International Scholarly Research Notices

International Scholarly Research Notices / 2013 / Article

Research Article | Open Access

Volume 2013 |Article ID 127287 | 6 pages | https://doi.org/10.1155/2013/127287

Population Dynamics of Horse Mackerel (Trachurus Mediterraneus Ponticus) in the Bulgarian Black Sea Coast

Academic Editor: C. P. Wheater
Received22 Jan 2013
Accepted17 Feb 2013
Published19 Mar 2013

Abstract

The horse mackerel Trachurus mediterraneus is a commercially important pelagic fish species in the Black Sea fishery. The present investigation was carried out between May and December 2010 along the Bulgarian coast of the Black Sea. Population parameters of horse mackerel from the trawl and fishing nets catches were estimated from length frequency data, by using ELEFAN-I computer program. The ELEFAN-I analysis gave the following Von Bertalanffy Growth Function (VBGF) parameters: the asymptotic length  cm, growth coefficient value was , and the hypothetical age at which length is zero was . Based on these growth parameters, the total mortality coefficient () during the study period was estimated to be 2.99. The estimated value for natural mortality () was 1.08; hence, the fishing mortality coefficient () was 1.91. The estimated value for the exploitation rate () using the length converted catch curve was 0.64. The estimated sizes of T. mediterraneus at 25, 50, and 75 percent probabilities of capture were 16.80 cm, 18.72 cm, and 20.64 cm, respectively.

1. Introduction

Family Carangidae in the Black Sea is represented by Trachurus trachurus and Trachurus mediterraneus ponticus. In the Bulgarian Black Sea territorial waters, only Trachurus mediterraneus ponticus is present. Entering of separate Trachurus trachurus specimens to the Black Sea from the Sea of Marmara is a quite rare phenomenon [1]. The systematic situation of the Black Sea mackerel was carefully examined by [24]. The same author stated that in the Black Sea, the species was represented by four local subpopulations: the south western (Bosporic), the northern (Crimean), the eastern (Caucasian) and the southern (Anatolian) each one with its own biological characteristics such as wintering grounds, fat content, spawning patterns, age composition, growth rate, feeding patterns.

On the basis of investigation carried out by [5, 6] on size composition and also tagging experiments of horse mackerel caught off the Bulgarian coast, they concluded that in the Black Sea, two subpopulations occur that belong to the small size-type of Trachurus mediterraneus ponticus, the eastern and western ones, respectively. According to the same authors, the Black Sea horse mackerel represents a single population, as the environmental conditions are almost one and the same in the whole inhabited area and there exists no positive evidence for the occurrence of two distinct subpopulations differing substantially in their biological parameters. Other authors using electrophoresis methods assume that no difference at species level can be found between T. mediterraneus ponticus and T. m. mediterraneus [7]. For this reason according to [8] the large size type occurrence can be explained as a result of heterosis effect between the aforementioned subspecies. This type being sterile does not produce further offspring and becomes extinct after completing its life span [9]. Examination of age and growth is very important in ichthyologic investigations, because fish growth is one of the four main factors (recruitment, natural mortality coefficient, and fishing mortality coefficient) determining stock condition [10]. Population parameters and growth of horse mackerel were investigated by [9, 11, 12]. Population parameters such as asymptotic length and growth coefficient , mortality (natural and fishing) rate, and exploitation level were studied with the major objective of rational management and resource conservation [13, 14].

The goal of the present paper is to establish the population parameters of horse mackerel and to determine its natural mortality coefficient value for the investigated period.

2. Materials and Methods

Length frequency data of T. mediterraneus were collected from trawl and fishing net catches in the Bulgarian Black Sea territorial waters (Figure 1) during the period May 2010 to December 2010. A total of 3400 fish were collected throughout the study period.

Monthly length frequency distributions of T. mediterraneus for each month were analyzed using the Compleat ELEFAN I computer program [15]. The program was also used to estimate the parameters of the Von Bertalanffy growth equation: where

For the seasonal Von Bertalanffy Growth Function (VBGF), is the length at time , the asymptotic total length (cm), the growth coefficient (year−1), and the age of fish at zero length (year). The ELEFAN I estimates only two of the three growth parameters ( and ); thus, we computed the third parameter () by the empirical equation for growth fitting: (see [16]). The growth performance of T. mediterraneus was compared using the index (see [17]). Longevity was calculated from the equation [18].

The instantaneous total mortality coefficient () was estimated using the length converted catch curve method which has been incorporated into the Compleat ELEFAN I computer program [15]. Natural mortality () was estimated by empirical formula; that is, (see [19]), where is expressed in cm (total length) and (°C) is the mean annual environmental temperature (it was taken at 14°C). The exploitation rate () was computed using expression (see [19]). The recruitment pattern was also derived using the Compleat ELEFAN I computer program [15]. The probability of capture was estimated by backwards extrapolation of the descending limb of the length-converted catch curve. A selectivity curve was generated using linear regression fitted to the ascending data points from a plot of the probability of capture against length, which was used to derive values of the lengths at capture at probabilities of 0.25 (), 0.5 (), and 0.75 (). The relative yield-per-recruit () was estimated using the knife-edge method of Beverton and Holt model (1957) [20] as follows where

3. Results and Discussion

The length range obtained in the horse mackerel was 8 to 19 cm, the majority of the catch being between 12 and 16 cm. The length frequency distribution of T. mediterraneus for the study period is shown in Figure 2. The ELEFAN-I analysis gave the following VBGF parameters:  cm, , and . The Powell-Wetherall plots are shown in Figure 3. The corresponding estimates of and for T. mediterraneus are 19.73 cm and 2.35 respectively. This additional estimate of is slightly smaller than the one estimated through ELEFAN-I.

Total mortality based on length converted catch curve gave a value of (intercept-a: 15.020, slope-b: −2.941, correlation coefficient : −0.9985, : 0.9969, : 3, confidence interval of : −5.009–0.873) (Figure 4). Our estimated natural mortality coefficient was = 1.08. The reliability of the estimated was ascertained using the ratio, which has been reported to be within the range of 1.12–2.5 for most fishes [21]. The ratio () in this study falls within the acceptable defined range. The value for exploitation rate () calculated in the present study was . This suggests that during the study period, the stock of T. mediterraneus in the investigated area is under high fishing pressure. The values for instantaneous total mortality coefficient (), natural mortality coefficient (), fishing mortality coefficient (), and the exploitation rate () calculated were 2.99, 1.08, 1.91, and 0.64, respectively. The mean length at first capture, or , was 18.72 cm (TL), and the lengths at capture at probabilities of 0.25 () and 0.75 () were 16.80 and 20.64 cm (TL), respectively (Figure 5). The relative yield-per-recruit () was determined as a function of (Figure 6). The exploitation rate of population obtained in this study exceeded the maximum allowable limit based on yield-per-recruit calculation () which was 0.38 year-1. Results of the analysis of the recruitment pattern of T. mediterraneus during theinvestigation are shown in Figure 7. The recruitment pattern showed one annual pulse of recruitment for horse mackerel (around June). This pulse produced 23.86% of the recruits. Our asymptotic length value compares favourably with those obtained by others researchers (Table 1). Horse mackerel is a species with a relatively long lifespan, but at the present study age groups of 5 and 6 were completely absent. If one assumes that longevity () equals , we obtain approximately as 4.7 years, which corresponds not well with other results (based on otolith readings) obtained from Bulgarian coast (Table 1). Growth performance index () derived for this study is higher than values estimated by others who used otolith readings. When compared with the otholith-based studies, this study shows relatively rapid growth, that is, higher parameter. The otoliths of T. mediterraneus were difficult to interpret similar to T. trachurus when age determination for older individuals is particularly imprecise [2226]. However, the otoliths of T. mediterraneus presented problems specific to assigning ages to younger individuals related to interpreting the first true annulus [27]. Misidentification of annual rings may lead to an underestimation of the parameter and overestimation of , resulting in lower values [28]. The growth coefficient () value from this study was determined to be high (0.64 per year) compared to the low value estimated by other investigations. This may probably be due to high mean annual water temperature in Bulgarian Black Sea waters during the summer, and partly as a result of dominance of 2-year-old fishes in the catches. Sea surface temperature showed cooperatively high values within the framework of 28–31°C, [29], Table 2. Sudden shifts in temperature can have disastrous effects on fish populations (e.g., thermal stress) [30]. Furthermore, fish growing in different water bodies have different values. It is observed that value is higher in young fish (1-year-old), [30]. ratio is the measure of validity of mortality estimate, and it is found to be 1.69; it is within the range of 1.5 to 2.5 recommended by [21]. The hypothetical age at which length is zero (to) values was negative. This result compared favorably with the general observation made by [16]. Many growth studies use methods that do not provide realistic estimates of , particularly in conditions where the sample sizes and ranges are not representative or smaller specimens are absent in the sample [31].


(cm) Method Locality

19.250.35−0.598.571Otolith2.113Bulgarian coast [9]
19.990.31−0.499.671Otolith2.093Bulgarian coast [32]
19.990.34−0.468.821Otolith2.134Bulgarian coast [31]
20.000.24−0.9812.51Otolith1.975Bulgarian coast [31]
19.450.23−0.9313.041Otolith2.031Bulgarian coast [31]
19.990.33−0.299.091Otolith2.077Bulgarian coast [31]
20.000.28−0.8110.71Otolith1.739Bulgarian coast [31]
17.550.45−0.196.661Otolith2.142Bulgarian coast [33]
18.780.34−0.828.821Otolith2.079Bulgarian coast [34]
19.950.64−0.554.71ELEFAN I2.406Bulgarian coast2

1Based on the Taylor’s [17] assumption that .
2Present study.

StationRateAugust, 2010Digression

Shabla21.927.88+5.98
Varna22.428.17+5.77
Bourgas23.828.48+4.68

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Copyright © 2013 Maria Yankova. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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