Increasing land reclamation in El-Fayoum governorate has led to increase the amount of drainage water that discharged without prior treatments to two main drains, El-Wadi and El-Bats drainages loaded by salts and heavy metals. So, the present investigation aims to evaluate quality of water samples collected from a branch of the river Nile (El-Lahon canal) and the main drains (El-Bats and El-Wadi) at Fayoum governorate on some biomarkers of the Nile catfish; Clarias gariepinus inhabiting the studied degradable aquatic habitats. Water and nighty fish samples colleted from the different studied sites of collection by the help of fishermen for physicochemical analyes of water and fish biochemical analyses and histopathological alteration. Results revealed highly significant differences at P ≤ 0.01 with the highest water ammonia, nitrite, heavy metals (Cu, Zn, Pb and Cd) and lowest dissolved oxygen content accompanied by metals bioaccumulation in vital organs of fish collected from the main drains (El-Bats and El-Wadi) in comparision with that collected from the studied branch of the river Nile. Higher bioaccumulation of the studied heavy metals in gills, liver, kidney and muscles of Clarias gariepinus collected from the main drains significant increase in serum glucose, liver and kidney functions, disturbance in protein profile of fish collected from the studied main drains than that of fish collected from the river Nile branch, El-Lahon that showed more or less normal values. Moreover, histopathological alterations in gills, liver, kidneys and clear DNA strand breaks in fish liver cells increased statistically in Clarias gariepinus collected from El-
Fayoum drainage canals. Generally, the results highlights on the importance of taking action through the responsible authorities towards quality of the drainage water that fed fish farms by law that could play a role as a main source of protein for human beings.
Drainage Water Catfish Genotoxicity Histopathology Biochemical Changes1. Introduction
Fish are important members of aquatic ecosystems and an important source of human food. However, fish distribution data in Egypt indicate a reduction in the commercially desirable fish species as the water conditions deteriorate. Agricultural, waste municipal and industrial effluents discharged directly to the natural water resources have been found to cause heavy fish mortality due to hypoxia, high levels of organic substances, inorganic salts and heavy metals [1] [2].
Two major drains called El-Bats and El-Wadi drains at El-Fayoum governorate receive agricultural drainage water, waste municipal and industrial effluents without prior treatments. The drainage water was estimated as 390 million cubic meters annually [3] [4] [5]. Due to the regulation rules for use of water resources in El-Fayoum province, fish farms which mainly established around El-Bats and El-Wadi drainage canals are allowed only to use water from the drainage network around [6]. Thus, these fish farms using agricultural drainage water may face the danger of negative effects on their cultured fish species [7] [8] [9].
Agricultural run-offs have cumulatively negative effects on the environmental quality of water in which decreased biodiversity and accidental fish die-offs have occurred. Water quality of the aquatic ecosystem is considered as the main factor controlling the state of health and disease in both cultured and wild fish [3] [4] [10]. Among the various toxic pollutants, heavy metals represent a very interesting group of elements due to their strong impact on stability of aquatic ecosystems, bioaccumulation in living organisms [11], toxicity persistence and tendency to accumulate in water and sediments. Heavy metals are used as indicators of pollution in the ecosystem, and have recently came to the forefront of dangerous substances causing serious health hazards for humans and other organisms [12] [13].
The exposure of aquatic organisms to environmental contamination often results in genotoxic insult, either via direct genotoxicity, or through the induction of cellular or oxidative stress. Fish are considered as common model species to evaluate the health of aquatic ecosystems because pollutants build up in the food chain and are responsible for adverse effects including death in the aquatic systems. Pollutants with a genotoxic potential for the aquatic organisms are of serious concern since they can bind to DNA molecules and provoke a damaging chain of biological changes such as impaired enzyme functions or general metabolism, cytotoxicity, immunotoxicity, inhibition of growth and/or carcinogenesis [14]. Moreover, histopathological changes in cells, tissues and organs used as biomarkers for more benefits; Confirmation of measurements evaluated by chemical and biochemical analysis, and permitting researchers to examine specific target organs and cells affected by exposure to toxicants. Paithane, et al., [15], pointed out that the histopathology biomarker is a higher level response following chemical and cellular interaction.
Therefore, the present study was conducted to evaluate the quality of water as well as provide comparable biomarkers data of Clarias gariepinus collected from three different degradable aquatic habitats (Branch of the river Nile and the main drains at El-Fayoum governorate, El-Bats and El-Wadi). The aforementioned aim of the present study achieved through carrying out the residual heavy metals (Cu, Zn, Pb and Cd) in some selected vital organs of fish (Gills, liver, kidney and muscles), serum glucose, liver and kidney functions and protein profile. In addition to recognize DNA damage degree in liver cells using comet assay and follw up histopathological alterations in gills, liver and kidney of the studied fish.
2. Materials and Methods
The present field study was carried out on water and Nile catfish; Clarias gariepinus samples collected directly from three different studied aquatic habitats at El-Fayoum governorate: Site (1): Area of the river Nile at Fayoum governorate, El-Lahon canal. Site (2): El-Bats drainage canal at El-Fayoum governorate where agricultural and waste municipal water discharged. Site (3): El-Wadi drainage canal at El-Fayoum governorate where agricultural drainage water discharged.
Water and fish sampling: Water and fish samples were collected from each site for the following investigations.
1) Water sampling and analysis: Water samples were collected approximately 20 cm below the surface water as reported by Ndimele and Kumolu-Johnson, [16], and kept in 500 ml sterile plastic containers. Samples were filtered and acidified with 10% HNO3 for preservation, placed in an ice bath and brought to the laboratory.
a) Physicochemical analysis of water: The water samples collected from different locations in the studied ecosystems were subjected to a number of physicochemical analyses as mentioned below:-
l pH was measured at the sampling site by means of a pocket-pH meter (Micro Checkit® pH+, Lovibond, England).
l Dissolved oxygen (mg/l) concentration was determined at the sampling site by means of Oxygen meter (model, YSI58).
l Salinity was measured by using a salinity-conductivity meter (model, YSI 58).
l Total hardness and total alkalinity were measured by titration method according to the American Public Health Association standard methods [17].
l Ammonia and nitrite were measured according to the method described by the American Public Health Association standard methods [17].
b) water analysis for heavy metals: Heavy metal concentrations in water were determined by atomic absorption spectrophotometer (Perkin Elmer, 2280). The samples were prepared and analyzed sequentialy for zinc, copper, lead and cadmium according to APHA [17].
2) Fish sampling and analysis: A total number of 90 adult fish of Nile catfish; Clarias gariepinus (30 fish/site), fishes were collected with the help of local fishermen for the following analyses:
a) Residual heavy metals in some selected vital organs of the studied Fishes:
Fish were dissected for its gills, liver, kidney and muscles tissues then, washed with de-ionized water, put in cleaned plastic bags and stored frozen until analysis was carried out. Known weight of the prepared tissue sample (wet weight) was dried at 65˚C until they reached to a constant weight. All samples were ashed in a muffle furnace for 6 hours at 650˚C. The tissue ash were then dissolved and diluted to 25 ml with 0.1 N hydrochloric acid. Heavy metal concentrations were determined using an atomic absorption spectrophotometer according to APHA [17].
Heavy metal concentration (μg/g) = reading of atomic absorption × volume of diluted solution/Weight of sample (g).
b) Blood sampling and biochemical analysis: The fishes, Clarias gariepinus for blood analysis were brought to the laboratory alive in an aerated tank. Blood samples were withdrawn from the arterial caudalies, sucked into the syringes. Moreover, serum was obtained by centrifugation (At 5000 rpm for 12 minutes) and stored at −20˚C for further analysis. The blood sample subjected to the following examinations:
l Biochemical analysis:
i) Serum analysis:
Serum glucose was measured by using BIOme-rieux kit according to the method described by Trinder [18]. Aminotransferase: Serum Aspartate aminotransferase (AST) and Alanine aminotransferase (ALT) activities were estimated colorimetrically as described by Reitmans and Frankel [19]. Serum ALP activity was determined using the method of Tietz, et al., [20]. Serum creatinine by the method of Tietz, [21]. Serum Uric acid the method described by Tietz, [22]. Serum total protein content was determined by Biuret test [23]. Serum albumin according to the procedure of Doumas et al. [24]. Serum globulin calculated as the difference between plasma total protein and albumin.
ii) DNA damage assay:
Isolation of cells from fish liver after fishing from different sites of collection, the livers of fish collected from the different studied aquatic habitat were dissected and placed in eppendorf tubes containing ice cold PBS. The liver tissues then washed and minced with scissors to release single cells from liver tissues in PBS buffer with 20 mM EDTA. The layer with cell suspension was separated in a new tube after settling of tissues pieces and cell debris from the sample. The cells were counted, washed in ice cold PBS and adjusted to 1x 105 cells/ ml. Quantification of DNA damage by single cell gel electrophoresis assay carried out according to Kumaravel and Jha [25].
3) Histological studies: Samples for histological evaluation of gills, liver and kidney tissues of the fish were obtained by dissection and then fixed in Bouinَ´s fixative for 24 h. After dehydration in graded concentrations of ethanol, the samples were embedded in paraffin wax. Histological sections of 4 μm thickness were stained with Haematoxylin and Eosin. Sections were reviewed by light microscopy Leitz Laborlux S and photographed (Sony DKC-CM30).
4) Statistical analysis: The results were statistically analyzed using analysis of variance (F-test) followed by Duncan’s multiple range test to determine differences in means using Statistical Analysis Systems, Version 6.2 [26].
3. Results
Water quality:
Physicochemical properties of water from the different studied aquatic ecosystems are illustrated in Table 1. It is clear that, analysis of variance (F-values) showed highly significant differences (p < 0.01) in the values of pH, oxygen content, total hardness, total alkalinity, salinity, ammonia and nitrite among the different studied sites (F-values = 79.9, 386, 401, 102, 331, 516 and 291 respectively). It is evident from Table 1 that, the highest value of dissolved oxygen (7.89 ± 0.02) was recorded at the studied area of the river Nile at Fayoum governorate and decreased in the main drainage canals, El-Bats and El-Wadi (5.75 ± 0.09 and 5.36 ± 0.07) respectively.
The present data (Table 1) also showed high values of water ammonia (4.19 ± 0.11 and 3.15 ± 0.11 respectively) and nitrite (0.65 ± 0.03, 0.41 ± 0.01 respectively) in water samples collected from El-Wadi and El-Bats drains at El-Fayoum governorate and the lowest ammonia and nitrite values were recorded at the studied site of the river Nile at Fayoum governorate (0.28 ± 0.02 and 0.03 ± 0.004 respectively). However, higher water salinity was recorded at El-Bats drain and El-Wadi drains (10.5 ± 0.42 g/l and 3.87 ± 0.27 g/l respectively).
Residual heavy metals:
Values of water heavy metals (zinc, copper, lead and cadmium) and their bioaccumulation in the studied vital organs of the Nile catfish, Clarias gariepinus are given in Table 2. It is clear that, there were highly significant differences (p < 0.01) in all studied heavy metal concentrations among the different studied sites.
Quality of water collected from branch of the river Nile and the main drains at El-Fayoum governorate, Egypt
Studied Sites of Collection
pH
Dissolved oxygen mg/l
Total Hardness as CaCO3 mg/l
Total alkalinity as CaCO3 mg/I
Salinity g/l
NH3 mg/l
NO2 mg/l
El-Lahon canal (Branch of the river Nile)
7.57 ± 0.03 C
7.89 ± 0.02 A
141 ± 1.69 C
113 ± 4.74 C
0.084 ± 0.003 C
0.28 ± 0.02 C
0.03 ± 0.004 C
El-Bats drainage canal
8.30 ± 0.04 A
5.36 ± 0.07 C
427 ± 10.9 A
290 ± 1.32 A
10.5 ± 0.42 A
3.15 ± 0.11 B
0.41 ± 0.01 B
El-Wadi drainage canal
8.05 ± 0.04 B
5.75 ± 0.09 B
385 ± 7.3 B
256 ± 1.54 B
3.87 ± 0.27 B
4.19 ± 0.11 A
0.65 ± 0.03 A
F-values
79.9**
386**
401**
102**
331**
516**
291**
Data are represented as means of eight samples ± Sterr. Means with the same letter for each parameter are not significantly different, otherwise they do (SAS, 2000). **Highly Significant difference (P < 0.01).
Residual heavy metals concentrations in water (mg/l) and some selected vital organs (mg/kg dry weight) of Clarias gariepinus collected from branch of the river Nile and the main drains at El-Fayoum governorate, Egypt
F-value
El-Wadi drainage canal
El-Bats drainage canal
El-Lahon canal (Branch of the river Nile)
Studied sites of collection Studied metals
163**
2.9 ± 0.13 B
3.35 ± 0.14 A
0.65 ± 0.04 C
Water P.l. = 5.0 mg/l
Zinc
220**
33.95 ± 0.90 B
37.05 ± 1.41 A
10.18 ± 0.34 C
Gills
189**
33.32 ± 0.61 A
31.77 ± 1.32 A
11.68 ± 0.42 B
Liver
37**
21.48 ± 1.81 B
28.25 ± 2.47 A
7.13 ± 0.21 C
Kidney
72**
2.85 ± 0.10 A
3.10 ± 0.25 A
1.25 ± 0.08 C
Muscles P.l. = 40 ppm
289**
0.38 ± 0.02 B
0.47 ± 0.02 A
0.04 ± 0.003 C
Water P.l. = 1.0 mg/l
Copper
84**
2.38 ± 0.16 A
2.91 ± 0.1 A
1.60 ± 0.46 B
Gills
256**
11.79 ± 0.42 B
14.59 ± 0.41 A
3.28 ± 0.24 C
Liver
353**
10.64 ± 0.27 A
10.55 ± 0.35 A
2.1 ± 0.07 B
Kidney
33**
1.10 ± 0.10 B
1.88 ± 0.15 A
0.63 ± 0.09 C
Muscles P.l. = 20 ppm
259**
0.41 ± 0.01 A
0.31 ± 0.015 B
0.025 ± 0.005C
Water P.l. = 0.05 mg/l
Lead
59**
1.94 ± 0.09 A
1.21 ± 0.18 B
0.173 ± 0.008 C
Gills
33**
0.88 ± 0.10 A
0.48 ± 0.03 B
0.178 ± 0.01 C
Liver
64**
0.42 ± 0.04 A
0.31 ± 0.008 B
0.025 ± 0.012 C
Kidney
18.3**
0.58 ± 0.10 A
0.165 ± 0.019 B
0.067 ± 0.008 C
Muscles P.l. = 0.6 ppm
162**
0.032 ± 0.001B
0.053 ± 0.003A
0.002± 0.0003C
Water P.l. = 0.01 mg/l
Cadmium
16**
0.25 ± 0.044 B
0.39 ± 0.06 A
0.022 ± 0.004 C
Gills
51**
0.156 ± 0.02 B
0.256 ± 0.02 A
0.038 ± 0.005 C
Liver
39**
0.30 ± 0.04 B
0.68 ± 0.08 A
0.015 ± 0.003 C
Kidney
12**
0.036 ± 0.01 B
0.065 ± 0.01 A
N.D.
Muscles P.l. = 0.5 ppm
Data are represented as means of eight samples ± Sterr. P.l. = Permissible level in fish tissues for human consumption according to WHO (1998). N.D. = Not Detectable. Means with the same letter for each parameter in each raw are not significantly different, otherwise they do (SAS, 2000). **Highly Significant difference (P < 0.01).
The results declared that in presence of the industrial and agricultural effluents which discharged directly to the main drains at El-Fayoum governorate (El-Bats and El-Wadi drains), the concentrations of zinc, copper, lead and cadmium in water were higher than that of water samples collected from the branch of the river Nile (El-Lahon canal) at Fayoum governorate and exhibit the following order:
Zinc: El-Bats drain > El-Wadi drain > River Nile Branch (El-Lahon)
Copper: El-Bats drain > El-Wadi drain > River Nile Branch (El-Lahon)
Lead: El-Wadi drain > El-Bats drain > River Nile Branch (El-Lahon)
Cadmium: El-Bats drain > El-Wadi drain > River Nile Branch (El-Lahon)
It is clear from the present results also that the highest concentrations of the different recorded heavy metals were found in fish tissues collected from El-Bats and El-Wadi drains at El-Fayoum governorate and exhibit the following order:
Gills > liver > kidney > muscles in case of zinc bioaccumulation;
liver > kidneys > gills > muscles in case of copper bioaccumulation.
Gills > liver > kidney > muscles in case of lead bioaccumulation;
Gills > kidney > liver > muscles in case of cadmium bioaccumulation.
The results also declared that the lowest concentrations of the studied heavy metals were recorded in tissues of fish collected from the river Nile branch at El-Fayoum governorate (El-Lahon canal).
Serum constituents
Data concerning the changes in serum glucose, aspartate amino transferase (AST), alanine amino transferase (ALT) and alkaline phosphatase activities (ALP), creatinine and uric acid of the Nile catfish; Clarias gariepinus collected from the different studied aquatic habitats, the branch of the river Nile and the main drains at Fayoum governorate are given in Table 3.
It is clear that, there is highly significant differences in the studied serum constituents of fish collected from the different studied habitats with the highest values in fish collected from El-Bats and El-Wadi drain canals compared to that of fish collected from the river Nile branch, El-Lahon at El-Fayoum governorate.
Serum Protein Profile:
Data of serum protein profile, total protein, albumin, globulin and A/G ratio of the studied fish species; Clarias gatiepinus collected from the river Nile branch, El-Lahon and the main drains at El-Fayoum governorate are given in Table 4. Results of serum protein profile of Clarias gatiepinus showed highly significant differences, with the highest values in serum total protein, albumin and globulin of fish collected from El-Bats and El-Waid drains, but the lowest values were recorded in serum samples of fish collected from the unpolluted
Serum constituents of Clarias gariepinus collected from branch of the river Nile and the main drains at El-Fayoum governorate, Egypt
Studied Sites of Collection
Glucose (mg/100 ml)
AST (u/l)
ALT (u/l)
ALP (u/l)
Creatinine (mg/100 ml)
Uric acid (mg/100 ml)
El-Lahon canal (Branch of the river Nile)
44.38 ± 3.11 B
18.25 ± 1.92 C
16.25 ± 1.08 B
21.63 ± 1.24 C
0.25 ± 0.05 C
3.85 ± 0.16 C
El-Bats drainage canal
158.5 ± 27.7 A
232 ± 15.5 A
45 ± 3.8 A
47.9 ± 3.1 A
2.19 ± 0.30 A
39.4 ± 3.15 A
El-Wadi drainage canal
112 ± 10.4 A
58.4 ± 3.5 B
48.8 ± 2.42 A
40.3 ± 1.86 B
1.49 ± 0.27 B
10.43 ± 1.09 B
F-values
11.2**
151**
44**
38**
18**
96**
Data are represented as means of eight samples ± Sterr. Means within the same column, with the same letter for each parameter are not significantly different, otherwise they do (SAS, 2000). **Highly significant difference at P ≤ 0.01.
Serum protein profile of Clarias gariepinus collected from branch of the river Nile and the main drains at El-Fayoum governorate, Egypt
Studied Sites of Collection
Total protein (g/100 ml)
Albumin (g/100 ml)
Globulin (g/100 ml)
A/G ratio
El-Lahon canal (Branch of the river Nile)
2.45 ± 0.22 C
1.98 ± 0.15 C
0.46 ± 0.08 C
4.84 ± 0.59 A
El-Bats drainage canal
5.30 ± 0.30 A
3.47 ± 0.15 A
1.74 ± 0.16 A
2.10 ± 0.12 C
El-Wadi drainage canal
3.38 ± 0.12 B
2.63 ± 0.16 B
0.75 ± 0.08 B
3.90 ± 0.60 B
F-values
41**
23**
34**
8.95**
Data are represented as means of eight samples ± Sterr. Means within the same column, with the same letter for each parameter are not significantly different, otherwise they do (SAS, 2000). **Highly significant difference at P ≤ 0.01.
branch of the river Nile, El-Lahon at Fayoum governorate. However, serum A/G ratio of Clarias gatiepinus collected from El-Bats and El-Wadi drains revealed significant decrease (F-value = 8.95) than that calculated for fish collected from the river Nile branch at Fayoum governorate.
Genotoxicity study, Comet assay:
The present study demonstrates genotoxic and mutagenic damage in fish liver cells (Figure 1 and Table 5). Results of comet assay using single cell of fish livers proved to be a sensitive technique for the detection of DNA damage. DNA % in the head, DNA % in the tail, Comet %, tail length and tail moment all are considered as important parameters in evaluating the DNA damage. DNA damage assay in liver cells of Clarias gariepinus with a percentage 25.6 in case of fish collected from El-Bats drainage canal and 17.43 for that of fish collected from El-Wadi drainage canal.
Histopathological studies:
The previous biochemical and physiological investigations were confirmed by histopathological alterations and clear damage of gills, liver and kidneys of the Nile catfish; Clarias gariepinus collected from the different studied aquatic habitats, the main drains at Fayoum governorate (El-Bats and El-Wadi) in comparison with that collected from the river Nile branch at Fayoum sector, El-Lahon.
Gills: The gills of Clarias gariepinus collected from the river Nile branch, El-Lahon are formed of four gill arches on either side of the head and protected externally by the operculum. Each gill arch consists of two hemi-branchs and each hemi-branch is composed of a row of long thin gill filaments (primary gill lamellae). Both sides of each gill filament bear numerous secondary gill lamellae which are the actual site of gas exchange. These lamellae are composed of a thin epithelial cell layer covering pillar cells which, in turn surround the blood sinusoids. At intervals along the layer of epithelial cells there were chloride cells and numerous mucus cells.
Gill sections of fish collected from the different studied sites are shown in Figure 2. Gills of fish collected from the El-Fayoum drainage canals showed clear damage and histopathological changes which include necrosis of epithelial
Comet assay in liver cells of Clarias gariepinus collected from branch of the river Nile and the main drains at El-Fayoum governorate, Egypt
Studied Sites of Collection
Tail moment
Tail DNA (%)
Tail length (PX)
Head DNA (%)
Head diameter (PX)
DNA damage (%)
Intact cells
El-Lahon canal (Branch of the river Nile)
0.065
3.3
0.76
96.7
12.33
2.97
96.7
El-Bats drainage canal
1.69
36.5
4.14
63.4
13.2
25.6
74.4
El-Wadi drainage canal
1.223
27.8
3.5
72.12
13.43
17.43
82.4
cells, epithelial hyperplasia with ballooning degeneration and desquamation of the epithelium.
Liver: Histologically, the liver of Clarias gariepinus collected from the river Nile branch, El-Lahon differs from that of mammals where there is no certain lobular pattern. However, the hepatic parenchyma is arranged radially around the central veins and blood sinusoids are irregularly distributed in the liver tissue. Hepatic cells are polygonal in shape and posses a central spherical or oval nucleus with prominent nucleolus. The nuclei appeared large, and exhibited noticeable variation in diameter from cell to cell. Liver sections of fish collected from the different studied aquatic habitats are shown in Figure 3. Liver sections of fish collected from El-Fayoum drainage canals showed marked histopathological changes with special parenchymal cells and disintegration and necrosis of hepatic cells.
Kidneys: The kidney of the fish collected from the river Nile branch, El-Lahon at Fayoum governorate was characterized by renal tubules surrounded by haemopoietic tissue. Also, glomeruli and renal blood vessels were found between the renal tubules.
Kidney sections of fish collected from the different studied aquatic habitats are shown in Figure 4. Sections of kidney of fish collected from El-Fayoum drainage canals, El-Bats and El-Wadi declared a progressive damage of kidney tubules associated with tubular necrosis, injury of the wall of renal blood vessels and depletion of haemopoietic tissue.
4. Discussion
Water quality of the aquatic habitats is considered the main factor controlling the state of health and disease in both cultured and wild fishes [27] [28]. In the present work, assessment of aquatic pollution depended upon physicochemical monitoring to identify and quantify toxicants and to provide data that, for regulatory purposes, could be compared to allowable concentrations in water.
In the present study, the highest water ammonia and nitrite and lowest dissolved oxygen in water samples collected from the studied drainage canals at Fayoum governorate in comparison with samples collected from the river Nile branch could be attributed to agricultural, industrial, and waste municipal effluents which characterized by high load of organic wastes and the microbial
activity that degraded the organic matter led to the oxygen consumption. These result may causes a bad impact on the water quality and decrease of dissolved oxygen as a result of oxygen consumption in decomposing organic matter and the oxidation of chemical constituents as previously reported by Ibrahim and Ramzy [29] and Zaghloul et al. [8]. The recorded higher total alkalinity in water of the studied drains at El-Fayoum compared to that collected from the river Nile branch may be attributed to the high content of waste municipal effluents discharged there which maintain the carbonate-bicarbonate buffer system. It may be also due to the increase in phytoplankton density which leads to an increase in photosynthesis that involves the uptake of free carbon dioxide from water and precipitation of calcium carbonate [30] [31].
Residual heavy metals:
Relative to water, metals are adsorbed on sediment and bioaccumulated in fish affect fish populations, reducing their growth, reproduction and/or survival and
may even kill fishes [32]. In the present study, bioaccumulation of metals in tissues varies from metal to metal and among different organs of the same organism that is in accordance with Masoud et al. [33]. Gills are in direct contact with the aquatic medium; therefore, metal concentrations in this organ reflect their concentrations in the external environment. In contrast, the concentrations in liver and kidney represent the rates of bioaccumulation and detoxification of pollutants, as a result concentrations of all studied heavy metals scored highly accumulation pattern, especially in these two organs.
Studied heavy metals concentrations were higher in the gill than in the muscle tissue of the studied fish (Clarias gariepinus). Metal concentration in the gill could be due to the element complexion with the mucus that is impossible to completely remove from the lamellae, before tissue is prepared for analysis. This evidence is in accordance with Heath [34]. Moreover, the low levels of the metals in the muscles may be due to the little blood supply to the muscular tissues as previously confirmed with Osman and Kloas [35].
Indicative biochemical Parameters:
Serum constituents:
Analysis of serum constituents have proved to be useful in the detection and diagnosis of metabolic disturbance and disease [34]. The use of biochemical and physiological changes of fish have been recommended by several authors for toxicological approaches [36].
Serum constituents of Clarias gariepinus collected from the unpolluted area of the river Nile, El-Lahon branch at El-Fayoum are in the normal ranges as previously reported [37]. However, the reported hyperglycemia in Clarias gariepinus collected from the main drains at El-Fayoum governorate may be due to an enhanced glycogen breakdown in liver, that may be due to the bioaccumulation of the studied heavy metals as revealed in the present study and recorded by Diwan et al. [38]. It is well-established facts that stress stimuli rapid secretion of glucocorticoids and catecholamines from adrenal tissue of the fish. Both hormones are known to produce hyperglycemia in animals [39] [40]. The hyperglycemic condition in this study may be related to secretion of these hormones which causes breakdown of liver glycogen as and the histopathological changes and cells damage in the present study.
Elevations in the activities of serum AST, ALT and ALP in Clarias gariepinus collected from the main drains at Fayoum governorate, El-Wadi and El-Bats drainages reflect hepatic and myocardial impairment, leading to extensive liberation of the enzymes into the blood circulation. Several histopathological alterations have been observed in the liver and kidney of the studied fish (Clarias gariepinus) which support the observed disturbance in the liver function and the increase in serum AST, ALT and ALP activities. The results are in agreement with Al-Attar, [41] who reported that the elevation of serum GOT, GPT and ALP may be due to liver dysfunction. In addition, Mohamed and Gad, [42] reported that the increase of serum GOT; GPT and ALP may be attributed to the hepatocellular damage or cellular degradation, perhaps in liver, heart or muscle. Moreover, Yang and Chen [43] reported that the increase of blood enzymatic activity may be due to increased enzymes synthesis. Increased serum activities of ALP have been explained by pathological processes such as liver impairment, kidney dysfunction and bone disease [43] [44].
Renal failure is usually associated with decrease in urea, uric acid and creatinine excretion, thus leading to its increase in serum. As a result, serum urea, uric acid and creatinine were useful in diagnosis of renal function impairment, renal tubular necrosis, renal insufficient and impaired nitrogen metabolism [45]. The increased blood uric acid and creatinine of Clarias gariepinus collected from El-Bats and El-Wadi drainages when compared with that of fish collected from the river Nile branch, El-Lahon channel may be attributed to gill dysfunction as aresult of gills structure damage in the present study. Moreover, kidney damage may result in reduced renal blood flow with reduction in glomerular filtration rate, resulting in azotemia characterized by increase in uric acid and creatinine. Similar increase in plasma urea, uric acid and creatinine were previously recorded by El-Boshy and Taha [46] in case of Nile tilapia exposed to mercuric chloride.
In the present study, several histopathological alterations have been observed in the gills, liver and kidney of Clarias gariepinus collected from the most polluted main drains at Fayoum governorate, El-Bats and El-Wadi which support the observed disturbances in all studied serum constituents.
Total plasma proteins play an important role in the metabolism and regulation of water balance. The normal range of plasma total protein concentration in fish (4.08 ± 0.61 g/dl) that reported by Sabae and Mohamed, [4]. So any disturbances make this reading up or down more useful in diagnosis of fish disease. The majority of plasma proteins which are synthesized in the liver, is used as an indicator of liver impairment as that mentioned by Yang and Chem [43]. In the present study, there was elevation in serum total protein (hyperproteinaemia), albumin and globulin in the studied fish, Clarias gariepinus collected from El-Bats and El-Wadi drainage canals when compared with that of fish collected from the branch of the rive Nile, El-Lahon channel at Fayoum governorate which were within range. This possibly due to activation of metabolic systems in response to pollutants exposure, degradation of the cellular material in the liver, several pathological conditions as damage of liver and kidney, as shown in the present study and relative changes in the mobilization of blood proteins, water loss in the plasma and/or induction of protein synthesis in liver as previously reported [41].
Genotoxicity: Evaluation of DNA damage:
Genotoxic biomarker, DNA fragmentation, was used to evaluate the complex metals genotoxic effects in the studied aquatic habitats at the DNA level in liver cells (the detoxification organ) of the studied fish species; Clarias gariepinus. The comet assay has been demonstrated to be a powerful tool for measuring the relationship between DNA damage and the exposure of aquatic organisms to genotoxic pollutants on environmental as that mentioned by Fatima, et al., [47]. In the present assay, we found that the DNA strand breaks in fish liver cells increased statistically in Clarias gariepinus collected from El-Bats and El-Wadi drainage canals compared to fish collected from El-Lahon branch of the river Nile at El-Fayoum governorate, and this damage represented in terms of percent cells with tail, tail length, and percent DNA in tail. In agreement with this study, comet fish exposed sub chronically and chronically to effluents from a Swine industry associated with greater DNA damage [48].
DNA of the liver cells of Clarias gariepinus collected from the highly polluted drainage canals showed signs of internucleosomal fragmentation as evidenced by a ladder pattern caused by cleavage of DNA into segments which is considered as hallmark of apoptosis. Internucleosomal fragmentation was also accompanied by some random fragmentation as detected by an overlying continuous smear of DNA which is considered as hallmark of necrosis.
Liver as an active metabolic organs which can accumulate more metals than other tissues. Accumulated heavy metals in tissues of fish may catalyze reactions that generate ROS which may lead to environmental oxidative stress [49]. Metal catalyzed formation of ROS is capable of damaging tissue macromolecules such as DNA, proteins and lipids [50]. These free radicals could activate the mitochondrial membrane permeability transition pore, which leads to rupture of the outer membrane of the mitochondria and release of substances such as apoptosis-inducing factor and cytochrome c that produce apoptotic cell death [51]. Another mechanism is that ROS stimulate endogenous endonuclease activity [49]. Degradation of internucleosomal DNA segments as a consequence of activation of endogenous endonucleases is considered a characteristic end point of apoptosis [7] and necrosis [52].
Nevertheless, the present investigation showed mixed smearing and laddering of DNA fragments which is most probably attributed to the nonspecific DNA fragmentation process encountered with apoptosis. This observation is in agreement with Razzaque [53] who stated that both fragmentation patterns may involve more than one mechanism of cell death and the combined effects of these events can induce apoptosis and/or necrotic cell death.
Histopathological studies:-
Histopathological evaluation as a category of biomarkers allows examining specific target organs, including gills, kidney and liver that are responsible for vital functions, such as respiration, excretion and the accumulation and biotransformation of xenobiotic in the fish as previously reported [11] [54].
Histopathological alterations of gills:
Owing to their direct and continuous contact with the external medium and their functions in respiratory gas exchange, osmoregulation, excretion of nitrogenous waste products and acid-base regulation, this organ is directly affected by contaminants [55] [59].
The most common histopathological alteration detected was the epithelial desquamation (separation or lifting) from the base towards the tips of most respiratory lamellae. Lifting of the secondary lamellar epithelium due to hypertrophy are the first signs that gills have been exposed to hazardous chemicals, or physical agents may have been a response to increase the diffusion distance between dissolved oxygen and blood, which accordingly was related to hypoxia in fish. Lamellar fusion, hyperplasia and necrosis of different lamellar and filament cells like chloride and pavement cells is another most commonly reported change, but is more common for metals than for organics or other pollutants, possibly since metals directly interact with ion transport proteins and inhibit their activity as previously noticed [54] [56].
Histopathological alterations of liver:
Microscopic examination of the liver of fish collected from the river Nile branch showed a normal structure with compactly arranged hepatocytes, sinusoids were scattered randomly in between the hepatocytes and the hepatocytes had uniform morphology along with central vein. Also, a typical parenchymal appearance at light microscopical level and hepatocytes with polygonal shape, central spherical and densely stained nuclei were seen.
Liver sections of fish collected from the ecological disturbed aquatic habitats (the main drains at Fayoum governorate) showed marked histopathological changes including vacuolar degeneration, infiltration of red blood cells through the hepatocytes with congestion, vacuolar structures, dilated intercellular space, karyomegaly (dark and condensed nuclei), degeneration in pancreatic tissue, peliosis (replacement of liver tissue with blood-filled cavities without an endothelial cell lining), loss of cord structure, infiltration of inflammatory cells, damage of parenchymal cells, cloudy swelling and tissue disorientation with rupture of parenchyma cells and single cell necrosis. These findings are in agreement with several authers [57] [58]. This histological change in liver tissues is thought to be a response of Kupffer cells (responsible for detoxification) to various pollutants and these results coincided with Koca et al. [59].
Histopathological alterations of kidney:
The normal kidney samples showed uniformly functional units (renal tubules) and the interstices of the tubules contain haematopoietic tissues. In contrast, the common lesion found in the kidney of fish collected from El-Bats and El-Wadi drains (main drains at Fayoum governorate) was glomerular shrinkage, glomerular splitting, Tubular degeneration and necrosis. Tubular epithelial cell separated from basement membrane resulting from edema. There was also some evidence of melanomacrophages aggregation accompanied with congestion and haemorrhage, glomerular shrinkage with increase in Bowman’s space, periglomerular oedema and glomerular necrosis. The evident alterations were previously [60] in case of white sea bass (Lates calcarifer). These results indicate that heavy-metal contamination definitely affects structural and functional attributes of fish kidney. Moreover, degeneration of tubular epithelial cells and tubular necrosis may be due to the accumulation of inflammatory cells associated with metals toxicity [1]. These changes may be also attributed to impaired blood supply due to toxic action of different pollutants including heavy metals, especially cadmium which is known as renal toxicity as previously mentioned [11] [61]. To sum up, this histological endpoint showed severe injuries and damages in all studied tissues suggesting too slow defense mechanisms in these tissues to immobilize or eliminate heavy metals demonstrating the sensitivity of fish cells to metals exposure.
One could conclude that, preserving the environment is not an entertainment or luxury any more, yet it became crucial to protect our resources for the coming generations. Moreover, protecting the environment is a national duty and laws shall regulate the procedures of keeping good environment.
Conflicts of Interest
The authors declare no conflicts of interest regarding the publication of this paper.
Cite this paper
Zaghloul, K.H., Mohamed, H.A., Abdullatef, A.M. and Khalil, M.W. (2020) Genotoxic and Histopathological Effects of Water Pollution on Clarias gariepinus Fish at Fayoum Governorate, Egypt. Natural Resources, 11, 499- 519. https://doi.org/10.4236/nr.2020.1111029
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