Reproductive Dynamics of the Blonde Ray (Raja brachyura) in Portuguese Waters: Timing, Maturity and Fecundity

Abstract

Within the Rajidae family, the blonde ray (Raja brachyura) is considered one of the less resilient species to fishing pressure and other anthropogenic pressures, primarily due to its late maturity and large maximum size, which can exceed 120 cm total length. This is the first study to provide comprehensive insights into the reproductive biology of Raja brachyura in the continental waters of Portugal, with insights into its timing, maturity, and fecundity. It was determined that egg-laying occurs from February to November, with a peak observed between April and September. Males were reproductively active throughout the year, with highest proportions of active males observed between January and May. The length at first maturity was estimated at 95.2 cm for females and 90.0 cm for males, corresponding to 85% of the maximum observed length in each sex. The potential fecundity was estimated at 115 follicles per female per year, and evidence suggests that the species has a determinate fecundity. The findings reinforce the appropriateness of current management measures in Portuguese continental waters, namely seasonal closure when overlapping with the peak of the reproductive season (May and June), and provide valuable scientific support for future conservation and management measures.

1. Introduction

Blonde ray (Raja brachyura Lafont, 1871) is a coastal benthic species of the Rajidae family with a wide distribution in the Northeast Atlantic, ranging from Norway to Morocco and the Mediterranean Sea [1,2,3]. It is commonly found in shallow sandy and sand-rocky bottoms, between 20 and 150 m deep [2,4,5].

As an elasmobranch species, and in contrast to most teleost fishes, R. brachyura has a K-strategist life-history pattern, characterized by a long life cycle, slow growth rate, late sexual maturity, low fecundity, extended incubation periods, and large offspring size. These life-history traits render the species vulnerable to fishing pressure [2,4,6,7]. Furthermore, the coastal distribution of R. brachyura increases its exposure to additional anthropogenic pressures, such as pollution, habitat loss, and the impacts of coastal development. This species is classified as “near-threatened” in the global assessment of the International Union for Conservation of Nature (IUCN), primarily due to its apparent rarity in the Mediterranean Sea and declining trends observed in research surveys in Northeast Atlantic waters [8].

In Portuguese continental waters, R. brachyura accounts for approximately 23% of the total landed weight of Rajidae species, which are mainly assigned to the polyvalent fleet (multispecies, multigear fisheries) mainly operating with trammel nets and gillnets [9]. Between 2019 and 2024, this fleet accounted for around 83% of species landings in weight [9,10].

The International Council for the Exploration of the Sea (ICES) provides advice for different stocks of R. brachyura in the Northeast Atlantic. The stock distributed in Portuguese continental waters, stock unit for ICES Division 9.a (west of Galicia, Portugal, and Gulf of Cadiz), has been considered a data-limited stock [11]. Currently, the assessment methodology applied to this stock follows the Maximum Sustainable Yield (MSY) approach, which involves the application of length-based indicators and estimated life-history parameters [10], in particular growth and maturity information. Given the general lack of biological data for R. brachyura in Portuguese continental waters, prioritizing updated information on the life cycle and ecology of this species is essential for effectively monitoring population responses to fishing pressure and other anthropogenic impacts.

While studies on the biology of R. brachyura have been conducted in other geographical areas and/or on different aspects of its life-history [2,3,6,12,13,14,15,16,17,18,19,20,21,22], information regarding its reproductive strategy and life-history parameters in Portuguese continental waters remains limited. In addition, it is known that latitudinal variation in biological parameters can occur in skates [23,24], which reinforces the need to estimate parameters at a regional level. The primary objective of this study is to provide detailed insights into the reproductive biology of R. brachyura, focusing on its seasonal reproductive activity patterns, length at first maturity, and fecundity.

2. Materials and Methods

2.1. Sampling

Specimens of R. brachyura were collected from (i) commercial landings from the Portuguese polyvalent fleet, particularly from two landing ports, Matosinhos (41°11′9.3156″ N, −8°41′52.7022″ W) and Peniche (39°21′22.0926″ N, −9°22′17.493″ W) (Figure 1), under the scope of the National Data Collection Program (PNAB, European Union Data Collection Regulation–Data Collection Framework, DCF) and (ii) bottom trawl research surveys carried out along the Portuguese continental shelf held by the Instituto Português do Mar e da Atmosfera (IPMA), also under PNAB/DCF.

The following measurements were registered for each sampled specimen: total length (L_T) measured to the nearest cm as the distance from the tip of the snout to the end of the tail, gutted body weight (W_B), gonad weight (W_G), and liver weight (W_L), all recorded to the nearest g. For females, additional measurements included oviducal gland width (OG_W), anterior uterus width (AU_W), and posterior uterus width (PU_W), measured in mm. Yolked follicles (here considered follicles with a yellowish color and diameter ≥4 mm) were counted, and their diameter was measured in mm. In males, clasper length (C_L) was measured in mm as the distance from the center of the cloaca to the posterior tip of the clasper.

Sex and maturity were assessed through visual inspection of reproductive organs, following the maturity scale proposed by the ICES Workshop on Sexual Maturity Staging of Elasmobranchs (WKMSEL2) for oviparous elasmobranchs [25] (

Table 1. Maturity scale adopted from WKMSEL2.

	Stage	Male	Female
Immature	1. Immature	Claspers: flexible, non-calcified, and shorter than pelvic fins. Testes: small and undeveloped (in skates, sometimes with visible lobules). Ducts: straight and thread-like.	Ovaries: small and whitish. Undistinguishable ovarian follicles. Oviducal gland: often not visible. In some species, a thickening of the uteri where the gland will develop may be visible. Uteri: thread-like and narrow.
	2. Developing	Claspers: flexible, partially calcified and usually as long as or longer than pelvic fins. Testes: developing (in skates, lobules clearly visible but not fully developed). Ducts: developing and beginning to coil.	Ovaries: follicles of different stages of development. Some small- and medium-sized yolked follicles may be present. Oviducal gland: distinguishable and developing. Uteri: enlarging.
Adults	3a. Capable to reproduce	Claspers: rigid, fully calcified, and longer than pelvic fins (in some sharks, they may only be as long as the pelvic fins). Testes: fully developed (in skates, with fully formed lobules). Ducts: tightly coiled and filled with sperm.	Ovaries: presence of large yolked follicles ready to be ovulated. Oviducal glands: fully developed. Uteri: fully developed.
	3b. Females: Egg-laying Males: Active	Claspers: similar to stage 3a, but with clasper glands dilated, sometimes swollen and reddish. Sperm may be present in clasper groove or glands. Testes: similar to stage 3a. Ducts: sperm observed inside (after a cut) or flowing out of the cloaca on pressure.	Uteri: presence of egg capsules.
	4a. Females: Post-laying	-	Ovaries: flaccid with few follicles of different sizes. Few large vitellogenic follicles enter atresia. POFs and atretic follicles may be visible. Oviducal glands: fully developed but may be reduced in size. Uteri: enlarged and flaccid.
	4b. Regenerating	-	Ovaries: large with small- and medium-sized yolked follicles. Pre-ovulatory follicles absent. Oviducal glands: fully developed but may be reduced in size. Uteri: enlarged.

). For analysis purposes, maturity stages were further classified into immature (immature and developing) and adult groups (capable to reproduce, egg-laying, post-laying, and regenerating individuals).

2.2. Data Analysis

2.2.1. Reproductive Season

The identification of a reproductive season was determined based on the monthly proportion of each maturity stage within adult male and female specimens. Male and female gonodosomatic (GSI) and hepatosomatic (HSI) indexes across the year, as well as female monthly variation in OG_W, were also analyzed. GSI, HSI, and OG_W analyses were conducted for females capable of reproducing and egg-laying together, as these are the individuals deemed capable of contributing to reproductive potential [26]. The GSI for each sampled specimen was determined as follows:

$${\displaystyle \frac{{\mathrm{W}}_{\mathrm{G}}}{{\mathrm{W}}_{\mathrm{B}}}}\times 100,$$

and HSI was determined as follows:

$${\displaystyle \frac{{\mathrm{W}}_{\mathrm{L}}}{{\mathrm{W}}_{\mathrm{B}}}}\times 100,$$

where W_B is the gutted body weight used in both GSI and HSI calculations to minimize variability associated with the weight of digestive and reproductive tracts. Box plots of the GSI and HSI indexes and OG_W were constructed by month for both males and females. Differences between months were assessed using an ANOVA model.

2.2.2. Length at First Maturity

Length at first maturity (L₅₀) for each sex, which corresponds to the length at which 50% of individuals are mature, was estimated by fitting a generalized linear model (GLM) [27] to the proportion of adult females and males by one-centimeter length intervals, considering data collected during the peak of the reproductive season. Females and males in stages 1 and 2 were considered immature, while those in stages capable of reproduction were considered mature. The model considered binomial error distribution and a logit link:

$$ln{\displaystyle \frac{p}{1-p}}=\alpha +\beta L_T+\epsilon ,$$

where $p$ is the proportion of adult fish at a given length-class interval; $\epsilon$ is the error term; and $\alpha$ and $\beta$ are parameters. The significance of the model was tested with an ANOVA. Percentiles $p$ of 25, 50, 75, and 95% of individuals who were mature in condition and size (L₂₅, L₅₀, L₇₅, and L₉₅) were estimated as follows:

$$L_{Tp}={\displaystyle \frac{ln\left(\frac{p}{1-p}\right)}{\beta }}-\alpha$$

2.2.3. Reproductive Organs Development

Morphological changes and development of reproductive organs were analyzed throughout the maturation process. The relationships between L_T and OG_W, AU_W, or PU_W for females, as well as between L_T and C_L for males by maturity stage, were assessed. The null hypothesis of no significant differences in reproductive organ measurements across maturity stages was tested using an ANOVA.

2.2.4. Ovarian Fecundity

Differences in the total number of yolked follicles (with diameters ranging from 4 to 34 mm) across different maturity stages were tested using a post hoc Tukey test. Fecundity was characterized and compared by maturity stage by plotting the frequency distribution of the follicle’s diameter.

The size and number of follicles retained in the ovary after the end of the spawning period (referred to as storage follicles and assumed not to contribute to the reproductive potential but instead continue to develop in the subsequent reproductive cycle) were determined based on the follicle diameter distribution of females at the post-laying stage. The maximum potential fecundity (FM) was estimated in two steps. First, a generalized linear model (GLM) was fit to the individual proportion of follicles larger than the storage follicle size ($\ge$14 mm) in females contributing to reproductive potential (capable to reproduce and egg-laying), considering the variable month [26]. The month in which the higher proportion was observed was set as the first month (i.e., as a reference for the model). The GLM was specified with a Gaussian error distribution and an identity link function, and is expressed as follows:

$$f{\displaystyle \frac{N_{largefollicles}}{N_{follicles}}}~{\alpha }_{month}+\epsilon ,$$

where $N_{largefollicles}$ is the individual number of follicles ≥14 mm and $N_{follicles}$ is the individual total number of follicles. Finally, FM was estimated as the product of the estimated maximum proportion of follicles and the observed maximum number of follicles.

Statistical analysis was carried out using R 4.4.0 [28], and the level of significance adopted for all the tests was α < 0.05.

3. Results

A total of 1064 R. brachyura specimens (604 females and 460 males) were sampled between 2003 and 2020. Total length ranged from 37 to 111 cm and 41 to 106 cm for females and males, respectively (Figure 2). Although some overlap in total lengths was observed between adjacent maturity stages, a clear increase in body size was evident from immature to reproduction stages, with a median asymptotic length reached around 100 cm in adults. Immature females ranged from 37 to 90 cm L_T (n = 159), developing females ranged from 46 to 102 cm L_T (n = 256), and adult females ranged (from capable to reproduce to regenerating stages) from 80 to 111 cm L_T (n = 189) (Figure 3a). Immature males ranged from 41 to 83 cm L_T (n = 99), developing males ranged from 46 to 99 cm T_L (n = 213), and adult males (capable to reproduce and being active) ranged from 74 to 106 cm L_T (n = 148) (Figure 3b).

3.1. Reproductive Season

The proportion of females capable to reproduce was highest from January to March, with a peak in March at 76%. Egg-laying females were observed from February to November, with the highest proportion occurring between April and September, when over 50% of the adult specimens were laying eggs (Figure 4a). In the remaining months, the percentage of egg-laying females was below 30%. Post-laying females were most common between August and November, while regenerating females showed higher proportions from November to January. Active males were observed year-round, with the highest proportions recorded between January and May, and again in October, when more than 60% of adult males were active (Figure 4b).

Median GSI values of capable to reproduce and egg-laying females peaked in May and gradually decreased until December. In January, GSI values began to gradually increase, reaching higher levels in April. Significant differences in GSI values were observed between months (ANOVA, F = 6.603, d.f. = 11, p < 0.05) (Figure 5a). In contrast, the median GSI values for males showed no significant variation throughout the year (ANOVA, F = 0.931, d.f. = 11, p > 0.05) (Figure 5b).

Median HSI values of capable to reproduce and egg-laying females combined showed a steady decline from January to June, when the lowest values were reached (mean around 4), before a marked increase from September to December (Figure 6a). HSI values differed significantly between months of the year (ANOVA, F = 10.46, d.f. = 11, p < 0.05). For males, median HSI values of capable to reproduce and active individuals were highest between October and March and were lowest from April to September, showing a significant monthly variation (ANOVA, F = 2.59, d.f. = 11, p < 0.05) (Figure 6b).

Median OG_W values for capable to reproduce and egg-laying females combined increased from January, attaining their highest values between April and August (Figure 7). After August, median values decreased until December. OGW values showed significant variation across months (ANOVA, F = 2.944, d.f. = 11, p < 0.05).

3.2. Length at First Maturity

The estimated L₅₀ for females was 95.2 ± 6.59 cm (ANOVA, F = 386.6, d.f. = 1, p < 0.01, R² = 0.817, n = 291) (Figure 8). The interquartile length at maturity (L₂₅–L₇₅) was estimated at 93.0–97.4 cm L_T, and L₉₅ was estimated at 101.3 cm L_T. The largest immature female measured 102 cm L_T, while the smallest and largest adult females measured 80 cm L_T and 111 cm L_T, respectively.

The estimated L₅₀ for males was 90.0 ± 8.49 cm (ANOVA, F = 156.6, d.f. = 1, p < 0.01, R² = 0.55, n = 217) (Figure 8). The interquartile length at maturity (L₂₅–L₇₅) was estimated at 85.9–94.0 cm L_T, and L₉₅ was estimated at 100.9 cm L_T. The largest immature male measured 99 cm L_T, while the smallest and largest mature males measured 76 cm L_T and 106 cm L_T, respectively.

For both females and males, the estimated L₅₀ corresponded to 85% of the maximum observed L_T.

3.3. Reproductive Organs Development

The reproductive structures showed a clear increase in size for both total body length and maturity stage, with the inflection point observed at the estimated L₅₀ (Figure 9). In females with L_T < 85 cm, the AU_W, PU_W, and OG_W grew slowly with increasing L_T, but accelerated as females approached maturity, particularly around 95.2 cm L_T (Figure 9a–d). In smaller males (<80 cm L_T), C_L increased gradually with L_T, before increasing at a faster rate as maturity was reached, around 90.0 cm L_T (Figure 9d). Statistically significant differences were observed across female maturity stages in AU_W (ANOVA, F = 272.7, d.f. = 2, p < 0.05), PU_W (ANOVA, F = 732.9, d.f. = 2, p < 0.05), and OG_W (ANOVA, F = 563.7, d.f. = 2, p < 0.05). Similarly, males exhibited statistically significant differences in C_L across maturity stages (ANOVA, F = 613.9, d.f. = 2, p < 0.05).

3.4. Ovarian Fecundity

The total number of follicles among females contributing to reproductive potential (i.e., capable to reproduce and egg-laying) and those in other stages showed significant differences (Tukey’s HSD, p < 0.05). Based on these results, two groups were defined: (1) developing, post-laying, and regenerating females, and (2) capable to reproduce and egg-laying females.

The follicle frequency distribution in developing (pre-laying), post-laying (immediately after egg-laying season) and regenerating (preparing for the next egg-laying season) females was dominated by follicles of 6 to 14 mm in diameter (Figure 10); therefore, a diameter of 14 mm was considered to represent a threshold that distinguishes these maturity stages from those contributing to the reproductive potential of the population during the egg-laying season. Post-laying females still presented a small number of follicles $\ge$34 mm entering atresia. Additionally, follicles <14 mm that were not released during the spawning season could be considered storage follicles, which will continue to develop in the subsequent reproductive cycle. The maximum number of storage follicles observed in regressing females was 36.

As no significant differences were found in the follicle distribution between capable to reproduce and egg-laying females, the analysis of fecundity was performed by combining observations from both maturity stages. The follicle size distribution in these females followed a similar overall pattern (Figure 11). However, when comparing the proportion of small (<14 mm) and large ($\ge$14 mm) follicles between the two maturity stages, significant differences were found (ANOVA: F = 22.14, d.f. = 1, p < 0.05). The mean proportion of small diameter classes was higher in capable to reproduce females, while the mean proportion of large diameter classes was higher in egg-laying females.

In females considered to be contributing to reproductive potential (females capable to reproduce and egg-laying), the number and the monthly variation in the proportion of follicles <14 mm and $\ge$14 mm in relation to the total number of follicles showed opposite patterns throughout the year (Figure 12). The proportion of follicles <14 mm was higher from August to March, while that for follicles $\ge$14 mm was higher in April and May, followed by a gradual decrease until September (Figure 12). In April, both follicle groups corresponded to around 50% of the follicles in the ovaries. Figure 13 illustrates these findings, showcasing the follicle distribution in three contexts: (1) a female at the beginning of the reproductive season (April, 100 cm L_T); (2) a female in the middle of the reproductive season (June, 105 cm L_T); and (3) a female nearing the end of the reproductive season (August, 103 cm L_T). Globally, the number of follicles <14 mm decreased throughout the reproductive season, reflecting their development and subsequent transition into the pool of follicles $\ge$14 mm, which are released during the actual egg-laying season.

April was set as the first month (i.e., as a reference for the model) for the GLM to estimate the maximum potential fecundity, since this was the month in which the maximum proportion of follicles $\ge$14 mm (0.94) was observed in a female. Results from the model indicate that the highest mean estimate of the proportion of follicles $\ge$14 mm corresponded to 0.76 ± 0.10, estimated for the month of May. Considering the maximum number of yolked follicles (152) observed in an egg-laying female (106 cm L_T) (in March, the month immediately preceding the egg-laying peak), this leads to an estimated maximum potential fecundity of 115 follicles per female per year (Akaike information criterion, AIC = −105.9, R²_adj = 0.65). The remaining proportion (0.24, 36 follicles) is assumed to correspond to storage follicles.

4. Discussion

The present study provides the first insight into the reproductive biology of Raja brachyura in Portuguese continental waters, highlighting key aspects of its reproductive timing, maturity, and fecundity. Although this species has a wide distribution across the Northeast Atlantic and Mediterranean Sea, such information was limited to the Irish Sea [17], British Isles [12,22], and parts of the Mediterranean Sea [3,20]. Given its high susceptibility to fisheries and to other anthropogenic pressures, understanding the reproductive biology of R. brachyura is crucial for assessing population status and developing effective management and conservation strategies, both in Portugal and across its distributional range.

Results suggest that, in Portugal, R. brachyura reproduces from February to November, exhibiting a prolonged but seasonal reproductive cycle, with a clear peak during spring and summer. The absence of egg-laying females in the winter months suggests the existence of a resting period, rather than continuous year-round reproduction. Within the reproductive season, not all adult females are reproductively active simultaneously, indicating individual-level asynchrony in the reproductive cycle at the population level.

The monthly variability in GSI, HSI, and OG_W further supports this hypothesis, indicating the coexistence of females at different reproductive stages and highlighting the existence of individual biological rhythms. Similar patterns have been observed for other Rajidae species inhabiting Portuguese continental waters, such as the thornback ray Raja clavata [29], cuckoo ray Leucoraja naevus [30], and undulate ray Raja undulata [27], for which long spawning periods with a peak were observed. It is important to note that sampling was opportunistic and carried on for a long period of time (2003–2020), which means that interannual variation was not considered. Despite some level of asynchrony in the reproductive timing at the population level, over 60% of the sampled adult females were egg-laying between April and September, indicating the existence of a reproductive peak (also supported by the monthly variation in the proportion of post-laying and regenerating females). Notably, the highest proportion of capable to reproduce females was observed in March, the month immediately preceding the egg-laying peak. Higher GSI values in May and their progressive decrease during the following months illustrate the release of follicles during the reproductive season. The HSI exhibited a temporal pattern that decreased from January to June, reflecting the conditioning of energy to produce gametes, vitellogenesis, and egg capsule formation [31]. Monthly variation in the OG_W also corroborated the existence of an egg-laying peak, with higher values being registered between April and August, when egg capsules were produced by a higher proportion of females. For R. brachyura, the existence of an egg-laying peak during the spring and summer months was also observed in other geographic areas, such as the Southwest of England [12] and in the Mediterranean Sea [3,20]. Holden et al. [13] suggested that temperature serves as a crucial environmental cue influencing reproductive timing and that warmer waters occurring during spring and summer seem to stimulate egg deposition. In the center of Portugal, in particular in the vicinity of Peniche landing port, where the great majority of our sampled specimens came from, average monthly water surface temperature during the study period started to increase in April, reaching the highest values in August when the average temperature was 18 °C, and progressively decreasing afterwards to less than 14 °C during autumn and winter months (EU Copernicus Marine Service information-https://marine.copernicus.eu, accessed on 20 January 2025).

The estimated L₅₀ for R. brachyura in Portuguese continental waters was 95.2 cm for females and 90.0 for males, which is higher than the estimates available for other geographic regions. In the Northeast Atlantic, first maturity was estimated at 83.6 for females and 81.9 cm for males in the Irish Sea [17] and as 83.4 for females and 78 cm for males in British waters [22]. In the Sardinian Seas, the L₅₀ was estimated at 87.2 and 80.8 cm for females and males, respectively [3]. In the present study, the largest immature female measured 102 cm, contrasting with previous studies, with reported lengths of around 92 cm [3,22]. These differences may arise from several factors, including environmental variations, influence of water temperature, species behavior, and different levels of fishing pressure. High levels of fishing exploitation can impact population densities and lead to changes in life-history traits, such as length at first maturity [32]. For example, increased growth rates and decreased length at first maturity due to rising fishing mortality have been reported for R. clavata in the central and northwestern North Sea [16]. Similar trends have been noted for other elasmobranch species, such as, for example, the lesser spotted dogfish Scyliorhinus canicula in the Mediterranean Sea [32] or the yellownose skate Dipturus chilensis in the southwestern Atlantic Ocean [33].

The analysis of the reproductive organs across maturity stages demonstrates quick development close to the length at first maturity (L₅₀), supporting the established profile of maturation processes in elasmobranchs [23,34,35]. Unlike most teleost species, elasmobranchs tend to mature late in their life cycle, reaching maturity at approximately 75 to 90% of their maximum L_T, which is characteristic of K-strategist species [34]. In Portuguese continental waters, R. brachyura reaches sexual maturity at approximately 85% of the maximum L_T sampled (111 and 106 cm for females and males, respectively), showing an extended immature phase and minimal growth post-maturity. The estimated L₅₀ for R. brachyura in Portuguese waters differed between sexes, which is consistent with findings from other geographic regions [3,6,22]. Such sexual dimorphism is common among elasmobranch species [34]. The larger size and age at maturity of female rajids likely relate to differing reproductive strategies between sexes [36]. For females, a larger size provides more abdominal space for carrying yolked follicles [3,29], while males’ faster growth rates enable them to reach sexual maturity sooner. These traits may optimize reproductive success in these species [2].

Holden et al. [13] observed, in captivity, the release of 90 eggs per female over a 77-day period. This is comparable to the results of the present study (115 follicles per female per year) when considering the full spawning season in Portuguese continental waters, which lasts approximately six months (about 180 days). In the Mediterranean Sea, Porcu et al. [3] reported an ovarian fecundity of 44 yolked follicles based on observations of 18 mature females. However, this estimate does not account for the continuous recruitment of small developing follicles into the ovulatory oocyte pool throughout the spawning season. In the present study, differences in follicle frequency distribution, particularly in small follicles, between females at the beginning and at the end of the spawning season illustrate this continuous follicular development throughout the reproductive cycle. The persistence/permanence of small developing follicles in females that reached the end of the reproductive season indicates that vitellogenesis is a continuous process occurring year-round once individuals reach maturity. Nevertheless, differences in biological parameters between the Northeast Atlantic and Mediterranean waters are not unexpected and have been reported for several elasmobranch species [37,38].

In females contributing to reproductive potential, the proportion of small follicles was higher in the first quarter of the year, immediately preceding the reproductive season. As the reproductive peak approached, these follicles underwent vitellogenesis, developing into larger yolked follicles ready for ovulation and fertilization. By the end of April, the proportion of large follicles peaked, followed by a gradual decline throughout the egg-laying season as egg capsules were released onto the sea floor. By the end of the reproductive season, the few large follicles that remained in the ovaries were likely to undergo atresia, while the remaining small follicles were retained, continuing to slowly develop, and contribute to the next egg-laying season. The observed decrease in small follicles along the egg-laying season, together with the absence of large follicles at its end, supports the hypothesis that R. brachyura exhibits determinate fecundity.

5. Conclusions

This study further supports the measures currently in place in Portuguese continental waters for the management and conservation of R. brachyura. In particular, a fishing closure period applied to all fisheries capturing Rajidae is implemented during May and June (Portaria nº 47/2016). This seasonal closure overlaps with the reproductive peak identified in this study, reinforcing its relevance as an important conservation measure aimed at protecting reproductive females. Additionally, a minimum landing size of 52 cm T_L was established in 2014 for all Rajidae species (Portaria no 170/2014), which was later updated to 60 cm TL (Portaria nº 255/2022). While this may provide some degree of protection to immature R. brachyura, our findings indicate that this management measure is not sufficient to protect adult individuals, since it is far lower than the estimated length at first maturity for both females and males. To support effective conservation and sustainable exploitation of R. brachyura, further studies on growth, habitat use, and species resilience are essential. These will enhance understanding of the species’ population dynamics, productivity, and susceptibility to environmental and human pressures, and inform the proposal of additional or refined protection measures as needed.