Submitted19-10-2018|
Accepted28-01-2019|
First Online 24-05-2019|
ABSTRACT
INTRODUCTION
A variety of studies has been conducted on the P. semisulcatus biology and ecology in the Arabian Gulf (Siddeek, 1991; Siddeek et al., 1999; Abdulqader and Naylor, 1995; Ben Hasan et al., 2018). This shrimp species occurs mostly in shallow, soft-sediment and coastal habitats with early life stages preferring the sheltered productive habitats of the Arabian Gulf (Abdulqader, 1999; Bishop and Khan, 1999; Al-Husaini et al., 2015; Rabaoui et al., 2017). Nursery grounds of penaeid shrimp larvae was recently studied by Rabaoui et al., (2017) which enabled to identify all coastal nursery areas of the green tiger shrimp along the Saudi waters of the Arabian Gulf. Numerous studies have been conducted so far on the biology and ecology of green tiger prawn in the Arabian Gulf of Kuwait (Siddeek, 1991 and Ben Hasan et al., 2018) and Bahrain (Abdulqader and Naylor, 1995 and Abdulqader, 1999) as well as in the Red Sea coast of Yemen (Abdul-Wahab, 2014) and Saudi Arabia (Alsolami and Jastania, 2017) but no such studies has been conducted in the Arabian Gulf of Saudi Arabia. Recently, Rabaoui et al., (2017) reported the biology and ecology of Penaeus semisulcatus juveniles in the coast of Saudi Arabia. However, it is still needed to observe biology and ecology of adult P. semisulcatus for better management of this species in future. Therefore, the present study was conducted within this regard and it aims to enrich the knowledge on the life history traits and populations dynamics of P. semisulcatus in the western Arabian Gulf. The specific objectives of this work are therefore i) to describe the size structure and sex-ratio of the green tiger prawn population occurring in Dareen area, ii) to examine the gender variations of growth parameters of this crustacean species and iii) to determine the other major parameters of population dynamics such as total mortality, natural mortality and fishing mortality. These parameters will certainly enable to evaluate the shrimp fisheries in Dareen area and help to make necessary recommendations for the protection and sustainable management of this valuable marine resource.
MATERIALS AND METHODS
The carapace length (CL) and total weight (W) of all individuals collected were measured to the nearest 0.1 mm and 0.1 g using digital Vernier calipers and digital balance, respectively. CL was taken from the posterior edge of the orbit to the dorsal posterior edge of the carapace. The length frequency data of related samples were classified separately into 2-mm intervals. The length-weight relationship of Penaeus semisulcatus was determined for both males and females using the commonly used equation of King (2007):
Where,
W= Weight (g).
LC= Carapace length (mm).
a= Intercept.
b= Slope.
The growth parameters of the green tiger shrimp, asymptotic carapace length CL¥ and growth rate K, were determined from the carapace length-frequency data using FiSAT II and based on the von Bertalanffy growth function (VBGF):
CLt= Carapace length at age t.
CL¥= Asymptotic maximum carapace length.
K= Growth rate.
t0= Age when carapace length is zero (King, 2007).
Both total (Z) and natural (M) mortalities were estimated as well. Total mortality rate (Z) was estimated using the length-converted catch curve method, which was involved by the integration between ELEFAN II and Beverton and Holt’s (1956) formulas. M was estimated using Pauly’s (1980) empirical equation incorporated in FiSAT II:
The estimation of M and related parameters requires the growth parameters CL¥ and K obtained from VBGF. Since seawater temperature can have an effect on the abundance of shrimps and hence on the catch, the annual average sea temperature T was taken into consideration to assess the natural mortality; in this study T = 25°C. Fishing mortality F was computed according to the equation:
Where as shrimp exploited rate E was estimated as follows:
The probability of the mean length of the first capture Lc was calculated from length-converted catch curve using Pauly’s method (1984).
RESULTS AND DISCUSSION
Table 1 summarizes most of the biological parameters of P. semisulcatus reported so far from the Arabian Gulf and some adjacent areas. The estimated growth parameters for both sexes were calculated and the asymptotic carapace lengths CL¥ were found (female = 62 mm and male 51.50 mm). Growth rates K attained 1.10 yr-1 for females and 1.77 yr-1 for males (Fig 4). These findings were close to most of the previous studies on the life history of P. semisulcatus in the Arabian Gulf and adjacent areas (Mohammed et al., 1996; Hosny, 2007; Mehanna et al., 2012b; Mohammed and El-Aiatt, 2012; Rabaoui et al., 2017). A significant difference for both sexes was found with the only in the study conducted in Dareen by Ye et al., (2003) who found that CL¥ and K for males and females were found to be 27.8 mm and 38.32 mm and 2.53 y-1 and 3.27 y-1, respectively. It appears that the difference of the growth parameters of the same research area might be attributed to some changes of trophic and environment conditions occurred in ten years period.
Table 1: Summary of life history parameters recorded with the green tiger, Penaeus semisulcatus, in the Arabian Gulf and other middle-east areas (Arabian Sea and Mediterranean Sea). M: Males; F: Females; CL¥: Asymptotic carapace length (mm), K: Growth rate (y-1); Z: Total mortality (y-1); M: Natural mortality (y-1); F: Fishing mortality (y-1); E: Exploitation rate (y-1).
Total mortality coefficients Z were close for both sexes; 3.37 yr-1 and 4.65 yr-1 for females and males respectively (Fig 5 and Table 1). Estimations of natural mortality M were also calculated for females (1.47 yr-1) and males (2.12 yr-1). The range of Z values recorded in the previous studies was (3.24-7.84 y-1) for males and (4.7-9.67 y-1) for females while the range values for M were (1.05-2.5 y-1) for males and (1.1-2.4 y-1) for females. This study records Z values were found close to the lowest values of the Z range whereas M values illustrated consistency with most of the values reported by other authors in Table 1. Both fishing mortality (F) and exploitation rate (E) were calculated and results showed a marginal variations between males and females for F values but not for E values (Fig 5). F values calculated for both sexes were found to be the lowest values compared to previous records, female was 1.90 yr-1 and male was 2.53 yr-1. Exploitation rate ‘E’ were estimated at 0.56 yr-1 and 0.54 yr-1 for females and males respectively. In contrast with our findings, most of the studies on the population dynamics of P. semisulcatus in the Arabian Gulf recorded higher exploitation rate (E) values but similarities was showed for fishing mortality (Table 1). The lengths at first capture Lc (CL50) were estimated at 42.2 mm for females and 41.52 mm for males (Fig 6). These findings of high Lc contradict (Mehanna et al., 2012a, Mehanna et al., 2012b and Mohammed and El-Aiatt, 2012).
CONCLUSION
ACKNOWLEDGEMENT
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