Physicochemical and Bacteriological Quality of Ground Water in the Basin of Gounti Yena Valley in Niamey City (Niger Republic)

The Gounti Yéna valley, the subject of this study, is a tributary of the Niger River, it is the main watercourse that divides the left bank of the city of Niamey into two unequal parts. The surface area of its watershed is estimated at about 62 Km 2 . The objective of the present study is on the one hand to evaluate the current state of the physico-chemical and bacteriological quality of the water of Gounti Yéna basin, and on the other hand to define the risks of water pollution and its origin in the face of the phenomenon of rising water table of this basin. In order to carry out this work, we proceeded to a study of the evolution of the physicochemical and bacteriological parameters of the water of the basin of Gounti Yéna during the period going from November 2020 to October 2021, at the level of four points of sampling chosen from the upstream to the downstream of the basin. The results obtained showed that the


Introduction
Today, the world is facing many challenges, including an ever-increasing population and often anarchic urbanization [1]. It is believed that population growth accompanied by rapid urbanization is causing numerous disturbances to the natural environment.
Not a single region of the world is immune to meteorological mood swings, only, depending on certain parameters such as their geographical position, their geological and geomorphological nature some are more exposed than others. In the Sahel, one of the parameters of climate change is an exacerbation of climatic hazards, including floods. For several decades, the populations of West African cities have been confronted with flooding problems. The causes of flooding in the various African cities are almost everywhere the same. They are always caused by climate change, accentuated by the effects of demography, the anarchic expansion of cities, the lack of drainage systems, deforestation, etc. In Niger, floods are now at the heart of the disaster risks faced by the country. They are the second most common natural disaster after droughts. Floods are not a new phenomenon in Niger because, since the beginning of the 1990s, there has been an increase in floods throughout the country. These can take many forms, including rising water tables and runoff due to climate change and anthropogenic effects.
In the city of Niamey, there are three types of flooding [2].
Pluvial floods due to the recording of heavy rains in the city of Niamey. These floods affect almost all the districts of the capital due to the inadequacy or lack of a sewerage system. River flooding: this is observed in the districts along the river, below 180 m in altitude. They occur most often during periods of flooding, which are of two types (local flooding and Guinean flooding). In Niamey, rainfall is characterized by great variability in space and time, from one year to the next and according to dry or wet periods [2]. In addition to these variabilities, the modification of the vegetation cover disrupts the distribution of water at the surface and in the soil. If the aquifers of CT1 and CT2 seem hydraulically not very active, the surface water table (CT3). On the contrary, it is regularly fed by the rains and the volumes circulating in it are much greater than in the levels below Niamey. For example, on the slopes and lowlands of southwestern Niger, the replacement of the natural savannah by millet crops has had a H. A. Hado et al. Journal of Water Resource and Protection triple action favoring runoff, the concentration of runoff in the lowlands and then the recharge of the water table, which is multiplied by ten [3] [4].
Throughout the Sahel, the droughts of the 1970s and 1980s led to a significant drop in groundwater levels. In recent years, with the return to normalcy, many studies have attempted to highlight the rise in the water table, for example [5] states that the water table in southwestern Niger has been rising continuously for the past decades (4 m rise from 1963 to 2007). Boubakar H., 2010 [6] who noted a rise of 2.2 m in ten years in the city of Niamey on a well and Alassane Hado H. et al., 2021 [2] having observed a rise of 20 and 40 m in 60 years in the same city where this water table can outcrop in some places with many impacts. In the city of Niamey, flooding by an accumulation of runoff water or by indirect overflow (water rises through the alluvial water table in the sewerage system) has been observed on the left bank of the river [7].
These floods lead to the collapse of wells or the submergence of access roads to water points, aggravating the sanitary conditions of water extraction and transport, and making the water unsafe to drink. In these areas, individual or collective sanitation (wastewater, rainwater and household waste disposal) is nonexistent or non-functional [8], which exposes this environment, in addition to being urban, to a pollution phenomenon. Indeed, the urban environment represents by definition a concentration of activities and populations, the importance of which conditions the complexity of the various equipment to be implemented. This problem of pollution is known in all the large cities of the world, and has been the subject of many debates. Wells are still very vulnerable to pollution, especially from latrines and septic tanks. Septic tanks play an important role in the transmission of bacteria, as well as the different layers of the soil. Nitrate pollution has already been highlighted by [9] and [10]. [11] recommends the monitoring of water quality in the city of Niamey. As far as microbiological pollution is concerned, [12] confirms that the water of this city is really impacted.
With this rise in surface water, we observe the stagnation of water that now constitutes permanent pools with the development of the female anopheles causing malaria, without noting the appearance of other water-borne diseases.
These floods also cause many environmental, social, economic and health impacts. Developing countries are the most affected by these health problems because, due to lack of resources, water does not undergo purification treatment before being consumed and the quality of this water has deteriorated during its transport. As a result, nearly two million people in poor countries die every year from diarrheal diseases caused by unsafe water, poor hygiene and inadequate sanitation [13]. It is most often difficult to prove that the cause is water. Some [14] believe that the problem affects more the vulnerable and poor populations of the disadvantaged neighborhoods, while the flooded SONUCI neighborhood in Niamey is rather a symbol of an economic success story of the 1980s.

Presentation of the Site
A small village in the 1930s, Niamey became the first urban center in Niger in 1952, with 11,790 inhabitants; in 1972, its population exceeded 100,000 [15]; this population exploded between 1960 and 2020. As of December 2012, the population of the study area is 1,026,848. The urban community of Niamey, today with city status forms an enclave in the department of Kollo (Figure 1). Its altitude ranges from 160 m to 258 m. It is divided administratively into five communal districts and today has nearly 1.5 million inhabitants and covers nearly 300 km 2 [16].
The relief of the city is not very marked, on the left bank of the river, upstream from the alluvial plain, a plateau rises to an altitude of about 230 m. The city of Niamey is mainly developed on this plateau covered by thin formations [7].
Annual rainfall has generally varied from 500 to 750 mm with a very exceptional extreme of more than 800 mm in 1998; the average annual temperature from 1995 to 2004 is 30˚C. The highest temperatures are recorded in April and May at 35˚C [17]. However, [6] states that in recent years, rainfall (annual accumulation) rarely exceeds 600 mm/year.  The Gounti Yéna valley, the subject of this study, is a tributary of the Niger River and has become one of the main sites of domestic wastewater in Niamey [18]. The Gounti Yéna is currently an almost permanent feature following the drainage of wastewater and groundwater [16] [19].
Located in communal districts I, II and III (Figure 1), this valley collects wastewater and rainwater from several districts of the city, from Boukoki to the Zongo district before discharging into the Niger River between the Palais des Congrès and the Gawaye Hotel ( Figure 1).
Overall, the groundwater in Niamey is polluted and this pollution has increased since 1995 [20].

Domestic Water Supply Sources
Water supply is provided by surface water (rivers, lakes, ponds, dams), groundwater (wells, boreholes, springs) and rainwater [21]. In the city of Niamey, water supply is provided by the Société des Eaux du Niger (SEEN), which distributes water from the Niger River after seven stages of treatment to subscribers divided into individual, private, social, standpipe, commercial, large-scale consumer, diplomatic representation, state budget administration, state subsidy, state subsidy offices and local authorities. After treatment, this water is sent to the distribution network. The rate of water supply to this population is 82% in 2014. The small part not yet served ( Figure 1) of Gounti Yéna basin exploits water from wells or boreholes often made without respecting standards for domestic needs.
Water needs are not constant over time. In Niamey, they are closely linked to population growth and the extension of the water supply network [22].

Surface Water
Surface water includes streams (rivers) and natural or artificial reservoirs. These surface water have a more or less regular quality depending on the discharges that flow into them or on rainfall runoff [23]. They have the advantage of quantity but the major disadvantage of being highly charged with suspended matter, and even with pathogenic elements; this implies often complex and expensive treatments to make the water drinkable for domestic use. The literature shows that surface water is only consumed directly in rural areas where there is no public water supply or where boreholes are out of order [24]. In the Niamey region, there are no permanent rivers other than the Niger River and the few significant intermittent rivers are on the right bank [25].

Groundwater
Groundwater is the preferred water resource for drinking water, as it is safer from pollutants than surface water [26]. They are the water of the aquifers, layers of permeable ground saturated with water.
The first water table encountered below the ground is the water table located at a depth of fewer than 50 meters and generally separated from the surface by a

Geology of the Study Area
The geology in Gounti Yéna basin is made up of three (3) geological entities: At depth, the Meta-Liptako basement of lower Proterozoic age is composed of plutonic (granites, granulites) and metamorphic (gneisses, quartzites, greenschists) rocks in different states of alteration; This basement is covered by the Terminal Continental of middle Eocene to Pliocene age and consists of alternating sandstones more or less clayey and versicolored clays with intercalations of levels of ferruginous oolites, these are the lands outcropping in the region west of Niamey belong to a vast spread quasi-horizontal sandy-loam reinforced by lateritic or grésifiés levels and crowned by a cuirassed plateau. However, Niamey being located on the extreme southwestern edge of the Iullemmeden basin, it comprises only one layer known as CT3 [27]. Finally, near the Niger River and at the level of the koris are the quaternary alluviums which are composed of coarse, loosely compacted sands.

Hydrogeology of the Study Area
The three geological formations give rise to different aquifers: the basement aquifer captured by the deep boreholes, the Continental Terminal 3 (CT3) aquifers and the alluvial aquifer captured by the shallow wells and sumps. The piezometric levels measured in 2020 and 2021 confirm a groundwater flow that runs mainly from NNW to the South [11] towards the river and a drainage towards the Gounti Yéna that is superimposed on this main flow axis [2]. The hydrogeological functioning of the Continental Terminal water table has been studied and detailed by Leduc et al., 1996 [28].

Origin of the Rise of the Water Table in Niamey
After the two great decades of drought that affected the Sahel, the return to normal is taking place through fairly normal rainfall. However, the annual rainfall total is not the only explanation for the phenomenon. Nor is the increase attributable to a decrease in withdrawals, since, on the contrary, there has been a multiplication of withdrawal points and a doubling of the population in 20 years.
The most obvious and logical explanation is that the change in vegetation cover has increased infiltration to the water table, with a decrease in the demand on the water table due to the expansion of the city's drinking water distribution network. off. However, in addition to the climatic and anthropogenic conditions leading to these rises, natural conditions linked to the geology and geomorphology of the area must be taken into account.

Setting up a Monitoring Network
The monitoring network is composed of one borehole and three wells (all private) ( Figure 1). The results of the measured parameters will be presented in correlation with the piezometric levels of the wells.

Piezometric and Rainfall Data
Piezometric readings have been conducted on private wells since 2019 at weekly measurement steps during the rainy season and monthly steps in the dry season. This is to assess and better understand the response of the water table to rainfall inputs. Even if a large part of these wells have levels below 3 m. As for the rainfall readings, they are taken from two direct-reading rain gauges set up as part of this work (upstream flooded sector and downstream flooded sector).

Frequency of Measurements
Within the framework of this study, various parameters were determined with regard to water quality: physicochemical and bacteriological parameters (E. Coli).
For the physical parameters, such as conductivity, temperature and pH, they were taken during the two main periods of variation of the water table during the year 2021, namely the "high water" period in September when the water table reached its maximum rise and the "low water" period in May when the lowest level of the water table is recorded. These measurements are made at the scale of the basin with a good distribution on wells (63 in total), which then allowed interpolating these values in order to establish a cartography. Thus, we can easily observe the variations of these parameters according to space and time.
Regarding the physicochemical analyses, major ions and some heavy metals were measured, they are: Calcium, Magnesium, Sodium, Potassium, Bicarbonates, Chloride, Sulfates, Nitrates, Lead, Ammonium, Cadmium, Copper, Nickel, Chromium, Zinc, Phosphorus and Iron. These elements were measured and monitored in the different samples mentioned above at monthly measurement steps for one year during the period from November 2020 to October 2021.
The microbiological characterization was focused on the levels of indicators of fecal contamination described by [29] and [30]. The levels of indicators of fecal contamination were focused on the determination of the rate of E-coli. These levels were determined and their evolution followed in the same samples. This time, during three periods: the rainy season, the cold dry season and the hot dry season.

Sampling Campaigns
Within the framework of this study, campaigns were carried out with the aim of For the physical parameters (T˚, C and pH); they were determined in situ as in [31].
The water is taken in two different 500 ml sterilized bottles. The bottle intended for the physicochemical analyses is filled to the brim to avoid the formation of air bubbles. For the determination of bacteriological parameters, the bottle is not completely filled in order to allow the bacteria to grow well. Both vials are stored in a cooler and transported to the laboratory.
A total of 816 measurements were made, 204 measurements per sample at the four selected sampling points.

Tools
For the determination of the physicochemical parameters, the materials used are: the digital titrimetry HACH, the spectrophotometer HACH DR/3800 and the flame photometer of mark JENWAY PFP 7.
For microbiology, we needed several tools such as 2 pipettes: 1ml and 9 ml, 1 pipette 8 tips, 4 trays, 4 sterile bottles of 15 ml, sterile tips, ringers lactate, 1 marker, gloves, a support for bottles and a trash can.
For piezometry, a 50 meter long light and sound piezometer probe was used.

Analytical Techniques for Physicochemical and Bacteriological Parameters
A small number of chemical contaminants in drinking water are harmful to human health when exposed for a long time. However, they represent a very small proportion of the chemicals from various sources that can enter the water. Physicochemical parameters related to the natural structure of water include temperature, pH, conductivity, major ions: bicarbonate, chloride, sulfate, calcium, magnesium, sodium, potassium and others [32].
In contrast to the microbiological risk, which is short-term, the chemical risk is essentially medium and long-term [33].

Methodological Approach  Physicochemistry
The different analytical techniques for chemical parameters are as follows:

Water Facies
To compare the water, we represented the chemical analyses as triangular (Piper) and semi-Logarithmic (Schoeller-Berkaloff) diagrams.  Nitrates are the main anions when mineralization is high while bicarbonates are more significant when mineralization is low [35], so in the face of relatively low mineralization, bicarbonates dominate over nitrates.

pH
The pH of water allows highlighting the chemical species present in a sample. It is referred to as acidic pH, neutral pH or basic pH. The pH is measured by a potentiometric method by measuring the potential difference between a glass electrode and a reference electrode. There are no health-based guide values for pH.
Although pH does not usually have a direct effect on consumers, it is one of the most important operational parameters of water quality.
All of the measured wells tap into the Ct3 water table. The temporal evolution of pH for all these wells shows a slight decrease during the rainy season. In particular, with the arrival of new rainfall, the mass of acid precipitation accumulated during the dry season recharges the water table and lowers its pH. These observations are in agreement with the work of [36] and [37].
The water of the CT3 aquifer is acidic with a pH ranging from 4.9 to 7.0 with a median value of 6.2 [38]. The pH values in this study indicate that the water is acidic to slightly basic with a pH ranging from 5 to 8 (Figure 4)    results. Furthermore, [38] states that the axis of Gounti Yéna appears to be a zone of relatively more basic or neutral pH and that the left bank was in 1986 a zone of generally neutral pH and locally weakly acidic or basic. This is reflected in the maps in Figure 4 and Figure 5.
The higher pH values may be the result of CO 2 consumption or degassing that results in a relative increase in 2 3 CO − ion compared to 3 HCO − ion.

Hardness
Water hardness is due to a variety of dissolved polyvalent metal ions, mainly calcium and magnesium cations. It is usually expressed in milligrams of calcium carbonate per liter. Hardness is the usual measure of the ability of water to react with soap, with hard water requiring considerably more soap to produce foam.
The total hardness of water is produced by the calcium and magnesium salts it After classification, the water in the study area range from very soft to soft (Table 1). Wells P1 and P9 have a soft character while well P4 and borehole F1 have a hardness that is in the "very soft" class.

Temperature
Groundwater temperature is related to factors such as its proximity to the ground surface and seasonal variations. The temporal evolution of temperature for all wells indicates that the water temperature follows the air temperature ( Figure 6 and Figure 7). These values reflect the annual atmospheric temperature at the Niamey station. They are consistent with results found by [7] Figure 6) and from 27˚C to 33˚C in high water (Figure 7).
However, high temperatures favor the development of microbiological activity, which is often the cause of pollution.

Electrical Conductivity
Conductivity allows a quick and approximate evaluation of the overall mineralization of the water. Conductivity is measured by measuring the conductance of water between 2 metal electrodes, it is the inverse of electrical resistivity. Deep aquifers are characterized by high conductivity and that of groundwater is low, with a median of 198 μs/cm and extreme values of 30 and 501 μs/cm [36]. After this characterization of [37] not having taken into account the character or at least the behavior of the water table in an urban environment, [2] also states that the free water table of the Continental Terminal appears to be poorly mineralized (generally less than 100 μs/cm). While since 1997, [39], had specified the range of variation of the conductivity of the Continental Terminal aquifer in Niamey which is quite wide (10 to 6800 μs/cm). The results found in this study are consistent with this variation and are close to those obtained by [40] fluctuating from 400 to 2400 us/cm and [41] to state that these conductivities can exceptionally reach values of 7000 us/cm.
Conductivities vary from 20 to 1500 μs/cm in the dry season ( Figure 8) and from 20 to 3000 μs/cm in the rainy season ( Figure 9). The increase in the conductivity of the water of the Gounti Yéna basin is due to the intense evaporation that induces a strong mineralization of the water in salts, which increases the conductivity of the water [41] on the one hand and on the other hand this electrical conductivity increases with the piezometry of the water table. The high mineralization can be explained by the infiltration into the water table of rainwater that has solubilized domestic waste, or of dirty water from latrines and poorly maintained gutters.
On the isoconductivity maps, it can be seen that the dissolved salt concentration nuclei correspond to areas with high population density, i.e., old neighborhoods such as Boukoki, Deyzeibon, Zongo, South Lazaretto, etc. This relationship between concentration of dissolved salts and population density is also clearly seen in the new settlement areas where the value of the latter is lower, such as the Karsamba district, upstream of the basin. It appears that in 1986, the whole of the urbanized left bank is an area of low electrical conductivity, less than 500 μs/cm [38], this value corresponds today to that of the semi-urbanized sector. It is not excluded that in addition to this very important factor of population density the lithological nature of the aquifer influences the concentration of dissolved salts.   Calcium is an alkaline earth metal that is extremely common in nature, especially in limestone rocks in the form of carbonates. It is the major component of water hardness. The arrival of the infiltration water corresponds to a decrease in the calcium content. We notice through Figure 10 that as soon as there is a rainfall, the level of the water table rises and the calcium content drops. These contents varying from 0 to 42 mg/l ( Figure 10) are below the standards fixed by the WHO.

2) Magnesium
Magnesium is the second significant element of water hardness after calcium.
The levels are low for groundwater with a maximum of 9.5 mg/l (Figure 11), the WHO standard being set at 50 mg/l.

3) Sodium
Sodium salts (e.g. sodium chloride) are present in virtually all foods (the main source of exposure) and in drinking water. Although sodium levels in drinking water are generally less than 20 mg/l, they can be much higher in some countries. Levels of sodium salts in air are normally low compared to levels measured in food or water. It should be noted that some water softeners can significantly increase the sodium content in drinking water. These levels increase inversely with the rise in the water table ( Figure 12).
The Sodium absorption rate (SAR) of the different samples and their conductivities ( Figure 13) demonstrate that they have a low alkalizing power through the Riverside diagram, which implies that these water can then be used on any type of soil in irrigated crops without danger of alkalization of the soils used.

4) Nitrite
Nitrite is produced either by incomplete oxidation of ammonia or by reduction Figure 11. Variation of Magnesium content in GY groundwater according to piezometry.

6) Potassium
Potassium is a mineral salt that plays an essential role in the proper functioning of the body. On the other hand, a very high level of potassium in the blood can be dangerous and have serious consequences (for example serious cardiac problems). It is an essential element for humans and is rarely, if ever, present in drinking water at levels that could present a risk to human health. The recommended daily intake is over 3000 mg. Potassium is widely distributed in the environment, including all natural water. It may also be present in drinking water as a result of the use of potassium permanganate as an oxidant in water treatment.  In some countries, potassium chloride is used in ion exchange columns for domestic water softening instead of or in mixture with sodium chloride, so that potassium ions are exchanged with calcium and magnesium ions.
Levels of this element are highest at the beginning of the rainy season, just at the first reaction of the water table (Figure 16). The fact that these levels are higher at the beginning of the season indicates that external inputs (atmospheric and anthropogenic) are more important at this period. We note levels exceeding the WHO standards, especially during the rainy period.

7) Bicarbonates
There is no WHO standard for this element, but a high concentration of bicarbonates gives a salty taste to the water. These levels are probably due to the low dissolution of carbon dioxide in the soil. They are lower during the hot dry period, especially in February, March, April and May ( Figure 17).

8) Sulfates
Sulfates are naturally present in many minerals and are marketed mainly to the chemical industry. Their presence in water comes from industrial waste and atmospheric deposition. However, the highest levels are usually found in groundwater and are naturally occurring. In general, the average daily intake of sulfates from drinking water, air and food is about 500 mg, with food being the major source. Sulfate levels are low, and levels recorded throughout the study period do not exceed the limited standard [13]. The variation in these levels is also consistent with the piezometry (Figure 18).   The main source of chloride exposure for humans is the addition of salt to food, and intake from this source is usually significantly greater than from drinking water. The chloride ion is never absorbed by geological formations, it is a special element. High chloride concentrations are related to water pollution.

9) Chlorides Journal of Water Resource and Protection
The concentrations of this element are heterogeneous ( Figure 19) with an almost similar evolution of the curves (piezometry-chloride content).

Heavy Metals
Heavy metals such as lead, cadmium, cyanides, mercury, etc. are dangerous, even in trace amounts.

1) Lead
The standard set by the WHO is 0.01 mg/L and no trace of lead has been detected in the various analyses.

2) Ammonium
The term ammonia includes both non-ionized (NH 3 ) and ionized ( 4 NH + ) species. Ammonia in the environment is generated by metabolic, agricultural and industrial processes; it can also come from disinfection with chloramine. Intensive livestock production can result in much higher levels in surface water. Ammonia contamination can also come from the lining of cement mortar pipes.   According to [9], the ammonia assay gave very low results in the wells, but high to very high in the surface water (Gounti-Yéna and pond). This ammonia pollution has also been demonstrated by [38] on a well in a garden in Gounti-Yéna.

3) Cadmium
Cadmium enters the environment through wastewater; diffuse pollution is due to contamination by fertilizers and local air pollution. Contamination of drinking water can also be caused by impurities in zinc used in galvanized pipes and welds and in some metal fittings.
Cadmium accumulates primarily in the kidneys and has a long half-life in humans (10 to 35 years). Cadmium has been shown to be carcinogenic when inhaled and IARC has classified cadmium and its compounds as Group 2A (probably carcinogenic to humans). However, there is no evidence of oral carcinogenicity of cadmium and no clear evidence of genotoxicity. The kidney is the primary target organ for cadmium toxicity. All values of the measurements are zero, thus below the WHO standards ( Figure 21).

4) Cuivre
Cuivre is both an essential nutrient and a contaminant of drinking water. Levels in running water or after complete purging tend to be low, while in samples Consumption of stagnant water or water from partially purged distribution systems can significantly increase total daily exposure to copper. No values during the monitoring period exceeded the WHO standard.

5) Nickel
The contribution of water to nickel exposure can be significant when, for example, the level of pollution is high and non-resistant materials are used in well construction. The most common effect of nickel in the general population is allergic contact dermatitis. The WHO standard is 0.07 mg/l and the measured levels in the groundwater (Figure 23) are well below this, and the levels also fall during the rainy season.

6) Chromium
Chromium is widely distributed in the earth's crust. It has a range of valences from +2 to +6. Chromium (III) is an essential nutrient. The maximum value accepted by the WHO is 0.05 mg/l. All measurements are heterogeneous and for a very large part exceed the WHO standards ( Figure 24).

7) Zinc
Zinc is an essential trace element found in virtually all foods and drinking water as salts or organic compounds. Although zinc levels in surface water and groundwater do not usually exceed 0.01 and 0.05 mg/l, respectively, concentrations in tap water can be much higher as a result of dissolution of zinc from pipes. The WHO standard is 3 mg/L, and groundwater is well below this ( Figure 25).    Phosphorus should not be monitored in groundwater because it has no known harmful effects in this environment, but we determined it anyway. For all analyses, high levels are observed in March ( Figure 26). This increase in phosphorus concentration in the water of Gounti Yéna basin during this period is due to the increase in organic compounds in the water, which favors a very thorough mineralization of organic matter.

9) Iron
The presence of iron in domestic water supplies is not desirable for a number of reasons. Iron is a fairly abundant element in rocks. It is soluble as Fe 2+ (ferrous ion) but insoluble as Fe 3+ (ferric ion).
Iron is one of the most abundant metals in the earth's crust. It is present in natural freshwater at levels between 0.5 and 50 mg/l. The presence of iron in water can promote the proliferation of certain strains of bacteria that precipitate iron. The WHO standard is 0.3 mg/L. Well P9 is the only well with a concentration exceeding the WHO norms ( Figure 27) and this, in the month of June. Journal of Water Resource and Protection

Microbiological Parameters (E-Colis)
The bacterial load is slightly elevated in the hot dry season for P9 sub-surface ( Figure 28); this load decreases during all the other two periods of the year for this sampling point. It is much higher in the wet season for wells P1 and P3 than in the hot dry season and finally in the cold season ( Figure 28). It remains constant throughout the year at well F1.
All sampling points except well F1 are contaminated by agents of fecal origin.
The quantity of microorganisms present in the water increases with rainfall, apparently for groundwater, although no study to date has been able to establish a simple law formally modeling these two parameters. Microorganisms are very common in surface water, but increasingly also in groundwater ( Figure 28).
This contamination occurs especially when the groundwater is fed by rainwater infiltration or directly by polluted water. They are the group of pollutants that cause the most diseases. It should be noted that the survival time of pathogens (bacteria) is shorter in acid soils (pH 3 -5) than in basic soils.
The comparison of results before and after chlorination and emptying of the wells shows no difference, which indicates that the contamination measured is that of the water table, and not that induced locally by operating conditions and by land use in the immediate vicinity of the wells.

Origin and Factors of Pollution of Water for Domestic Use
The origin of water pollution can be natural or anthropogenic [42]. The main factors that control the physical-chemical and bacteriological quality of water are anthropogenic activities, hydrogeological context and climate [43]. [42] clarifies that the main sources of anthropogenic pollution are agriculture, which is applied diffusely over the territory; industries, which are the source of very diverse Journal of Water Resource and Protection

Conclusions
The path followed by water from the soil surface to the aquifer system gives it its characteristic chemical quality. It acquires several forms before reaching its final location (the water table) where it stays with more or less long contact with the reservoir rock for the acquisition of its mineralization. The surface water is gen-H. A. Hado et al. Journal of Water Resource and Protection erally shallow and outcropping in the context of this study with a maximum level of less than 3 m, which means that they create permanent pools in some places that are much more exposed to pollution, especially in urban areas like Niamey. The communication between surface water and subsurface water leads to the transfer of certain water quality parameters.
This study of monthly follow-up over a period of one year is carried out with the aim of characterizing, for the first time, the quality of the water of Gounti Yéna basin in front of the new phenomenon of flooding due to the water table.
This work provides important information based on physico-chemical and bacteriological descriptors.
The wastewater discharges and the septic tank-groundwater interconnection in this area are therefore largely responsible for any bacterial and chemical pollution of the groundwater. The communication between the SEEN drinking water distribution network and the contaminated water bodies makes the distributed water potentially polluted, constituting a source of waterborne diseases.
Groundwater has a relatively constant content of various elements, but this can change rapidly with the arrival of the first rains. The results obtained show that the spatio-temporal variation of the bacterial load of the water of Gounti Yéna is much higher in the hot dry season, relatively high in the rainy season and lower in the cold dry season.