Fish is rich
in
essential nutrients but can remain a potential source of food poisoning. A study was
,
therefore
,
carried out with the general objective of highlighting the probable biological and chemical dangers associated with the consumption of fish and freshwater fruits from
the
Guéssabo river. The
present study was conducted on 50 carp fish, 50 mackerel f
i
sh, 50 frog
s
and 50 mollusks caught in the Guéssabo River. Microorganisms were enumerated by conventional tests and heavy metals were investigated by Inductively Coupled Plasma Optical Emission Spectrometry. The enumeration showed high levels of thermotolerant Coliforms (2.5 × 104), Enterobacteriaceae (3.4 × 104), S. aureus (2.3 × 103) and Yeast/Molds (2.1 × 104), in all samples the standards were not in conformity with the required standards. High levels of Al (7230 μg/kg) and Cd (21.57 μg/kg) were observed in carp fish and these values are above the standard. In conclusion
,
the fish caught in the Guéssabo River
could be a health risk factor for the consumer.
Fish Microorganisms Heavy Metals Sanitary Quality Guéssabo River of Côte D’Ivoire1. Introduction
Fish is recognized as one of the richest food for accessing a well-balanced diet. Nutrients such as high-quality protein, vitamins, polyunsaturated fatty acids, and omega-3s, strengthen the body as well as reduce the risk of coronary heart disease and neurological disease [1] [2] [3]. Thus, for their good health, it is recommended the consumption of fish should be at least per week [1]. However, the consumption of fish and seafood can potentially harmful because of their biochemical, microbiological, and physicochemical quality due to their sources of origins [4]. Indeed, fish normally accumulates heavy metals from food, water, and sediments [5] [6] [7] and this is a good indicator of heavy metals contamination in water [8]. While microbiological contamination is responsible for gastroenteritis, this is not the case for heavy metals. Several unfavorable effects of heavy metals on human health have been known for a long time [4]. This includes serious threats like renal failure, liver damage, cardiovascular diseases, and even death [9] [10]. Thus, many local and international monitoring programs have been established to assess the quality of fish for human consumption and to monitor the health of the aquatic ecosystem [11].
In Côte d’Ivoire, fish is the primary source of animal protein for the Ivorian consumer. National fish consumption is estimated to vary between 250,000 and 300,000 tons/year for an average local production of 80,000 tons [12]. Given its relatively low price compared to that of meat, fish is accessible to the most modest households [13]. Local production comes from high seas fishing but also from many rivers and streams that cover the country. In the region of Haut Sassandra, the halieutic products sold on the different markets come from the Guessabo River [14]. The study of the sanitary quality of these products is, therefore, of paramount importance given the strong demand for freshwater fish and fruits by the populations of Upper Sassandra. It seemed appropriate to us to study the quality of these products with a view to answering the questions of health safety related to the consumption of these products. A study was, therefore, carried out and aimed at highlighting the probable biological and chemical dangers associated with the consumption of fish and freshwater fruits from the Guéssabo River. It focused on the evaluation of microbiological quality by researching germs such as enterobacteria, fungal flora and the heavy metals toxicity of fish and freshwater fruits from the Guéssabo River.
2. Material and Methods2.1. Study Area
This study was carried out in the town of Guéssabo. This city is located in central western Côte d’Ivoire. She is from the department of Zoukougbeu, in the Haut-Sassandra region. Its geographic coordinates are latitude 6˚44'12'' north latitude and 6˚57'17.5'' west longitude. The town of Guéssabo has a river (Figure 1) which is a tributary of the Sassandra River, and which bears the same name as the town. It has a landing stage where the populations of the department and the region come to stock up on fishery products [14].
2.2. Data Collection
The calculation of the size of the fish and seafood samples was analyzed according to the formula of Dagnelie et al. [15]:
n = U 1 − a 2 2 × p ( 1 − p ) d 2
where: n: size of the surveyed population; p: prevalence of consumption of freshwater fish and fruit; d: margin of error. The various samples were taken during the rainy season in July. The fish (Cyprinus carpio and Arius africanus), frog (Rana brama) and mollusca (Pomacea canaliculat) samples were purchased on board (Figure 2). The samples consist of 50 frogs 50 carp fish, 50 jaws and 50 mollusks. They were collected randomly and transported in coolers with ice accumulators to the Microbiology Laboratory of the University of Jean Lorougnon Guédé in ice accumulator’s container for microbiological analysis and research for heavy metals.
2.3. Microbiological Analysis
Bacteria isolation and identification
The microbiological analysis consisted in looking for the following germs: Total and thermotolerant coliforms (NF ISO 4831), Staphylococcus aureus (NF EN ISO 6888-1), Salmonella sp (NF V 08-052), yeasts and molds (ISO 7954) [16]. The culture media below in summer use according to the manufacturer’s recommendations is in Table 1.
2.4. Sample Analysis
Bacteria isolation and identification
Twenty-five (25) grams of each sample are weighed aseptically and then placed in a sterile Erlenmeyer flask. A volume of 225 ml of Buffered Peptone
Media used
Target microorganisms
Culture media used
Thermotolerant coliforms
VRBG agar (diagnostici-liofilchem)
Total coliforms
VRBL agar (diagnostici-liofilchem)
Fungal flora
Sabouraud with chloramphenicol (alpha biosciences)
Staphylococcus aureus
Baird parker (Eur pharm)
Salmonella
Hektoen, (biosciences) rappaport de vassiliadis (bio rad)
Water is added thereto. The mixture was homogenized for 2 min to obtain the stock suspension corresponding to the 10−1 dilution. This solution is left to stand for 30 min, to dissolve and allow revivification of the microorganisms at room temperature (about 25˚C). From this suspension, a series of decimal dilutions is then carried out. Two types of inoculation were carried out during this manipulation. These are mass seeding which concerned Sabouraud media with chloramphenicol, VRBL, and VRBG, and surface seeding by spreading which considered the media, Baird Parker, surface seeding by streak which concerns the Hecktoen medium. The isolation and identification of salmonella was carried out according to Adane et al. [17] protocol.
Colony enumeration
Colony forming units per milliliter of sample (CFU/g) were calculated according to standard NF/ISO 7218: 2007 using the following formula:
N = ∑ C V × ( n 1 + 0.1 × n 2 ) × d
ΣC: sum of characteristic colonies counted on all retained Petri dishes; n1: number of Petri dishes retained at the first dilution; n2: number of Petri dishes retained at the second dilution; d: dilution rate corresponding to the first dilution; V: inoculated volume (mL); N: number of microorganisms (CFU/g).
Quality assessment criterion
This evaluation was carried out using as supports, the standard analysis techniques reported by Joffin and Joffin [18] according to the two-class plan with reference to the microbiological criteria for fresh animal products specified by the French Legislative and Regulatory Guide No. 8155 (GLF 2000). The tolerance thresholds are M = 10 3 CFU/g or ml for the total flora; at 10 CFU/g or ml for fecal coliforms and the absence in 25g of product analyzed for salmonella.
2.5. Trace Metals Analysis
The metal (Al, As, Cd, Co, Cr, Cu, Fe, Hg, Mg, Ni, Mn, Pb, Sb, Zn, B and Ba) content in the sample were determined by the method of Inductively coupled plasma optical emission spectroscopy (ICP/OES) according to the protocol of Bozorgzadeh et al. [19]. The fish samples were washed thoroughly by water and wrapped into separate polyethylene bags and were immediately frozen and stored at −20˚C until examination. Before analysis the fish specimens were thawed, and a stainless-steel knife was used to cut the tissues. Samples of fish fillets were quickly removed and washed with Milli-Q water. The fish fillets (0.5 g) were thoroughly homogenized in a food blender with stainless steel cutters. The prepared sample was added to 25 mL of 3:2 ratios of HNO3: H2O2 (32%) in a screw cap polypropylene sample tube. The cap was tightened, and the tube was placed in a water bath at 85˚C for 2 h. After digestion, the liquid portion was separated, vacuum dried to 1 mL and used for further analysis.
2.6. Statistical Analysis
The results were statistically analyzed of variance method (ANOVA) using the STATISTICA 7.1 software (Statsoft, France). The comparison of means is carried out by the test of the smallest significant difference the test of Tukey. The differences are significant when p < 0.05. When the probability is greater than 0.05 (p > 0.05) the statistical differences are not significant. In the event of a significant difference (p < 0.05) between the means, Tukey’s test was performed to determine the different classes of homogeneity.
3. Results3.1. Results of the Microbiological Analysis of Samples of Fresh Fish (Carp and Jawbones), Mollusks, Frogs
Table 2 shows the results of the analyzes of our different samples from the
Results of the microbiological analyzes
Sample types
Fresh fish (Carp and jawbones)
Mollusks
Frogs
Germs sought (in CFU/g)
Total coliforms
3.99 × 103 ± 0.62
0
3.49 × 104 ± 1.71
Thermotolerant coliforms
4.16 × 103 ± 5.71
0
2.57.10 4 ± 8.45
Fungal flora
5.55 × 102 ± 0.17b
5.55 × 102 ± 0.17c
2.11 × 104 ± 0.74
S. aureus
2.24 × 103 ± 0.03
9.16 × 102 ± 0.16
2.36 × 103 ± 0.56
Salmonella sp
+
-
+
+: presence of Salmonella sp; -: absence of Salmonella sp; Values assigned the same letter are statistically identical, at the 5% threshold.
Guessabo River. These results we notice that the mollusks are not contaminated by total and thermotolerant coliforms. They are only contaminated by the fungal flora with a load of 5.55 × 102 ± 0.17 CFU/g and by S. aureus with a microbial load of 9.16 × 102 ± 0.1 CFU/g. Fresh fish have the lowest microbial load concerning total coliforms (3.99 × 103 ± 0.62 CFU/g) and thermotolerant coliforms (4.16 × 103 ± 5.71 CFU/g). As for Salmonella contamination, it is present in samples of frogs and fresh fish.
3.2. Contamination of Fish and Seafood by Heavy Metals
The heavy metal content of samples of fresh fish, frogs and Mollusca is presented in Table 3. The concentration of heavy metals: As, Co, Cr, Cu, Ni, Sb, Cu, Hg, is below the detection limit (5 µg/g) in all samples. Only fresh fish contain aluminum with a content of 7230 µg/kg. Cd and Mn are present in the different samples. The content of these two metals is high in fresh fish with levels of 21.57 µg/kg and 95.4 µg/kg respectively for Cd and Mn.
4. Discussion
This study helped to know the sanitary quality of fish and seafood caught in the Guessabo River. It was reported that freshwater fish and fruits are excellent sources of protein and other nutrients (minerals and vitamins) essential for human health [2] [3]. However, human activities and pollution induce several damages such as environment contaminations. This can make foods be contaminated by pathogenic microorganisms coming from human, animal, water or land-based present in fresh or salt water [20]. Thus, the analysis of the microbiological quality of the different samples in our study showed that they are contaminated by enterobacteria,
Heavy metal content of analyzed samples of fresh fish, frogs and Mollusca
Heavy metals
Frogs
Fresh fish (carp and jawbones)
Mollusca
Maximum permitted
µg/kg
Al
<5
7230
<5
-
As
<5
<5
<5
1
Cd
12.77
21.57
3.439
2
Co
<5
<5
<5
-
Cr
<5
<5
<5
1
Cu
<5
<5
<5
500
Fe
<50
<50
<50
-
Hg
<0.5
<0.5
<0.5
0.5
Mn
8.7
95.4
654
-
Ni
<5
<5
<5
30
Pb
<5
<5
<5
6
Sb
<5
<5
<5
1
Zn
7868
4562
4028
500
B
3104
1872
246.4
-
Ba
1768
706.6
796.9
-
fungal flora, S. aureus and Salmonella. The microbial flora of frog, fish and Mollusca may be the reflect of the microbiological quality of the water in which they were collect [21]. Thus, we can say that the water from which the samples were collected is not safe of microbial contamination. It was observed that the microbial load of these bacteria varies from one type of sample to another. This load is higher than the recommended standard: Enterobacteria’s ≤ 10 CFU/g, fungal flora ≤ 105 CFU/g and Salmonella (absent). Enterobacteriaceae represent the highest bacterial load. This observation is identical to the work of Kolda et al. [22]. However, fresh poisons and frogs are the most contaminated. The presence of Enterobacteriaceae indicates fecal contamination and their main reservoir is the human digestive tract. Indeed, certain rivers are the place of dumping of all types of human waste [22] [23]. The contamination is therefore explained by the fact that the Microbiota of water and fish are interconnected in the aquatic environment, with the possibility of bacteria colonizing the host’s skin, gills or intestinal tract [24]. In the second part of this study, we evaluated the level of chemical contamination by heavy metals. The main heavy metals that have a strong negative impact on human health are lead, cadmium, mercury and arsenic [25]. The analysis of our different samples showed that none of the seafood products exceeded the EU maximum level for mercury and the cadmium in fish of 0.50 mg/kg. Our results for mercury and cadmium agree with those of Naess et al. [26] who found values below the limit recommended in the chemical analysis of seafood from 2015 to 2018 in Norway. On the other hand, we observed a high concentration of aluminum content in the fresh poisons (7230 µg/Kg). This effect is the fact that the toxicity of aluminum with respect to aquatic organisms depends on the physicochemical conditions of the environment. Studies on this subject have shown that the inorganic forms of this metal are particularly toxic to fish depending on the pH [27]. Aluminum is the 3rd mineral element most common in the earth’s crust after silica. It is therefore omnipresent in the environment. It is never found in nature in metallic form, but always combined with other elements, notably with oxygen [28]. Acid precipitation which passes through soils can induce the mobilization of certain elements (Al, Mn, Fe, Zn, etc.), sometimes in quantities toxic to aquatic ecosystems [29]. This high load of aluminum rate could therefore be explained by the fact the southwest zone where the Guéssabo river is located is a rainy zone where precipitations very often reach 1200 to 1400 mm per year [30].
5. Conclusion
At the end of this study, we can retain that the fish and seafood from the Guéssabo River are made up of carp, mollusks and frogs. The consumption of these products presents some risks for human health. In fact, the microbiological analysis of the different samples showed contamination by enterobacteria including Salmonella. This bacterium is responsible for typhoid fever. In addition, some trace metals (mercury, cadmium, and arsenic) were recorded below the thresholds of dangerousness for human health. These are mercury, cadmium, and arsenic. Unfortunately, the level of lead remains very high in fresh fish.
Conflicts of Interest
The authors declare no conflicts of interest regarding the publication of this paper.
Cite this paper
Attien, P., Toe, E., Kouassi, K.A., Zébré, A.C., Gomé, M.N., Sina, H., Assohoun-Djeni, N.M.C., Konan, A., Coulibaly, I., Lamine, B.-M. and Dadie, A. (2022) Evaluation of Health Risks Related to the Consumption of Fish from the Guéssabo River. Food and Nutrition Sciences, 13, 55-64. https://doi.org/10.4236/fns.2022.131006
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