GROUND WATER EXPLORATION

Disposition of Aquifer System

Field Study under NAQUIM

Evaluation of NAQUIM Through Expert Committee


Groundwater Quality Index: Drinking and Irrigation Assessment

Across much of the world, the water that emerges from a kitchen tap or feeds a drip-irrigation line has travelled through fractured rock, weathered sediment, or carbonate aquifers for years or decades. Its chemistry tells a story of the catchment, the land use above it, and the time it has spent underground. Translating that chemistry into a single, defensible number is the job of the Groundwater Quality Index, a tool now used across ministries, research institutes, and farmer cooperatives to judge whether an aquifer can sustain drinking supply, agriculture, or both. India and Australia share a deep reliance on subsurface storage, from Punjab alluvium to the Great Artesian Basin, both having developed systems that convert raw laboratory results into defensible operational decisions.

This piece walks through how the index is built, the parameters that drive it, how the same calculations translate to Australian conditions, and where open data portals such as NAQUIM are making aquifer information accessible to non-specialist professionals, the wider research community, and the general public.

Foundations of the Groundwater Quality Index

The index is a weighted arithmetic mean of sub-indices, one for each measured parameter, normalised against a benchmark such as the World Health Organization drinking water guidelines or a country's own standards. The sub-index for a parameter is usually calculated as the measured concentration divided by its standard limit, multiplied by 100. Weights reflect relative health or agronomic importance, and the sum of weights across all parameters is normalised to one. The result is a single dimensionless score that ranks the water from "excellent" through "unsuitable" without forcing the reader to compare dozens of individual numbers.

Parameter Indian Standard (BIS 10500:2012) Australian Drinking Water Guideline Type
pH 6.5–8.5 6.5–8.5 Aesthetic
Total Dissolved Solids 500 mg/L desirable, 2000 mg/L permissible 600 mg/L Aesthetic
Total Hardness (as CaCO₃) 200 mg/L desirable, 600 mg/L permissible 200 mg/L Aesthetic
Nitrate (as NO₃) 45 mg/L 50 mg/L Health
Fluoride 1.0 mg/L 1.5 mg/L Health
Sulphate 200 mg/L 250 mg/L health, 500 mg/L aesthetic Both
Iron 0.3 mg/L 0.3 mg/L Aesthetic
Chloride 250 mg/L 250 mg/L Aesthetic

The table illustrates an important point: standards are not identical across jurisdictions, but the underlying logic is shared. Australian guidelines tend to be slightly more permissive on sulphate, reflecting local geochemistry where gypsum-rich strata are common, while Indian guidelines tighten fluoride because of widespread endemic fluorosis in crystalline basement aquifers.

Parameters That Drive the Calculation

A typical assessment measures physico-chemical parameters (pH, electrical conductivity, total dissolved solids), major cations and anions, plus trace metals such as iron, manganese, and arsenic where warranted. Sample handling follows APHA standard methods, with field preservation for metals, refrigeration for nutrients, and ion-balance checks to catch transcription errors. Standard workflows rely on duplicate runs, blank spikes, and reference-laboratory comparison every tenth batch.

The weight each parameter receives depends on the intended outcome. For drinking water, fluoride, nitrate, arsenic, and lead carry the largest weights because chronic exposure produces documented health effects. For irrigation, the index is recomputed with electrical conductivity, Sodium Adsorption Ratio, Residual Sodium Carbonate, and a permeability term taking the largest shares, because these determine whether long-term use will salinise or sodically degrade a soil.

Regional patterns matter. In the Indo-Gangetic plain, nitrate contamination follows fertiliser and sewage patterns, while in coastal Tamil Nadu and Andhra Pradesh the index is dominated by chloride and sodium from seawater intrusion. In Western Australia, the Gnangara Mound north of Perth shows nitrate hot spots beneath market gardens and septic-tank clusters, a pattern familiar to Indian hydrogeologists working with peri-urban aquifers around Bengaluru or Hyderabad.

Drinking Water Suitability Assessment

For potability, the index is usually mapped against a five-band classification: Excellent (under 50), Good (50–100), Poor (100–200), Very Poor (200–300), and Unsuitable (above 300). These bands are convenient for routine reporting and can be communicated to village water committees or ratepayer associations without specialist training. Where the index shifts between seasons, planners use the worst reasonable observation as the design point for treatment.

In Australia, the National Health and Medical Research Council's Australian Drinking Water Guidelines define aesthetic and health thresholds, with regular updates following national reviews. The framework is built around risk management plans that require suppliers to identify hazards, validate barriers, and document operational monitoring, an approach that closely mirrors the Water Safety Plan methodology advocated by the World Health Organization and increasingly adopted by Indian utilities. Australian authorities place particular emphasis on lead and on disinfection by-products because of legacy plumbing in older suburbs. For readers looking for an authoritative starting point, the Central Ground Water Board's aims-cgwb.org portal collates block-level chemistry across Indian states and applies the same indexing logic, providing a model that state geological surveys in Australia could usefully emulate for community outreach.

Long-term exposure to fluoride above 1.5 mg/L produces skeletal fluorosis, while chronic arsenic exposure is linked to cardiovascular disease and cancers of the skin and bladder. Nitrate above roughly fifty milligrams per litre can cause methaemoglobinaemia in infants, which is why shallow wells beneath intensive horticulture warrant particular scrutiny. Where the index flags these parameters, household treatment, deeper bore construction, or piped surface-water alternatives become part of the response toolkit, ideally combined with community-level monitoring that keeps the index live rather than treating it as a one-off characterisation.

Irrigation Suitability Assessment

For farmers, the index must be read alongside irrigation-specific metrics such as Sodium Adsorption Ratio, Residual Sodium Carbonate, and the Permeability Index. These determine whether water will gradually degrade soil structure, reduce infiltration, or leave salt residues that suppress yields. The Food and Agriculture Organization has long classified irrigation waters using electrical conductivity and SAR, and Indian practice under NAQUIM adopts equivalent thresholds.

Australia's Murray-Darling Basin illustrates the scale of the challenge. Irrigators drawing from alluvial aquifers along the Murray, Murrumbidgee, and Namoi rivers grow rice, cotton, and pasture for dairy herds, and seasonal salinity rises can make the difference between profitable and marginal seasons. Generic arguments built on EC alone miss the sodium hazard, so the index must be paired with cation chemistry. Where SAR climbs above 26, gypsum applications or blending with lower-sodium sources are typically recommended to protect soil tilth.

Climate variability adds another layer. During the Millennium Drought, groundwater levels fell across much of the basin, concentrating salts and forcing some irrigators to deepen wells or shift to less salt-sensitive crops. Dashboards that integrate WQI outputs with borehole hydrographs help communities anticipate these shifts. In Western Australian broad-acre farming, similar logic guides wheat-lupin-canola rotations, with soil conductivity mapping alongside groundwater quality to set paddock-scale management zones.

Mapping and Data Access Through NAQUIM

Modern aquifer management rests on open, queryable data. The NAQUIM portal, operated by India's Central Ground Water Board, allows users to query by state, district, and block, returning aquifer geometry, water levels, and chemistry that can be recomputed into local WQI maps. For Australian readers, the parallel is the borehole data warehouses held by state geological surveys in New South Wales, Victoria, and Western Australia, or the Bureau of Meteorology's Groundwater Information pages. A practical starting point for anyone unfamiliar with the platform is this walkthrough on finding block-level data, which translates neatly to state-level hydrogeology archives on this side of the Indian Ocean.

Spatial layers matter because water quality varies across short distances. A single farm in the Gnangara Mound north of Perth can have nitrate-free bore water at one end and contamination from market gardens or septic tanks at the other. Combining WQI with lithology, land use, and depth-to-water surfaces produces risk maps that help regulators target monitoring rather than impose blanket restrictions that penalise low-risk users alongside high-risk ones. Geographic information system overlays also support emergency response, where a sudden spill or flood event can be traced through the same portal logic to identify downstream bores at risk.

From Indices to Sustainable Aquifer Management

An index is only useful if it changes behaviour on the ground. Across India, NAQUIM outputs guide tanker-truck deployment in drought-affected blocks, recharge structure siting in hard-rock aquifers, and regulatory clearance for new industrial abstractions. In Australia, similar logic underpins the Great Artesian Basin Strategic Management Plan, where water quality data inform capping of free-flowing bore drains that waste pressure and promote salt mobilisation.

The next frontier is real-time monitoring. Affordable multi-parameter probes can stream EC, pH, and nitrate into cloud dashboards that recompute the index hourly. Combining these with groundwater storage estimates from GRACE-FO closes the loop between observation and management action. Pilot projects in Rajasthan and Andhra Pradesh are testing near-real-time indices, and Australian state agencies are piloting comparable telemetry in the Surat Basin and Lower Burdekin.

For anyone planning a bore, an irrigation switch, or a community water-supply upgrade, begin with the index, but end with the hydrogeology. The two together explain not just whether the water is fit for purpose today, but whether it will remain so under the climate and demand pressures of the coming decade. Reach out to your state geological survey, your local catchment authority, or the Central Ground Water Board through the NAQUIM portal, and treat the index as a starting conversation rather than a final verdict.

know your aquifer


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