Research Article | | Peer-Reviewed

Physico-chemical and Bacteriological Characterization of Well Water Consumed in the Neighbourhoods of N'Zerekore, Guinea

Received: 27 May 2025     Accepted: 10 June 2025     Published: 25 June 2025
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Abstract

The unsatisfactory distribution of water by the Guinea Water Company (SEG) has favoured the presence of boreholes and private wells in the urban commune of N'Zérékoré. The aim of this research is to examine the physico-chemical and bacteriological quality of water from wells in two of the town's neighbourhoods, Belle-vue and Mohomou. Nine wells in these neighbourhoods were sampled for the study. Analyses focused on 07 physical descriptors measured in situ; 04 chemical descriptors and 02 bacteriological descriptors, namely total coliforms and fecal coliforms determined in the laboratory. Two multivariate analyses were used to characterise the well water, including Principal Component Analysis and Hierarchical Ascending Classification. The data show a pronounced acidity in all the wells, with mean values ranging from 4.32±0.22 to 5.45±0.00. The water was poorly mineralised, but high levels of turbidity exceeding World Health Organization thresholds were recorded. All three well water points studied were contaminated with total coliform bacteria and faecal streptococci, which are good indicators of faecal contamination leading to bacteriological contamination making the water unsuitable for consumption. Principal Component Analysis (PCA) and Hierarchical Ascending Classification (HAC) were used to discriminate between the nine wells. According to the trends observed, the quality of the wells in the water analysed has deteriorated as a result of multiple factors associated with poor maintenance of the wells. These results call for action to be taken to disinfect wells, in order to guarantee a safe drinking water supply that poses no major health risk to the population.

Published in International Journal of Environmental Monitoring and Analysis (Volume 13, Issue 3)
DOI 10.11648/j.ijema.20251303.13
Page(s) 94-102
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2025. Published by Science Publishing Group

Keywords

Bacteriological, Physico-chemical, Well Water, Diseases, N'Zérékoré, Guinea

1. Introduction
Since antiquity, water has been regarded as the "lifeblood of the Earth," essential to life on our planet and considered one of the most vulnerable and scarce natural resources. Increasing pressure is being placed on this resource particularly groundwater due to rapid population growth and rural exodus. In 2022, at least 1.7 billion people worldwide relied on a drinking water source contaminated with fecal matter. Microbial contamination resulting from fecal pollution represents the greatest risk to drinking water safety . Poor water quality can result from various anthropogenic activities, including environmental pollution, improper waste disposal, and agricultural runoff. It is also often exacerbated by inadequate sanitation infrastructure and poor hygiene practices surrounding water collection and storage at the source . In sub-Saharan Africa, waterborne diseases such as cholera, dysentery, typhoid fever, and viral hepatitis A and E have become prevalent, as reported by . Thus, access to drinking water in both sufficient quantity and adequate quality has become a key criterion in evaluating human well being and satisfaction . In both rural and urban areas, communities use groundwater via boreholes and springs, as access to sanitation infrastructure is often lacking. Research carried out in urban areas of Republic of Côte d'Ivoire by described the borehole water used for domestic purposes in Abidjan's slums, and revealed the pollution factors affecting these boreholes. Water quality refers to the suitability of water for various uses. Consequently, any specific use of water must be measured in terms of acceptable levels of its physical, chemical and biological properties . In particular, drinking water must meet global standards for concentrations of several elements . To achieve the objective of monitoring and assessing groundwater and surface water quality, various physical, chemical and biological parameters are used for indexing. Consequently, regular water quality assessments are essential to identify these specific problems . The Republic of Guinea benefits from a dense hydrographic network composed of both surface and groundwater resources, the full inventory of which remains incomplete. Thanks to this substantial water potential, populations both in urban and rural areas have found alternative means to access water, compensating for the shortcomings of supply from the Guinea Water Company (SEG).
Faced with a steadily increasing demand due to population growth and the limited capacity of the supply infrastructure, the majority of the population turns to various alternative water sources, including public standpipes, traditional wells, and other local water resources. Consequently, the region experiences a resurgence of waterborne diseases, which contribute significantly to mortality rates particularly among children.
Hence the need to carry out various physico-chemical analyses to determine the quality of water for human consumption, in order to sound the alarm about the dangers facing consumers. It is against this backdrop that this study, which looks at the pollution of water from traditional wells, has been undertaken to assess the physico-chemical and bacteriological quality of well water in the Belle-vue and Mohomou neighbourhoods of the urban district of N'Zérékoré, with the aim of identifying health risks.
2. Materials and Methods
2.1. Study Area
Guinea, a West African country, has an estimated population of nearly 14 million according to the most recent census conducted in 2021. Its capital city is Conakry. From a geo-ecological perspective, the country is divided into four major regions: Forested Guinea, Upper Guinea, Maritime Guinea, and Middle Guinea. Forested Guinea, the region in which this study was conducted, is located in the southeastern part of the country, with N’Zérékoré as its administrative center.
The topography of the Forested Region is notably rugged, characterized by hills with altitudes ranging from 400 to 800 meters, as well as significant mountain ranges such as Nimba, Ziama, and Simandou, the highest peak reaching 1752 meters above sea level. The average annual rainfall ranges between 1800 and 2300 mm. The climate is mild throughout the year, with minimal temperature variation, generally fluctuating around 25°C .
This study was carried out primarily in the urban commune of N’Zérékoré, located approximately 945 km from the capital, Conakry. The city lies between 7°32' and 8°22' North latitude and 9°04' West longitude. It is the capital of the administrative region of N'Zérékoré and covers an area of 47.4 km² with a population of 196 823 (RGPH, 2014) resulting in a population density of approximately 1744 inhabitants per km². The population is distributed across 96 sectors forming 22 neighborhoods, including Belle-vue and Mohomou.
Figure 1. Geographic plan of the sampling neighbourhoods.
2.2. Sampling and Analysis Method
The sampling campaign was conducted between March and May 2024 (March 12-15; April 26-29 and May 20-22) on nine wells located in two different neighborhoods of the commune. Samples were taken at each well each well using a small, weighted bucket. Water samples were collected in 1500mL polyethylene bottles and analyzed immediately after collection. Before filling, the bottles were washed three times with the water to be analyzed. The bottles were filled to the brim, then the cap was sealed to prevent any gaseous interaction with the atmosphere. A total of thirteen parameters eleven physicochemical and two bacteriological were assessed both in situ and in the laboratory, following the techniques described by .
The physical descriptors, namely Temperature, pH, Electrical Conductivity, Total Dissolved Solids (TDS), and Dissolved Oxygen, were measured in situ by electrometric methods using a waterproof HANNA 98194 multiparameter device, 2015 version. Color was determined by photometric analysis using the 7500 photometers, based on the Beer-Lambert law. Turbidity values were obtained using a compact turbidimeter operating by nephelometry, also based on the Beer-Lambert principle.
In the laboratory, chemical parameters such as Suspended Solids, Nitrites, Nitrates, and free Chlorine were analyzed. All samples were examined within two hours of collection. Suspended Solids were measured using the gravimetric method with an analytical balance and a drying oven. Nitrites, Nitrates, and Active Chloride were quantified by photometric analysis using the 7500 photometers.
Regarding bacteriological analyses, the main parameters assessed were fecal coliforms and total coliforms, as they are sufficient to characterize the bacteriological quality of water. These microorganisms were enumerated using the membrane filtration technique as described by . This method is widely used for the quantification of microbial organisms in water intended for human consumption.
2.3. Data Processing Method for the Charactezisation of the Chemical Composition of Well Water
To characterize the physicochemical and bacteriological composition of well water, both univariate and multivariate statistical methods were employed. A water sample was deemed non-compliant if at least one of the physicochemical or bacteriological parameters assessed failed to meet the standard. Principal Component Analysis (PCA) was used to analyze the composition matrix of the wells and the abiotic descriptors of the water. PCA was complemented by Hierarchical Cluster Analysis (HCA) of the first four principal components. The Euclidean distance metric was used, and the Ward’s method was applied, The resulting dendrogram allowed for the grouping of the wells into homogeneous clusters based on the studied variables. The mean and standard deviation of these variables were calculated. All variables were standardized prior to the analyses. The R4.4.1 software was used for the statistical analyses. These methods were employed to identify and highlight the major sources of anthropogenic effects on the groundwater quality, specifically the wells under study . The suitability of physicochemical and bacteriological characteristics was examined according to the water potability standards suggested by the WHO .
3. Results
3.1. Physico-chemical Characteristics of Water Samples
The results of the chemical analyses of well water from the Mohomou and Belle Vue districts in the urban commune of N’Zérékoré are presented in Table 1. Analysis of these results reveals a marked acidity of the water from the various wells (average pH = 4.87), as well as low mineralization, as indicated by the electrical conductivity (EC), which ranges from 66 μS/cm to 476 μS/cm with an average of 186.89 μS/cm. This trend is consistent with the Total Dissolved Solids values (average TDS = 93.33mg/L).
Regarding color, the average value indicates that the water is highly colored (51.67 TCU). Turbidity was found to be excessive in several well water samples, with values ranging from 1.65 NTU to 84.4 NTU, and an average of 17.83 NTU. Suspended Solids content ranged from 0mg/L to 55mg/L, with a mean of 12.18mg/L.
Chlorine (Cl₂) concentrations in the well water varied between 0mg/L and 0.08mg/L, with an average of 0.02mg/L. As for the concentrations of major ions, nitrates had a mean value of 12.52mg/L, while nitrites averaged 0.2mg/L. The dissolved iron content showed a mean value of 0.41mg/L, with a maximum of 1.43mg/L and a minimum of 0.16mg/L.
Furthermore, in terms of compliance with WHO standards , the analysis of the results generally indicates that parameters such as pH, water color, turbidity, temperature, and iron exceeded the thresholds recommended by the World Health Organization (WHO). Other indicators, notably Electrical Conductivity (EC), Total Dissolved Solids (TDS), Chlorine, and Nitrates, showed values below the recommended limits. Finally, Suspended Solids (SS) and nitrites, highlighted in yellow, reached the threshold limits set by WHO guidelines.
Table 1. Results of physico-chemical analyses of well water in the study area.

Paramètres

Max

Min

Mean

E-T

Var

Normes OMS

Conformity

pH

5.3

4.16

4.87

0.43

0.18

6.5-8.5

CE (μS/cm)

476

66

186.89

135.56

18 377.86

≤ 1 500

TDS (mg/L)

238

33

93.33

67.89

4 608.75

≤ 1 000

Coul (UCV)

210

5

51.67

72.54

5 262.50

≤ 15

Turb (UTN)

84.4

1.65

17.83

28.97

839.15

≤ 5

Temp (°C)

27.76

26

26.5

0.56

0.32

< 25

SS (mg/L)

55

0

12.18

18.52

343.06

-

NO3- (mg/L)

29

1.34

12.52

11.87

140.99

≤ 50

NO2- (mg/L)

0.6

0.01

0.2

0.17

0.03

≤ 0.2

Cl2 (mg/L)

0,08

0

0.02

0.03

0.0006

0.2-0.5

Fe (mg/L)

1.43

0.16

0.41

0.39

0.16

≤ 0.3

3.2. Bacteriological Characteristics of Water Points
Bacteriological analysis of the water samples focused on the quantification of two indicator organisms: total coliforms and fecal coliforms present in 100mL of water. To classify water samples from the various wells, the WHO guidelines (2004) primarily rely on fecal coliforms (FC), which are considered the most reliable indicators of fecal contamination. Total coliforms (TC), which may include species of non-fecal origin, are therefore not prioritized under this rigorous WHO classification. Accordingly, Table 2 categorizes the water sources as excellent (A), acceptable (B), unfit for consumption (C), or heavily polluted (D), as defined by WHO .
The fecal coliform counts in wells P1, P2, P3, P4, P5, and P7 ranged from 11 to 66 CFU/100mL, placing them in category C, i.e., unfit for consumption. In contrast, water from wells P6, P8, and P9 was deemed acceptable for consumption (category B), with fecal coliform counts ranging from 3 to 6 CFU/100mL. From a bacteriological perspective, the majority of wells were therefore unsuitable for human consumption (Table 2).
Table 2. Number of faecal coliforms in 100ml of water sampled.

Sample

CF (UFC/100mL)

WHO category

Classification

P1

45

C

Unfit

P2

38

C

Unfit

P3

11

C

Unfit

P4

62

C

Unfit

P5

66

C

Unfit

P6

4

B

Acceptable

P7

19

C

Unfit

P8

6

B

Acceptable

P9

3

B

Acceptable

3.3. Correlations Between Different Physico-chemical and Bacteriological Water Parameters
Principal Component Analysis (PCA) performed on the 13 measured physico-chemical and bacteriological descriptors revealed that the first two principal components explain 65.85% of the total variance (Figure 2), which is sufficient for a comprehensive characterization of the sampled wells. The first principal component accounts for 41.88%, while the second explains 23.97% of the variance. Overall, the variables that exhibit strong correlations with these principal components are those that contribute most significantly to their formation.
Figure 2. Correlation of well water chemical parameters in the plane formed by the PC1 and PC2 components.
Coul: Couleur (UCV), Temp: Température (°C), Cond: Conductivité (µS/cm), TDS (mg/l), Turb: Turbidité (UTN), CF (UFC/100ml), CT (UFC/100ml), MES (mg/l), NO2: Nitrites (mg/l), NO3: Nitrates (mg/l), Cl: Chlore (mg/L), Fer (mg/L)
Variables that exhibit a strong, positive, and statistically significant correlation with PC1 include turbidity (r = 0.919; p = 0.000), color (r = 0.912; p = 0.000), fecal coliforms (FC) (r = 0.860; p = 0.003), iron (r = 0.842; p = 0.004), and total coliforms (TC) (r = 0.802; p = 0.009). A strong and significant positive correlation was also observed between PC2 and nitrate ions (r = 0.872; p = 0.002), as well as nitrite ions (r = 0.693; p = 0.039).
On the third axis (PC3), conductivity showed a strong, positive, and significant correlation (r = 0.780; p = 0.013), while pH exhibited a strong, negative and significant correlation, indicating an inverse relationship on this axis. Finally, only chlorine concentration was strongly, positively, and significantly correlated with the fourth principal component (PC4).
3.4. Typology of Wells Sampled
The dendrogram resulting from Hierarchical Cluster Analysis (HCA) performed on the principal component scores from the PCA identified five homogeneous well groups (QP1 to QP5) (Figure 3). These groups show strong and statistically significant associations with the first two principal components (PC1: η² = 0.992; p = 0.000 and PC2: η² = 0.891; p = 0.033) (η²: correlation ratio; v. test: variable comparison statistic across axes or groups).
1. Group 1 (QP4) includes wells P3 and P8, whose chemical composition is significantly different from that of the other wells. Water from these wells shows higher electrical conductivity (401 ± 106.07 μS/cm; p = 0.011), is more acidic (pH 4.32 ± 0.22; p = 0.039), and has a higher nitrite ion concentration (0.46 ± 0.21mg/L; p = 0.021) (Table 3).
2. Group 2 (QP5) comprises wells P6, P7, and P9, whose water contains the lowest concentrations of nitrate ions (2.18 ± 0.83mg/L), total coliforms (TC: 20.67 ± 13.32 CFU/100mL), and fecal coliforms (FC: 8.67 ± 8.96 CFU/100mL). However, these wells exhibit the highest temperatures (26.96 ± 0.70°C), indicating relatively warmer water.
3. Group 3 (QP3) includes wells P1 and P2, whose chemical composition is relatively close to that of group QP2. The water from these wells is relatively cooler (26.12 ± 0.09°C) and exhibits a lower total dissolved solids (TDS) concentration (36.00 ± 1.41mg/L).
4. Group 4 (QP2) is characterized by well P4, whose water composition differs significantly from the first three groups. It is particularly and significantly richer in chlorine (0.08 ± 0.00mg/L; p = 0.014) compared to the other groups (Table 3).
5. Group 5 (QP1) consists solely of well P5. The water from this well is significantly more colored (210 ± 0.00 CU; p = 0.021), richer in iron (1.43 ± 0.00mg/L; p = 0.006), and more turbid (84.40 ± 0.00 NTU; p = 0.015), with a very high suspended solids (TSS) content (55 ± 0.00mg/L; p = 0.014) (Table 3).
Figure 3. Dendrogram representing the Ascending Hierarchical Classification of the 09 wells.
Table 3. Descriptive characteristic (m (σ)) of the chemical composition of the water in the wells (QP1 to QP5) investigated.

Paramètre

QP1

QP2

QP3

QP4

QP5

CF

11.00 (7.07)

8.67 (8.96)

41.5 (4.95)

62.00 (0.00)

66.00 (0.00)

Chlorine

0.02 (0.00)

0.01 (0.02)

0.01 (0.01)

0.08 (0.00)

0.01 (0.00)

Conductivity

401.00 (106.07)

129.33 (61.13)

73.00 (2.83)

186.00 (0.00)

160.00 (0.00)

Colour

22.50 (17.68)

13.33 (7.64)

15.00 (0.00)

140.00 (0.00)

210.00 (0.00)

CT

29.00 (16.97)

20.67 (13.32)

68.00 (2.83)

82.00 (0.00)

92.00 (0.00)

Iron

0.28 (0.08)

0.25 (0.07)

0.32 (0.23)

0.31 (0.00)

1.43 (0.00)

Nitrate ion

19.00 (0.00)

2.18 (0.83)

11.75 (10.25)

19.00 (0.00)

2.60 (0.00)

Nitrite ion

0.46 (0.21)

0.09 (0.10)

0.20 (0.00)

0.17 (0.00)

0.07 (0.00)

TSS

1.05 (1.34)

17.33 (8.62)

0.15 (0.21)

0.20 (0.00)

55.00 (0.00)

pH

4.32 (0.22)

4.86 (0.47)

5.17 (0.18)

5.24 (0.00)

5.00 (0.00)

TDS

200.50 (53.03)

64.67 (30.57)

36.00 (1.41)

93.00 (0.00)

80.00 (0.00)

Temperature

26.47 (0.66)

26.96 (0.7)

26.12 (0.09)

26.11 (0.00)

26.33 (0.00)

Turbidity

5.53 (4.21)

4.02 (1.71)

2.48 (1.17)

48.00 (0.00)

84.40 (0.00)

4. Discussion
The physico-chemical and bacteriological analyses of well water from the Belle-Vue and Mohomou neighborhoods in the urban municipality of N’Zérékoré revealed an alarming situation. Several key water quality parameters were found to significantly exceed the World Health Organization (WHO) standards for safe drinking water. These results indicate a clear deterioration in groundwater quality, most likely linked to anthropogenic pressures such as inadequate sanitation, waste disposal practices, and unregulated urban development.
Indeed, from a physico-chemical perspective, the well water samples exhibited relatively low temperatures, ranging between 25°C and 26°C. These values are consistent with those reported in previous studies on groundwater in the Pointe-Noire region of Cameroon, suggesting similar hydrogeological and climatic conditions . However, according to WHO guideline values these temperatures are not compliant with recommended standards. It is important to note that water temperatures between 25°C and 28°C provide favorable conditions for the proliferation of environmental microorganisms . This suggests that the elevated temperatures observed in the well water could create favorable conditions for microbial proliferation, especially under tropical climatic conditions where warm environments accelerate bacterial growth and survival.
Regarding pH, the well waters in N’Zérékoré are acidic and potentially aggressive to the gastrointestinal tract. with average values ranging from 4.32 to 5.24. These observations are consistent with the findings of , who reported average pH values between 5.75 and 6.40, emphasizing that water with a pH below 6.5 is corrosive, while values above 8.5 may lead to scaling risks. Similarly, attributed the acidity of groundwater in the Abidjan municipalities (Ivory Coast) to the decomposition of organic matter around residential areas.
In the same vein, this acidic character of well water could also be linked to runoff infiltration during the rainy season, as observed by . Furthermore, highlighted that water acidity may result from the acidic geochemical nature of regional soils or from anthropogenic inputs, which may in turn promote the mobilization of metals such as iron. This situation easily explains the presence of iron in our samples, with concentrations close to the WHO limit values, except for well P5 located in the Mohomou neighborhood, where the levels greatly exceed the recommended guideline values. noted that, despite the toxicity of iron at low concentrations, high levels of iron can alter the taste of water and promote the formation of biofilm on the surfaces of well slabs and boreholes.
The average values for TDS (93.33mg/L) and electrical conductivity (186.89 µS/cm) obtained for all the water points indicate low mineralization of the water. These conductivity values are similar to those reported by . However, the high turbidity observed in some of our samples (84.4 NTU), significantly above the 5 NTU threshold set by the WHO , clearly indicates the presence of suspended particles, as well as microorganisms and organic debris in the water. In Burkina Faso, highlighted high turbidity levels in well water, which were associated with the absence of well covers, direct runoff into the wells, and the use of contaminated ropes and buckets.
The average color value was 51.67 UCV, significantly higher than the 15 UCV threshold accepted by the WHO. This coloration is likely due to the oxidation of iron . These values are higher than those reported by , whose study on well water in Congo-Brazzaville found color values ranging from 7 to 10 UCV. Furthermore, the nearly zero levels of active chlorine in our water samples suggest an absence of treatment, which could potentially exacerbate microbiological risks.
The presence of chemical elements, particularly nitrate ions, generally showed values below the WHO threshold. However, values significantly exceeding 20mg/L were recorded in wells P1, P3, P4, and P8, which may indicate moderate nitrogen pollution. This is likely linked to the proximity of latrines near household compounds and water sources, or could be a result of agricultural and domestic effluents. These findings align with the work of . As for nitrites, certain threshold values were reached in a few wells, indicating a concerning situation that could be the result of recent contamination by fecal pollution.
From a bacteriological perspective, indicator organisms, namely total coliforms and fecal coliforms, were found in almost all the water samples, indicating widespread contamination, as none of the samples met the WHO standards for potable water (0 CF/100mL). Among the nine wells studied, 33.3% had an acceptable level, while 66.7% were deemed unsuitable for drinking, highlighting a public health risk that could be exacerbated. A study conducted by revealed that 70% of well water samples they analyzed were unfit for consumption due to fecal contamination. According to , the concentration of indicator organisms of bacterial pollution is higher in well water compared to source water and boreholes. This is likely because well water is stagnant, promoting the deposition of suspended particles.
Multivariate analyses, specifically Principal Component Analysis (PCA) and Hierarchical Cluster Analysis (HCA), were used to spatially structure the pollution through the grouping of variables, highlighting anthropogenic activities, particularly the presence of nitrates, fecal coliforms, and high turbidity, confirming that anthropogenic factors play a decisive role in the deterioration of water quality. The study of spatial variability was demonstrated by in Bamako, Mali, where significant disparities were observed between neighborhoods in terms of water quality, which were related to socio-environmental conditions.
5. Conclusions
The physico-chemical and bacteriological quality of well water in the Mohomou and Belle-vue neighborhoods of the urban municipality of N’Zérékoré was evaluated, revealing that the water does not meet the WHO guidelines and recommendations regarding drinking water standards. The high levels of certain parameters (Iron, pH, Turbidity, Conductivity), along with their non-compliance with the WHO thresholds, indicate pollution of both natural origin, related to the geological nature of the aquifers, and anthropogenic sources, such as domestic wastewater infiltration, the use of animal manure fertilizers, and the proximity of deep latrines. Bacteriologically, 70% of the well water analyzed was contaminated with fecal contamination germs and should not be consumed without prior treatment. Furthermore, the wells were classified based on their pollution levels using Principal Component Analysis (PCA) and Hierarchical Cluster Analysis (HCA), highlighting the need for targeted public health interventions. Preventive measures, such as chlorination, as well as the use of coagulants like quicklime and aluminum sulfate, should be implemented to mitigate the pollution of these well waters.
Abbreviations

WHO

World Health Organization

Conflicts of Interest
The authors declare no conflicts of interest.
References
[1] UN-Water. Summary progress update 2021 - SDG 6 - water and sanitation for all (Version: July 2021). Geneva, Switzerland, 2021.
[2] Davis, R., Hirji, R. Water resources and environment technical note D. 1: Water quality - Assessment and protection. The World Bank, 2003.
[3] Melake, D., Amare, W., Eritrea, T., Seid, M., Tamirat, G. Module sur les maladies transmises par l’eau. Université d’Alemaya, Éthiopie, 2003.
[4] Sintondji, LO., Awoye, HR., Agbossou, KE. Modélisation du bilan hydrologique du bassin versant du Klou au Centre-Bénin: Contribution à la gestion durable des ressources en eau. Bulletin de la Recherche Agronomique du Bénin. 2008, (59), 35-48.
[5] Yapo, OB., Mambo, V., Seka, A., Ohou, MJA., Konan, F., Gouzile, V., Tidou, AS., Kouamé, KV. et Houenou, P. Evaluation de la qualité des eaux de puits à usage domestique dans les quartiers défavorisés de quatre communes d’Abidjan (Côte d’Ivoire): Koumassi, Marcory, Port-Bouet et Treichville. International Journal of Biological and Chemical Sciences. 2010, 4(2), 289-307.
[6] Imran, M., Wani, MA., Mayer, IA., Ibraheem, M., Rashid, S. Evaluation of water quality assessment and its bearings on the residents of Sindh River along Great Himalayan region, J&K-India. International Journal of Research and Analytical Reviews. 2018, 5, J110-J115.
[7] Bashir, S., Aslam, Z., Niazi, NK., Khan, MI., Chen, Z. Impacts of water quality on human health in Pakistan. Water Resources of Pakistan: Issues and Impacts. 2021, 9, 225-247.
[8] Ganaie, MI., Dev, A., Mayer, IA., Ahmed, P., Ganaie, SA. Quality assessment of drinking water sources in the upper Jhelum basin of Kashmir Himalaya, J&K, India. International Journal of River Basin Management. 2022,
[9] Lanta, CH. Poursuite de la description des circuits de distribution du poisson de la pisciculture dans la ville de N’Zérékoré et sa contribution à la sécurité alimentaire des acteurs en aval de la filière. Agriculture, économie et politique, 2023
[10] Rodier, J., Legube, B., Merlet, N. L’analyse de l’eau, eaux naturelles, eaux résiduaires, eau de mer, chimie, physico-chimie, microbiologie, biologie, interprétation des résultats. Ed. Dunod, Paris, 2005, 1384 p.
[11] Ward Jr, JH., Hook, ME. Application of an hierarchial grouping procedure to a problem of grouping profiles. Educational and Psychological Measurement. 1963, 23(1), 69-81.
[12] R Core Team R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, 2024.
[13] Soro, G., Soro, T. D., N’Guessan, M.-R. F., Oi, A., Soro, N. Application des méthodes statistiques multivariées à l’étude hydrochimique des eaux souterraines de la région des Lacs (centre de la Côte d’Ivoire). International Journal of Biological and Chemical Sciences. 2019, 13(3), 1870-1889.
[14] Organisation Mondiale de la Santé. Lignes directrices pour la qualité de l’eau de boisson (4e éd., incorporant le 1er addendum). OMS, 2017.
[15] Organisation mondiale de la santé. Guidelines for drinking-water quality (3rd ed.). World Health Organization, 2004.
[16] Mbilou. UG., Tchoumou, M., Ngouala Mabonzo, M., Balounguidi. J. Caractérisation hydrogéochimique et microbiologique des eaux souterraines dans le système d’aquifères multicouche de la région de Pointe-Noire en République du Congo. Larhyss Journal. 2016, 28. 257-273.
[17] Obami Ondon. H., Mbilou. UG., Nkounkou Tomodiatounga. D., Ngouala Mabonzo. M., Gentil Elenga. R., Mabiala. B. Physicochemical characterization of water of the Plateau of Mbe in Pool-North in Republic of Congo Brazzaville. American Journal of Environmental Protection. 2018, 7(3), 40-54.
[18] Kraemer. SA., Ramachandran. A., Perron. GG. Temperature and microbial dynamics in drinking water. Nature Reviews Microbiology. 2020, 18(8), 439-450.
[19] Tchoumou. M., Louzayadio Mvouezolo. R F., Malera Kombo. MA., Moussoki Nsona. P., Ouamba. JM. Évaluation de la qualité physico-chimique et microbiologique des eaux de puits consommées dans le quartier Kombé à Brazzaville. European Scientific Journal (ESJ). 2024, 20(12), 82.
[20] Koffi, YB., Soro, N., Kouamé, KF. Qualité physico-chimique des eaux souterraines dans la ville d’Abidjan. International Journal of Biological and Chemical Sciences. 2014, 8(4), 1632-1645.
[21] Razanadrasoa, VB., Rasoarahona, J., Rasolomampianina, R., Ratiarimananjatovo, N., Rija, RS., Ridwan, M., Ngbolua, K., Robijaona Baholy, RR. Evaluation of the Physico-Chemical Quality of Well Water in the Analamanga Region (Antananarivo), Madagascar. Budapest International Research in Exact Sciences (BirEx) Journal. 2022, 4(2), 193-201.
[22] Chakrabarti, S. Environmental geochemistry: A global perspective. Springer. 2020.
[23] Deumić, S., El Sayed. A., Hsino. M., Glamočak. A., Crnčević. N., Avdić. M. Investigating the effect of iron salts on E. coli and E. faecalis biofilm formation in water distribution pipelines. 2025. Water. 17(6). 886.
[24] Matini, L., Moutou, JM., Kongo-Mantono, MS. Évaluation hydro-chimique des eaux souterraines en milieu urbain au Sud-ouest de Brazzaville. Afrique SCIENCE. 2009, 5(1), 82-98.
[25] Ouedraogo, B., Sanou, B., Kinda, A. Étude de la contamination des eaux souterraines par les nitrates à Ouagadougou. Revue Africaine de l’Environnement. 2016, 12(3), 28-35.
[26] Rodier, J., Legube, B., Merlet, N., Coll. L’analyse de l’eau: eaux naturelles, eaux résiduaires, eau de mer (9e éd.). Dunod. 2009.
[27] Barhé, TA., Bouaka, F. Caractérisation physicochimique et chloration des eaux de puits consommées dans la ville de Brazzaville-Congo. VJ. Mater. Environ. Sci. 2013, 4(5), 605-612.
[28] Diop, C., Ndiaye, A., Gaye, CB. Pollution des eaux souterraines en milieu urbain: Cas des puits de Dakar. Hydro-Sciences Journal. 2018, 23(1), 34-43.
[29] Camara, M., Diallo, A., & Barry, B. Évaluation de la qualité microbiologique des eaux de puits à Conakry (République de Guinée). Journal Africain des Sciences de l’Environnement. 2020, 15(2), 45-53.
[30] Nanfack, NAC., Fonteh, FA., Payne, VK., Katte, B., Fogoh, JM. Eaux non conventionnelles: un risque ou une solution aux problèmes d’eau pour les classes pauvres. Larhyss Journal. 2014, 17: 47-64.
[31] Traoré, K., Keita, M., Doumbia, L. État de la qualité des eaux de puits à Bamako et risques pour la santé publique. Journal Malien de Recherche Scientifique. 2017, 6(1), 19-29
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  • APA Style

    Zinsou, H. L., Diallo, A. 1., Djidohokpin, G., Cisse, A., Amouzoun, A. A. M. B. (2025). Physico-chemical and Bacteriological Characterization of Well Water Consumed in the Neighbourhoods of N'Zerekore, Guinea. International Journal of Environmental Monitoring and Analysis, 13(3), 94-102. https://doi.org/10.11648/j.ijema.20251303.13

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    ACS Style

    Zinsou, H. L.; Diallo, A. 1.; Djidohokpin, G.; Cisse, A.; Amouzoun, A. A. M. B. Physico-chemical and Bacteriological Characterization of Well Water Consumed in the Neighbourhoods of N'Zerekore, Guinea. Int. J. Environ. Monit. Anal. 2025, 13(3), 94-102. doi: 10.11648/j.ijema.20251303.13

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    AMA Style

    Zinsou HL, Diallo A1, Djidohokpin G, Cisse A, Amouzoun AAMB. Physico-chemical and Bacteriological Characterization of Well Water Consumed in the Neighbourhoods of N'Zerekore, Guinea. Int J Environ Monit Anal. 2025;13(3):94-102. doi: 10.11648/j.ijema.20251303.13

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  • @article{10.11648/j.ijema.20251303.13,
      author = {Hermann Leonce Zinsou and Alhassane 1 Diallo and Gildas Djidohokpin and Aboubacar Cisse and Akhenaton Adonai Mahouklo Bada Amouzoun},
      title = {Physico-chemical and Bacteriological Characterization of Well Water Consumed in the Neighbourhoods of N'Zerekore, Guinea},
      journal = {International Journal of Environmental Monitoring and Analysis},
      volume = {13},
      number = {3},
      pages = {94-102},
      doi = {10.11648/j.ijema.20251303.13},
      url = {https://doi.org/10.11648/j.ijema.20251303.13},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijema.20251303.13},
      abstract = {The unsatisfactory distribution of water by the Guinea Water Company (SEG) has favoured the presence of boreholes and private wells in the urban commune of N'Zérékoré. The aim of this research is to examine the physico-chemical and bacteriological quality of water from wells in two of the town's neighbourhoods, Belle-vue and Mohomou. Nine wells in these neighbourhoods were sampled for the study. Analyses focused on 07 physical descriptors measured in situ; 04 chemical descriptors and 02 bacteriological descriptors, namely total coliforms and fecal coliforms determined in the laboratory. Two multivariate analyses were used to characterise the well water, including Principal Component Analysis and Hierarchical Ascending Classification. The data show a pronounced acidity in all the wells, with mean values ranging from 4.32±0.22 to 5.45±0.00. The water was poorly mineralised, but high levels of turbidity exceeding World Health Organization thresholds were recorded. All three well water points studied were contaminated with total coliform bacteria and faecal streptococci, which are good indicators of faecal contamination leading to bacteriological contamination making the water unsuitable for consumption. Principal Component Analysis (PCA) and Hierarchical Ascending Classification (HAC) were used to discriminate between the nine wells. According to the trends observed, the quality of the wells in the water analysed has deteriorated as a result of multiple factors associated with poor maintenance of the wells. These results call for action to be taken to disinfect wells, in order to guarantee a safe drinking water supply that poses no major health risk to the population.},
     year = {2025}
    }
    

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  • TY  - JOUR
    T1  - Physico-chemical and Bacteriological Characterization of Well Water Consumed in the Neighbourhoods of N'Zerekore, Guinea
    AU  - Hermann Leonce Zinsou
    AU  - Alhassane 1 Diallo
    AU  - Gildas Djidohokpin
    AU  - Aboubacar Cisse
    AU  - Akhenaton Adonai Mahouklo Bada Amouzoun
    Y1  - 2025/06/25
    PY  - 2025
    N1  - https://doi.org/10.11648/j.ijema.20251303.13
    DO  - 10.11648/j.ijema.20251303.13
    T2  - International Journal of Environmental Monitoring and Analysis
    JF  - International Journal of Environmental Monitoring and Analysis
    JO  - International Journal of Environmental Monitoring and Analysis
    SP  - 94
    EP  - 102
    PB  - Science Publishing Group
    SN  - 2328-7667
    UR  - https://doi.org/10.11648/j.ijema.20251303.13
    AB  - The unsatisfactory distribution of water by the Guinea Water Company (SEG) has favoured the presence of boreholes and private wells in the urban commune of N'Zérékoré. The aim of this research is to examine the physico-chemical and bacteriological quality of water from wells in two of the town's neighbourhoods, Belle-vue and Mohomou. Nine wells in these neighbourhoods were sampled for the study. Analyses focused on 07 physical descriptors measured in situ; 04 chemical descriptors and 02 bacteriological descriptors, namely total coliforms and fecal coliforms determined in the laboratory. Two multivariate analyses were used to characterise the well water, including Principal Component Analysis and Hierarchical Ascending Classification. The data show a pronounced acidity in all the wells, with mean values ranging from 4.32±0.22 to 5.45±0.00. The water was poorly mineralised, but high levels of turbidity exceeding World Health Organization thresholds were recorded. All three well water points studied were contaminated with total coliform bacteria and faecal streptococci, which are good indicators of faecal contamination leading to bacteriological contamination making the water unsuitable for consumption. Principal Component Analysis (PCA) and Hierarchical Ascending Classification (HAC) were used to discriminate between the nine wells. According to the trends observed, the quality of the wells in the water analysed has deteriorated as a result of multiple factors associated with poor maintenance of the wells. These results call for action to be taken to disinfect wells, in order to guarantee a safe drinking water supply that poses no major health risk to the population.
    VL  - 13
    IS  - 3
    ER  - 

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  • Abstract
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    1. 1. Introduction
    2. 2. Materials and Methods
    3. 3. Results
    4. 4. Discussion
    5. 5. Conclusions
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