The analysis and interpretation of the geophysical results are helpful to identify different geoelectric layers. From top to bottom, the study area is composed of topsoil, travertines, sandy clay, clayey sand, fractured shales, ferruginous sediments, and metaconglomerates covering granitic bedrock. In addition, complex fault/fracture systems affect the study area making some layers appear in some VES but not in others. These inferred faults on the North and South sides control the flow and accumulation of groundwater in the area.
Geoelectric data processing reveals conductive anomaly areas of low resistivity, which could be interpreted as targets of groundwater. In Ngam camp these areas are highlighted in two geoelectric units (fourth unit and fifth unit), which form the upper and lower aquifers of the area respectively (Fig. 6). The upper aquifer is about 8 to 13 m deep; and the lower aquifer at about 12 to 27 m deep (Fig. 8b). Groundwater in this camp mainly occurs in the altered soils of clayey sand and low permeability fractured rocks such as shales (Fig. 6) with a large thickness (Fig. 10). Despite their low permeability, this aquifer could be exploited in this community (MacDonald and Davies 1998, 2019; MacDonald et al. 2001). However, due to the limited water resources of aquifers in this environment, special attention must be paid to the establishment and management of wells or boreholes, otherwise the possibility of success is very low (Davies and Dochartaigh 2002).
In Borgop camp, the conductive zones occur in shallow fractured bedrocks between 8 and 19 m deep (Fig. 11a). All these aquifers are similar to those obtained by Betah (1976), Djeuda Tchapnga (1987), Kana et al. (2015) and Meying et al. (2018) in Northern Cameroon, and Teikeu et al. (2012) in Yaoundé. Thus, these aquifers constitute the main aquifers in the area and are independent (Mafany et al. 2006). In addition, some geoelectric layers were also depicted in the altered soils, which are ferruginous sediments and metaconglomerates. Ferruginous sediments disrupt good data collection during field measurements through their important telluric field. This characteristic may be attributed to their ferruginous cement (Stafford et al. 2010). According to Stafford et al. (2010), ferruginous sediments show typical features of metaconglomerates and initially unmetamorphosed. As for metaconglomerates, they appear discontinuously in the study area in some VES (0, 5, 11, 24, 25 and 41). This could be due to their location near faults and consequently follows different dips and strike directions (Stafford et al. 2010). Furthermore, their presence in the study area may relate to the Metaconglomerates of Borgop stream, formerly known as ‘‘Borogounous conglomerates’’ (Bresson et al. 1952; Roch 1953), and to the Metaconglomerates of Bah stream and Ka-Borgop mountain (Le Maréchal and Vincent 1972).
Interpretation of the apparent resistivity maps (Fig. 5) shows an irregular distribution of resistivity values in the area with a decrease in low-apparent resistivity values with depth. In fact, low apparent resistivity areas reflecting conducting anomaly could be associated with target of groundwater and high resistivity to the laterite and travertines. For instance, in surficial apparent resistivity maps (Fig. 5), low apparent resistivity areas are associated with the zones of interest for dry season agriculture while at the apparent depth of 6.60 – 8.80 m downwards; they may indicate the existence of aquifers or clay layers. Meanwhile, from the apparent depths of 9.5 – 12.66 m and 13.75 – 18.33 m downwards, these areas are well surrounded by high resistivity, which can be attributed to granitic bedrock. The corresponding low resistivity areas are conducive to groundwater research. This corroborates the findings of Mbog et al. (2019) in the Douala sedimentary basin.
The analysis of true resistivity maps and depth maps of the study area (Figs. 8 – 11) allows mapping low and high resistivity contours and depths, which could be useful for determination of future location areas for new wells in the study area. In fact, the definition of such areas must obey the following criteria: first, select areas with large aquifer thickness and moderate depth. This is to avoid or reduce any potential groundwater contamination or pollutants (Mafany et al. 2006; Ako et al. 2014; Li et al. 2018; Koelmans et al. 2019; Akenji and Tarkang 2019; Mintenig et al. 2019; Sako et al. 2020; Tantoh and McKay 2020; Genter et al. 2021). Second, select highly fractured zones to avoid possible wells dehydration during the dry season. This may be related to the migration of water to deep fractures in the same seasons. Therefore, in Ngam camp, the future location areas follow NE – SW trend, while in Borgop camp, their direction is N – S, more specifically the east side. Moreover, the two orientations (NE – SW and N – S) are consistent with the flow trend of hydrographic network (such as Mbere and streams) and faults in the study area (Figs. 1 and 3). In other words, the groundwater in the study area is likely to flow to the Mbere River and its streams, which constitute the main drainage axes of the area.