Aquifer Transmissivity Calculator

Compute aquifer transmissivity for engineering and hydrogeology tasks. Choose models, enter data, see results instantly. Export tables and interpret values for better groundwater designs.

Tip: Use pumping-test methods for field estimates.
Assumes steady radial flow in a confined aquifer and one well pumping at constant rate.
Use Δs from the straight-line portion of drawdown versus log(time) for a confined aquifer at late time.
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Formula used
  • Conductivity–Thickness: T = K × b, where K is hydraulic conductivity and b is saturated thickness.
  • Thiem (steady-state, confined): T = (Q ln(r2/r1)) / (2π (s2 − s1)), using drawdowns at two observation radii.
  • Cooper–Jacob (straight-line): T = (2.3 Q) / (4π Δs), where Δs is drawdown change per log cycle of time.
Transmissivity has units of area per time and reflects how easily groundwater moves through the full saturated thickness.
How to use this calculator
  1. Select the method that matches your data source.
  2. Enter values and choose units for each input.
  3. Press Calculate to display results above the form.
  4. Use Download CSV or Download PDF to export.
  5. Review the details list to confirm conversions and equations.
Example data table
Scenario Method Key inputs Typical output
Lab-based estimate K × b K = 3.0 m/day, b = 20 m T ≈ 60 m²/day
Steady field drawdown Thiem Q = 1200 m³/day, r1=20 m, r2=80 m, s1=0.9 m, s2=0.4 m T ≈ 331 m²/day
Late-time straight line Cooper–Jacob Q = 1200 m³/day, Δs = 0.22 m T ≈ 314 m²/day
Values are illustrative; real tests depend on aquifer conditions and analysis choices.
Interpretation notes
  • Higher T usually indicates greater well yield for the same drawdown.
  • Lower T suggests tighter materials, requiring more drawdown for pumping.
  • Compare results from multiple methods when possible.
  • Ensure drawdown data reflect the intended flow regime and time window.

Aquifer transmissivity and why it matters

Transmissivity (T) describes how much water an aquifer can transmit through its full saturated thickness. It combines material permeability and thickness into one field-ready metric. In practice, higher T generally supports higher well yields with less drawdown, while lower T indicates tighter formations and larger pumping impacts for the same discharge.

Typical conductivity ranges used with T = K × b

Hydraulic conductivity spans many orders of magnitude. Clean gravel and coarse sand often fall near 10−3 to 10−2 m/s, while fine sands may be closer to 10−5 to 10−4 m/s. Silts commonly drop to about 10−8 to 10−6 m/s, and clays may reach 10−11 to 10−9 m/s. Multiplying by thickness quickly turns these into transmissivity estimates for screening.

How thickness changes productivity

For a fixed conductivity, transmissivity increases linearly with saturated thickness. For example, if K = 5 m/day and b rises from 10 m to 30 m, T increases from 50 to 150 m²/day. This is why partially penetrating wells, seasonal water-table changes, or layered aquifers can produce noticeably different yields even when the sediment type stays the same.

Using the Thiem method with two observation points

The Thiem equation estimates T from steady drawdown differences measured at two radii around a pumping well. Because the relationship contains ln(r2/r1), spacing observation wells farther apart can increase stability, as long as both remain within the same aquifer and flow regime. Accurate, steady pumping rate data are essential, and drawdowns should be taken after trends flatten.

Cooper–Jacob straight-line data requirements

The Cooper–Jacob approximation uses the slope Δs from drawdown plotted against log(time). The straight-line segment typically appears after early-time wellbore storage effects fade. Sampling at consistent intervals, recording time precisely, and ensuring constant discharge improve the slope estimate. A small error in Δs can materially change T because T is inversely proportional to that slope.

Unit handling and common reporting formats

Transmissivity is often reported in m²/day for hydrogeology reports and in ft²/day for many engineering standards. This calculator converts internally to m²/s, then returns m²/day and ft²/day for quick comparison. When comparing studies, confirm that reported “K” values are not mixed with “T” values and that thickness refers to the same saturated interval.

Quick screening benchmarks for field decisions

While site-specific factors dominate, T values below roughly 10 m²/day often indicate limited productivity, whereas values above about 100 m²/day commonly support higher-capacity supply wells. Highly transmissive alluvial or fractured systems may exceed 1000 m²/day. Use these as screening indicators, not pass–fail rules, and pair them with water-quality, sustainability, and boundary assessments.

Practical quality checks before exporting results

Confirm that r1 and r2 are measured from the pumping well center, and that drawdowns use the same datum. If Thiem returns a negative or unrealistic T, recheck whether s2 − s1 has the correct sign and whether the aquifer is truly confined. For Cooper–Jacob, verify that Δs comes from the straight-line segment and not from early transient curvature or late boundary effects.

FAQs

1) What is transmissivity in simple terms?

It is the aquifer’s ability to transmit water through its full saturated thickness. Higher transmissivity generally means more water can flow to a well for a given drawdown.

2) When should I use T = K × b instead of pumping-test methods?

Use K × b for quick screening from lab tests or literature values. Prefer pumping-test methods when you have field drawdown data and need a site-specific estimate.

3) Why does the Thiem method need two radii?

Two radii allow transmissivity to be solved from the difference in drawdown, reducing sensitivity to an unknown constant. It also leverages the logarithmic radial flow relationship.

4) What does Δs mean in the Cooper–Jacob approach?

Δs is the change in drawdown per one log cycle of time on a semi-log plot. A steeper slope indicates lower transmissivity because T is inversely related to Δs.

5) Can this calculator be used for unconfined aquifers?

The included pumping-test formulas are for confined assumptions. For unconfined conditions, corrections and different analysis methods may be needed, especially at larger drawdowns.

6) Why do I get an unrealistic transmissivity value?

Common causes are incorrect units, r1 and r2 swapped, drawdowns taken before stabilization, or using a slope from a non-linear time segment. Recheck inputs and the stated method assumptions.

7) What output unit should I report?

Report the unit used in your project standard. m²/day is common in hydrogeology reports, while ft²/day is common in some engineering contexts. Keep units consistent across comparisons.

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