A total amount of 13.145 kg (1134 individuals) of
P.
semisulcatus was used for this study. The biggest sample catch was found in July 2013 (160 females and 212 males) whereas the smallest sample (18 females and 16 males) was in winter (December 2013) with summer catch was accounted for over 48%. Similar studies indicated also that summer catch is more than other seasons
(Hettler and Chester, 1982; Costa et al., 2005; Castilho et al., 2008; Luchmann et al., 2008). The average CL was 38 mm for females and 36.7 mm for males, with highest values were found in July and the lowest in December 2013. These findings were also found in most of the fisheries studies in tropical and subtropical waters
(Farmer, 1986; Ye et al., 2003; Amin et al., 2009; Mehanna et al., 2012b; Abdul-Wahab, 2014). The overall sex ratio was estimated at 1:0.85 for males and females with 10% more males comparing to females along the study period. The monthly variations in sex ratio were not significant (P>0.05; Fig 2). Taking into account the length groups, males dominated the catch of the range 38-46 mm, while females dominated the large individual sizes (>48 mm). This indicates that females of the green tiger prawn are more exposed to commercial catch because of their bigger size compared to males. This observation is concordant with those of
Hosny (2007) on the same species and
Mehanna et al., (2012a) on the Indian prawn,
Fenneropenaeus indicus. Some researchers observed variations of length-weight relationship between the sexes for green tiger shrimp
(Maheswarudu et al., 2011) while other did not for green tiger shrimp
(Mohamed and El-Aiatt, 2012), chub
(Benzer, 2013), dark sleeper
(Haihua and Yanping, 2018) and sergestid shrimp
Amin et al. (2009) which is in accordance with our findings (Fig 3).
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.
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 (CL
50) 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).