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Paper ID:IJSREM67032

Groundwater Quality Assessment Using active Monitoring and GIS Technologies: A Case Study of Zirabad Reservoir Area, Madhya Pradesh, India

Stream/Area:

-

Subject:

-

Paper ID:

IJSREM67032

Volume:

10 |

8 |

Aug 2026

Pages:

1-12

Publication Frequency:

Monthly (12 issues per year)

DOI
Digital Object Identifier
10.55041/IJSREM67032

License:International Journal of Scientific Research in Engineering and Management follows the Creative Commons Attribution 4.0 (CC BY 4.0) License, allowing free use and distribution with proper attribution.

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Authors

KS

Kanya Solanki

School of Studies in Earth Science

Samrat Vikramaditya Vishwavidyalaya, Ujjain, M.P.

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DK

Dr.Vinita Kulshreshtha

Dept.Of Geology

Govt. PG College Mandsaur

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MKK

Manish Kumar Kothe

PVG College of Engineering Mhasrul

PVG College of Engineering Mhasrul, Nashik Maharashtra,India

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Abstract

Across rural India, daily life and the local economy depend entirely on groundwater—whether it is needed for household chores, farming, industry, or keeping local ecosystems alive. But around the Zirabad Reservoir, the landscape is shifting. Because farming practices are intensifying and land usage is transforming so fast, the actual quality of this subsurface water is now a major concern. To see what is really happening chemically, our approach combined physical field tracking with lab tests and GIS mapping. We didn't just look at one source type. Right before the monsoons hit in 2021–2022, fifty water samples were collected directly from a mix of borewells and traditional dug wells spread across the entire study area. While doing this fieldwork, logging the fluctuating water quality parameters became our primary focus. We dropped sensors into key observation wells scattered around Zirabad to keep a close eye on everything from pH and electrical conductivity (EC) to TDS. We also tracked the specific ion concentrations Ca2+, K+, Na+, Mg2+ , and Cl-, So42-, Co32-,Fe, NO3- . Once we pulled all that raw chemical data, we brought it straight into a GIS platform. Doing this we could easily spot exactly where the pollution hotspots were hiding. From there, we put together a Groundwater Quality Index. The point of this index is straightforward. It tells us exactly which zones contain safe drinking water, and which zones are only good enough to water crops or supply industrial sites. What the maps exposed was pretty clear. We found distinct pockets of localized contamination tying directly back to heavy fertilizer runoff and poor waste management right next to the farming zones. Mapping things out visually made interpreting these results much easier, which helps a lot when planning targeted interventions. The bottom line is that merging spatial maps with active tracking actually works. If applied correctly, this exact setup could become the standard framework for managing groundwater sustainably in other rural pockets of Madhya Pradesh.

KEYWORDS

Groundwater quality assessment reservoir active monitoring GIS.

Cite This Article

Kanya Solanki, Dr.Vinita Kulshreshtha, Manish Kumar Kothe, "Groundwater Quality Assessment Using active Monitoring and GIS Technologies: A Case Study of Zirabad Reservoir Area, Madhya Pradesh, India," International Journal of Scientific Research in Engineering and Management, vol. 10, no. 8, pp. 1-12, Aug 2026. https://doi.org/10.55041/IJSREM67032

Full Article/Conclusion

In the current study active monitoring techniques and GIS were used to analyzed the groundwater physio-chemical properties in the Zirabad reservoir area have been visualized in Arc GIS environment. The 3D representation of groundwater parameters like pH,TDS, EC,Chloride, calcium etc were mapped using interpolation methods to find out the special alterations of  all the groundwater variables in the Zirabad reservoir study area. It is analyzed that Dugwells and Borewells were varied with depth in different localities of the Zirabad reservoir study area.   These  different variables shows variations in their concentration in  groundwater, shown which observed in maps are given below; The 3D map of pH shows the spatial distribution of its variation across the Zirabad reservoir watershed which illustrated different hydro-geochemical variations associated with the depth of dugwell. The lower pH values 7.0-7.5 found in the southern and southwestern parts indicates shallow depth  dugwells  which are effected by surface recharge while, in the central and eastern parts the higher values pH zones have highest enriched values which instance the attenuated water-rock interactions as well as deepest effects of aquifer in the study area. However, the range 7.0-8.5 demonstrate the overall alkaline conditions in the watershed area.   The TDS 3D map demonstrates varied qualities in the groundwater across all over  the watershed area. In the Zirabad reservoir study area, TDS values ranging from 130-990mg/l, classified it into seven zones. The values ranging between 130-417mg/l has light shaded which indicate good quality of the groundwater, while Central and southeastern areas shows elevated TDS, which reflecting intense rock-water interaction i.e. contamination of the watershed area.   The thematic Chloride concentration variability map illustrates variation of its concentration across the watershed area. On the based of raster-interpolation techniques the Cl- is classified into multiple ranges from 20.3-441 mg/l, characterized among low(green) to high(pink). In the central,southern, northwestern parts Chloride has low concentration values which is 20.3-114mg/l, suggest minimum human-induced effects with natural rechargeable circumstances.   The value above 302mg/l considered as high concentration showing the noticeable hot-spots in central and northwestern regions, the peak level 396-441mg/l indicating the contamination from agriculture, domestic lithological characteristics.   The spatial separation map of Calcium(Ca2+) exemplify the variability of groundwater hardness across the watershed. The concentration values are ranging from 13-171mg/l, classified into seven zones with a colour gradients from low(green) to high(pink). In the western and southern regions the value range between 13-48.3mg/l, signifying defeated dominated  recharge areas with limited mineral partition. The embellishment is distributed unequally with elevated areas which is coincidence for discharge region ans water-rock interaction zones. The presence of highly concentrated values includes potential assistance of limestone, dolomite with filtering procedure. 

References

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Publication Date

8/31/2026

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