular cells were seen in the lumen (Fig. 3b). This stage was predominant in November and December (~ 60%), whereas in January–March an almost equal proportion (~ 50%) of females were in stages F2 and F3. In April, 72% of females were in stage F3 (late active stage) and 28% were still in stage F2. Stage F3 oocytes were considerably larger and most were in the previtellogenic and pedunculated stages. Pedunculated oocytes protruded into the lumen of the follicle through their stalk, whereas a small number of vitellogenic oocytes were seen free in the lumen (Fig. 3c). In May, 95% of females had ripe gonads (F4A stage) with pedunculated and vitellogenic oocytes filling the lumen (Fig. 3d). In March, a small fraction of females (14%) were already in the ripe stage. Evidence of partial release (F4B, partially spawned stage) was detected since May (5%); this stage became more represented in June and July, when females with full or partially empty gonads were in almost equal proportion (~ 50%). The partially empty follicles indicated that a first release event had already occurred. In F4B females new and residual pedunculated and vitellogenic oocytes were detected in the lumen together with oocytes in an earlier stage of development attached to the wall, indicating the resumption of gametogenesis (Fig. 3e). In August, 67% of females had regressing gonads (stage F5) with residual oocytes in the collapsed lumen and connective tissue and indeterminate cells surrounding the gonad area (Fig. 3f). In September, we collected a single female (stage F5). In October, the gonads had completely regressed and females could no longer be identified, since all individuals were in the inactive stage (M1/F1).

In November, males were in the early gametogenesis stage (M2) with fully formed acini, spermatogonia surrounding the walls and vesicular cells filling the lumen (Fig. 4b). Between December and February, males were almost exclusively (94–100%) in late active gametogenesis (stage M3), with germ cells of decreasing size – spermatocytes and spermatids – arranged centripetally and projecting into the lumen (Fig. 4c). From March to July, most males (67–100%) had ripe gonads (stage M4A), with the lumen of the acini filled with spermatids and spermatozoa (Fig. 4d). Partial release events (stage M4B) spanned from June to September, peaking in August (84.5%). In M4B males, new spermatids and spermatozoa occupied a portion of the partially emptied acini, although cells in earlier development stages were also detected along the acinar walls (Fig. 4e). Gonad regression (stage M5) began in August, the majority of males in this stage being observed in September (73.9%); the acini were collapsed, with connective tissue and indeterminate cells beginning to surround the gonad area; residual spermatozoa were present except where a total release event had occurred (Fig. 4f). In October, a residual of 0.7% of males were still in regression, whereas all the other individuals (97.3%) had inactive gonads.

Size at sexual maturity

A total of 504 additional individuals (227 females, 243 males and 34 indeterminate), collected during the ad hoc sampling carried out in the middle of the reproductive season, were analyzed to assess TL50 in both sexes. The smallest females and males with well-developed gametes measured 9.6 mm and 9.9 mm TL, respectively; TL50 was ~ 11.0 for females and 11.5 mm for males, whereas the TL50 of the entire sample was ~ 11.2 mm (Fig. 5). Above 15 mm TL, all males and females were sexually mature.

Fig. 5
figure 5

Size at sexual maturity assessed in C. gallina a females, b males and c pooled sexes

Partial fecundity

The gonad volume ranged from 25.2 to 280 mm3 and was significantly and positively related to size (Gv = 17.2 × TL – 304.5; adj. R2 = 0.97; F1,24 = 772.5; p < 0.001). The percent Gv occupation by all types of oocytes was significantly different between maturity stages (ANOVA, F1,24 = 64.4; p < 0.001) and was 39.6 and 21.8% in stage 4A and stage 4B, respectively. Two-way ANOVA, testing for the effect of Maturity stage and Oocyte development stage on the percent Gv occupation, highlighted significant differences between the two parameters and their interaction. Although the interaction was statistically significant (Table 1), the Gv occupied by mature and immature oocytes (19.1 and 20.5%, respectively) in 4A females was not significantly different, whereas in 4B females immature oocytes occupied almost twice the volume compared with mature oocytes (14.0 and 7.8%, respectively; Table 1).

Table 1 Results of two-way Analysis of Variance (ANOVA) and the Tukey HSD test for the effects of Maturity stage (4A and 4B), Oocyte development stage (Mature / Immature), and the interactions of the two terms

The size frequency distribution of oocyte dmax between the two maturity stages showed that the mode was 53 mm in stage 4A and 41 mm in stage 4B (Fig. 6). In mature oocytes, the largest dmax values were 154.89 μm and 139.21 μm in stages 4A and 4B, respectively, and the smallest dmax values were 5.85 μm and 9.54 μm, respectively. The mean diameter of mature and immature oocytes was respectively 70.3 μm, 41.5 μm in stage 4A and 70.1 μm and 38.6 μm in stage 4B.

Fig. 6
figure 6

Size frequency distribution of maximum oocyte diameter in 4A and 4B females. The vertical line divides oocytes into those larger and smaller than 60 μm in maximum diameter

There was a strong positive and significant linear relationship between the number of any type of oocytes and TL, irrespective of maturity stage (Fig. 7). Two-way ANCOVA indicated that, while controlling for TL, there was a significant difference in the total number of oocytes between 4A and 4B females (ANCOVA, F1,47 = 121.638; p < 0.001). Similarly, there was a significant two-way interaction between Maturity stages and Oocyte development stages in the number of oocytes while controlling for TL (ANCOVA, F2,47 = 186.131; p < 0.001). A simple main effects test for Maturity stage and Oocyte development stage demonstrated that mature oocytes were more numerous in 4A than 4B females (F1,23 = 30.8; p < 0.001), whereas the difference between 4A and 4B females in terms of number of immature oocytes was not significant (F1,23 = 0.185; p < 0.671).

Fig. 7
figure 7

Scatterplots illustrating the relationship between oocyte number and total length. The log-scale emphasizes the differences between and within maturity stages (4A and 4B) in terms of oocyte maturity (mature / immature)

In 4A mature females size ranged from 19.2 to 29.9 mm TL with a PF from 3.6 × 104 to 3.7 × 105 oocytes/female depending on size (average, 1.6 × 105 oocytes/female). The linear regression analysis (PF = 3.01 × 104 TL − 5.21 × 105; adj. R2 = 0.85; F1,14 = 83.8; p < 0.001) suggested that 4A females can release ~ 1.4 × 105 (95% confidence interval, CI ± 2.3 × 104) oocytes/female at size 22 mm TL (present MCRS) and 2.3 × 105 (95% CI ± 2.7 × 104) oocytes/female at size 25 mm TL (ex-MCRS).


Reproductive biology

This study describes the year-round reproductive cycle of the commercially valuable species, C. gallina, in the western Adriatic Sea. The gonad development of C. gallina exhibits a cyclical annual pattern influenced by BST and Chl-a. In November, when we began sampling, gametogenic activity was already detectable and an important fraction of females and males were in the early active stage (F2/M2). In November, the high Chl-a concentration and the high BST, which was similar to the one recorded in June (~ 16 °C), when the clams were spawning, may have acted as a trigger. Indeed, temperature abnormalities (> 14–18 °C) have been suggested account for the advanced stage of maturity and reproduction seen in clams in autumn and winter [15, 46, 47]. In temperate climates the most common bivalve gametogenesis pattern is initiated by the seawater temperature reaching a certain threshold [48].

High energy stores in late autumn – related to the high Chl-a concentration detected in November – combined with high BST values, probably drive gonad development to the next stage (F3/M3). In December, Chl-a and BST both dropped; in January and February – the two coldest months, with BST under 10 °C – gonad maturation stopped. The percentage of females and males in the different stages of maturity remained almost unchanged. Our observations agree with studies indicating that clam growth [49] and gonad development [50] slow down when BST is less than 10 °C. In March, when BST exceeded 10 °C and Chl-a began to increase, gametogenic activity resumed and ripe gonads were first detected, especially in males. Most spawning events, highlighted by evidence of partial release and gonad recovery, occurred from May to August as both BST and Chl-a rose.

In August, when BST peaked, some clams began to show gonad regression (F5/M5). This stage was predominant in September and was followed by the inactive stage (F1/M1) in October. Similarly, a study of Ensis arcuatus in north-western Spain highlighted that the last spawning event before gonad regression was associated with an increase in surface temperature [51]. Several studies have demonstrated that water temperature and food availability significantly influence the reproductive cycle of C. gallina [19, 22, 24] and other bivalves [51,52,53]. This is especially true in temperate regions, where increasing temperature and food supply accelerate gonad development in numerous clam species [54,55,56]. Indeed, the striped venus clam shows an opportunistic reproductive strategy, since gonad development and sexual maturation are closely associated with nutrient accumulation, i.e. food availability [29, 57]. Whereas we detected two Chl-a peaks, one in early autumn and the other in late-spring/early-summer, in other temperate areas Chl-a peaks in late autumn [24] or in late summer and winter [19], despite similar seasonal seawater temperature patterns. However, bivalve reproductive activity is controlled not only by environmental factors, but also by their interaction with endogenous processes [53, 57, 58].

In recent years, the reproductive cycle of C. gallina has widely been investigated, especially along the Spanish, Portuguese and Turkish coasts, whereas the majority of studies in the Adriatic are fairly dated (Additional file 1). An extended spawning period has been described by most studies in all areas [14, 23, 24, 59], although a shorter period has also been reported [22, 47, 50]. In the Adriatic Sea, the reproductive cycle of C. gallina commonly spans from March to September, with some additional reproductive events in early autumn, whereas studies conducted at different temperate latitudes have described reproductive events only from late spring to late summer (Additional file 1). The reproductive plasticity of C. gallina can be explained by changes in local environmental and trophic conditions over time and by geographical location [46, 57]. In temperate areas eggs are released in favourable conditions for the development of planktotrophic larvae, when phytoplankton and Chl-a concentrations are abundant and when the water temperature ranges from 18 to 27 °C [15].

In the present study, evidence of partial gamete release and developing gametes in the same acinus/follicle in 4B individuals, heralded further spawning events as long as environmental conditions would be favourable for reproduction within the same reproductive season, otherwise gametes are reabsorbed at the end of it. These findings confirm that the striped venus clam is a multiple partial spawner [19,20,21, 42], even though single spawning events have been described by other authors [17, 24, 60]. In our study, all specimens were gonochoric, albeit cases of hermaphroditism have been reported [7, 21]. Gonad development was synchronous in females and males, as reported in several studies [24, 50, 59], a strategy that maximizes reproductive success. Another well-established feature of C. gallina is interindividual asynchrony, whereby specimens in different maturity stages coexist in the same period (Additional file 1). In contrast, intraindividual asynchrony – where different maturity stages coexist in the same individual – has rarely been described before the present study [19,20,21].

Both sexes of the striped venus clam reach sexual maturity at about 11.2 mm TL, in the first year of life; indeed, the first year specimens grow to about 15 mm TL [61]. Clams longer than 15 mm TL were all found sexually mature. Our findings are consistent with previous studies reporting a similar or even smaller size at sexual maturity [18, 46, 59, 62,63,64]. Yet, a TL50 of 9 to 18 mm is commonly described in the Adriatic Sea and elsewhere (Additional file 1). Such different values, reported even in the same area, may be attributed to the intrinsic reproductive variability of the species in relation to local environmental conditions such as seawater temperature, food availability and to anthropogenic, genetic and physiological factors [57], as well as to the different methods adopted to asses maturity.

Although the estimation of potential annual fecundity is critical to understand bivalve production and population dynamics, it is little explored [65]. Chamelea gallina is characterized by indeterminate fecundity, or better by a potential annual fecundity that is not known before the onset of spawning, since unyolked oocytes continue to mature and be spawned throughout the reproductive season [66]. Even though we were able to estimate the PF related to a single egg release event, in multiple partial spawning bivalves the number of spawning events occurring in the same reproductive season and the intensity of each reproductive peak are unknown [41], and are different in different years [67]. Only another study by Delgado et al. [19], conducted in the Gulf of Càdiz (south-western Spain), has assessed the fecundity of C. gallina. The results of the two investigations are quite similar; in particular, Delgado and co-workers analysed females in a size interval (20–30 mm TL) similar to ours, they found similar estimates of gonad volume (range, 37.25–205.95 mm3) and reported that the percent Gv occupied by all types of oocytes and by mature oocytes was respectively 37.71 and 18.38% in 4A females and 31.30 and 14.23% in 4B females. Nevertheless, their estimated PF (range, 7.6 × 104–7.9 × 105 oocytes/female) is higher than ours, despite a similar order of magnitude of oocyte number in relation to TL. The difference may lie in the method used to calculate PF: we only considered oocytes sectioned through the nucleus, which involves that the actual number of oocytes in the gonad may have been underestimated, whereas Delgado et al. [19] did not report it. Before egg release, the oocytes can reach a diameter of 110–120 μm [18], which is comparable with the dmax values we found in 4A and 4B mature oocytes. We found that fecundity is related to size, as noted by other authors [38, 44, 68], since in younger individuals growth is fast and the investment in reproduction limited, whereas in older bivalves energy is switched from growth to reproduction [44, 45].

A variety of studies have tried to estimate fecundity in various bivalve species, despite the problem of gonad tissue diffusion in the visceral mass. For example, in Spondilus calcifer the mean number of spawned oocytes per female has been estimated at 48.9 million [68], whereas the number of eggs per female has been put at 4.15 million in Ruditapes philippinarum [41] and at 1.65 million in Anadara antiquata [38]. The order of magnitude of the mean number of spawned eggs per female, reported in these studies, is up to two times higher than the one we calculated. However, egg number strongly depends on the species, its size range and the estimation method.

The reproductive strategy of C. gallina results in high fecundity. As near-sessile organisms, their lifecycle is strongly affected by environmental factors [36]. To ensure reproductive success, large amounts of gametes are released in the water column and, after fertilization, develop into planktotrophic larvae [15, 69]. However, as demonstrated by Beninger et al. [65] in Cerastoderma edule using Neutral Red vital staining, not all the oocytes released during a spawning event are viable, as dead/non-viable oocytes accounted for 34–85%. Moreover, oocytes age after spawning and 4–8 h after their release they can no longer be fertilized [70]: this involves that synchronization of gamete release in the environment is crucial for the reproductive success of the species [7]. Egg number is further reduced by predation by filter-feeding organisms in the water column. In addition, early offspring mortality is also substantial, due to oceanographic and ecological factors (e.g. food availability, current transport to unsuitable habitats, predation [71];) as well as to biological (e.g. reproductive strategy of the species, larval duration and larval behaviour [72];) and genetic factors [43].

Management implications

Italian clam fishery is the sole fishery where the number of vessels and operators has not declined in the past four decades [6]. The biological and management factors that allowed the clam fishing stocks to withstand the high fishing effort include:

  1. i)

    the high reproductive potential (clams of 22 mm TL produce 1.4 × 105 oocytes/female, a fairly high fecundity whose order of magnitude is shared with 25 mm clams) and the multiple spawning events occurring within the same reproductive season;

  2. ii)

    the early maturation, since all clams > 15 mm TL are sexually mature within the first year of life;

  3. iii)

    the closure of the area within 0.3 NM of the coast (Regulation (EC) 1967/2006 [10]) to dredging activity; this measure has halved the area previously suitable for clam harvesting and provides a large area (581.7 km2) where a huge amount of breeders contribute to the reproductive output of the population;

  4. iv)

    the daily quota (reduced to 400 kg/vessel from the previous 600 kg/vessel; Delegated Regulation (EC) 2016/2376 [12]) has strongly reduced the fishing effort, because the boats take less time to achieve the predetermined quota;

  5. v)

    the two-months fishing closure adopted in summer during the peak of reproduction;

  6. vi)

    the technical measures set for the fishing gear (for both the dredge and the sieve on board) reduce the catch of juveniles and the fraction below 22 mm TL almost to zero [73];

  7. vii)

    the setting of restocking areas, entered into force in 2017, where fishing is banned and where fishermen are required to discard undersized specimens harvested elsewhere (Delegated Regulation (EC) 2016/2376 [12]);

  8. viii)

    the high survival rate of C. gallina (higher than 95% [74]); the specimens returned to the sea can grow and contribute to the spawning fraction of the population;

  9. ix)

    the seeding and fishing area rotation applied by Management Consortia, the bodies responsible for fishery management, make the exploitation more sustainable and responsive.

The Scientific, Technical and Economic Committee for Fisheries (STECF), in the Joint Recommendation 20–01, reported that since the first implementation of the new MCRS in 2017 (Commission Delegated Regulation (EC) 2016/2376 [12]) an increase of abundance of > 22 mm individuals has been observed in the stock in certain areas of the Adriatic Sea. STECF also noted that the status of the stocks seems to have been stable or improving depending on the areas. Furthermore, it concluded that, since the reduced MCRS for Venus shells is still larger than the size at maturity (previously reported between 15 and 17 mm), it will probably not be detrimental to the reproductive capacity of the stock and is likely to have little effect on the exploitation rate on juveniles [75]. Therefore, our estimated TL50 at an even smaller size supports what stated by STECF.

Moreover, the EU Commission has considered that, based on information available in the Joint Recommendations and STECF assessments [75, 76], the derogation to the MCRS is in line with the objectives of the sustainable exploitation of the Venus shells stock in the Italian territorial waters. The lower MCRS also contributed to reduce the impact of the fishing activity on the marine ecosystem by allowing a significant decrease in fishing time and in the area being dredged as the quota is reached faster. On this basis, it appears that the proposed reduced MCRS would comply with the requirements established for technical measures in Article 15 and Article 18 of Regulation (EC), 2019/1241 [77].

However, there is necessity to:

  1. (i)

    collect accurate fishery data on fishing effort through the implementation of automatic monitoring system (GPS device) onboard each vessel; the boats’ movement control by the bodies in charge for the inspections (Coast Guard) would allow the coastal area within 0.3 NM of the coast to be preserved in an inexpensive way from illegal fishing activities, and therefore to safeguard a large fraction of the reproductive stocks;

  2. (ii)

    conduct at least two annual samplings. This would allow to constantly monitor the resource and to relate the biomass landed with those present at sea (exploitation rate). This index, calculated for each Consortium, would be essential to ensure rational and sustainable exploitation. When a threshold value is exceeded, effort management measures and targeted closures should be put in place [6]. Such close monitoring would make it possible to immediately verify any situations of overexploitation.

Populations of marine bivalves are subject to large interannual fluctuations as a result of their sensitivity to unfavourable environmental conditions [78]. Along the Italian Adriatic coasts, extensive dying-off phenomena for C. gallina took place several times in the last 30 years [6]. Although it is not always easy to identify the causes of these mass mortality events, they are generally caused by sudden changes in the coastal environment (e.g. hypo-anoxia, fresh water inputs, sea storms, pollution, sudden temperature and seabed grain size variations) and presence of pathogen agents [6]. Considering that the physical and chemical parameters of the seas are changing due to water acidification, global warming, sea level rise and decreased nutrient availability [79,80,81], the environmental perturbations are likely to frequently raise increasing the pressure on the species. For example, Huntley & Scarponi [82] found an association between sea level rise and increasing prevalence of digenean trematodes in C. gallina fossil records from a Holocene shallow marine succession in the Po coastal plain. Moreover, Delgado & Silva [83] noted that, where levels of prevalence of diagenetic-trematode-like parasite were higher they induced castration in the wedge clam (Donax trunculus) specimens. However, at present, the possible effects induced by climate change on the life-history traits of C. gallina are mainly unknown. For this reason, its main biological traits (e.g. growth, size at sexual maturity, reproductive potential) should be constantly monitored in relation to a changing environment, to guarantee the adoption of suitable management actions for a responsive fishery. Therefore, a careful periodic review of the adopted technical measures based on the biology of the species should be warrant for its protection over time.

Nevertheless, genetic studies [84] confirmed that, despite the fluctuations exhibited by the species in the last four decades, its high level of genetic diversity has not been negatively affected, conferring to this species a good adaptive potential to face the environmental perturbations.


In conclusion, this study provides some crucial biological information that can help adjust fishery management measures to clam biology. It also confirms that in the Adriatic Sea C. gallina reproduces in spring-summer, thus supporting the adoption of fishing closures in this period: closures ensure that the larger individuals contribute to reproduction and that the offspring attach to the substrate. Chamelea gallina reaches sexual maturity in the first year of life and partial fecundity is size-related. Even though the MCRS reduction to 22 mm TL affects partial fecundity (specimens measuring 25 mm TL produce 40% more oocytes per female), we suggest that the ability of Adriatic clam stocks to withstand the strong fishing pressure of the past 40 years and the present one is due to their high reproductive potential, multiple spawning events and high genetic variability combined with the effect of management measures (closed areas/seasons, quota, MCRS) and technical constraints on the gear and the sieve on board.


Sample and data collection

Clam samples were collected monthly, from November 2018 to October 2019, during commercial fishing operations conducted on sandy bottoms (depth, 5 to 12 m) in the Ancona Maritime District (central Adriatic Sea, Fig. 8). From 2 to 3 individuals per size class (width, 2 mm) were measured to the nearest 0.1 mm with a Vernier calliper along the anterior-posterior shell axis. The number of specimens each month analysed depended on the size classes available in the sample (maximum size range 18–36 mm TL, overall mean size (± Standard Deviation, SD) 25.4 ± 3.8 mm TL). Testing for differences in the gametogenic cycle in relation to shell size was not considered, however a gonad fragment from each specimen was placed in Dietrich solution [85] for subsequent histological analysis.

Fig. 8
figure 8

Map of the sampling area generated through the QGIS software version 3.20 “Odense” ( Dots indicate the sampling positions. The star marks the Tele–Senigallia research pylon, where the bottom seawater temperature data were recorded

Bottom seawater temperature (BST) data were obtained from the Tele–Senigallia pylon, a research tower located 1.3 NM off Senigallia, which is close to the sampling area and has been collecting oceanographic data since 1988 [86]. Temperature data were recorded every 10 min on a daily scale at 12.5 m depth. The daily Chl-a values were freely downloaded from the EU Copernicus Marine Service Information website [87] by tracing a polygon overlapping with the sampling area. Mean monthly values were than calculated for both parameters to observe how in parallel gonadal maturity stages changed over months.


The gametogenic cycle of females and males was investigated using a standard histological protocol. Gonads were dehydrated through increasing ethanol concentrations and embedded in paraplast. Serial 6-μm-thick transverse sections were cut with a microtome, mounted on slides, stained with Harris haematoxylin and eosin [88] and finally examined under a light microscope at 5–40 × magnification. Maturity stages were assigned according to the 6-stage scale proposed by Joaquim et al. (2014) for both sexes, with a slight modification of the last stage, as follows: F1/M1, inactive; F2/M2, early active; F3/M3, late active; F4A/M4A, ripe; F4B/M4B, partially spawned; and F5/M5 regressing (rather than “spent” as in the original scale). When multiple stages coexisted in an individual, the predominant stage was assigned.

Size at sexual maturity

TL50 was determined in specimens obtained from additional samples collected on alternate weeks in the central part of the reproductive season (May to August, 8 additional samples). From 3 to 4 individuals per size class (width, 1 mm) were measured and analysed and the total number of individuals per each sample always varied depending on the size classes available in the sample (maximum size range 4–36 mm TL, overall mean size 18.7 ± 9.5 mm TL). An ad hoc dichotomous maturity scale (1, not sexually mature; 2, sexually mature) was applied to classify specimens based on microscopic features. Gonad material was smeared on slides and examined under a light microscope linked to a video analysis system (Las Image Analysis, Leica). Females were classified as immature if only previtellogenic (immature) oocytes (dmax ≤ 60 μm) were detected, and as mature when vitellogenic (mature) oocytes (maximum diameter, dmax > 60 μm) began to develop. This threshold (≤ or > 60 μm) was set based on what described by Corni et al. [18, 21] in the Adriatic where C. gallina previtellogenic oocytes had a different shape (more irregular) and dimension (dmax ≤ 60 μm) compared to vitellogenic ones. Males were classified as mature/immature based on the presence/absence of spermatozoa with well elongated branched tails. Whenever not possible to assess the sex of small individuals they were classified as indeterminate and excluded from the calculation of TL50. TL50 was assessed in both sexes by fitting a logistic model to the proportion of mature specimens per size class:


where y is the relative frequency of mature individuals; x the size of individuals, exp. is the basis of the Neperian logarithms, a and b are the regression constant, using the R package sizeMat [89].

Partial fecundity

A total number of 26 females (20 in stage 4A and 6 in stage 4B) ranging from 19 to 33 mm TL, collected during the reproductive season, were examined to investigate the relationship of gonad volume (Gv) with TL, the number of oocytes contained in gonadal tissue and the percent Gv occupied by oocytes. PF was assessed in stage 4A females by histological and video analysis methods, to provide an estimate of the number of gametes released in a single release event in relation to TL. Histological analysis and image post-processing took at least 8 h per individual.

All specimens were measured and opened. All the organs (shell, mantle, siphons, gills) except the visceral mass and the foot were removed before storage in Dietrich solution for subsequent histological analysis. A procedure similar to the one described by Delgado et al. [19] was employed for Gv calculation. In brief, the entire visceral mass was cut into sections; a 6-μm-thick section every 100 μm was stained with Harris haematoxylin and eosin and viewed under a stereomicroscope connected to a video analysis system (Leica Application Suite V4.12) using reflected light at low magnification (0.76 ×). The area of the gonad (Ga) was measured in each section using Image J software, which allowed calculating Gv. In addition, 6 randomly chosen fields per gonad were digitized under a light microscope at 10 × magnification and used to assess the dmin (minimum diameter) and dmax of oocytes, which were sectioned through the nucleus. Oocyte volume was then calculated assuming cells to be spheroid (Ov = 4/3 × π × dmin × dmax2). The total oocyte number of each clam was estimated by standardizing the observations from each field to the entire gonad volume. PF was estimated by summing the number of mature oocytes in each 4A female. The relationship between PF and TL was explored by regression analysis.

Statistical analysis

The percent Gv occupied by all types of oocytes was used to test for statistical differences between maturity stages. The use of percentages allowed to control for differences in Gv between individuals. One-way analysis of variance (ANOVA) was applied to establish whether 4A and 4B females showed a significantly different mean percent Gv occupation. Two-way ANOVA was applied to investigate possible differences in mean percent Gv occupation between maturity stages and between oocyte development stages (mature and immature). Before result interpretation, the data were explored to check the assumption of normality, homoscedasticity and independence. All assumptions were met. After the tests, the Tukey HSD test was performed to explore differences among the levels of significant terms.

Analysis of covariance (ANCOVA) was used to test for statistical differences in oocyte number accounting for differences in TL between individuals. Analogously, a two-way experimental design was used to test for the effect of Maturity stage (2 levels: 4A and 4B) and Oocyte development stage (2 levels: mature and immature) controlling for the covariate, TL. Prior to statistical analysis, the data were explored to check the assumption of normality, homoscedasticity, independence, linearity of regression and homogeneity of slopes. Abundance and length data were log-transformed to meet the assumptions. Finally, a simple main effects test was conducted to explore the interaction between the levels of each term.

All statistical analyses and visualizations were produced in R (v 4.0.3; R Core Team [90]).

Availability of data and materials

The datasets generated during and/or analysed during the current study are available from the corresponding author on reasonable request.



Minimum Conservation Reference Size


Nautical miles


Total length

TL50 :

Size at sexual maturity


Bottom seawater temperature




Partial fecundity


Standard deviation

dmax :

Maximum diameter

Gv :

Gonad volume

Ga :

Gonad area

Ov :

Oocyte volume


European Commission


European Union


Honestly significant difference


Confidence interval


Scientific, Technical and Economic Committee for Fisheries

Repr. season:

Reproductive season

Repr. traits:

Reproductive traits


















Multiple partial spawner


Interindividual asynchrony


Intraindividual asynchrony


Histological analysis


Microscopic analysis


  1. Morello EB, Froglia C, Atkinson RJA, Moore PG. The effects of hydraulic dredging on the reburial of several molluscan species. Biol Mar Mediterr. 2006;13:610–3.

    Google Scholar 

  2. Lucchetti A, Sala A. Impact and performance of Mediterranean fishing gear by side-scan sonar technology. Can J Fish Aquat Sci. 2012;69:1806–16.

    Article  Google Scholar 

  3. Pérès JM, Picard J. New manual for benthic bionomics in the Mediterranean Sea. Trav la Stn Marittime Endoume. 1964;31:137.

    Google Scholar 

  4. Romanelli M, Cordisco CA, Giovanardi O. The long-term decline of the Chamelea gallina L.(Bivalvia: Veneridae) clam fishery in the Adriatic Sea: is a synthesis possible. Acta Adriat. 2009;50:171–205.

    Google Scholar 

  5. Wittmer JM, Dexter TA, Scarponi D, Amorosi A, Kowalewski M. Quantitative bathymetric models for late Quaternary transgressive-regressive cycles of the Po Plain, Italy. J Geol. 2014;122:649–70.

    Article  Google Scholar 

  6. DGPEMAC. The National Management Plan for fishing with hydraulic dredges and boat-operated shell-rakes as identified in the classification of fishing equipment use by mechanical dredges including mechanised dredges (HMD) and boat dredges (DRB). Public Law No. 9913 17/06/2019. Ministry for Agricultural, Food and Forestry Policies (MiPAAF). Rome, Italy; 2019.

  7. Carlucci R, Piccinetti C, Scardi M, Del Piero D, Mariani A. Evaluation of the effects on the clam resource in the light of a new minimum landing size and a better biological and commercial management of the product. Final Report: 76. 2015.

    Google Scholar 

  8. Lucchetti A, Piccinetti C, Meconi U, Frittelloni C, Marchesan M, Palladino S, et al. Transferable fishing concessions (TFC): a pilot study on the applicability in the Mediterranean Sea. Mar Policy. 2014;44:438–47.

    Article  Google Scholar 

  9. Italian Ministry. Ministerial Decree (DM) of 22 December 2000 Subject: Discipline for fishing for bivalve molluscs. Changes to the Ministerial Decree 21.7.98 being registered at the Central Budget Office. 2000:14.

  10. European Council. Council Regulation (EC) No 1967/2006 of 21 December 2006 concerning management measures for the sustainable exploitation of fishery resources in the Mediterranean Sea, amending Regulation (EEC) No 2847/93 and repealing Regulation (EC) No 1626/94. Official Journal of ther European Union, L 409/11. 2006:75.

  11. European Council. Commission Delegated Regulation (EU) 2020/2237 of 13 august 2020 amending Delegated Regulation (EU) 2020/3 as regards the derogation for the Minimum Conservation Reference Size of Venus shells (Venus spp.) in certain italian territorial waters. Off J Eur Union. 2020;L436/1:1–3.

    Google Scholar 

  12. European Council. Commission Delegated Regulation (EU) 2016/2376 of 13 October 2016 establishing a rejection plan for bivalve molluscs Venus spp. in Italian territorial waters. Official Journal of ther European Union, L 352/48. 2016:2.

  13. European Council. Commission Delegated Regulation (EU) 2020/3 of 28 August 2019 establishing a discard plan for Venus shells (Venus spp.) in certain Italian territorial waters. Official Journal of the European Union, L2/1. 2020:4.

  14. Valli G, Zecchini-Pinesich G. Considerations on biometrics and the reproduction of Chamelea gallina (L) (Mollusca, Bivalvia) from the Gulf of Trieste (Upper Adriatic). Nov Thalass. 1981;5:57–73.

    Google Scholar 

  15. Cordisco CA, Romanelli M, Trotta P. Annual distribution and description of the larval stages of Chamelea gallina and Mytilus galloprovincialis in the central-southern Adriatic. Assoc Ital di Oceanol e Limnol. 2003;16:93–103.

  16. Scopa M, Nerone E, Recchi S, Barile NB. Trends in the Chamelea gallina Production from Molise Region (Adriatic Sea, Italy): A Ten-Year Survey. Glob J Sci Front Res Agric Vet. 2014;14:18.

    Google Scholar 

  17. Poggiani L, Piccinetti C, Piccinetti MG. Observations on the biology of bivalve molluscs Venus gallina L. and Tapes aureus Gmelin in the northern Adriatic. Note del Lab di Biol Mar e Pesca. Fano. 1973;4:189–212.

    Google Scholar 

  18. Corni MG, Cattani O, Mancini L, Sansoni G. Aspects of the Venus gallina L. life cycle in relation to the protection of existing stocks. (In Italian). Pubbl a cura del Consorzio per Cent Univ di Stud e Ric sulle Risorse Biol Mar di Cesenatico. 1980:2–12.

  19. Delgado M, Silva L, Juárez A. Aspects of reproduction of striped venus Chamelea gallina in the Gulf of Cádiz (SW Spain): implications for fishery management. Fish Res. 2013;146:86–95.

    Article  Google Scholar 

  20. Marano G, Casavola N, Saracino C, Rizzi E. Reproduction and growth of Chamelea gallina (L.) and Venus verrucosa (L.) (Bivalvia: Veneridae) in the southern Adriatic. Mem Biol Mar Oceanogr. 1982;12:97–114.

    Google Scholar 

  21. Corni MG, Farneti M, Scarselli E. Histomorphological aspects of the gonads of Chamelea gallina (Linné) (Bivalvia: Veneridae) in autumn. J Shellfish Res. 1985;5:73–80.

    Google Scholar 

  22. Dalgiç G, Karayucel S, Okumua I. Reproduction cycle of striped venus Chamelea gallina from the Black Sea coast of Turkey. J Anim Vet Adv. 2009;8:2009–12.

    Google Scholar 

  23. Rodríguez De La Rúa A, Prado MA, Bruzón MA. Study of the reproductive cycle of Chamelea gallina (L., 1758) (Mollusca: Bivalvia) in three populations of the Andalusian coast. Bol Inst Esp Oceanogr. 2011;19:57–63.

    Google Scholar 

  24. Joaquim S, Matias D, Matias AM, Moura P, Roque C, Chícharo L, et al. Biochemical and energy dynamics throughout the reproductive cycle of the striped venus Chamelea gallina (Mollusca, Bivalvia). Invertebr Reprod Dev. 2014;58:284–93.

    Article  CAS  Google Scholar 

  25. Chavez-Villalba J, Barret J, Mingant C, Cochard J-C, Le Pennec M. Influence of timing of broodstock collection on conditioning, oocyte production, and larval rearing of the oyster, Crassostrea gigas (Thunberg), at six production sites in France. J Shellfish Res. 2003;22:465–74.

    Google Scholar 

  26. Braley RD. Reproductive periodicity in the indigenous oyster Saccostrea cucullata in Sasa Bay, Apra Harbor. Guam Mar Biol. 1982;69:165–73.

    Article  Google Scholar 

  27. Kautsky N. Quantitative studies on gonad cycle, fecundity, reproductive output and recruitment in a Baltic Mytilus edulis population. Mar Biol. 1982;68:143–60.

    Article  Google Scholar 

  28. Thompson RJ, Newell RIE, Kennedy VS, Mann R. Reproductive processes and early development. East oyster Crassostrea virginica. 1996:335–370.

  29. Llodra ER. Fecundity and life-history strategies in marine invertebrates. Adv Mar Biol. 2002;43:87–170.

  30. Hamel J-F, Conand C, Pawson DL, Mercier A. The sea cucumber Holothuria scabra (Holothuroidea: Echinodermata): Its biology and exploitation as beche-de-mer. Adv Mar Biol. 2001;41:131–226.

    Google Scholar 

  31. Utting SD, Millican PF. Techniques for the hatchery conditioning of bivalve broodstocks and the subsequent effect on egg quality and larval viability. Aquaculture. 1997;155:45–54.

    Article  Google Scholar 

  32. Fong PP, Deguchi R, Kyozuka K. Serotonergic ligands induce spawning but not oocyte maturation in the bivalve Mactra chinensis from central Japan. Biol Bull. 1996;191:27–32.

    Article  CAS  PubMed  Google Scholar 

  33. Pouvreau S, Gangnery A, Tiapari J, Lagarde F, Garnier M, Bodoy A. Gametogenic cycle and reproductive effort of the tropical blacklip pearl oyster, Pinctada margaritifera (Bivalvia: Pteriidae), cultivated in Takapoto atoll (French Polynesia). Aquat Living Resour. 2000;13:37–48.

    Article  Google Scholar 

  34. Hendriks IE, Van Duren LA, Herman PMJ. Image analysis techniques: A tool for the identification of bivalve larvae? J Sea Res. 2005;54:151–62.

    Article  Google Scholar 

  35. Hendriks IE, van Duren LA, Herman PMJ. Effect of dietary polyunsaturated fatty acids on reproductive output and larval growth of bivalves. J Exp Mar Biol Ecol. 2003;296:199–213.

    Article  CAS  Google Scholar 

  36. Galinou-Mitsoudi S, Sinis AI. Reproductive cycle and fecundity of the date mussel Lithophaga lithophaga (Bivalvia: Mytilidae). J Molluscan Stud. 1994;60:371–85.

    Article  Google Scholar 

  37. Moles KR, Layzer JB. Reproductive ecology of Actinonaias ligamentina (Bivalvia: Unionidae) in a regulated river. J North Am Benthol Soc. 2008;27:212–22.

    Article  Google Scholar 

  38. Mzighani S. Fecundity and population structure of cockles, Anadara antiquata L. 1758 (Bivalvia: Arcidae) from a sandy/muddy beach near Dar es Salaam, Tanzania. West Indian Ocean J Mar Sci. 2005;4:77–84.

    Google Scholar 

  39. Joaquim S, Matias D, Matias AM, Moura P, Arnold WS, Chícharo L, et al. Reproductive activity and biochemical composition of the pullet carpet shell Venerupis senegalensis (Gmelin, 1791)(Mollusca: Bivalvia) from Ria de Aveiro (northwestern coast of Portugal). Sci. 2011;75:217–26.

    CAS  Google Scholar 

  40. Kang S-G, Choi K-S, Bulgakov AA, Kim Y, Kim S-Y. Enzyme-linked immunosorbent assay (ELISA) used in quantification of reproductive output in the pacific oyster, Crassostrea gigas, in Korea. J Exp Mar Biol Ecol. 2003;282:1–21.

    Article  Google Scholar 

  41. Park K-I, Choi K-S. Application of enzyme-linked immunosorbent assay for studying of reproduction in the Manila clam Ruditapes philippinarum (Mollusca: Bivalvia): I. Quantifying eggs. Aquaculture. 2004;241:667–87.

    Google Scholar 

  42. Erkan M. Ultrastructure of ovary and oogenesis in Chamelea gallina (Linné, 1758) (Bivalvia, Veneridae). Invertebr Reprod Dev. 2009;53:201–9.

    Article  Google Scholar 

  43. Plough LV, Shin G, Hedgecock D. Genetic inviability is a major driver of type III survivorship in experimental families of a highly fecund marine bivalve. Mol Ecol. 2016;25:895–910.

    Article  CAS  PubMed  Google Scholar 

  44. Johnson KD, Smee DL. Size matters for risk assessment and resource allocation in bivalves. Mar Ecol Prog Ser. 2012;462:103–10.

    Article  Google Scholar 

  45. Honkoop PJC, Van der Meer J, Beukema JJ, Kwast D. Does temperature-influenced egg production predict the recruitment in the bivalve Macoma balthica? Mar Ecol Prog Ser. 1998;164:229–35.

    Article  Google Scholar 

  46. Cordisco CA, Trotta PMR. Reproductive plasticity of the common clam Chamelea gallina (Linnaeus, 1758). Biol Mar Mediterr. 2005;12:385–8.

    Google Scholar 

  47. Rizzo G, Cernigai F, Marceta T, Bressan M, Marin MG. Physiological and reproductive features in Chamelea gallina as a contribution to stock management in the northern Adriatic Sea. Biol Mar Mediterr. 2011;18:324.

    Google Scholar 

  48. Dang C, De Montaudouin X, Gam M, Paroissin C, Bru N, Caill-Milly N. The Manila clam population in Arcachon Bay (SW France): can it be kept sustainable? J Sea Res. 2010;63:108–18.

    Article  Google Scholar 

  49. Froglia C. Observations on the growth of Chamelea gallina (L.) and Ensis minor (Chenu) in the middle Adriatic. Quad di Lab di Tecnol della Pesca. 1975;2:37–48.

    Google Scholar 

  50. Salvatorelli G. Observations on the annual reproductive cycle of Venus gallina (Lamellibranch Molluscs). Ann dell’Università di Ferrara (Nuova Ser Sez XIII). Anat Comp. 1967;2:15–22.

    Google Scholar 

  51. Darriba S, San Juan F, Guerra A. Reproductive cycle of the razor clam Ensis arcuatus (Jeffreys, 1865) in northwest Spain and its relation to environmental conditions. J Exp Mar Biol Ecol. 2004;311:101–15.

    Article  Google Scholar 

  52. Dridi S, Romdhane MS, Elcafsi M. Seasonal variation in weight and biochemical composition of the Pacific oyster, Crassostrea gigas in relation to the gametogenic cycle and environmental conditions of the Bizert lagoon, Tunisia. Aquaculture. 2007;263:238–48.

    Article  CAS  Google Scholar 

  53. Enríquez-Díaz M, Pouvreau S, Chávez-Villalba J, Le Pennec M. Gametogenesis, reproductive investment, and spawning behavior of the Pacific giant oyster Crassostrea gigas: evidence of an environment-dependent strategy. Aquac Int. 2009;17:491–506.

    Article  Google Scholar 

  54. Ojea J, Pazos AJ, Martınez D, Novoa S, Sanchez JL, Abad M. Seasonal variation in weight and biochemical composition of the tissues of Ruditapes decussatus in relation to the gametogenic cycle. Aquaculture. 2004;238:451–68.

    Article  CAS  Google Scholar 

  55. Yan H, Li Q, Yu R, Kong L. Seasonal variations in biochemical composition and reproductive activity of Venus Clam Cyclina sinensis (Gmelin) from the yellow River Delta in Northern China in Relation to Environmental Factors. J Shellfish Res. 2010;29:91–9.

    Article  Google Scholar 

  56. Yan H, Li Q, Liu W, Yu R, Kong L. Seasonal changes in reproductive activity and biochemical composition of the razor clam Sinonovacula constricta (Lamarck 1818). Mar Biol Res. 2010;6:78–88.

    Article  Google Scholar 

  57. Da Costa F, Aranda-Burgos JA, Cerviño-Otero A, Fernandez-Pardo A, Louzán A, Nóvoa S, et al. Clam reproduction. In: Clam Fisheries and Aquaculture. New York: Nova Science Publisher; 2013. p. 45–71.

  58. Normand J, Le Pennec M, Boudry P. Comparative histological study of gametogenesis in diploid and triploid Pacific oysters (Crassostrea gigas) reared in an estuarine farming site in France during the 2003 heatwave. Aquaculture. 2008;282:124–9.

    Article  Google Scholar 

  59. Bratoš Cetinić A, Gavrilović A, Dupčić Radić I, Pećarević M, Tomšić S, Marčelja E, et al. Reproductive characteristics of baby clam Chamelea gallina Linnaeus, 1758 (Bivalvia, Mollusca) from the river Neretva estuary. Proceedings 42nd Croatian and 2nd International symposium on agriculture: Opatija (Croatia), February 13-16, 2007. In: Zbornik sažetaka. Opatija, Croatia; 2007. p. 192–3.

  60. Gaspar MB, Monteiro CC. Reproductive Cycles of the razor clam Ensis Siliqua and the clam Venus Striatula off Vilamoura, Southern Portugal. J Mar Biol Assoc United Kingdom. 1998;78:1247–58.

    Article  Google Scholar 

  61. Bargione G, Vasapollo C, Donato F, Virgili M, Petetta A, Lucchetti A. Age and Growth of Striped Venus Clam Chamelea gallina (Linnaeus, 1758) in the Mid-Western Adriatic Sea: A Comparison of Three Laboratory Techniques. Front Mar Sci. 2020;7:807.

    Article  Google Scholar 

  62. Giansante C, Angelini L, Angioni SA, Biase P, Di Giacomandrea A, Gatti G, et al. Management and protection of the natural banks of Chamelea gallina. Abruzzo Region: (Adriatic clam) in the Pescara Maritime Department; 2006. p. 181.

  63. Delgado M, Pérez CA. A study of gonadal development in Ruditapes decussatus (L.)(Mollusca, Bivalvia), using image analysis techniques: influence of food ration and energy balance. J Shellfish Res. 2003;22:435–42.

    Google Scholar 

  64. Silva L, Juárez A. Study on the striped venus clam (Chamelea gallina) fishing with hydraulic dredgers and towed rakes in the fishing ground of the Gulf of Cádiz; 2009.

    Google Scholar 

  65. Beninger PG, Chérel D, Kessler L. Examining bivalve fecundity: oocyte viability revealed by Neutral Red vital staining. Aquac Int. 2021;29:1219–31.

  66. Murua H, Kraus G, Saborido-Rey F, Witthames P, Thorsen A, Junquera S. Procedures to estimate fecundity of marine fish species from field samples in relation to reproductive strategy. J Northwest Atl Fish Sci. 2003;33:33–54.

    Article  Google Scholar 

  67. Morvan C, Ansell AD. Stereological methods applied to reproductive cycle of Tapes rhomboides. Mar Biol. 1988;97:355–64.

    Article  Google Scholar 

  68. Soria G, Tordecillas-Guillen J, Cudney-Bueno R, Shaw W. Spawning induction, fecundity estimation, and larval culture of Spondylus calcifer (Carpenter, 1857)(Bivalvia: Spondylidae). J Shellfish Res. 2010;29:143–9.

    Article  Google Scholar 

  69. Krug PJ. Poecilogony in an estuarine opisthobranch: planktotrophy, lecithotrophy, and mixed clutches in a population of the ascoglossan Alderia modesta. Mar Biol. 1998;132:483–94.

    Article  Google Scholar 

  70. André C, Lindegarth M. Fertilization efficiency and gamete viability of a sessile, free-spawning bivalve, Cerastoderma edule. Ophelia. 1995;43:215–27.

    Article  Google Scholar 

  71. Cushing DH. Plankton production and year-class strength in fish populations: an update of the match/mismatch hypothesis. Adv Mar Biol. 1990;26:249–93.

    Google Scholar 

  72. Cowen RK, Paris CB, Srinivasan A. Scaling of connectivity in marine populations. Science (80-). 2006;311:522–7.

    Article  CAS  Google Scholar 

  73. Sala A, Brčić J, Herrmann B, Lucchetti A, Virgili M. Assessment of size selectivity in hydraulic clam dredge fisheries. Can J Fish Aquat Sci. 2017;74.

  74. Bargione G, Petetta A, Vasapollo C, Virgili M, Lucchetti A. Reburial potential and survivability of the striped venus clam (Chamelea gallina) in hydraulic dredge fisheries. Sci Rep. 2021;11:1–9.

    Article  Google Scholar 

  75. STECF. Scientific, Technical and Economic Committee for Fisheries – 63rd Plenary Report – Written Procedure (Plen-20-01). Luxembourg; 2020.

    Google Scholar 

  76. STECF. Scientific, Technical and Economic Committee for Fisheries (STECF) - Multiannual Plan for the fisheries exploiting demersal stocks in the Adriatic Sea (STECF-19-02). Luxembourg; 2019.

    Google Scholar 

  77. European Council. Regulation (EU) 2019/1241 of the European Parliament and of the Council of 20 June 2019 on the conservation of fisheries resources and the protection of marine ecosystems through technical measures, amending Council Regulations (EC) No 1967/2006, (EC) No. 2019:97.

  78. Rufino MM, Vasconcelos P, Pereira F, Moura P, Gaspar MB. Bivalve sanctuaries to enhance stocks along the Algarve coast of southern Portugal: A spatio-temporal approach. Aquat Conserv Mar Freshwat Ecosyst. 2018;28:1271–82.

    Article  Google Scholar 

  79. Doney SC. The dangers of ocean acidification. Sci Am. 2006;294:58–65.

    Article  PubMed  Google Scholar 

  80. Belkin IM. Rapid warming of large marine ecosystems. Prog Oceanogr. 2009;81:207–13.

    Article  Google Scholar 

  81. Wohlers J, Engel A, Zöllner E, Breithaupt P, Jürgens K, Hoppe H-G, et al. Changes in biogenic carbon flow in response to sea surface warming. Proc Natl Acad Sci. 2009;106:7067–72.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  82. Huntley JW, Scarponi D. Parasitism and host behavior in the context of a changing environment: The Holocene record of the commercially important bivalve Chamelea gallina, northern Italy. PLoS One. 2021;16:e0247790.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  83. Delgado M, Silva L. Timing variations and effects of size on the reproductive output of the wedge clam Donax trunculus (L. 1758) in the littoral of Huelva (SW Spain). J Mar Biol Assoc United Kingdom. 2018;98:341–50.

    Article  Google Scholar 

  84. Carducci F, Biscotti MA, Trucchi E, Giuliani ME, Gorbi S, Coluccelli A, et al. Omics approaches for conservation biology research on the bivalve Chamelea gallina. Sci Rep. 2020;10:1–15.

    Article  Google Scholar 

  85. Gray P. The microtomist’s formulary and guide. New York: The Blakiston Company. Inc.; 1954.

    Book  Google Scholar 

  86. Ravaioli M, Bergami C, Riminucci F, Langone L, Cardin V, Di Sarra A, et al. The RITMARE Italian Fixed-Point Observatory Network (IFON) for marine environmental monitoring: A case study. J Oper Oceanogr. 2016;9:202–14.

    Google Scholar 

  87. E.U. Copernicus Marine Service Information. Accessed 1 Jun 2021.

  88. Pearse AGE. Analytical Tehnology. Histochem Theor Appl vol 2 Churchill Livingstone. 1985;2:726.

  89. Torrejon-Magallanes J. sizeMat: an R package to estimate size at sexual maturity. CRAN R-Project; 2019.

    Google Scholar 

  90. R Core Team. R: A language and environment for statistical computing: R Foundation for Statistical Computing. Vienna, Austria; 2020.

    Google Scholar 

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The research leading to these results has been conceived under the International PhD Program “Innovative Technologies and Sustainable Use of Mediterranean Sea Fishery and Biological Resources” ( This study represents partial fulfilment of the requirements for the PhD thesis of G. B.1. The authors are grateful to Word Designs for the language revision.


The study was made on the agreement signed between Italian Ministry for Agricultural, Food and Forestry Policies (MiPAAF) and CNR IRBIM (Ancona) as part of the study preparatory to the drafting of management plans for bivalve molluscs fisheries. The activities were financially supported by the MiPAAF.

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G.B.1 wrote the manuscript with contributions (in order of importance) from G.B.2, M.V. and A.L.. G.B.1 and F.D. conducted the laboratory activities. G.B.2 and P.P. performed the statistical analysis. A.L. was the Scientific Responsible of the study. The author(s) read and approved the final manuscript.

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Correspondence to Giada Bargione.

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Supplementary Information

Additional file 1: Suppl. Mat 1.

Summarizes the reproductive traits of Chamelea gallina described in the present study and by other authors in different geographical areas.

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Bargione, G., Donato, F., Barone, G. et al. Chamelea gallina reproductive biology and Minimum Conservation Reference Size: implications for fishery management in the Adriatic Sea. BMC Zool 6, 32 (2021).

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