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Article

Every Fish Counts: Challenging Length–Weight Relationship Bias in Discards

by
Carlos Rodríguez-García
1,2,*,
Jairo Castro-Gutiérrez
1,3,
Ángel Rafael Domínguez-Bustos
1,
Alberto García-González
1 and
Remedios Cabrera-Castro
1,2
1
Departamento de Biología, Facultad de Ciencias del Mar y Ambientales, Campus Río San Pedro, Universidad de Cádiz, 11510 Puerto Real, Spain
2
Instituto Universitario de Investigación Marina (INMAR), Campus de Excelencia Internacional del Mar (CEIMAR), 11510 Puerto Real, Spain
3
Departamento de Ciencias Agroforestales, Escuela Técnica Superior de Ingeniería, Campus El Carmen, Universidad de Huelva, 21007 Huelva, Spain
*
Author to whom correspondence should be addressed.
Fishes 2023, 8(5), 222; https://doi.org/10.3390/fishes8050222
Submission received: 30 March 2023 / Revised: 19 April 2023 / Accepted: 23 April 2023 / Published: 24 April 2023
(This article belongs to the Section Biology and Ecology)
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Abstract

:
Bycatch is a significant issue in global fisheries and understanding the length–weight relationships (LWR) of fish species can provide valuable insights for stock assessment and management efforts. In this study, we estimated the LWR of 74 fish species in trawl fleet discards from the Gulf of Cadiz, including 24 species for which LWR data had not been previously reported in this region. LWR was calculated from the formula W = aLb where parameter a is the intercept of the equation, related to body shape, and parameter b is the slope, which indicates the type of growth of the species. A total of 20,007 individuals from 40 families were measured and weighed. The most abundant species were Engraulis encrasicolus, Trachurus trachurus, Serranus hepatus, Sardina pilchardus, Capros aper, and Diplodus bellottii, and the Sparidae family was the most represented with ten species. The parameter b, which represents the type of growth, ranged from 2.1607 to 3.7040. A positive allometric growth trend was observed in 64% of the species. The inclusion of individuals with a low sample size proved useful, particularly for first reports in a new study area. However, caution should be taken when using these data, as the estimates of the length–weight relationship for these species may be less precise. Further studies with larger sample sizes are needed to confirm the results and improve the accuracy of the estimates. Overall, our findings contribute to the understanding of the LWR of fish species in the Gulf of Cadiz, informing future research and management efforts in the region.
Keywords:
fisheries; body length; fish biometrics; growth; professional fleet; measurements
Key Contribution: This work has reported for the first time in the Gulf of Cadiz, the length–weight relationships of 24 species including the length–weight relationship of the non-native species Cynoscion nebulosus. After analysis of the low sample size data, the bias from these data can be assumed for a first comparison of length–weight relationships, concluding that species from discards are useful in length–weight relationships studies.

1. Introduction

Bycatches are one of the main current global problems for fisheries [1,2]. Discards are specimens of both species with little or no commercial interest and commercial species that cannot be marketed due to deterioration or not meeting the legal size, which are returned, alive or dead, to the sea and are not counted among the catch [3,4]. Discarding is a particularly common practice in trawl fisheries [3,5,6]. These discards produce a series of ecological and economic consequences, such as endangering the sustainability of marine organism populations or wasting large amounts of natural resources [1,3,4,6,7].
Discards in fisheries may be biased by the way in which catches are selected. Bias can occur when the data used to fit the model do not adequately represent the underlying population. This can occur when non-target species are selectively discarded because of their size, age, or shape, which can lead to underestimates of the amount of unwanted catch, affecting the precision of estimates and having implications for fisheries management [8]. In addition, it is important to keep in mind that results obtained from a biased model may not be generalizable to other populations or contexts [9].
Knowing length–weight relationships (LWR) is important because it allows for numerical estimates of fish condition, comparisons between living conditions in different regions for the same species, biomass calculations from length data, or transformations of length growth equations to weight growth, all of which have different applications in stock assessment and management models [10,11,12,13,14,15,16,17,18,19,20,21]. LWR can also be used to estimate the amount of discard of a given species through its size distribution [22,23].
Understanding the LWR of fish species is essential for sustainable fisheries management and conservation, as it enables the estimation of fish species distribution, their condition, and morphological comparison [17,24]. Incorporating LWR in fisheries management can help address discard issues and improve sustainability:
(1)
Informing the development of size-based regulations: length–weight relationships can be used to determine the size at which a fish species reaches maturity [17]. This information can inform the establishment of minimum landing sizes, helping to protect juveniles and ensuring that fish can reproduce before being harvested [25].
(2)
Assessing the impact of fishing practices: comparing the length–weight relationships of discarded and retained fish can reveal the effects of fishing practices on size distribution and species composition [26]. This knowledge can be used to modify fishing gear, practices, or policies to minimize the capture of unwanted species or sizes, reducing discards and promoting sustainability.
(3)
Monitoring ecosystem health: regular analysis of length–weight relationships can provide insights into the overall health of an ecosystem [27]. Shifts in these relationships may signal changes in the abundance, growth, or reproductive success of a species, which could be linked to the impacts of fishing or other anthropogenic pressures [28]. Tracking these changes can inform adaptive management strategies to maintain ecosystem health and ensure the long-term sustainability of fisheries [29].
Sustainable fisheries management is crucial for maintaining the health and productivity of marine ecosystems, ensuring food security, and supporting the livelihoods of coastal communities [30,31].
In the Gulf of Cadiz and Southern Portugal several LWR works have been carried out for different species [23,32,33,34,35,36,37,38], with some more focused on species of commercial interest [39,40,41].
The present study seeks to address the gap in knowledge regarding the LWRs of discarded fish species in the Gulf of Cadiz, with a focus on species not previously studied in this area. This research aims to provide valuable insights into the biology and ecology of these species, which can ultimately inform management, conservation, and recovery plans for exploited species in the region. The low-sampled LWRs have been compared with results from adjacent areas in order to assess their utility and applicability to other study areas.

2. Materials and Methods

The data analyzed were collected through the ECOFISH, ECOFISH2, ECOFISH+, and ECOFISH 4.0. projects, carried out by the University of Cadiz, during the period 2019–2022. The main objective was to analyze and characterize the composition and structure of the discard associated with the trawl fishery in the Gulf of Cadiz (Figure 1). To this end, samplings were carried out with the professional fleet of Sanlúcar de Barrameda and El Puerto de Santa María. The Gulf of Cadiz trawl fleet uses trawls nets with a mesh size of 55 mm. In each haul, an average of 11 kg of discard were collected randomly. Discards in this fleet are caused mainly because the species are not of commercial interest, because they do not have legal size, or because they are species subject to TACs (total allowable catches) in the Gulf of Cadiz and, in addition, because they cannot be caught with this gear, such as anchovy (Engraulis encrasicolus, Linnaeus 1758). A total of 90 hauls were analyzed. The depth range was between 15–549 m. Specimens were identified to species level following the descriptions of Whitehead et al. [42] and Lloris [43]. Following Froese [17], rare species with low sample size values were taken into account, despite their low occurrence.
All specimens were measured for total length (TL) and total weight (TW) to the nearest ±0.1 cm and ±0.01 g, respectively.
LWRs were calculated following the equation W = aLb [44,45], where W is the total weight of the fish and L is the total length. The parameters of LWR were estimated by linear regression, according to the least squares method: ln(W) = ln(a) + bln(L). Where a is the intercept of the regression curve, related to the body shape, and b is the slope, related to the type of growth, with b < 3 being a tendency to negative allometric growth (having a greater growth in length than in weight), b = 3 an isometric growth and b > 3 a tendency to positive allometric growth (growing more in weight than in length) [17]. From this equation, the coefficient of determination (R2) was calculated with a confidence level of 95%. A plot of log a vs. b was used to detect outliers in LWR within species [17,46]. The residuals vs. leverage plot was used to identify those potential outliers through Cook’s distance comparisons [47].
Validity of the LWRs of the species with a low sample size (n < 12) was checked by comparing the parameters of the relationships with the studies saved in FishBase database [24] and with similar studies carried out in areas adjacent to the study area (southern coast of Portugal). Thus, the growth type of each species was compared and the differences between parameters a and b were interpreted taking into account the length ranges sampled and the number of specimens.
All statistical analyses were carried out with R version 4.2.1. and RStudio version 1.1.463 [48,49].

3. Results and Discussion

In this study, 20,007 individuals of 74 different species (40 families) were analyzed. The most abundant species were anchovy E. encrasicolus, Atlantic horse mackerel Trachurus trachurus (Linnaeus, 1758), brown comber Serranus hepatus (Linnaeus, 1758), European sardine Sardina pilchardus (Walbaum, 1792), boarfish Capros aper (Linnaeus, 1758), and Senegal seabream Diplodus bellottii (Steindachner, 1882). The most represented family was Sparidae with ten species. In this work, the LWR of 24 species is cited for the first time in the Gulf of Cadiz, highlighting Spotted weakfish Cynoscion nebulosus (Cuvier, 1830), a non-native species in the area [50,51].
The species are shown in Table 1, where the sample size, the minimum, mean, and maximum values of TL (cm) and TW (g), as well as the parameters a and b of the LWR, their 95% confidence intervals, the coefficient of determination (R2), and p-value are indicated.
Linear regressions were significant for all species (p < 0.05). The R2 ranged from 0.707, for Transparent goby Aphia minuta (Risso, 1810), to 0.996, for Rendezvous fish Polymetme corythaeola (Alcock, 1898) and comber Serranus cabrilla (Linnaeus, 1758). The variance explained was greater than 95% for 84% of the species. Parameter a had values between 0.005, for European conger Conger conger (Linnaeus, 1758), and 0.0454, for Wedge sole Dicologlossa cuneata (Moreau, 1881). Parameter b ranged from 2.161, for Red bandfish Cepola macrophthalma (Linnaeus, 1758), to 3.7040, for P. corythaeola. Regarding growth type, it was observed that five species showed strong negative allometric growth (b < 2.5), 12 species showed a tendency to negative allometric growth (b < 3), eight species showed isometric growth (b = 3), 46 species showed a tendency to positive allometric growth (b > 3), and three species showed strong positive allometric growth (b > 3.5). These results are in agreement with those observed by Froese [17] where, after analyzing data from 2989 species from FISHBASE [22], he showed that 90% of the b parameter values were between 2.5 and 3.5.
The results of plotting log a vs. b are shown in Figure 2. Three possible outliers were identified through the model residuals vs. leverage plot (Figure 3). Those outliers corresponded to the species C. macrophthalma (a = 0.015, b = 2.16), C. conger (a = 0.0005, b = 3.278), and D. cuneata (a = 0.0454, b = 2.3162). Froese [17] explains that the presence of outliers in the log a vs. b regression may be due to few observations for species, outliers in those observations, or a small size range; however, he also says that these outliers may come from species with different body shapes than other species, as is the case for this species, which have a more elongated body shape. These differences due to the body shape of the species can be observed in works such as [52], in which the authors demonstrated the existence of significant differences in the log a vs. b regression due to this factor.
Small red scorpionfish Scorpaena notata (Rafinesque, 1810) is the only one species whose values differ to both studies in the Gulf of Cádiz, having in this work a higher b value than those [23,35]. These differences could be explained by the differences in the number of specimens examined and by the high number of individuals with a higher length than the first maturity length, 8.8 cm [53].
LWR of C. nebulosus is referenced for the first time in the Gulf of Cadiz in this study, showing a higher b value than in works carried out in its natural distribution area [54,55].
The a and b parameters obtained in these LWRs come from samples taken monthly, therefore should be taken as annual averages for comparisons, since the data were not collected at any season preferentially. The existence of differences in the values of the b parameters may be due to several factors, such as differences in the number of specimens sampled, different depths between studies, bigger or smaller ranges in size, as well as the presence of specimens captured at a certain time of the year where they present different conditions. Likewise, the existence of possible biological or environmental differences between regions can cause these differences. Furthermore, LWRs are not constant throughout the year, varying according to certain factors such as food availability, sex, gonadal development, temperature, salinity, presence, or absence of small specimens or the spawning season [17,23,45,56,57,58]. Possible differences in species of commercial interest may also be due to the fact that the individuals used in this work came from discards, so the commercial sizes of these species have not been used. In addition, as in Borges et al. [34], juveniles and small sizes of some species are not present due to the selectivity of the net.

Low-Sample Specimens

For the low-sampled specimens (n < 12) further use of LWR should be limited to the size ranges used for the estimation of the parameters [18]. The LWRs of some individuals are biased due to the sample collection method and low sample size, but they are included in this paper because they are the first reports of these species in the study area. The number of studies that are available for each of these species in the global FishBase database are in Table 2. Redbanded seabream Pagrus auriga (Valenciennes, 1843) and P. corythaeola only have one LWR available in FishBase. In particular, P. auriga LWR had obtained with only one individual, keeping b constant (b = 3), giving a value of parameter a = 0.0191, similar to that obtained in this work (a = 0.0142).
Given the lack of information about some of those individuals, these first estimates may be useful in future research for this and other adjacent areas. A comparison was made between the results obtained in this study for nine species with low abundance values with those of other studies carried out on adjacent study areas (Southern Portugal) [32,33,34,36,59] (Table 3). Specifically, it was observed that all species had similar or higher b values than those obtained in these works, except for Piper gurnard Trigla lyra (Linnaeus, 1758), dragonet Callionymus lyra (Linnaeus, 1758), and pouting Trisopterus luscus (Linnaeus, 1758), which had lower b values. This result is likely because these individuals with low b values are still growing and allocating energy towards developing their reproductive organs, which may lead to a less efficient conversion of food into biomass [60,61,62]. On the other hand, fish that have reached sexual maturity and are at their maximum length have been shown to have a value of b > 3, indicating a more rapid increase in weight compared to length [63,64,65,66,67]. This increase in weight is likely due to the allocation of resources towards reproduction, as mature fish must invest a significant amount of energy into producing and carrying eggs or sperm. Therefore, the differences in the value of b between our study and others are likely due to differences in the length and sexual maturity of the fish, highlighting the importance of considering these factors when interpreting the weight–length relationship in fish. In addition to this factor, it has been observed that LWRs can vary whether individuals are captured in warm or cold periods, as well as depending on the season [68], variables that, together with the low sample size, may explain these variations.
Despite the valuable insights provided by this study, there are some limitations that should be acknowledged. First, as mentioned earlier, the sample sizes for some species were small, which may affect the accuracy of the LWR estimates [17]. Second, this study focused on discarded fish species, which does not fully represent the fish community in the Gulf of Cadiz. Third, the study did not account for possible seasonal variations in the LWRs, which may influence the results. Regardless of these considerations, studies such as this one, are essential for the knowledge of the species and their management when there are few data in a given area.

4. Conclusions

The use of small sample sizes in fisheries research may lack statistical power or be subject to bias. However, in this study, we argue that even with a small sample size, the weights–length relationship of discarded fish can still provide valuable insights into the biology and ecology of fish populations. Our results demonstrate that the parameter “b” in the LWR of fish can provide a useful indicator of maturity and reproductive biology, even with a small sample size. Furthermore, by including data from discarded fish, we can gain a better understanding of the population dynamics and life history strategies of fish species, which can inform conservation and management efforts. Therefore, we believe that the inclusion of weight–length data from small sample sizes can still be a valuable tool for fisheries research, provided that appropriate statistical methods and careful consideration of potential biases are employed. Due to the fact that LWRs depend on the temporal moment in which the data were taken [15], knowing what these LWRs are like for the different species in an area over time is very useful for the knowledge and management of the populations in that study area. This is more important for discarded species due to possible interspecific relationships, since these species may have an influence on species of commercial interest in, for example, food webs [5,69].
It is hoped that the results of this study will contribute to the knowledge of the species and populations in this area, as well as to future management, conservation, and recovery plans for exploited species.

Author Contributions

Conceptualization, methodology, formal analysis, investigation, writing—original draft, Writing—review and editing, and data curation, C.R.-G.; methodology, formal analysis, writing—original draft, and writing—review and editing, J.C.-G.; methodology, formal analysis, writing—original draft, and writing—review and editing, Á.R.D.-B.; investigation, writing—original draft, and writing—review and editing, A.G.-G.; investigation, writing—original draft, writing—review and editing, data curation, and supervision, R.C.-C. All authors have read and agreed to the published version of the manuscript.

Funding

This research has been carried out within the framework of the ECOFISH project: eco-innovative strategies for sustainable fishing in the Gulf of Cadiz SPA. This initiative has been supported by the Biodiversity Foundation, the Ministry for Ecological Transition and Demographic Challenge, through the Pleamar Program, co-financed by the European Maritime and Fisheries Fund (EMFF) [grant number: 2019-016/PV/PLEAMAR18/PT; 2020-013/PV/PLEAMAR19/PT; 2020-055/PV/PLEAMAR20/PT; 2021/PV/PLEAMAR20-21/PT; 2021-060/PV/PLEAMAR21/PT].

Institutional Review Board Statement

The specimens used in this work have never been subjected to animal experimentation. These specimens come from catches made by professional fishermen and are subject to European regulations on Fish.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data will be available on reasonable request.

Acknowledgments

The publication of this work has been possible thanks to the ECOFISH, ECOFISH2, ECOFISH +, and ECOFISH 4.0. projects with the collaboration of the Biodiversity Foundation of the Ministry of Ecological Transition, through the Pleamar Program, co-financed by the FEMP. The authors would like to thank the observers (Félix, Andrea, Tania, and Zaida), the project technician (Eli), the professional fleet of Puerto de Santa María and the Cofradía de Pescadores de Sanlúcar de Barrameda, as well as Lucía, Sara, Ana, Jessi, Chari, and Daniel for their help during sample processing. Authors would also like thank Samantha Blakeman for proofreading the manuscript in English. We would like to thank the journal team and specially the three reviewers for their comments.

Conflicts of Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

References

  1. Bellido, J.M.; Santos, M.B.; Pennino, M.G.; Valeiras, X.; Pierce, G.J. Fishery discards and bycatch: Solutions for an ecosystem approach to fisheries management? Hydrobiologia 2011, 670, 317–333. [Google Scholar] [CrossRef]
  2. Despoti, S.; Milisenda, G.; Ligas, A.; Bentes, L.; Maynou, F.; Vitale, S.; Garofalo, G.; Sbrana, M.; Erzini, K.; Tserpes, G.; et al. Marine spatial closures as a supplementary tool to reduce discards in bottom trawl fisheries: Examples from southern European waters. Fish. Res. 2020, 232, 105714. [Google Scholar] [CrossRef]
  3. Kelleher, K. Discards in the world’s marine fisheries: An update. In FAO Fisheries Technical Paper; FAO: Rome, Italy, 2005; p. 131. [Google Scholar]
  4. Despoti, S.; Stergiou, K.I.; Machias, A.; Vassilopoulou, V.; Tsagarakis, K.; Valavanis, V.; Adamidou, A.; Gionnoulaki, M. Assessing the spatial distribution of five non-commercial fish species in the Aegean Sea (Greece, Eastern Mediterranean Sea) based on discards data. Reg. Stud. Mar. Sci. 2021, 44, 101736. [Google Scholar] [CrossRef]
  5. Alverson, D.L.; Freeberg, M.H.; Murawski, S.A.; Pope, J.G. A Global Assessment of Fisheries Bycatch and Discards; Food and Agriculture Organization: Rome, Italy, 1994; Volume 339. [Google Scholar]
  6. Gamaza, M.A.; Torres, M.A.; Acosta, J.J.; Erzini, K.; Sobrino, I. Are we ready to implement a discard ban in the gulf of Cádiz? Stakeholders’ perceptions. Mar. Policy 2020, 116, 103711. [Google Scholar] [CrossRef]
  7. Catchpole, T.L.; Ribeiro-Santos, A.; Mangi, S.C.; Hedley, C.; Gray, T.S. The challenges of the landing obligation in EU fisheries. Mar. Policy 2017, 82, 76–86. [Google Scholar] [CrossRef]
  8. Catchpole, T.L.; Enever, R.; Maxwell, D.L.; Armstrong, M.J.; Reese, A.; Revill, A.S. Constructing indices to detect temporal trends in discarding. Fish. Res. 2011, 107, 94–99. [Google Scholar] [CrossRef]
  9. Stone, J.C.; Glass, K.; Munn, Z.; Tugwell, P.; Doi, S.A. Comparison of bias adjustment methods in meta-analysis suggests that quality effects modeling may have less limitations than other approaches. J. Clin. Epidemiol. 2020, 117, 36–45. [Google Scholar] [CrossRef]
  10. Le Cren, E.D. The length-weight relationship and seasonal cycle in gonad weight and condition in the perch (Perca fluviatilis). Society 1951, 20, 201–219. [Google Scholar] [CrossRef]
  11. Anderson, R.; Gutreuter, S. Length, weight, and associated structural indices. In Fisheries Techniques; Nielsen, L., Johnson, D., Eds.; American Fisheries Society: Bethesda, MD, USA, 1983; pp. 283–300. [Google Scholar]
  12. Pauly, D. Fishbyte section. Naga ICLARM Q. 1993, 16, 26. [Google Scholar]
  13. Petrakis, G.; Stergiou, K.I. Weight–length relationships for 33 fish species in Greek waters. Fish. Res. 1995, 21, 465–469. [Google Scholar] [CrossRef]
  14. Morato, T.; Afonso, P.; Lourinho, P.; Barreiros, J.P.; Santos, R.S.; Nash, R.D.M. Lenght-Weight relationships for 21 coastal fish species of the Azores, north-eastern Atlantic. Fish. Res. 2001, 50, 297–302. [Google Scholar] [CrossRef]
  15. Koutrakis, E.T.; Tsikliras, A.C. Length–weight relationships of fishes from three northern Aegean estuarine systems (Greece). J. Appl. Ichthyol. 2003, 19, 258–260. [Google Scholar] [CrossRef]
  16. Kimmerer, W.; Avent, S.R.; Bollens, S.M.; Feyrer, F.; Grimaldo, L.F.; Moyle, P.B.; Nobriga, M.; Visintainer, T. Variability in length–weight relationships used to estimate biomass of estuarine fish from survey data. Trans. Am. Fish. 2005, 134, 481–495. [Google Scholar] [CrossRef]
  17. Froese, R. Cube law, condition factor and weight–length relationships: History, meta-analysis and recommendations. J. Appl. Ichthyol. 2006, 22, 241–253. [Google Scholar] [CrossRef]
  18. Yapici, S.; Karachle, P.K.; Filiz, H. First length–weight relationships of 11 fish species in the Aegean Sea. J. Appl. Ichthyol. 2015, 31, 398–402. [Google Scholar] [CrossRef]
  19. Al Kamel, N.A.M.; Becheker, A.; Kara, H.M. Length-weight relationship of three commercially important fish species from Mocka water, southern Red Sea, Yemen. J. Appl. Ichthyol. 2020, 36, 366–368. [Google Scholar] [CrossRef]
  20. Coello, D.; Herrera, M.; Zambrano, R. Length-weight relationship of 74 fish species caught in the continental coast of Ecuador. J. Appl. Ichthyol. 2021, 37, 129–134. [Google Scholar] [CrossRef]
  21. Soykan, O.; Kinacigil, H.T. Length-weight relationship of some discarded fish species with emphasis on length at maturity from the Central Aegean Sea, Turkey. Thalassas 2021, 37, 505–511. [Google Scholar] [CrossRef]
  22. Lamprakis, M.K.; Kallianiotis, A.; Moutopoulos, D.K.; Stergiou, K.I. Weight–length relationships of fishes discarded by trawerls in the North Aegean Sea. Acta Ichthyol. Piscat. 2003, 33, 145–152. [Google Scholar] [CrossRef]
  23. Torres, M.A.; Ramos, F.; Sobrino, I. Length-weight relationships of 76 fish species from the Gulf of Cadiz (SW Spain). Fish. Res. 2012, 127–128, 171–175. [Google Scholar] [CrossRef]
  24. Froese, R.; Pauly, D.; FishBase. World Wide Web Electronic Publication. 2005. Available online: http://www.fishbase.org (accessed on 19 January 2023).
  25. Beverton, R.J.H.; Holt, S.J. On the dynamics of exploited fish populations. In Fishery Investigations Series II; Springer: Dordrecht, The Netherlands, 1957; Volume 19, pp. 1–533. [Google Scholar]
  26. Benoît, H.P.; Swain, D.P. Impacts of environmental change and direct and indirect harvesting effects on the dynamics of a marine fish community. Can. J. Fish. Aquat. Sci. 2008, 65, 2088–2104. [Google Scholar] [CrossRef]
  27. Pauly, D.; Christensen, V.; Dalsgaard, J.; Froese, R.; Torres, F., Jr. Fishing down marine food webs. Science 1998, 279, 860–863. [Google Scholar] [CrossRef] [PubMed]
  28. Rochet, M.J.; Trenkel, V.M. Factors for the variability of discards: Assumptions and field evidence. Can. J. Fish. Aquat. Sci. 2005, 62, 224–235. [Google Scholar] [CrossRef]
  29. Hilborn, R.; Walters, C.J. Quantitative Fisheries Stock Assessment: Choice, Dynamics and Uncertainty; Springer Science & Business Media: Berlin, Germany, 1992. [Google Scholar]
  30. Pauly, D.; Christensen, V.; Guénette, S.; Pitcherm, T.J.; Rashid-Sumaila, U.; Walters, C.J.; Watson, R.; Zeller, D. Towards sustainability in world fisheries. Nature 2002, 418, 689–695. [Google Scholar] [CrossRef]
  31. Worm, B.; Barbier, E.B.; Beaumont, N.; Duffy, J.E.; Folke, C.; Halpern, B.S.; Jackson, J.B.C.; Lotze, H.K.; Micheli, F.; Palumbi, S.R.; et al. Impacts of biodiversity loss on ocean ecosystem services. Science 2006, 314, 787–790. [Google Scholar] [CrossRef]
  32. Gonçalves, J.M.S.; Bentes, L.; Lino, P.G.; Ribeiro, J.; Canario, A.V.M.; Erzini, K. Weight–length relationships for selected fish species of the small-scale demersal fisheries of the south and south-west coast of Portugal. Fish. Res. 1997, 30, 253–256. [Google Scholar] [CrossRef]
  33. Santos, M.N.; Gaspar, M.B.; Vasconcelos, P.; Monteiro, C.C. Weight–length relationships for 50 selected fish species of the Algarve (southern Portugal). Fish. Res. 2002, 59, 289–295. [Google Scholar] [CrossRef]
  34. Borges, T.C.; Olim, S.; Erzini, K. Weight–length relationships for fish species discarded in commercial fisheries of the Algarve (southern Portugal). J. Appl. Ichthyol. 2003, 19, 394–396. [Google Scholar] [CrossRef]
  35. Mata, A.J.; Morales, J.; Márquez, L. Weight-length relationships for 26 demersal fish species of the Spanish South-Atlantic coastal waters. J. Appl. Ichthyol. 2008, 24, 330–333. [Google Scholar] [CrossRef]
  36. Veiga, P.; Machado, D.; Almeida, C.; Bentes, L.; Monteiro, P.; Oliveira, F.; Ruano, M.; Erzini, K.; Gonçalves, J.M.S. Weight-length relationships for 54 species of the Arade estuary, southern Portugal. J. Appl. Ichthyol. 2009, 25, 493–496. [Google Scholar] [CrossRef]
  37. Compairé, J.C.; Soriguer, M.C. Lenght-weight relationships of seven fish species from tidepools of an intertidal rocky shore in the Gulf of Cadiz, Spain (NE Atlantic). J. Appl. Ichthyol. 2020, 36, 852–854. [Google Scholar] [CrossRef]
  38. Compairé, J.C.; Gómez-Cama, C.; Soriguer, M.C. Length-Weight relationships of six fish species of a rocky intertidal shore on the subtropical atlantic coast of Spain. Thalassas 2021, 37, 267–271. [Google Scholar] [CrossRef]
  39. Jiménez, M.P.; Sobrino, I.; Ramos, F. Distribution pattern, reproductive biology, and fishery of the wedge sole Dicologlossa cuneata in the Gulf of Cadiz, southwest Spain. Mar. Biol. 1998, 131, 173–187. [Google Scholar]
  40. Millán, M. Reproductive characteristics and condition status of anchovy Engraulis encrasicolus L. from the Bay of Cadiz (SW Spain). Fish. Res. 1999, 41, 73–86. [Google Scholar] [CrossRef]
  41. Velasco, E.M.; Del Árbol, J.; Baro, J.; Sobrino, I. Age and growth of the Spanish chub mackerel Scomber colias off southern Spain: A comparison between samples from the NE Atlantic and the SW Mediterranean. Rev. Biol. Mar. Oceanogr. 2011, 46, 27–34. [Google Scholar] [CrossRef]
  42. Whitehead, P.J.P.; Bauchot, M.L.; Jureau, J.C.; Nielsen, J.; Tortonese, E. Fishes of the North-Eastern Atlantic and the Mediterranean; UNESCO: Paris, France, 1986; Volume III. [Google Scholar]
  43. Lloris, D. Ictiofauna Marina: Manual de Identificación de los Peces Marinos de la Península Ibérica y Baleares; 954 Especies; Omega: Biel/Bienne, Switzerland, 2015. [Google Scholar]
  44. Ricker, W.E. Linear regressions in fishery research. Can. J. Fish. Aquat. Sci. 1973, 30, 409–434. [Google Scholar] [CrossRef]
  45. Ricker, W.E. Computation and interpretation of biological statistics of fish populations. In Bulletin of the Fish; Refugee Board of Canada: Ottawa, ON, Canada, 1975. [Google Scholar]
  46. Stergiou, K.I.; Moutopoulos, D.K. A review of length–weight relationships of fishes from Greek Marine Waters. ICLARM Q. 2001, 24, 23–39. [Google Scholar]
  47. Cook, R.D.; Weisberg, S. Residuals and Influence in Regression; Chapman and Hall: London, UK, 1982. [Google Scholar]
  48. RStudio Team. RStudio: Integrated Development for R; RStudio, Inc.: Boston, MA, USA, 2016; Available online: http://www.rstudio.com/ (accessed on 29 March 2023).
  49. R Core Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2020; Available online: https://www.R-project.org/ (accessed on 29 March 2023).
  50. Acosta, J.J.; Canoura, J.; Juárez, A. First record of Cynoscion nebulosus in the Spanish waters of the Gulf of Cadiz (ICES Division IXa South). Mar. Biodivers. Rec. 2013, 6, e112. [Google Scholar] [CrossRef]
  51. Bañon, R.; Arias, A.; Arana, D.; Cuesta, J.A. Identification of a non-native Cynoscion species (Perciformes: Sciaenidae) fron the Gulf of Cádiz (southwestern Spain) and data on its current status. Sci. Mar. 2017, 81, 19–26. [Google Scholar] [CrossRef]
  52. López-Pérez, C.; Olivar, M.P.; Hulley, P.A.; Tuset, V.M. Length–weight relationships of mesopelagic fishes from the equatorial and tropical Atlantic waters: Influence of environment and body shape. J. Fish Biol. 2020, 96, 1388–1398. [Google Scholar] [CrossRef]
  53. Ordines, F.; Quetglas, A.; Massutí, E.; Moranta, J. Habitat preferences and life history of the red scorpion fish, Scorpaena notata, in the Mediterranean. Estuar. Coast. Shelf Sci. 2009, 85, 537–546. [Google Scholar] [CrossRef]
  54. Matlock, G.C.; Strawn, K. Standard Length-Weight Relationships of 22 Fishes from Upper Galveston Bay; Texas Agricultural Experiment Station: College Station, TX, USA, 1976; Volume 1286, pp. 1–4. [Google Scholar]
  55. Vega-Cendejas, M.E.; Peralta-Meixuiero, M.A.; De Santillana, M.H. Length–weight relations of fishes inhabiting a hyperhaline coastal lagoon in Yucatan, Mexico. Acta Ichthyol. Piscat. 2017, 47, 411–415. [Google Scholar] [CrossRef]
  56. Bagenal, T.B.; Tesch, F.W. Age and growth. In Methods for Assessment of Fish in Freshwaters, 3rd ed.; Bagenal, T., Ed.; IBP Handbook No. 3; Blackwell Scientific Publications: Oxford, UK, 1978; pp. 101–136, Chapter 5. [Google Scholar]
  57. Pauly, D. Fish Population Dynamics in Tropical Waters: A Manual for Use with Programmable Calculators; ICLARM Studies and Reviews; ICLARM: Manila, Philippines, 1984; Volume 8, 325p. [Google Scholar]
  58. Safran, P. Theoretical analysis of the weight–length relationships in the juveniles. Mar. Biol. 1992, 112, 545–551. [Google Scholar] [CrossRef]
  59. Mendes, B.; Fonseca, P.; Campos, A. Weight-length relationships for 46 fish species of the Portuguese west coast. J. Appl. Ichthyol. 2004, 20, 355–361. [Google Scholar] [CrossRef]
  60. King, P.A.; Fives, J.M.; Mcgrath, D. Reproduction, growth and feeding of the dragonet, Callionymus lyra (Teleostei: Callionymidae), in Galway Bay, Ireland. J. Mar. Biol. Assoc. UK 1994, 74, 513–526. [Google Scholar] [CrossRef]
  61. Alonso-Fernández, A.; Domínguez-Petit, R.; Bao, M.; Rivas, C.; Saborido-Rey, F. Spawning pattern and reproductive strategy of female pouting Trisopterus luscus (Gadidae) on the Galicia shelf of north-western Spain. Aquat. Living Resour. 2008, 21, 383–393. [Google Scholar] [CrossRef]
  62. Agbali, M.; El-Mor, M. Some aspects of the Reproductive Biology of the Piper Gurnard Trigla Lyra (Linnaeus, 1758) in Dernah Coast-Eastern Libya. Int. J. Pharm. Life Sci. 2015, 6, 4445–4451. [Google Scholar]
  63. Marques, A. Some data on the biology of Polymetme corythaeola (phosich-thyidae), from off the Portuguese south coast, North East Atlantic. Cybium 2001, 25, 100–102. [Google Scholar]
  64. D’Onghia, G.; Sion, L.; Maiorano, P.; Mytilineou, C.; Dalessandro, S.; Carlucci, S.; Desantis, S. Population biology and life strategies of Chlorophthalmus agassizii Bonaparte, 1840 (Pisces: Osteichthyes) in the Mediterranean Sea. Mar. Biol. 2006, 149, 435–446. [Google Scholar] [CrossRef]
  65. Ilhan, D.; Akalin, S.; Tosunoglu, Z.; Özaydin, O. Growth characteristics and reproduction of comber, Serranus cabrilla (Actinopterygii, Perciformes, Serranidae), in the Aegean Sea. Acta Ichthyol. Piscat. 2010, 40, 55–60. [Google Scholar] [CrossRef]
  66. Orhan, A.K.; Kutlu, S.; Karayücel, I. Some reproductive characteristics of Uranoscopus scaber Linnaeus, 1758 (Pisces: Uranoscopidae) in the Black Sea (Turkey). Cah. Biol. Mar. 2011, 52, 253–260. [Google Scholar]
  67. Curtis, J.M.R.; Santos, S.V.; Nadeau, J.L.; Gunn, B.; Bigney-Wilner, K.; Balasubramanian, H.; Overington, S.; Lesage, C.M.; D’Entremont, J.; Wieckowski, K. Life history and ecology of the elusive European short-snouted seahorse Hippocampus hippocampus. J. Fish Biol. 2017, 91, 1603–1622. [Google Scholar] [CrossRef] [PubMed]
  68. Jisr, N.; Younes, G.; Sukhn, C.; El-Dakdouki, M.H. Length-weight relationships and relative condition factor of fish inhabiting the marine area of the Eastern Mediterranean city, Tripoli-Lebanon. Egypt J. Aquat. Res. 2018, 44, 299–305. [Google Scholar] [CrossRef]
  69. Yapıcı, S.; Filiz, H. Estimation of age, growth and reproduction of boarfish, Capros aper, in the South Aegean Sea. Pak. J. Zool. 2014, 46, 1061–1068. [Google Scholar]
Fishes 08 00222 g001 550
Figure 1. Map of the Gulf of Cadiz (SW Spain).
Figure 1. Map of the Gulf of Cadiz (SW Spain).
Fishes 08 00222 g001
Fishes 08 00222 g002 550
Figure 2. Plot of log a vs. b for the LWRs for the 74 fish species studied. Red points are species with outlier values. Blue points are species with a low number of individuals caught. Black points are the other species analysed.
Figure 2. Plot of log a vs. b for the LWRs for the 74 fish species studied. Red points are species with outlier values. Blue points are species with a low number of individuals caught. Black points are the other species analysed.
Fishes 08 00222 g002
Fishes 08 00222 g003 550
Figure 3. Residuals vs. Leverage plot. Circles represent individual observations. The solid red line represents a residual regression line that should be close to zero. The dashed red lines indicate influence limits (Cook’s distance; 0.5 and 1) used to identify potential outliers. Observations 15, 22, and 55 have been identified as influential points in the analysis.
Figure 3. Residuals vs. Leverage plot. Circles represent individual observations. The solid red line represents a residual regression line that should be close to zero. The dashed red lines indicate influence limits (Cook’s distance; 0.5 and 1) used to identify potential outliers. Observations 15, 22, and 55 have been identified as influential points in the analysis.
Fishes 08 00222 g003
Table
Table 1. Parameters obtained for LWR and statistical description for 74 fish species discarded by the trawl fleet in the Gulf of Cádiz (SW Spain): n: number of specimens analyzed, length in cm (minimum, maximum, mean, and standard deviation (SD)), weight in g (minimum, maximum, mean, and standard deviation (SD)), LWR parameters (a: intercept (95% confidence interval (95% CI)), b: slope (95% confidence interval (95% CI)), R2: coefficient of determination and p-value) and type of growth (allometric (positive or negative) or isometric). In bold are marked species without parameters for LWR in the Gulf of Cádiz.
Table 1. Parameters obtained for LWR and statistical description for 74 fish species discarded by the trawl fleet in the Gulf of Cádiz (SW Spain): n: number of specimens analyzed, length in cm (minimum, maximum, mean, and standard deviation (SD)), weight in g (minimum, maximum, mean, and standard deviation (SD)), LWR parameters (a: intercept (95% confidence interval (95% CI)), b: slope (95% confidence interval (95% CI)), R2: coefficient of determination and p-value) and type of growth (allometric (positive or negative) or isometric). In bold are marked species without parameters for LWR in the Gulf of Cádiz.
Family—SpeciesNLength (cm)Weight (g)Parameters of the LWRGrowth Type
Min.Max.Mean (±SD)Min.Max.Mean (±SD)a (95% CI)b (95% CI)R2p-Value
Batrachoididae
Halobatrachus didactylus2313.533.521.72 (±4.89)38.96556.67214.43 (±139.77)0.0114 (0.0036–0.0317)3.1464 (2.6152–3.6753)0.962<0.001Allometric +
 
Blennidae
Blennius ocellaris294.314.711.18 (±2.39)0.8345.9121.76 (±11.90)0.0092 (0.0063–0.0133)3.1641 (3.0100–3.3183)0.985<0.001Allometric +
 
Callionymidae
Callionymus lyra122.720.210.91 (±5.82)0.1867.9517.28 (±20.67)0.0093 (0.0040–0.0214)2.9038 (2.5409–3.2667)0.966<0.001Allometric −
Callionymus maculatus1242.317.07.57 (±2.20)0.0936.572.83 (±3.37)0.0152 (0.0124–0.0186)2.4930 (2.3914–2.5946)0.950<0.001Allometric −
Synchiropus phaeton218.617.611.72 (±2.16)3.7544.7110.87 (±9.01)0.0037 (0.0012–0.0108)3.1895 (2.7484–3.6305)0.919<0.001Allometric +
 
Caproidae
Capros aper9352.913.45.80 (±1.14)0.5944.004.46 (±3.60)0.0246 (0.0228–0.0264)2.8909 (2.8487–2.9331)0.951<0.001Allometric −
 
Carangidae
Trachurus mediterraneus3268.632.018.21 (±3.05)4.83239.3048.72 (±31.07)0.0099 (0.0086–0.0114)2.8997 (2.8503–2.9491)0.976<0.001Allometric −
Trachurus picturatus9512.217.514.34 (±1.31)14.150.6526.09 (±8.06)0.0059 (0.0037–0.0093)3.1430 (2.9713–3.3148)0.934<0.001Allometric +
Trachurus trachurus23335.232.616.79 (±3.97)0.91316.4344.74 (±35.44)0.0064 (0.0061–0.0068)3.0752 (3.0562–3.0943)0.977<0.001Allometric +
 
Centracanthidae
Spicara flexuosa369.120.416.83 (±2.30)6.78101.7657.62 (±22.96)0.0042 (0.0027–0.0076)3.3491 (3.1381–3.5602)0.967<0.001Allometric +
Spicara smaris336.118.714.95 (±2.82)2.1273.3940.56 (±18.54)0.0081 (0.0055–0.0117)3.1140 (2.9646–3.2533)0.985<0.001Allometric +
 
Centriscidae
Macroramphosus scolopax175.613.29.21 (±2.30)0.9510.914.93 (±3.12)0.0086 (0.0047–0.0155)2.8016 (2.5334–3.0697)0.969<0.001Allometric −
 
Cepolidae
Cepola macrophthalma1487.863.826.41 (±11.17)0.96107.6321.70 (±19.37)0.0153 (0.0126–0.0186)2.1607 (2.0999–2.2214)0.971<0.001Allometric −
 
Chlorophthalmidae
Chlorophthalmus agassizi510.814.813.72 (±1.68)7.7523.9518.31 (±6.21)0.0033 (0.0000–0.2701)3.2756 (1.5900–4.9612)0.9030.008Allometric +
 
Chimaeridae
Chimaera monstrosa1722.078.538.07 (±17.44)6.89375.4062.80 (±90.29)0.0152 (0.0124–0.0186)2.4930 (2.3914–2.5946)0.950<0.001Allometric −
 
Citharidae
Citharus linguatula6084.819.311.41 (±2.35)0.8155.3312.34 (±7.31)0.0052 (0.0047–0.0058)3.1339 (3.0904–3.1773)0.971<0.001Allometric +
 
Clupeidae
Alosa alosa1720.242.229.88 (±5.45)71.60721.44246.19 (±173.52)0.0030 (0.0001–0.0071)3.2949 (3.0383–3.5515)0.979<0.001Allometric +
Alosa fallax5314.044.031.56 (±5.77)21.81878.17276.23 (±146.39)0.0090 (0.0058–0.0141)2.9626 (2.8330–3.0923)0.976<0.001Allometric −
Sardina pilchardus10268.020.913.97 (±3.09)2.6483.8924.22 (±16.39)0.0071 (0.0065–0.0078)3.0259 (2.9911–3.0676)0.966<0.001Isometric
 
Congridae
Conger conger31921.277.134.95 (±7.46)6.40868.9563.60 (±62.74)0.0005 (0.0003–0.0007)3.2778 (3.1199–3.4086)0.888<0.001Allometric +
 
Cynoglossidae
Symphurus nigrescens1325.212.39.12 (±1.54)1.0316.777.48 (±3.80)0.0050 (0.0038–0.0065)3.2620 (3.1403–3.3837)0.956<0.001Allometric +
 
Engraulidae
Engraulis encrasicolus32314.016.710.10 (±2.08)0.3124.466.58 (±4.18)0.0045 (0.0042–0.0048)3.0916 (3.0629–3.1202)0.933<0.001Allometric +
 
Etmopteridae
Etmopterus spinax4129.333.716.11 (±4.75)2.85144.4819.76 (±23.34)0.0029 (0.0025–0.0035)3.0652 (3.0018–3.1285)0.957<0.001Allometric +
 
Gadidae
Gadiculus argenteus1586.416.19.49 (±1.60)1.7148.988.55 (±5.33)0.0047 (0.0037–0.0061)3.2816 (3.1694–3.3938)0.955<0.001Allometric +
Micromesistius poutassou20812.829.120.77 (±2.95)11.32158.356.66 (±25.58)0.0022 (0.0016–0.0028)3.3292 (3.2412–3.4171)0.964<0.001Allometric +
Trisopterus luscus818.123.020.41 (±1.66)62.00126.1594.21 (±21.56)0.0190 (0.0030–0.1204)2.8157 (2.2034–3.4280)0.947<0.001Allometric −
 
Gobiidae
Aphia minuta2933.05.74.55 (±0.47)0.161.160.50 (±0.17)0.0060 (0.0043–0.0083)2.8875 (2.6734–3.1016)0.707<0.001Allometric −
Gobius niger1674.710.06.96 (±1.18)0.7811.173.53 (±2.06)0.0056 (0.0047–0.0067)3.2623 (3.1687–3.3559)0.966<0.001Allometric +
 
Haemulidae
Pomadasys incisus6134.522.911.28 (±4.33)0.88166.6027.06 (±28.30)0.0074 (0.0071–0.0077)3.2049 (3.1875–3.2222)0.995<0.001Allometric +
 
Lophiidae
Lophius budegassa2414.327.79.74 (±3.42)1.09348.6817.07 (±34.35)0.0110 (0.0094–0.0129)3.0354 (2.9650–3.1059)0.968<0.001Isometric
Lophius piscatorius685.028.510.78 (±4.08)1.51426.8325.14 (±53.21)0.0102 (0.0074–0.0139)3.0723 (2.9394–3.2052)0.927<0.001Allometric +
 
Merluccidae
Merluccius merluccius3965.027.110.61 (±2.90)0.69128.958.96 (±10.68)0.0047 (0.0042–0.0052)3.0906 (3.0421–3.1390)0.976<0.001Allometric +
 
Mugilidae
Chelon ramada4824.343.630.59 (±4.38)97.30716.75244.44 (±134.11)0.0017 (0.0009–0.0034)3.4406 (3.2398–3.6413)0.962<0.001Allometric +
 
Pentanchidae
Galeus melastomus16912.757.721.21 (±6.12)5.33492.4731.57 (±44.53)0.0024 (0.0018–0.0031)3.0201 (2.9315–3.1087)0.964<0.001Isometric
 
 
Peristediidae
Peristedion cataphractum1611.125.116.36 (±4.07)6.3387.1927.45 (±24.98)0.0025 (0.0015–0.0042)3.2481 (3.0700–3.4262)0.990<0.001Allometric +
 
Phycidae
Phycis blennoides246.316.212.74 (±2.33)1.3426.4612.58 (±5.69)0.0039 (0.0026–0.0058)3.1366 (2.9813–3.2920)0.987<0.001Allometric +
 
Phosichthydae
Polymetme corythaeola515.621.517.98 (±2.23)15.0949.7126.89 (±13.51)0.0006 (0.0002–0.0016)3.7040 (3.3378–4.0702)0.996<0.001Allometric +
 
Sciaenidae
Cynoscion nebulosus3616.625.519.86 (±1.8)52.10194.8589.49 (±30.1)0.0073 (0.0033–0.0160)3.1388 (2.8755–3.4020)0.945<0.001Allometric +
Umbrina canariensis1812.227.320.27 (±4.76)20.17243.59118.31 (±72.17)0.0093 (0.0061–0.0144)3.0887 (2.9449–3.2326)0.992<0.001Allometric +
Umbrina ronchus6210.226.317.03 (±3.13)11.27211.4666.04 (±42.14)0.0101 (0.0070–0.0145)3.0603 (2.9312–3.1893)0.974<0.001Allometric +
 
Scombridae
Scomber colias5217.428.021.87 (±2.10)38.35206.5287.51 (±28.95)0.0095 (0.0033–0.0274)2.9487 (2.6048–3.2926)0.853<0.001Allometric −
Scomber scombrus4813.431.025.58 (±4.77)12.07241.2140.52 (±63.81)0.0037 (0.0022–0.0060)3.2227 (3.0708–3.3746)0.975<0.001Allometric +
 
Scophthalmidae
Lepidorhombus whiffiagonis557.813.811.29 (±1.48)1.8917.269.24 (±3.74)0.0015 (0.0009–0.0026)3.5651 (3.3406–3.7896)0.949<0.001Allometric +
 
Scorpaenidae
Scorpaena notata715.817.011.85 (±2.17)3.35103.3236.70 (±20.77)0.0137 (0.0102–0.0186)3.1475 (3.0255–3.2695)0.974<0.001Allometric +
 
Scyliorhinidae
Scyliorhinus canicula2619.556.526.54 (±10.78)2.44651.1091.06 (±126.76)0.0021 (0.0017–0.0027)3.0907 (3.0188–3.1626)0.965<0.001Allometric +
 
Sebastidae
Helicolenus dactylopterus1094.416.97.93 (±2.33)1.2480.7810.18 (±11.92)0.0111 (0.0097–0.0127)3.1499 (3.0833–3.2165)0.988<0.001Allometric +
 
Serranidae
Serranus cabrilla318.423.820.23 (±3.09)72.78181.95109.9 (±62.41)0.0025 (0–1.3845)3.5373 (1.4275–5.6471)0.9960.030Allometric +
Serranus hepatus15193.414.59.20 (±1.74)0.5244.0614.33 (±7.83)0.0105 (0.0098–0.0112)3.1996 (3.1696–3.2296)0.966<0.001Allometric +
 
Soleidae
Dicologlossa cuneata896.421.511.61 (±3.27)2.7072.2215.07 (±10.58)0.0454 (0.0328–0.0629)2.3162 (2.1823–2.4501)0.931<0.001Allometric −
Microchirus boscanion8224.917.48.87 (±1.37)1.1438.428.26 (±3.91)0.0074 (0.0066–0.0083)3.1777 (3.1232–3.2321)0.941<0.001Allometric +
Microchirus ocellatus275.215.412.04 (±2.24)2.1755.6728.34 (±11.51)0.0146 (0.0090–0.0240)3.0070 (2.8067–3.2074)0.974<0.001Isometric
Microchirus variegatus884.915.89.31 (±2.31)0.9939.4610.32 (±8.31)0.0084 (0.0055–0.0128)3.1033 (2.9134–3.2932)0.924<0.001Allometric +
Solea solea209.319.813.87 (±2.75)7.4981.9928.08 (±17.38)0.0090 (0.0054–0.0151)3.0161 (2.8189–3.2132)0.982<0.001Isometric
 
Sparidae
Boops boops4226.731.219.96 (±4.40)2.19346.7291.15 (±63.12)0.0051 (0.0046–0.0057)3.2137 (3.1789–3.2485)0.987<0.001Allometric +
Dentex canariensis2811.923.716.33 (±3.21)25.35172.7869.13 (±43.38)0.0214 (0.0150–0.0305)2.8567 (2.7290–2.9842)0.987<0.001Allometric −
Diplodus annularis6984.718.610.81 (±2.62)1.05113.7222.41 (±16.30)0.0069 (0.0064–0.0074)3.3140 (3.2849–3.3430)0.986<0.001Allometric +
Diplodus bellottii9234.720.010.55 (±2.82)1.10130.1620.88 (±18.51)0.0070 (0.0066–0.0073)3.2896 (3.2689–3.3103)0.991<0.001Allometric +
Diplodus vulgaris18110.622.818.31 (±2.60)15.36185.7298.52 (±39.93)0.0068 (0.0056–0.0083)3.2699 (3.2001–3.3396)0.979<0.001Allometric +
Pagellus acarne5812.322.617.60 (±2.08)20.13143.0969.94 (±25.60)0.0107 (0.0069–0.0167)3.0477 (2.8926–3.2029)0.965<0.001Allometric +
Pagellus bellottii5965.323.415.34 (±2.73)1.76196.0449.71 (±23.80)0.0091 (0.0084–0.0098)3.1171 (3.0875–3.1467)0.986<0.001Allometric +
Pagellus erythrinus4014.727.814.20 (±4.34)1.33195.9444.98 (±36.33)0.0117 (0.0107–0.0128)3.0155 (2.9810–3.0499)0.987<0.001Isometric
Pagrus auriga615.022.318.12 (±2.56)57.77192.16110.69 (±47.79)0.0142 (0.0044–0.0454)3.0760 (2.6735–3.4786)0.989<0.001Allometric +
Spondyliosoma cantharus2819.426.417.96 (±4.17)10.14347.6391.57 (±57.74)0.0101 (0.0086–0.0119)3.0967 (3.0413–3.1521)0.977<0.001Allometric +
 
Syngnathidae
Hippocampus hippocampus67.211.19.47 (±1.62)1.726.143.97 (±1.74)0.0148 (0.0002–0.9529)2.4595 (0.5570–4.3621)0.7040.023Allometric −
 
Torpedinidae
Torpedo marmorata9710.945.020.87 (±7.17)28.352288.71262.32 (±320.93)0.0322 (0.0258–0.0401)2.8698 (2.7963–2.9433)0.984<0.001Allometric −
 
Trachinidae
Echiichthys vipera429.927.716.91 (±3.09)6.02166.1732.03 (±24.63)0.0057 (0.0035–0.0094)3.0084 (2.8350–3.1818)0.968<0.001Isometric
Trachinus draco1565.725.016.43 (±3.30)1.05100.2329.15 (±14.87)0.0074 (0.0063–0.0086)2.9211 (2.8647–2.9775)0.985<0.001Allometric −
 
Triglidae
Chelidonichthys lastoviza1211.422.819.17 (±3.73)14.75141.1580.33 (±43.12)0.0050 (0.0008–0.0321)3.2378 (2.6009–3.8747)0.921<0.001Allometric +
Chelidonichthys lucerna244.134.014.66 (±10.01)0.74494.3170.93 (±117.70)0.0147 (0.0108–0.0200)2.8274 (2.7067–2.9480)0.990<0.001Allometric −
Chelidonichthys obscurus518.622.516.62 (±2.76)4.6787.5940.07 (±19.61)0.0055 (0.0038–0.0079)3.1343 (3.0046–3.2641)0.979<0.001Allometric +
Lepidotrigla cavillone2073.922.58.845 (±2.23)0.5493.299.00 (±9.17)0.0079 (0.0070–0.0090)3.1298 (3.0721–3.1874)0.982<0.001Allometric +
Lepidotrigla dieuzeidei1602.713.910.26 (±2.54)0.2430.0014.32 (±8.55)0.0076 (0.0067–0.0087)3.1594 (3.1036–3.2151)0.988<0.001Allometric +
Trigla lyra416.026.621.07 (±4.39)34.74169.8991.33 (±57.93)0.0054 (0.0006–0.0481)3.1603 (2.4390–3.8815)0.9920.003Allometric +
 
Uranoscopidae
Uranoscopus scaber814.724.521.00 (±3.17)49.01286.15170.04 (±77.61)0.0055 (0.0007–0.0446)3.3674 (2.6799–4.0550)0.953<0.001Allometric +
Table
Table 2. Number of studies available in FishBase [24] for nine species with a low number of individuals: Mean N: mean number of individuals of studies available in FishBase, Geometric Mean a and Mean b are values of parameter a and parameter b calculated by FishBase from all available studies. Pagrus auriga LWR was obtained by keeping the b-parameter constant at three (marked with *).
Table 2. Number of studies available in FishBase [24] for nine species with a low number of individuals: Mean N: mean number of individuals of studies available in FishBase, Geometric Mean a and Mean b are values of parameter a and parameter b calculated by FishBase from all available studies. Pagrus auriga LWR was obtained by keeping the b-parameter constant at three (marked with *).
SpeciesNumber of StudiesMean NGeometric Mean aMean b
Polymetme corythaeola190.00343.1160
Pagrus auriga110.01913.0000 *
Hippocampus hippocampus4490.00233.0000
Chlorophthalmus agassizi82260.00493.1100
Callionymus lyra112620.01662.6900
Trisopterus luscus143950.00813.1400
Trigla lyra157420.01102.9400
Uranoscopus scaber21950.01413.0500
Serranus cabrilla352430.01702.8600
Table
Table 3. Comparison of sample sizes and LWR parameters of the nine species with lowest sample size with other studies from adjacent study areas (southern Portugal waters). Key: n, number of specimens analyzed; a, intercept of the LWR; b, slope of the LWR.
Table 3. Comparison of sample sizes and LWR parameters of the nine species with lowest sample size with other studies from adjacent study areas (southern Portugal waters). Key: n, number of specimens analyzed; a, intercept of the LWR; b, slope of the LWR.
Our Work[32][33][34][59][36]
Speciesnabnabnabnabnabnab
Serranus cabrilla30.00253.53731710.000073372.6610510.07292.4100---950.02132.7760---
Trigla lyra40.00543.1603---150.02172.735070.008583.1380420.00563.1230---
Chlorophthalmus agassizi50.00333.2756------60.007862.9090------
Polymetme corythaeola50.00063.7040------90.003373.1160------
Pagrus auriga60.01423.0760---------------
Hippocampus hippocampus60.01482.4595------------90.00642.7300
Trisopterus luscus80.01902.8157220.000019212.9310560.00313.4400---17000.00893.0850---
Uranoscopus scaber80.00553.3674---------330.03052.8290---
Callionymus lyra120.00932.9038240.000841772.11702350.10532.1070310.056302.3100600.08002.1710240.00783.0200
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Rodríguez-García, C.; Castro-Gutiérrez, J.; Domínguez-Bustos, Á.R.; García-González, A.; Cabrera-Castro, R. Every Fish Counts: Challenging Length–Weight Relationship Bias in Discards. Fishes 2023, 8, 222. https://doi.org/10.3390/fishes8050222

AMA Style

Rodríguez-García C, Castro-Gutiérrez J, Domínguez-Bustos ÁR, García-González A, Cabrera-Castro R. Every Fish Counts: Challenging Length–Weight Relationship Bias in Discards. Fishes. 2023; 8(5):222. https://doi.org/10.3390/fishes8050222

Chicago/Turabian Style

Rodríguez-García, Carlos, Jairo Castro-Gutiérrez, Ángel Rafael Domínguez-Bustos, Alberto García-González, and Remedios Cabrera-Castro. 2023. "Every Fish Counts: Challenging Length–Weight Relationship Bias in Discards" Fishes 8, no. 5: 222. https://doi.org/10.3390/fishes8050222

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