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Analysis of Diet and Biochemical Composition of Nile Tilapia (O. niloticus) from Tekeze Reservoir and Lake Hashenge, Ethiopia | OMICS International
ISSN: 2332-2608
Journal of Fisheries & Livestock Production
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Analysis of Diet and Biochemical Composition of Nile Tilapia (O. niloticus) from Tekeze Reservoir and Lake Hashenge, Ethiopia

Natarajan P1 , Tesfay Z1 and Teame T2*

1Ambo University, Department of Biology, Ambo, Ethiopia

2Tigray Agricultural Research Institute (TARI), Mekelle, Ethiopia

*Corresponding Author:
Teame T
Tigray Agricultural Research Institute (TARI)
Mekelle, Ethiopia
Tel: (+251) 34 440 2801
E-mail: [email protected]

Received Date: December 24, 2015; Accepted Date: February 22, 2016; Published Date: March 15, 2016

Citation: Natarajan P, Tesfay Z, Teame T (2016) Analysis of Diet and Biochemical Composition of Nile Tilapia (O. niloticus) from Tekeze Reservoir and Lake Hashenge, Ethiopia. J Fisheries Livest Prod 4:172. doi:10.4172/2332-2608.1000172

Copyright: © 2016 Natarajan P, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

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Abstract

A study was conducted to investigate the biochemical composition and diet type of Nile tilapia (Oreochromis niloticus) collected from Tekeze reservoir and Lake Hashenge, Ethiopia between December, 2014 and March, 2015. A total 100 fishes were collected from the two water bodies 50 from each by gill nets of 10, 12 and 14 cm stretched mesh size. The stomach contents were analyzed using frequency of occurrence and numerical methods. The food items in the stomach covered a wide variety, ranging from various types of phytoplankton to zooplankton and macrophytes. The food composition of O. niloticus showed that, there was variation within the fish species across the study areas. The major food items in terms of frequency of occurrence collected from the stomach of O. niloticus in Tekeze reservoir were Pediastrum (68.85%), Microcystis (60.45%), Peridinium (59.70%) and Staurastrum (41.56%) and from Lake Hashenge were Daphnia (63.12%), Copepods spp (56.90%), Nauplii (52.11%), and Macrophytes (45.56%).The contribution of zooplankton (Daphnia, copepods and Nauplii) was higher in case of Lake Hashenge but Pediastrum spp., Microcysts spp. and Peridinium spp. which were phytoplankton type were the dominant food items of the fish in Tekeze Reservoir. The fish species from the water bodies were transported to the laboratory for the estimation of biochemical composition such as crude protein, crude fat, moisture, ash, carbohydrate and some minerals. The chemical analysis revealed that the crude protein content of the fish species collected from the two water bodies were ranged from 15.31-16.32% of wet weight. The crude fat content and ash ranged between 1.20 and 2.45, 0.81 and 1.16% of the wet weight, correspondingly. The concentrations of some elements were significantly different (P<0.05) between sexes and location were the fish was collected. The analyzed mineral content in each species was in the order K>Na>Ca>Mg>P>Fe>Zn>Cu>Mn. This investigation is an important measure towards the data needed to create information of the relationship between food type and biochemical composition. As the present study revealed that the fish species are good sources proteins and fats, there is need to investigate in detail the types of amino acids and fatty acids of the sampled fishes.

Keywords

Daphnia; Food items; Lake Hashenge; Nile tilapia; proximate composition

Introduction

Nile tilapia (Oreochromis niloticus) [1] is widely distributed in tropical and subtropical Africa in the Volta, Gambia, Senegal, Niger Rivers and the Nile River basin and is native to Lakes Chad, Tanganyika, Albert, Edward, and Kivu [2,3].

Ethiopia has relatively large area of inland water bodies that contain diverse aquatic ecosystems giving great scientific interest and economic importance. There are different economically and ecologically important species of fish that are found in these water bodies. Adult O. niloticus have a high degree of plasticity and opportunism in their feeding behaviour and are hence classified as omnivorous [4]. They are capable of consuming a wide variety of feed items including phytoplankton, zooplankton detritus and macrophyts [5]. O. niloticus is one of the most known members of the tropical and subtropical freshwater fishes. It is recommended by the FAO as a culture fish species because of its importance in aquaculture and its capability in contributing to the increased production of animal protein in the world. Therefore, it is now globally distributed and has become very popular through the advances in the cultivation techniques.

In Ethiopia it is widely distributed in the lakes, rivers, reservoirs and swamps which contribute about 60% of total landings of fish [6]. It is reported that O. niloticus from Lakes of Hawassa, Ziway and Chamo mainly feeds on phytoplankton, macrophytes and detritus [7-9].

Fish and shell fish are important animal protein and have been widely accepted as a good source of protein and other elements for the maintenance of healthy body [10]. Most developing countries are located in tropical or sub-tropical areas, and fish is a vital component of food security for these countries. Rivers and lakes in these countries were more accessible and kinder sources of fish, and also carry over 40% of the world’s known fish species [11]. A recent study found evidence that, contrary to popular belief, size dimorphism between the sex’s results from differential food conversion efficiency rather than differential amounts of food consumed. Hence, although males and females eat equal amounts of food, males tend to grow larger due to a higher efficiency of converting food to energy [12].

The body composition of fish has recently received attention in studies on nutrition, genetics, and health [13] because of the increasing interest in the quality and safety of fish products [14]. Body composition is an important aspect of nutritional quality [15] and affects the nutritional value and consumption quality of fish [16]. Fish fillet consists of several components, such as moisture, protein, fats, vitamins and minerals, all of which contribute to the overall meat composition. Fish body composition is affected by both exogenous and endogenous factors [17]. Exogenous factors that affect fish body composition include the diet of the fish (composition, frequency) and the environment in which it is found (salinity, temperature). The main exogenous factor affecting proximate composition is diet. Various studies have examined the effects of temperature, light, salinity, pH and oxygen concentration on the proximate composition of fish but these factors would seem to have very limited effects. On the other hand, endogenous factors are genetic and linked to the life stage, age, size, sex and anatomical position in the fish [17]. These endogenous factors govern the majority of principles that determines the composition of fish [17]. Proximate composition of body muscles of Puntius stigma (male and female) analyzed shows that the moisture content was found to be higher in female, while protein, fat, ash, carbohydrate and minerals contents were higher in male. Moreover, different sexes were observed to have varying chemical composition [18].

Literature on biochemical analysis of O. niloticus includes those of [12,19-24]. None of these studies however reports on the biochemical analysis of the species collected from two different water bodies which the present study is designed.

Materials and Methods

Description of study areas

Tekeze reservoir: Tekeze reservoir is a hydropower reservoir constructed on 2009 over the Tekeze River. Tekeze River is a major river in Ethiopia and it is a Nile tributary. Tekeze reservoir is with a maximum length of 75 km and maximum width of 6 km, and covering an area of about 160.4 km2. According to National Statistics of Agency (NSA) (2008) Tekeze River is 608 kilom long. Mana, Tsilare, Seletsa, Avera and Ariqua rivers are the main tributaries of the Tekeze River joined in to the reservoir. The canyon which it has created is the deepest in Africa and one of the deepest in the world, at some points having a depth of over 2000 m. Tekeze River originates in the central Ethiopian Highlands near Mount Qachen within Lasta, at 14°11 N 37°31.7 E and 14.18.3°N 37.52 83°E. The reservoir is located at an elevation of 1107 m above sea level. It is approximately 155 km from Mekelle city. The capacity of the reservoir is about 9.293 billion m3 (9.293 km2) of water. Although Tekeze reservoir is constructed entirely in Tigray region, the water of the reservoir is shared by Amhara region. The reservoir is communal for five districts (Tanqua Abergelle district from Tigray region and Abergelle, Zikuala, Sahla and Tselemti districts from Amhara region). The main aim of constructing of the Reservoir was to produce electricity, but the reservoir fisheries were later recognized as a significant socio-economic importance to Tigray and Amhara people. The reservoir also facilitates the transportation of goods and passengers and the provision of services for Tigray and Amhara people found on both sides of the reservoir.

Lake Hashenge: In addition to Tekeze Reservoir, the study was extended in Lake Hashenge. Lake Hashenge is one of the highland lakes of Ethiopia found in Tigray region. It is located in Ofla district Southern Tigray Administrative Zone, about 628 km North of Addis Ababa and about 152 km South of Mekelle and 8 km North of Korem town in the coordinates of 12°34′50″N and 39°30′00″E and at an elevation of 2440 m above sea level. It is one of the crater lakes in the country and not associated with the East African rift system; instead it is the result of volcanism. This lake has no outlet to drain its water. Hashenge Lake is 5 km long and 4 km wide, with a surface area of 20 km2 and maximum depth of 25 m. Its drainage area is 129 km2.

Methods

Physico-chemical param of the water

Physico-chemical param of the water like temperature, pH, conductivity, TDS, dissolved oxygen and transparency were monitored monthly in the field using the methods as described in APHA (1998). Temperature, DO, Conductivity and TDS were measured using portable digital water quality multi m model CO 411 and pH was measured with portable pH m model CP 401.

Food analysis

100 matured fishes were collected from each water body for stomach content analysis. The stomach content analysis was carried out in the laboratory by using preserved stomach contents in 5% formalin. The stomach contents were examined using dissection microscope (Leica MS5) and also compound microscope (Leica DME).

Frequency occurrence of food items

The number of stomach samples contains one or more of a given food item was expressed as a percentage of all non-empty stomachs examined. The proportion of the population that feeds on particular food item was estimated and the frequency of occurrence was calculated [25,26].

Fi = 100* ni/n

Where, Fi: Frequency of occurrence of the i food item in the sample

ni: Number of stomachs in which the i item is found

n: Total number of stomachs with food in the sample

Proximate Analysis

A total of 80 fishes, 20 from each sex and each water body were examined for proximate composition and mineral contents. 20 males and 20 females were collected each water body (from Tekeze reservoir and Lake Hashenge) landing sites. 50 gm of dorsal fillet were taken from each fish and make a composite to each sample. The proximate composition and mineral content were analyzed based on standard procedures of AOAC (2000). The moisture content of the fillet of the fish was determined by oven drying at 105°C overnight, ash by incineration of 2 g of each sample in a muffle furnace at 600°C for 2 h, crude protein by the Micro-Kjeldahl method then (N x 6.25), crude fat was extracted with n-hexane in a soxhlet extractor, while available carbohydrate was calculated by difference. The result of the proximate composition were analyzed in triplicate and reported as mean on percentage wet weight basis.

Mineral Analysis

The mineral content (Calcium, Potassium and Sodium) were determined using Flame photometric method (Jenway Digital Flame Photom: PFP7 model). Phosphorus was estimated using Vanadomolybdate colorimetric method while other mineral elements such as Iron, Zinc, Manganese, Magnesium and Copper were determined using Atomic Absorption Spectrophotometric method. The content of the mineral were done in triplicate and reported as mean mineral content in mg/kg of dry matter.

Data Analysis

The data collected were stored in a database created in MS Excel, a variety of subjects were analyzed by combining quantitative and qualitative social scientific methods. One-way ANOVA model was used to evaluate the association of proximate composition and mineral contents with the fish species using SAS software (SAS version 9.0).

Results and Discussion

Physico-chemical param of Tekeze reservoir and lake Hashenge

The values of physico-chemical properties of water are presented in Table 1. Most of the values of water quality param during the study period were in the optimum condition for fish production except for the low dissolved oxygen value observed in the month of January in Tekeze reservoir. The mean transparency, pH, and temperature were 189 ± 32.5 cm, 8.03 ± 0.2, 26.05 ± 1.2°C and 62.00 ± 11.8 cm, 7.71 ± 0.2, 19.77 ± 0.6°C in Tekeze reservoir and Lake Hashenge respectively. The conductivity of the two water bodies showed the mean value of 462 ± 26.4 uS/cm for Tekeze reservoir and 537.75 ± 9.5 uS/cm for Lake Hashenge. TDS showed a mean value of 1.53 ± 0.2 g/L and 8.99 ± 0.3 g/L for Tekeze and Lake Hashenge respectively. The mean Dissolved Oxygen was 4.25 ± 2.2 in Tekeze reservoir and it varied between 1.03 mg/L (January) and 5.86 mg/L (March). In Lake Hashenge, the dissolved oxygen ranged from 4.97 in February to 5.88 mg/L in December with a mean value of 5.33 ± 0.4 mg/L.

Water body
Physico-chemical
 parameters
Tekeze Reservoir Lake Hashenge
                           Months                                          Months
  Dec Jan Feb Mar Mean ± SD Dec Jan Feb Mar Mean ± SD
DO (mg/L) 5.02 1.03 5.1 5.86 4.25 ± 2.2 5.88 5.46 4.97 5.02 5.33 ± 0.4
pH 7.77 8.19 8.05 8.09 8.03 ± 0.2 7.92 7.56 7.8 7.54 7.71 ± 0.2
Temperature (°C) 25.78 24.5 26.8 27.13 26.05 ± 1.2 18.9 19.82 20.05 20.32 19.77 ± 0.6
Conductivity (uS/cm) 362 356 349 381 362 ± 26.4 547 535 544 525 537.75 ± 9.5
TDS (g/L) 1.37 1.79 1.52 1.43 1.53 ± 0.2 9.11 8.11 9.34 8.78 8.99 ± 0.3
Transparency (cm) 207 145 185 219 189 ± 32.5 76 55 50 67 62 ± 11.8

Table 1: Monthly Physico- chemical parameters of Tekeze reservoir and Lake Hashenge water.

The low level of DO (1.03 mg/L) in Tekeze reservoir may be due to the turnover of the lake. During that time there was fish mortality due to dissolved oxygen depletion (personal observation, 2015). The mean range of values of physico-chemical factors of the reservoir and the lake are within limit for fish tolerance, survival and production and indicated good quality of water in the study areas according to APHA (1998) [27]. The desirable level of DO, temperature and pH for optimum growth of fish are >5 mg/L, 26-30°C and 6.5-8 respectively [28]. This study also shows that the water param were in the optimum range except for DO in Tekeze reservoir in January month which were very low and the mean temperature of Lake Hashenge seems low for tilapia growth. This may lead to the less abundance of Nile Tilapia in the lake.

Diet composition of Nile tilapia (O. niloticus)

The diet of O. niloticus in Tekeze reservoir is composed of phytoplankton, detritus, macrophytes zooplankton and silt. The brown color and rough texture of the stomach contents indicate that the fish fed more on benthic plant material and mud at the water sediment interface than on suspended particles, which was in line with the report of Fryer and Iles, (1972). Since the productivity of the reservoir is low because of high light attenuation, O. niloticus has to rely on any plant material available in the reservoir, which is why detritus constitutes the bulk of its diet. The most abundance food items identified from the stomach of O. niloticus from Tekeze reservoir were Pediastrum (68.85%), Microsystis (60.45%) and Peridinium (59.70%), whereas the diet type of O. niloticus collected from Lake Hashenge were Daphnia (63.12%), Copepods (56.90%) and Nuaplii (52.11%) (Table 2). The analysis showed that the diet composition of O. niloticus from Tekeze reservoir were mostly phytoplankton and in case of Lake Hashenge zooplankton were the most abundance food items. The types of food items found in the stomachs of O. niloticus collected from Tekeze reservoir were difference from the stomach content of fish collected from Lake Hashenge in type and abundance. In addition to zooplankton and phytoplankton, detritus and aquatic macrophytes were also considerable importance in the diet of O. niloticus due to some nutritional benefits. Several authors have provided similar interpretations about the importance of detritus and macrophyte in different parts of Africa [2,29]. In the present study, proportion of phytoplankton was higher from the stomach of O. niloticus collected from Tekeze reservoir. The stomach content proportion of the fish collect from Lake Hashenge was higher in zooplankton than in phytoplankton. The composition differences and relative contribution of food items may partly explained by difference in habitat occupied of the fish.

Water body
Tekeze reservoir Lake Hashenge
  Food items Frequency occurrence   Food items Frequency occurrence
Number percentage Number percentage
Pediastrumspp. 41 68.85 Pediastrumspp. 15 10.88
Peridiniumspp. 23 59.7 Spirogyra spp. 3 1.24
selenastrumspp. 35 40.12 Staurastrumspp. 6 5.16
Melosiraspp. 27 39.45 Anabaena spp. 14 12.23
Staurastrumspp. 20 41.56 Microcystisspp. 21 32.13
Eudorinaspp. 11 34.38 Peridiniumspp. 23 30.56
Microcystisspp. 32 60.45 Daphnia spp. 54 63.12
Euglena spp. 7 41.18 Diaphanosomaspp. 39 44.67
Scenedesmusspp. 13 31.71 Copepods spp. 51 56.9
Calanoidspp. 7 20 Naupliispp. 47 52.11
Copepods spp. 5 12.42 Keratellaspp. 23 31.95
Keratellaspp. 8 16.54 Naviculaspp. 24 34.7
Moinaspp. 9 28.57 Nitzschiaspp. 20 33.21
Copepod spp. 12 27.78 Aulacoseiraspp. 18 27.77
Nauppliispp. 4 8.56 Macrophyte 42 45.56
Fish eggs 8 5.38 Attached algae 38 40.22
Fish scale 10 18.75 Insects 28 36.09
Dertitus 22 31.67 Fish scale 17 22.06
Insects 20 6.45 Fish eggs 8 18.41
Macrophyte 3 8.61 Debris 30 40.23

Table 2: Frequency of occurrence of different food items consumed by O. niloticus in Tekeze reservoir and Lake Hashenge.

Proximate composition of Nile tilapia

The proximate composition of the muscle of O. niloticus was estimated and presented in Table 3. Data on moisture, crude protein, crude fat, ash and carbohydrate content were expressed as percentage composition. The proximate composition of the fillet of O.niloticus collected from the two water bodies showed significant difference (P<0.05). This variation may be many possible factors such as size, sex, maturity of samples and sampling locations that can affect the differences in proximate composition of fish [30].

Proximate Nile Tilapia collected from Hashenge Nile Tilapia collected from Tekeze
Composition Male Female Male Female
Moisture 77.69 ± 0.39b 77.55 ± 0.22b 79.83 ± 0.34a 79.11 ± 0.14a
Ash 0.81 ±  0.08b 0.97 ±  0.11ab 1.05 ±  0.09a 1.16 ±  0.07a
Crude fat 2.45 ± 0.18a 2.35 ± 0.09a 1.27 ± 0.15b 1.41 ± 0.13b
Crude protein 16.13 ± 0.29a 16.32 ± 0.30a 15.32 ± 0.28b 15.77 ± 0.13ab
Carbohydrate 1.61 ± 0.42a 1.22 ± 0.14a 1.46 ± 0.21a 1.36 ± 0.17a

Table 3: Proximate composition of fish species (% wet weight).

Sex has no significant (P>0.05) effect in the proximate composition (moisture, ash, crude fat, crude protein and carbohydrate) of the fish species collected from the two water bodies. Moisture content among the fish species was observed between 77.55 and 79.83%. The results showed that there was significant difference (P<0.05) in the moisture content of the fish species collected from the two water bodies. The moisture content of male fishes was higher than the female fishes within the species even though they were not statistically significant (P>0.05). This result was in line with the results of Edirisinghe, et al [30]. Results obtained from the moisture analysis of the fish species collected from the two water bodies showed that the fish samples, O. niloticus from Tekeze reservoir, which was locally harvested in large quantities had the highest percentage of moisture content (79.83 ± 0.34 for male and 79.11 ± 0.14% for female) than O. niloticus from Lake Hashenge had the lowest moisture content (77.55 ± 0.22% for female and 77.69 ± 0.39% for male). This shows that, O.niloticus from Hashenge have concentrated nutrients than O. niloticus from Tekeze Reservoir which agreed with the report of Egbal et al. [31] between C. lazera and O. niloticus. Zmijewski et al [32] found a reverse correlation between the fat and water content to be common among fish species, and it was in line with the present result in some extent. Job et al. [1] reported that the moisture content of O. niloticus was 80.90% which is almost similar with the current report (77.55%-79.83%). According to FAO [33] moisture and lipid contents in fish fillets are inversely related. The percentage range of the moisture content of fish muscle was within the acceptable level (60%-80%) in all the samples which could be due to the stable water levels in the environmental location where the fish were collected [34]. In this study, the moisture content of male fish was higher than the female fish, and this may be due to the higher level of organic materials in females [35]. In connection with this work different researchers have reported that moisture content of male fish was higher than the female fish [36,37].

The content of crude protein of the fish species collected from the two water bodies ranged between 15.32 and 16.32%, which was in the range of permissible limit (15-28%) for fish and fisheries products, and the protein content of female O. niloticus from Hashenge was higher (16.32 ± 0.30%) and male O.niloticus from Tekeze reservoir showed significantly lower (p<0.05) protein content (15.32 ± 0.28%) [38]. Alemu et al. [23] reported that the protein content of male and female O. niloticus collected from Zeway was 14.5 and 14.6% respectively which was lower than the result of present study. Higher crude fat and protein content in O. niloticus collected from Lake Hashenge may associate with the presence of abundance zooplankton food items of the fish in the lake then in the reservoir. El-Serafy et al. [20] reported that feeding conditions has association with proximate composition content. Among the male and female O. niloticus collected from Tekeze reservoir, there was significantly higher protein (P<0.05) in male as shown in (Table 1). In connection with this De Silva et al. [39] reported that the protein content of O. niloticus collected from Kattakaduwa reservoir was significantly higher (P<0.05) in male than female. In contrast this was not true for the fish collected from Lake Hashenge. The values of crude protein were higher from the fish species collected from Lake Hashenge. This may be due to the diet composition of the fish as shown from the stomach of the fish collected from Lake Hashenge was mostly it was zooplankton, in case of Tekeze reservoir it as phytoplankton. This result was in line with Zenebe [40].

The crude fat content values showed significant difference (p<0.05) within the species with male O. niloticus from Hashenge had the highest value (2.45%) and male O.niloticus from Tekeze had the lowest (1.27%). More similar reports are available from the studies of various researchers.

The crude fat content of O. niloticus was reported in the range of 0.7 to 8.5% Visentainer et al. [41] and the value of this investigation was within this range. The crude fat content of O. niloticus collected from Lake Hashenge was significantly higher (P<0.05) than the value found from Tekeze reservoir within the species. This may be due to the water temperature difference between the two water bodies and the type of diet of the fish. In this connection, Favalora et al. [42] and Flos et al. [43] reported that, the quality of fish is affected by param such as feed type, level of dietary intake and growth. A number of factors influence the concentration of lipids in tilapia such as water temperature, stage of life, environmental salinity, food type and species Fabiola & Martha [44] and diet of the fish [40].

Based on the fat content O. niloticus from both water bodies was distinguished as lean fish as fat contents of these fishes were lower than 5% by weight [45]. The low concentrations of fat in the muscles of the fresh water species could be due to poor storage mechanism and the use of fat reserves during spawning activities [46].

The ash content ranged between 0.81% and 1.16% in the sampled fishes. This indicates that, the species is a good source of minerals such as Calcium, Potassium, Zinc, Iron and Magnesium since ash is a measure of the mineral content of food item and the inorganic residue that remains after the organic matter has been burnt off. The highest ash content was recorded from O. niloticus collected from Tekeze reservoir (1.16% in male) and lowest value from female O. niloticus from Lake Hashenge (0.81%). Similar values of ash have also been reported by Alemu et al. [23] for O. niloticus Lake Ziway. Results of Job et al. [1] are in disagreement with the present results in the ash content of O. niloticus which was lower (0.57%).

The carbohydrate content ranged between 1.22% for female O.niloticus and 1.61% for male O. niloticus from Tekeze Reservoir. The results observed for carbohydrate showed no significant difference (p > 0.05) within fish species collected from the two water bodies (Table 3).

The biochemical composition of tilapia varies considerably depending on growing conditions (temperature, dissolved oxygen, pH, salinity, turbidity, altitude, light or luminosity, among others factors) and in terms of certain characteristics of the species (age, environment and season) [44].

Minerals analysis

Concentrations of mineral contents of O. niloticus collected from the two water bodies are presented in Table 4. A total of 9 macro and micro elements (Ca, Mg, Na, K, P, Zn, Cu, Fe and Mn) were considered for the investigation and the contents observed within the fish species were statistically different (P<0.05).

Mineral contents Nile tilapia from Hashenge Nile tilapia from TekezeResrevoir
Female Male Female Male
Ca  628.65 ± 5.78b 629.05 ± 2.36b 673.38 ± 0.86a 673.29 ± 1.91a
Mg 756.39 ± 2.80b 753.17 ± 3.77b 877.16 ± 2.59a 875.25 ± 2.03a
Na 1536.57 ± 2.90b 1532.04 ± 2.99b 2071.82 ± 4.69a 2064.15 ± 3.15a
14043.65 ± 4.39b 14021.34 ± 8.00c  18616.37 ± 5.47a 18610.06 ± 6.89a
P 396.89 ± 1.30b 393.62 ± 7.62b 486.38 ± 9.54a 487.91 ± 6.86a
Zn 21.25 ± 2.31c 22.17 ± 0.35c 34.07 ± 1.06a 27.29 ± 1.02b
Cu 2.87 ± 0.15a 2.98 ± 0.09a 1.19 ± 0.15b 1.18 ± 0.07b
Fe 45.78 ± 2.10ab 49.09 ± 0.33a 32.63 ± 2.98c 41.06 ± 0.09b
Mn 0.65 ± 0.03a 0.62 ± 0.03a 0.42 ± 0.05b 0.46 ± 0.04b

Table 4: Mineral contents of fish species given as mg/kg dry weight.

The pattern of elemental concentration in the muscle of each of the fish species was in the order of K>Na>Ca>Mg>P>Fe>Zn>Cu>Mn. The concentration of K was highest from the elements analyzed from fish species and Mn was found in lowest concentration.

The Mn concentration levels in the three fish species did not exceed the WHO limit of 2.50 mg/kg for fish and fish products in present study (0.12-0.65 mg/kg) [46].

The lowest content of Cu (1.18 ± 0.07 mg/kg) was investigated from male O. niloticus from Tekeze reservoir and highest (2.98 ± 0.09 mg/ kg) in male O. niloticus from Lake Hashenge. In the present study the concentrations of Cu in the muscle of O. niloticus was in the range of the concentration found from the muscle of O. niloticus collected from Lake Awassa and Ziway (1.68-4.95 mg/kg of dry weight) [47]. The Cu concentration levels recorded in muscles of the sampled fish species (1.18-2z.98 mg/kg) were below the WHO recommended limit of 3.0 mg/kg in fish and fish products) [48].

The level of Iron (Fe) was highest in male O. niloticus from Lake Hashenge (49.09 ± 0.33 mg/kg) and lowest in female O. niloticus from Tekeze (32.63 ± 2.98 mg/kg). The range was from 32.63 to 49.09 mg/ kg of dry weight which, was in the range of the permissible limit (10-56 mg/kg) for fish and fisheries product [49].

The results obtained from this study showed that the Zinc content of the fish species was between 21.25 ± 2.31 and 34.07 ± 1.06 mg/kg which was in the range of tolerable value (10-75 mg/kg) of fish [50]. Zn content was significantly different (P<0.05) with in the species and sex. Abraha et al. [51] reported that the concentrations of Fe, Zn and Mn in the muscle of O. niloticus collected from Lake Hashenge were 64.87, 24.95 and 1.01 mg/kg of dry weight respectively which was higher than the present study.

The results obtained from this study revealed that the phosphorous (P) and magnesium (Mg) contents of fish species were between 393.62 and 487.91 mg/kg; 753.17 and 877.16 mg/kg respectively. The highest average concentration of P was observed in male O. niloticus from Lake Hashenge. Stanek and Janicki [52] reported that the concentration of calcium in the muscle of male and female roach was not significantly different. This study is also agreed with the present work.

The levels of potassium (K) and sodium (Na) in all samples ranged from 11184.09 to 18616.37 mg/kg and 1532.04 to 2092.22 mg/kg, respectively. Highest concentration of K was observed in female O. niloticus from Tekeze reservoir. The concentration of K in male and female O. niloticus from Lake Hashenge showed significant difference (P<0.05) which was higher in female fish.

Variations in the concentration of minerals in fish muscles could be due to their concentration in the water bodies, the physiological state of the fish and or the ability of the fish to absorb the elements from the diets and the water bodies [53,54].

This agrees with the report of Farkas et al. [55] that the concentrations of element in fish body could be related primarily to their feeding habits [56-58].

Conclusion

From the present study it can be concluded that, there is variation in abundance of food items of O. niloticus collected from the two water bodies. The difference in the abundance of food items O. niloticus between the two water bodies may cause in variation in moisture content, crude protein, crude fat, crude ash and carbohydrate content. Water qualities have an effect on the biochemical composition content of the fish. Water temperature of Lake Hashenge was lower than that of Tekeze reservoir. Female fish contained slightly higher protein and fat as compared to male. Generally O. niloticus in Tekeze reservoir and Lake Hashenge was found to be omnivorous fish mainly feeding on Zooplankton, phytoplankton, detritus, insects and macrophytes. This study shows that the superiority of O.niloticus from Hashenge in crude protein and crude fat content than O. niloticus from Tekeze reservoir. O. niloticus in Tekeze reservoir and Lake Hashenge, is all rich sources of protein, moisture, lipid, ash and minerals.

The study also providing update information in fish fillets composition and mineral contents to food composition database and consumers can have sufficient knowledge in the biochemical contents of O. niloticus fish species.

Acknowledgements

The authors of this paper are thankful to Tigray Agricultural Research Institute (TARI) for full support of the research and Ambo University for free tuition fee. We gratefully acknowledge Abergelle Agricultural Research Center for logistic support.

References

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