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From the IFT source library

Groundwater Management

Text from the existing IFT website. Sources and claims are still under editorial review.

Original source ↗

Section 01

Where the problem happens

Define the service failure before selecting infrastructure.

Groundwater is invisible, shared and connected to rivers and ecosystems.

A recharge structure cannot compensate for unlimited extraction.

Required local context

Record state, district, city/block, village/ward or supply zone; season and date; source or asset; affected users; observed service; measurement or sample method; photo/document where safe; and uncertainty. Never imply 100-metre accuracy unless the evidence genuinely supports it.

Data reference table

Evidence Snapshot

Read each value with its reporting period, population and limitations. A historical national reference is not a local baseline or proof that an IFT proposal works.

5 source-linked reference records. 3 measurement records still need data and a review of their relevance.

Data references for Groundwater Management
SignalReference ValuePeriod / PopulationHow to Read ItSource Status
Assessed annual groundwater recharge

446.90 billion cubic metres

Historical reference

Groundwater assessment water year 2024

India; national groundwater-resource assessment

An estimate of annual groundwater recharge in the assessment.

Limitations: National recharge hides aquifer, seasonal and local variation; it is not a measured balance for a chosen village.

Ministry of Jal Shakti / Central Ground Water Board and States/UTs

Official government release

Record type: official resource assessment estimate

Ministry of Jal Shakti year-end review: Ground Water Resources

Published: 2025-01-25

Publication checked: 2026-11-04

Value, period and coverage checked in publication

Assessed annual extractable groundwater resource

406.19 billion cubic metres

Historical reference

Groundwater assessment water year 2024

India; national groundwater-resource assessment

The extractable resource is distinct from total annual recharge.

Limitations: Not a guarantee of water available to every user or of acceptable water quality; use local assessment units for local decisions.

Ministry of Jal Shakti / Central Ground Water Board and States/UTs

Official government release

Record type: official resource assessment estimate

Ministry of Jal Shakti year-end review: Ground Water Resources

Published: 2025-01-25

Publication checked: 2026-11-04

Value, period and coverage checked in publication

Assessed annual groundwater extraction for all uses

245.64 billion cubic metres

Historical reference

Groundwater assessment water year 2024

India; extraction across all uses

A national extraction estimate for the groundwater resource balance.

Limitations: It is not agriculture-only extraction or a metered count of every borewell. Local and sectoral distributions need separate data.

Ministry of Jal Shakti / Central Ground Water Board and States/UTs

Official government release

Record type: official resource assessment estimate

Ministry of Jal Shakti year-end review: Ground Water Resources

Published: 2025-01-25

Publication checked: 2026-11-04

Value, period and coverage checked in publication

Average stage of groundwater extraction

60.47%

Historical reference

Groundwater assessment water year 2024

India; national groundwater-resource assessment

Relates assessed extraction to the assessed annual extractable resource.

Limitations: A national average can coexist with severe local over-extraction; it is not a safe pumping limit for a farm or aquifer.

Ministry of Jal Shakti / Central Ground Water Board and States/UTs

Official government release

Record type: official resource assessment ratio

Ministry of Jal Shakti year-end review: Ground Water Resources

Published: 2025-01-25

Publication checked: 2026-11-04

Value, period and coverage checked in publication

Assessment units classified as over-exploited

751 of 6,746 assessment units

Historical reference

Groundwater assessment water year 2024

India; assessed blocks, mandals and talukas

Counts assessment areas assigned to the over-exploited category.

Limitations: Units are not equal in area or population. The count is not the share of people exposed, and does not establish conditions in an unmeasured local area.

Ministry of Jal Shakti / Central Ground Water Board and States/UTs

Official government release

Record type: official resource assessment classification

Ministry of Jal Shakti year-end review: Ground Water Resources

Published: 2025-01-25

Publication checked: 2026-11-04

Value, period and coverage checked in publication

Groundwater trend

Not established

Data required — not zero

Reporting period: Information Required

Population and geography: Information Required

Proposed measure; no observed value is established here.

Limitations: Define the measure, unit, reporting period and covered population; obtain a traceable dataset and review its suitability for this topic before using a number.

Source organisation: Information Required

Direct source URL: not yet verified

Source publication date: not established

Verification status: Data required

Extraction/recharge balance

Not established

Data required — not zero

Reporting period: Information Required

Population and geography: Information Required

Proposed measure; no observed value is established here.

Limitations: Define the measure, unit, reporting period and covered population; obtain a traceable dataset and review its suitability for this topic before using a number.

Source organisation: Information Required

Direct source URL: not yet verified

Source publication date: not established

Verification status: Data required

Quality trend

Not established

Data required — not zero

Reporting period: Information Required

Population and geography: Information Required

Proposed measure; no observed value is established here.

Limitations: Define the measure, unit, reporting period and covered population; obtain a traceable dataset and review its suitability for this topic before using a number.

Source organisation: Information Required

Direct source URL: not yet verified

Source publication date: not established

Verification status: Data required

Different surveys, administrative records, estimates and reporting years are not interchangeable. No combined IFT score is calculated from these rows.

Section 02

Why the problem happens

Test the full source-to-service chain.

Well-level decisions ignore aquifer scale

Treat this as a hypothesis until records, field observation, seasonal evidence and credible alternatives are checked.

Extraction measurement is incomplete

Treat this as a hypothesis until records, field observation, seasonal evidence and credible alternatives are checked.

Energy and crop incentives drive pumping

Treat this as a hypothesis until records, field observation, seasonal evidence and credible alternatives are checked.

Recharge claims lack hydrogeological validation

Treat this as a hypothesis until records, field observation, seasonal evidence and credible alternatives are checked.

Section 03

How the parts work together

Components that must work together.

Aquifer mapping

Define the responsible actor, operating standard, input, handoff, maintenance requirement, failure trigger and evidence record.

Water-level and quality monitoring

Extraction estimates

Recharge mapping

Over-exploited zones

Agriculture, industry and community budgeting

Section 04

A solution suited to India

Match intervention to hydrogeology, settlement and service capacity.

Use aquifer-based accounts and seasonal monitoring.

Estimate extraction transparently where metering is impractical.

Combine demand management, crop choices and enforceable industrial rules.

Verify recharge effect rather than structure count.

Decision checks

Safety; Water balance; Affordability; Equity; Operations; Ecology; Climate risk; Accountability

Section 05

Roadmap

Diagnose, protect, pilot, measure and institutionalise.

  • 0–90 DAYS
  • Verify & protect

Confirm the location, affected users, service chain, immediate health or safety risk, responsible agency and existing evidence.

  • 3–18 MONTHS
  • Controlled pilot

Co-produce one aquifer management plan with users, monitoring wells and seasonal allocation choices.

  • 1–5+ YEARS
  • Durable system

Fund operations, preventive maintenance, skilled teams, monitoring, public reporting, correction pathways and independent evaluation.

Section 06

Results

Measure service and outcomes—not assets alone.

KPI 01

Groundwater trend
Baseline · target · actual · unit · source · period · distribution

KPI 02

Extraction/recharge balance
Baseline · target · actual · unit · source · period · distribution

KPI 03

Quality trend
Baseline · target · actual · unit · source · period · distribution

KPI 04

Essential-use reliability
Baseline · target · actual · unit · source · period · distribution

KPI 05

Recharge intervention effect
Baseline · target · actual · unit · source · period · distribution

Section 07

Risks and protections

Water interventions can transfer risk across people, places and time.

  • Risk: Community capture
    Prevention · accountable owner · trigger · remedy
  • Risk: Monitoring wells unrepresentative
    Prevention · accountable owner · trigger · remedy
  • Risk: Recharge contaminating aquifers
    Prevention · accountable owner · trigger · remedy

15 questions, answered clearly

Questions about Groundwater Management

What does Groundwater Management focus on?

Groundwater is invisible, shared and connected to rivers and ecosystems.

What changes does the page propose?

Use aquifer-based accounts and seasonal monitoring. Estimate extraction transparently where metering is impractical. Combine demand management, crop choices and enforceable industrial rules. Verify recharge effect rather than structure count.

Which parts need to work together?

The proposed system connects Aquifer mapping; Water-level and quality monitoring; Extraction estimates; Recharge mapping; Over-exploited zones; Agriculture, industry and community budgeting. Assign a responsible team, service standard, handoff and maintenance plan for each part

What local information is needed before taking action?

Record state, district, city/block, village/ward or supply zone; season and date; source or asset; affected users; observed service; measurement or sample method; photo/document where safe; and uncertainty. Never imply 100-metre accuracy unless the evidence genuinely supports it.

What could be causing the problem?

Possible causes to investigate include Well-level decisions ignore aquifer scale; Extraction measurement is incomplete; Energy and crop incentives drive pumping; Recharge claims lack hydrogeological validation. Treat these as questions to test against local records and experience, rather than confirmed causes in every location.

What evidence should researchers collect?

Record the starting conditions, service records, affected users’ experience, costs and the source and date of each observation. Compare more than one explanation and state what is still uncertain. Use this evidence to assess Groundwater Management.

What could a first trial of Groundwater Management look like?

Co-produce one aquifer management plan with users, monitoring wells and seasonal allocation choices. Agree the place, responsible team, comparison, safety checks and measurement period before starting. The trial described here is a proposal, not a reported result.

How should improvement be measured?

The page proposes tracking Groundwater trend; Extraction/recharge balance; Quality trend; Essential-use reliability; Recharge intervention effect. Define each measure, record the starting value and reporting period, then compare later results using the same method. Report who benefits and any harm or uncertainty.

What risks and safeguards need attention?

Community capture. Monitoring wells unrepresentative. Recharge contaminating aquifers.

What is the suggested order of work?

Diagnose, protect, pilot, measure and build lasting services. 0–90 DAYS. Verify & protect. Confirm the location, affected users, service chain, immediate health or safety risk, responsible agency and existing evidence. 3–18 MONTHS. Controlled pilot. Co-produce one aquifer management plan with users, monitoring wells and seasonal allocation choices. 1–5+ YEARS. Durable system. Fund operations, preventive maintenance, skilled teams, monitoring, public reporting, correction pathways and independent evaluation. These stages are planning ranges. Actual timing depends on local conditions, resources, permissions and delivery capacity.

Who should take responsibility for delivery?

Information Required: the named organisation and accountable local team. Responsibilities must cover Aquifer mapping; Water-level and quality monitoring; Extraction estimates; Recharge mapping; Over-exploited zones; Agriculture, industry and community budgeting. Assign an owner for each handoff, record how problems will be escalated, and agree who will fund and maintain the work.

What costs should be checked before approval?

Define the responsible actor, operating standard, input, handoff, maintenance requirement, failure trigger and evidence record. Safety; Water balance; Affordability; Equity; Operations; Ecology; Climate risk; Accountability. Information Required: a local cost estimate, funding source and ongoing operating and maintenance budget. Include costs shifted to households or other services when comparing options.

How should access and fairness be checked?

Safety; Water balance; Affordability; Equity; Operations; Ecology; Climate risk; Accountability. Compare access, costs, safety and results across the groups affected in this location. Record missing information and correct exclusion before expanding the proposal.

When should the approach expand, change or stop?

Use the proposed measures — Groundwater trend; Extraction/recharge balance; Quality trend — to review benefit, harm, cost and the ability to keep the service working. Expand only when the evidence supports it; change a partly effective design and stop an unsafe or ineffective approach.

Does this page establish that the proposal has succeeded?

No verified local result should be inferred from the proposal alone. Information Required: a dated starting measurement, later results, costs, affected groups and an independent assessment. The proposed review should examine Groundwater trend; Extraction/recharge balance; Quality trend.