The importance of water, sanitation and hygiene for health and development is reflected by the findings of a series of international policy forums. Among the most recent is the adoption of the Sustainable Development Goals by countries in 2015 including a target and indicators for the safety of drinking water. In addition, the United Nations General Assembly declared in 2010 that safe and healthy drinking water and sanitation were a human right essential to the full enjoyment of life and the enjoyment of all Human Rights. These commitments are in line with longstanding support, including the adoption by the United Nations General Assembly of the Millennium Development Goals in 2000 and the proclamation of the 2005-2015 International Decade for Action on the theme “Water is the source of life”, OMS (2017). As the international authority responsible for public health and water quality, WHO leads global efforts in order to prevent the spread of water-borne diseases. To this objective, it promotes health regulations to governments and works with partners to encourage water providers, communities and households to adopt effective risk management practices. In past centuries, the use of water by humans has had no impact on the availability of water on the earth planet until the mid-nineteenth century Boyd (2007), but this water availability becomes a serious threat due to human demographics that experienced an exponential growth especially after the Second World War where the number of the world population tripled from 2.3 to 7.3 billion between 1940 and 2015, LeRoy (1995), and UN (2015). The water consumption per capita, has increased in the world, Boyd (2007). Nowadays, it takes 730,000 litres of water each year to feed and support an inhabitant of the planet, or 2000 lifters per day, ConsoGlobe (2019). Over the world, the largest per capita water users are Americans; for example, water volume consumed per capita for production of goods and services in the United States was only estimated at 2483 m3/person/year (2.4 million litres per person or 6580 litres per day), and approximately 2332, 1682, 1103 and 675 m3 are statistics of the volume of water consumed by each person per year in Italy, Switzerland, Poland and Ethiopia, respectively; while the world average is estimated in the order of 1243 m3/person/year, ConsoGlobe (2019). In France, the volume of drinking water taken in 2012 was 5.4 billion m3. Today, the average consumption of a Frenchman was 148 litres per inhabitant per day Planete (2018); while in Morocco, the average consumption of a Moroccan man was about 70 litres per day. In some countries in Africa and in Asia which have a major lack of water quantity and quality, disequilibria is probably impossible to be controlled while some other parts of Asia, Latin America and Europe risk to face the same situation, Cosgrove & Rijsberman (2014). Moreover, in rural communities in developing countries, the rationale for promoting safe drinking water in rural communities in developing countries is the persistently high levels of water associated morbidity and mortality, WHO (2003). Worldwide, drinking of unsafe water coupled with poor sanitation leads to mortality of at least 1.6 million children under the age of five every year; 84% of them are living in rural areas. If the current trend persists, nearly 1.7 billion rural dwellers will not have access to safe water and improved sanitation by 2015, WHO & UNICEF (2006). In this regards, provision of good quality household drinking water remains an important means of improving public health in rural communities especially in Africa; and is the rationale behind protecting drinking water sources and promoting healthy practices at and around such sources, Gwimbi (2011). The main objective of this study was to evaluate the microbiological quality of different drinking water originated from sources, faucets, fountains and wells in the Beni Mellal city in Morocco and its agricultural surrounding areas.
2. Materials and Methods
2.1. Sampling Zones
This work was performed in the Beni mellal city located in the north-central area of Morocco (Figure 1). Beni Mellal city is precisely situated in the administrative region of Beni Mellal-Khenifra in the center of Morocco. This city is limited to the west by the provinces of Kalaat Es-sraghna and Al Haouz, to the north by the provinces of Khouribga and Settat, to the east by the provinces of Errachidia and Khenifra and to the south by the province of Ouarzazate. From its location between two phosphate plateaus and the Middle Atlas, the region of Beni mellal-Khenifra with an average altitude of 400 to 700 m is characterized by a very continental climate, and the amount of rainfall varies between 300 and 750 mm depending on the year. Jellies are not uncommon in winter. The summer is very hot because of the hot south westerly winds-east “chergui” that increases mercury above 40˚C, these heat waves sometimes end with violent storms that cool the ground.
2.2. Sampling Methods
For what is related to the nature of sampling, we followed the protocol required
Figure 1. Beni Mellal city localization.
by certain international standards ISO (2004), and ISO (2006), (case of the French standard NF ISO 5667-3 (June 2004) and NF ISO 19458 (November 2006)) which describe the way to perform a representative sampling for a microbiological analysis at a faucet, at a source and how to also take a sample from a well using a diver. Transport and conservation of a collected sample for analysis were carried out according to Henri (2002). Of note, weekly sampling in the morning between 10am and 1pm (time of rejection) was regularly carried out at the points chosen during the study period extended from April to June 2018, with one sampling per each selected point repeated each 15 days.
2.3. Sampling Preparation
According to aforementioned guidelines, a total of 120 samples water was collected from Beni Mellal city and in its agricultural surrounding areas at different points randomly selected (point 1 = Treated water represented by faucets water in Beni Mellal city; point 2 = Untreated water representing by natural water of fountains in Beni Mellal city; point 3 = Untreated water representing by natural surface water of sources, Beni Mellal city provinces and point 4 = Groundwater representing by natural water of wells, agricultural surroundings of the Beni Mellal city) for microbiological analysis.
2.4. Microbiological Analysis
Water has been collected in sterile glass vials. Microbiological analyses have been started less than six hours after collection. If the transport exceeds six hours and the outside temperature is above 10˚C; transport has been done in a cool box at a temperature below 4˚C. Finally, the samples are placed in the cold of their arrival at the laboratory before the beginning of the analysis, AFNOR (1987). The researched germs, by using filtration methods, are: revivable germs ISO (1999), Coliforms AFNOR (1985), faecal Streptococci Rodier (1996), Spheres of Anaerobic Sulpho-Reducers ISO (1993), Salmonella AFNOR (1993), and S. aureus, Rodier (1996). The filtered bacteria on discs were inoculated on specific media and incubated at growth temperature corresponding for each bacterium. All microbiological analysis was performed at Biological Engineering Laboratory, Sultan Mouly Slimane University.
The results of the obtained microbiological analyses performed in faucets, fountains and sources waters showed a total absence of faecal coliform count, total coliforms count and Streptococcus D count, S. aureus, Salmonella and Spheres of Anaerobic Sulpho-Reducers, respectively. However, the results of microbiological analyzes of wells waters were contaminated with an important load amount of faecal coliform, total coliforms, Streptococcus D, and S. aureus at threatening levels, which does not meet the standards of potability. Conversely pathogenic germs such as Salmonella and Spheres of Anaerobic Sulpho-Reducers were totally absent in wells waters. The essential of results of the microbiological analysis of waters in different studied points of Beni Mellal city and its agricultural surrounding areas are presented in Tables 1 to 4.
Drinking water is water that can be drunk without risk to health; standards have been established to define a specific drinking water, including the maximum levels that should not be exceeded for a number of harmful substances that may be
Table 1. Microbiological determinations at Fountains.
R.G: Revivable Germs, TC: Total Coliforms, FC: Fecal Coliforms, Stre. D: Streptococcus D, S. aures: Staphylococcus aureus, S.A.S: Spheres of Anaerobic Sulpho-Reducers.
Table 2. Microbiological determinations at Sources.
Table 3. Microbiological determinations at Wells.
Table 4. Microbiological determinations at Faucets.
present in the water. According to these standards, drinking water must be free of pathogens (bacteria, viruses) and parasitic organisms, due to the health risks associated with these micro-organisms. Indeed, water microbiological analyzes allow to assess the risk of pathogenic micro-organisms, which can be found in the waters destined to domestic use, and that could by consequent cause diseases, and also makes it possible to control the effectiveness disinfection treatments, MakhloufI & Abdelouahid (2011).
The results obtained from this study carried out in certain randomly selected faucets, sources, fountain waters, in the Beni Mellal city and its agricultural surrounding environs, are generally proper for consumption, as the results obtained from isolation and enumeration of bacteria reflecting hygienic degree such as Total Coliforms, Fecal Coliforms, Streptococcus D and germs that threat consumer’s health such as S. aureus, Anaerobic Sulphite-reducing Bacteria and Salmonella, were negative (total absence) especially for faucets (treated water), sources (natural water) and fountains (no-treated water). However, water analysis of wells shows a high load amount of bacteria reflecting hygienic degree and also an important charge has been found for S. aureus. Conversely, wells waters were negative for Salmonella and Anaerobic Sulphite-reducing Bacteria enumeration. According to Al Otaibi (2009), the presence of coliforms in drinking water is enough grounds for assuming that a potential health hazard existed (possible presence of pathogens). Water quality requires guidelines and standards setting permissible limits for each parameter, UNICEF & WHO (2008), and Kravitz, Nyaphisi, Mandel, et al. (1999). In addition, the guidelines conferred by WHO on water are generally adopted as the international reference point for standards by those countries not having their own standards. The WHO, data on faecal coliform bacteria group them into the following risk categories: 0 CFU/100 ml (conformity); 1 - 10 CFU/100 ml (low risk); 10 - 100 CFU/100 ml (intermediate risk); 100 - 1000 CFU/100ml (high risk); and 41,000 CFU/100 ml (very high risk), WHO (1997). Concerning Moroccan and Canadian recommendations for the quality of drinking water, in Morocco as in Canada, the maximum acceptable concentration of total coliforms in drinking water has been established at “no detectable micro-organisms per 100 ml volume”, Norme Marocaine (1991). Taken at whole, these national and international standards; we can conclude that all the analyzed samples (faucets, fountains and sources waters) remains generally consumable at microbiological point of view. This is indicating that there is no recent contamination of the analysed water, by human or animal faeces in these analysed points. As a result, these findings indicate highly proper quality compared to previously reported data in developing countries. Thus, Gwimbi (2011) in drinking water in Manonyane community in Lesotho especially for sources water. From this study, Gwimbi (2011) showed that the number of total coliform and E. coli counts found in unprotected water sources suggest that poor source water protection leads to a poor sanitation conditions which are potential reasons for the high presence of microbiological contaminants. The big difference in the microbial counts from water samples of similar protection status might be indicative of widely varying hygiene behaviours in the households. In our study, the analysed water originated from wells (groundwater) remains generally improper for consumption in comparison with available national and international standards and to previous studies. The results obtained in this station show that almost of wells samples were contaminated at advancing levels by reflecting hygienic bacteria. These load amounts are principally reflected by high charges of faecal contamination indicator parameters (faecal coliforms, total coliforms and Streptococcus D) encountered in groundwater originated from wells, which is due in most cases to human activities in the well environment. According to Diop (2006), the absence of these bacteria in 100 ml of filtered water is standardized by regulation. Faecal streptococci are also among the most commonly used as faecal contamination indicator group for drinking water. Faecal streptococci are much more resistant to disinfection including chlorine than most pathogenic organisms and coliforms. This explains their presence in drinking water and gives them a certain interest for the control of treatment efficiency, Diop (2006). Total coliforms are a group of bacteria that are frequently found in the environment, for example in soil or vegetation, as well as in the intestines of mammals, including humans. Total coliforms generally do not cause disease, but their presence indicates that a source of water can be contaminated by more harmful microorganisms. E. coli is the only member of the total coliform group found exclusively in the intestines of mammals, including humans. The presence of E. coli in water indicates recent faecal contamination, and may indicate the possible presence of disease-causing pathogens Ministère de l’Environnement (2004), and Ivey, deLoe, Kreutzwiser et al. (2006), such as bacteria, viruses and parasites. According to Ivey, deLoe, Kreutzwiser et al. (2006), the presence of E. coli in water suggests enteric pathogens and faecal pollution; this has been also reported to be the causative agent of haemorrhagic colitis, diarrhoea, urinary tract infection, and haemolytic uraemia syndrome in similar studies elsewhere according to Esrey, Feachen, & Hughes (1985).
The interest of the detection of these coliforms makes it possible to detect a faecal contamination resulting for example from infiltrations of polluted water in the pipes. They are also good indicators of the effectiveness of water treatment. Regarding the search of revivable germs in the waters analyzed, our findings showed high loads for water mainly originated from sources, and fountains. However, there is a total absence of these germs in water wells originated from faucets (treated water).
Concerning pathogenic bacteria, the search of germs such as S. aureus, Salmonella and Anaerobic Sulphite-reducing Bacteria in the whole analyzed samples revealed a total absence in all almost faucets, sources and fountains waters while S. aureus was only detected, at treating levels, in well waters. In general, this contamination could occur during and after precipitation, bacteria and other dangerous micro-organisms can enter rivers, lakes and groundwater. A poorly constructed or poorly maintained well can increase the risk of contamination. As a result, these waters are considered unfit for consumption. In literature reviews, the harmful effect of wastewater on the quality of surface and groundwater and also on the quality of food stuffs and human health has been demonstrated by several studies, Kholtei, Bouzidi, Bonini et al. (2003), Montiel (2004), El Kettani & Azzouzi (2006), Talouizte, Merzouki, El Ouali et al. (2007), and El Ouali, Zanibou, Bekhti et al. (2014). As well, urban wastewater contains also a lot of nutrients (macronutrients N, P, K, Ca, Mg and micronutrients Fe, Zn, Cu, Mn...) which are extensively utilized by bacterial populations, El Ouali, Zanibou, Bekhti et al. (2014), and Thomas (1995).
Nowadays, several diseases that affect the planet’s population are described to be partially associated to the inadequacy of the evacuation of domestic and industrial wastewater. These have become increasingly enormous in the face of industrial development, economic growth, population growth and the high density of urban areas. Without any treatment, these wastewaters present an increasing danger to human health and the natural environment because of their toxic chemical charges and pathogenic microorganisms (bacteria, viruses, parasites, etc.). They are therefore permanent and serious threats to both human and animal health, Talouizte, Merzouki, El Ouali et al. (2007), Ait melloul, Amahmid, Hassani et al. (2002), and Nimri, El Nasser, & Batchoun (2004). Of note, several studies of the impact of liquid effluents, particularly in Morocco, on groundwater quality have led to the wastewater being discharged without treatment, Zakari, Fekhaoui, & Bahou (1993), Lyakhloufi, ER-Rouane, Ouazzani et al. (1999), Chalbaoui (2000), Tazi, Fahde, & El Younoussi (2001), Kholtei, Bouzidi, Bonini et al. (2003), El Guamri & Belghyti (2006), El Mostafa, Bouzidi, Koulali et al. (2006), Aboulkacem (2007), and El Mostafa, El Kettani, Koulali et al. (2010). From this, it appears the necessity and the importance of treatment of these wastewaters avoiding their random evacuation in environment.
In general, the majority of the water originated from faucets, fountains and sources is proper for consumption in microbiological point of view. Moreover, the water originated from wells is improper for consumption, because these waters were grossly polluted with coliforms and streptococcus D. Wells waters were also contaminated with pathogenic germs such as S. aureus. The effects were generally attributed to a set of factors such as wastewaters evacuation in environment; poor wells water protection, poor sanitation and low level of hygiene practices, and lack of monitoring and healthcare awareness. It appears, from the results obtained, that the potential risk of infection of water consumers especially (groundwater) calls for prompt intervention in order to alleviate the potential health impact of water-borne diseases in the community. From this, a proper sanitary survey and implementation of water and sanitation projects in the community is recommended.
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