Cumulative Drawdown as a Primary State Variable: The Absement Method for Leaky-Aquifer Pumping-Test Analysis
Abstract
1. Introduction
2. Methodology
2.1. Governing Equation and Absement Formulation
2.2. Absement A(t) Analysis
2.3. Time-Averaged Absement A(t)/t Analysis
2.4. Discretized ΔA/Δt Analysis
2.5. Normalized Absement Derivative (NAD) Analysis
2.6. Illustrative Synthetic Examples
3. Results and Discussions
3.1. Walton [32]—Texas Hill, Salt Flat Drainage Program
3.2. De Ridder [33]—Netherlands Leaky Aquifer
3.3. Vekol Valley, Arizona [34]—Medium-Grained Sandstone Aquifer
4. Implications for Sustainable-Yield Assessment
5. Practical Limitations
6. Conclusions
- Governing equations and operators. Time integration of the Hantush–Jacob governing equation yields S·s = T∇2A − C·A, in which T and C occupy structurally distinct terms unavailable in the drawdown domain where they are entangled within W(u, r/B). This structural separation is an exact consequence of the governing physics and provides the analytical reason why the four operators carry complementary information: A(t), the full cumulative integral; A(t)/t, the time-averaged drawdown converging to ; ΔA/Δt, the windowed incremental rate tracing T(rcone) as the cone expands; and NAD, the normalized absement derivative identifying the flow regime and leakage onset. The A(t)/t asymptote recovers = Q/(2πT)·K0(r/B) from transient data without reaching true steady state and independently of S. This is a direct reading when the late-time plateau is actually approached; when convergence is incomplete, and B are obtained indirectly, as model-based estimates from the curvature of the record, and carry higher uncertainty than a direct reading of the asymptote. The NAD decays to zero at leakage equilibrium—a flow-regime diagnostic absent from derivative-based methods.
- Performance under measurement noise. Monte Carlo assessment under realistic composite noise shows that A(t)/t and ΔA/Δt recover T, S, and B with negligible bias and standard deviations approximately 3–4 times smaller than those of A(t). Leakage factor B is recovered with standard deviations of approximately 15–16 m for A(t)/t and ΔA/Δt, compared with about 61 m for A(t). The governing equation provides the analytical rationale for why each operator weights a different temporal segment of the drawdown record, an observation that Copty et al. [19] demonstrated through stochastic analysis of discrete interpretation methods in heterogeneous leaky aquifers.
- Homogeneous and heterogeneous diagnosis. In a homogeneous aquifer, all four operators return consistent {T, S, B} across all observation wells—operator agreement is the indicator. In a heterogeneous aquifer, systematic disagreement between operators becomes part of the interpretation rather than simply a fitting error. The three field cases illustrate distinct heterogeneity signatures: Walton shows an outward decline in T (≈14%, W1 to W3) with spatially uniform B, revealed by non-overlapping T(rcone) bands; De Ridder shows approximately homogeneous T (≈1750–1950 m2/d) with outward-declining B (W1: 2057 m to W3: 940 m), flagged by NAD type-curve crossing before any fitting; and Vekol shows approximately homogeneous T (≈790–930 m2/d) with B increasing outward (ob1: 587 m, ob2: 1060 m), placing it in the B-heterogeneity category alongside De Ridder. Divergent A(t)/t asymptotes and NAD type-curve crossing are visible indicators of B-heterogeneity before formal parameter fitting.
- Sustainability assessment. When test duration and data quality are sufficient, the framework delivers three sustainability-relevant outputs from a standard pumping-test record without additional instrumentation. The A(t)/t asymptote constrains smax and B most reliably when the leakage-transition curvature and late-time approach to the plateau are sufficiently represented, defining the steady-state drawdown envelope for long-term yield. At incomplete convergence, the asymptote is under-constrained, so greater weight should then be placed on the curvature-sensitive operators (s(t), ΔA/Δt) and on NAD consistency than on the A(t)/t asymptote. The T(rcone) profile identifies transmissivity (T, m2/d) at the operating cone scale; storativity (S) and the leakage factor (B, m) are constrained by the A(t)/t asymptote and the curvature transition. The value differs from the near-well value by up to 14% in Walton, implying a 16% T separation between ob1 and ob2 in Vekol. The NAD confirms whether the leakage regime is fully established, used primarily as a flow-regime and leakage-pattern diagnostic, not as a standalone precise estimator of B. Together, these outputs provide hydraulic constraints for sustainable-yield assessment from routine pumping tests, provided that test duration, data quality, and model assumptions are adequate.
Funding
Data Availability Statement
Conflicts of Interest
References
- Kruseman, G.P.; de Ridder, N.A. Analysis and Evaluation of Pumping Test Data, 2nd ed.; Publication 47; International Institute for Land Reclamation and Improvement (ILRI): Wageningen, The Netherlands, 1992. [Google Scholar]
- Woessner, W.W.; Stringer, A.C.; Poeter, E.P. An Introduction to Hydraulic Testing in Hydrogeology: Basic Pumping, Slug, and Packer Methods; The Groundwater Project: Guelph, ON, Canada, 2023. [Google Scholar] [CrossRef]
- Theis, C.V. The relation between the lowering of the piezometric surface and the rate and duration of discharge of a well using groundwater storage. Trans. Am. Geophys. Union 1935, 16, 519–524. [Google Scholar] [CrossRef]
- Hantush, M.S.; Jacob, C.E. Non-steady radial flow in an infinite leaky aquifer. Trans. Am. Geophys. Union 1955, 36, 95–100. [Google Scholar] [CrossRef]
- Hantush, M.S. Analysis of data from pumping tests in leaky aquifers. Trans. Am. Geophys. Union 1956, 37, 702–714. [Google Scholar] [CrossRef]
- Hantush, M.S. Modification of the theory of leaky aquifers. J. Geophys. Res. 1960, 65, 3713–3725. [Google Scholar] [CrossRef]
- Neuman, S.P.; Witherspoon, P.A. Applicability of current theories of flow in leaky aquifers. Water Resour. Res. 1969, 5, 817–829. [Google Scholar] [CrossRef]
- Neuman, S.P.; Witherspoon, P.A. Theory of flow in a confined two-aquifer system. Water Resour. Res. 1969, 5, 803–816. [Google Scholar] [CrossRef]
- Batu, V. Aquifer Hydraulics: A Comprehensive Guide to Hydrogeologic Data Analysis; Wiley: New York, NY, USA, 1998. [Google Scholar]
- Walton, W.C. Aquifer Test Modelling; CRC Press: Boca Raton, FL, USA, 2007. [Google Scholar]
- Dashti, Z.; Nakhaei, M.; Vadiati, M.; Karami, G.H.; Kisi, O. A literature review on pumping test analysis (2000–2022). Environ. Sci. Pollut. Res. 2023, 30, 9184–9206. [Google Scholar] [CrossRef] [PubMed]
- Bourdet, D.; Whittle, T.M.; Douglas, A.A.; Pirard, Y.M. A new set of type curves simplifies well test analysis. World Oil 1983, 196, 95–106. [Google Scholar]
- Barker, J.A.; Herbert, R. Pumping tests in patchy aquifers. Groundwater 1982, 20, 150–155. [Google Scholar] [CrossRef]
- Butler, J.J. Pumping tests in nonuniform aquifers—The radially symmetric case. J. Hydrol. 1988, 101, 15–30. [Google Scholar] [CrossRef]
- Butler, J.J.; Liu, W.Z. Pumping tests in nonuniform aquifers: The radially asymmetric case. Water Resour. Res. 1993, 29, 259–269. [Google Scholar] [CrossRef]
- Manewell, N.; Doherty, J.; Hayes, P. Translating pumping test data into groundwater model parameters: A workflow to reveal aquifer heterogeneities and implications in regional model parameterization. Front. Water 2024, 5, 1334022. [Google Scholar] [CrossRef]
- Copty, N.K.; Sarioglu, M.S.; Findikakis, A.N. Equivalent transmissivity of heterogeneous leaky aquifers for steady state radial flow. Water Resour. Res. 2006, 42, W04416. [Google Scholar] [CrossRef]
- Trinchero, P.; Sanchez-Vila, X.; Copty, N.K.; Findikakis, A.N. A new method to interpret pumping tests in leaky aquifers. Groundwater 2008, 46, 133–143. [Google Scholar] [CrossRef] [PubMed]
- Copty, N.K.; Trinchero, P.; Sanchez-Vila, X.; Sarioglu, M.S.; Findikakis, A.N. Influence of heterogeneity on the interpretation of pumping test data in leaky aquifers. Water Resour. Res. 2008, 44, W11419. [Google Scholar] [CrossRef]
- Zhuang, C.; Li, Y.; Zhou, Z.; Illman, W.A.; Dou, Z.; Yang, Y.; Wang, J. Effects of exponentially decaying aquitard hydraulic conductivity on well hydraulics and fractions of groundwater withdrawal in a leaky aquifer system. J. Hydrol. 2022, 607, 127439. [Google Scholar] [CrossRef]
- Zhuang, C.; Zhan, H.B.; Xu, X.D.; Wang, J.G.; Zhou, Z.F.; Dou, Z. Effects of aquitard windows on groundwater fluctuations within a coastal leaky aquifer system: An analytical and experimental study. Adv. Water Resour. 2023, 177, 104473. [Google Scholar] [CrossRef]
- Zhuang, C.; Lü, C.; Yan, L.; Li, Y.; Zhou, Z.; Wang, J.; Dou, Z.; Illman, W.A. Pumping-induced well hydraulics and groundwater budget in a leaky aquifer system with vertical heterogeneity in aquitard hydraulic properties. Acta Geol. Sin.—Engl. Ed. 2024, 98, 477–490. [Google Scholar] [CrossRef]
- Meng, X.; Zhang, W.; Wang, Q.; Yin, M.; Liu, D. Modeling of low-velocity non-Darcian flow with nonlinear consolidation in a leaky aquifer system induced by a fully penetrating confined well. Water Resour. Res. 2025, 61, e2024WR038370. [Google Scholar] [CrossRef]
- De Smedt, F. Determination of aquitard storage from pumping tests in leaky aquifers. Water 2023, 15, 3735. [Google Scholar] [CrossRef]
- van Leer, M.D.; Zaadnoordijk, W.J.; Zech, A.; Griffioen, J.; Bierkens, M.F.P. Mapping the spatial sensitivity of aquitard hydraulic parameters on pumping test drawdowns. Groundwater 2025, 64, 41–48. [Google Scholar] [CrossRef] [PubMed]
- Li, W.; Nowak, W.; Cirpka, O.A. Geostatistical inverse modeling of transient pumping tests using temporal moments of drawdown. Water Resour. Res. 2005, 41, W08403. [Google Scholar] [CrossRef]
- Zhu, J.; Yeh, T.C.J. Analysis of hydraulic tomography using temporal moments of drawdown recovery data. Water Resour. Res. 2006, 42, W02403. [Google Scholar] [CrossRef]
- Blasingame, T.A.; Johnston, J.L.; Lee, W.J. Type-curve analysis using the pressure integral method. In Proceedings of the SPE California Regional Meeting, Bakersfield, CA, USA, 5–7 April 1989. SPE 18799. [Google Scholar] [CrossRef]
- Palacio, J.C.; Blasingame, T.A. Decline-curve analysis using type curves—Analysis of gas well production data. In Proceedings of the SPE Rocky Mountain Regional/Low Permeability Reservoirs Symposium, Denver, CO, USA, 26–28 April 1993; SPE 25909. Available online: https://blasingame.engr.tamu.edu/0_TAB_Public/TAB_Publications/SPE_025909_(Palacio)_Blasingame_Gas_Well_Dec_TC_Anl.pdf (accessed on 28 June 2026).
- Avcı, C.B.; Sahin, U.; Ciftci, E. Aquifer parameter estimation using an incremental area method. Hydrol. Process. 2011, 25, 2584–2596. [Google Scholar] [CrossRef]
- Avcı, C.B. Cumulative drawdown as a primary state variable: The Absement Method for confined aquifer pumping-test analysis. Water 2026, 18, 1143. [Google Scholar] [CrossRef]
- Walton, W.C. Selected Analytical Methods for Well and Aquifer Evaluation; Illinois State Water Survey Bulletin 49; Illinois State Water Survey: Urbana, IL, USA, 1962. [Google Scholar]
- De Ridder, N.A. Analysis of the Aquifer Test at Dalfsen in the Eastern IJssel-Vecht Area; TNO Rapport; Dienst Grondwaterverkenning; TNO: Delft, The Netherlands, 1961. [Google Scholar]
- Marie, J.R.; Hollett, K.J. Determination of Hydraulic Characteristics and Yield of Aquifers Underlying Vekol Valley, Arizona, Using Several Classical and Current Methods; U.S. Geological Survey Water-Supply Paper 2453; U.S. Geological Survey: Reston, VA, USA, 1996; 63p.








| Operator | T | S | smax | B |
|---|---|---|---|---|
| A(t) | Reliable; early-time slope gives T (though A(t)/t and ΔA/Δt reach lower σT) | Reliable; sets curve position, well resolved from full-record fit | Not direct; derived from T and B after fitting | Estimable but less precise than A(t)/t; ~5× larger uncertainty (Table 3) |
| A(t)/t | Reliable; from global curve shape, S separates analytically | Weakly constrained; drops out of the asymptote | Direct from late-time plateau; only operator giving smax without first fitting T, B; independent of S | Most precise; from smax and T via K0(r/B) |
| ΔA/Δt | Spatial T(rcone) profile per window | Not direct; enters via rcone axis only | Not available; use A(t)/t | Indirect; late-time ΔA/Δt → smax gives a second B near the plateau, else qualitative (plateau-onset timing only) |
| NAD | Indirect; shifts type curve in time, not separable from B without fitting | Indirect; shifts type curve like T, not separable from NAD alone | Not estimated; flow-regime diagnostic only | Diagnostic constraint on r/B pattern; not a standalone B estimator |
| Operator | T | S | smax | B |
|---|---|---|---|---|
| A(t) | Time-weighted average T over the cone path; near-well dominates (early data weighted most) | Weighted average S over the cone path; not a local value | Indirect; depends on cone-path averages of T, B; may differ from true smax | Cone-path average B; blends near-well and far-field leakage |
| A(t)/t | Effective T over the leakage-bounded cone at convergence | Not recovered; drops out of the asymptote | Most stable smax; anchored at steady state, S-independent even under heterogeneity | Effective B at the cone boundary; per-well values map the spatial B pattern |
| ΔA/Δt | Apparent T(rcone) per window; systematic slope flags radial T variation or model mismatch | Not resolved; S shifts the rcone axis, not separable | Not available; use A(t)/t | Qualitative; differing leakage-transition timing between wells indicates B(r) variation |
| NAD | Indirect; systematic NAD shift between wells flags T variation | Indirect model check; early-time NAD above the Hantush–Jacob curve may indicate aquitard storage S’ | Not estimated; flow-regime and model-check diagnostic only | Spatial B signal; migration across r/B type curves flags B(r) variation |
| Analysis Method | T Mean (m2/s) | T Std (m2/s) | S Mean | S Std | B Mean (m) | B Std (m) | RMS Mean |
|---|---|---|---|---|---|---|---|
| Absement A(t) | 0.010033 | 1.11 × 10−3 | 1.03 × 10−4 | 1.05 × 10−5 | 257.2 | 61.2 | 3.23 × 10−3 m |
| Absement A(t)/t | 0.010011 | 3.18 × 10−4 | 1.01 × 10−4 | 4.49 × 10−6 | 251.0 | 15.2 | 3.03 × 10−3 m |
| Discr. ΔA/Δt (Δln t = 0.2) | 0.009987 | 3.45 × 10−4 | 9.98 × 10−5 | 4.95 × 10−6 | 250.0 | 16.4 | 3.03 × 10−3 m |
| NAD | 0.010032 | 4.53 × 10−4 | 9.08 × 10−5 | 2.08 × 10−5 | 291.0 | 60.4 | 2.01 × 10−2 m |
| True values | 0.010000 | — | 1.00 × 10−4 | — | 250.0 | — | — |
| Method | W1 r = 12.19 m | W2 r = 24.38 m | W3 r = 48.77 m | RMSE (m) W1 | RMSE (m) W2 | RMSE (m) W3 | ||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| T [m2/d] | S | B [m] | T [m2/d] | S | B [m] | T [m2/d] | S | B [m] | — | — | — | |
| A(t) | 3305 | 0.00359 | 488 | 3109 | 0.00444 | 287 | 2810 | 0.00356 | 247 | 0.1580 | 0.0384 | 0.0142 |
| A(t)/t | 3189 | 0.00416 | 388 | 3070 | 0.00457 | 273 | 2777 | 0.00360 | 241 | 0.1300 | 0.0326 | 0.0139 |
| ΔA/Δt | 3212 | 0.00406 | 414 | 3083 | 0.00453 | 278 | 2775 | 0.00361 | 240 | 0.1430 | 0.0350 | 0.0134 |
| Hantush–Jacob s(t) | 3212 | 0.00406 | 413 | 3084 | 0.00453 | 278 | 2774 | 0.00361 | 240 | 0.1420 | 0.0344 | 0.0135 |
| [m] | 4.41 | 3.23 | 2.44 | — | — | — | ||||||
| Conv. [%] | 87 | 92 | 93 | — | — | — | ||||||
| Method | W1 (r = 30 m) | W2 (r = 60 m) | ||||||
| T [m2/d] | S | B [m] | RMSE | T [m2/d] | S | B [m] | RMSE | |
| s(t) | 1928 | 0.00095 | 2057 | 0.0009 | 1883 | 0.00185 | 1194 | 0.0012 |
| A(t) | 1867 | 0.00109 | 1561 | 0.0011 | 1857 | 0.00193 | 1175 | 0.0013 |
| A(t)/t | 1967 | 0.00088 | 3664 | 0.0011 | 1959 | 0.00172 | 2363 | 0.0015 |
| ΔA/Δt | 1920 | 0.00096 | 1920 | 0.0009 | 1887 | 0.00183 | 1195 | 0.0012 |
| smax [m] | — | — | — | — | — | — | — | — |
| Method | W3 (r = 90 m) | W4 (r = 120 m) | ||||||
| T [m2/d] | S | B [m] | RMSE | T [m2/d] | S | B [m] | RMSE | |
| s(t) | 1749 | 0.00169 | 940 | 0.0013 | 1792 | 0.00150 | 1219 | 0.0016 |
| A(t) | 1744 | 0.00172 | 997 | 0.0015 | 1678 | 0.00165 | 965 | 0.0018 |
| A(t)/t | 1886 | 0.00160 | 1897 | 0.0020 | 1921 | 0.00145 | 2400 | 0.0020 |
| ΔA/Δt | 1770 | 0.00169 | 995 | 0.0014 | 1803 | 0.00150 | 1252 | 0.0016 |
| smax [m] a | — | — | 0.143 (obs.) | — | — | — | 0.129 (obs.) | — |
| Method | ob1 (r = 61 m) | ob2 (r = 122 m) | ||||||
|---|---|---|---|---|---|---|---|---|
| T [m2/d] | S | B [m] | RMSE | T [m2/d] | S | B [m] | RMSE | |
| s(t) | 790 | 0.00160 | 587 | 0.125 | 920 | 0.00071 | 1060 | 0.097 |
| A(t) | 780 | 0.00161 | 565 | 0.128 | 834 | 0.00080 | 803 | 0.133 |
| A(t)/t | 815 | 0.00152 | 649 | 0.135 | 980 | 0.00067 | 1550 | 0.130 |
| ΔA/Δt | 800 | 0.00156 | 608 | 0.127 | 935 | 0.00070 | 1142 | 0.100 |
| Heterogeneity Type | Field Case | Key Diagnostic Signal | Yield Assessment Action |
|---|---|---|---|
| Mild outward T decline; S approximately constant | Walton | NAD decays to zero at all three wells; T(rcone) declines 14% from W1 to W3 | Use outer-well T (≈2794 m2/d) for large-scale yield; near-well T (≈3175 m2/d) for near-field. Min = 2.44 m (W3) defines the sustainability envelope |
| Approximately homogeneous T; spatially variable B | De Ridder | NAD type-curve crossing between wells flags B-heterogeneity before fitting | Use T ≈ 1750–1950 m2/d; account for outward B variation when estimating leakage-supported long-term response (T-homogeneous within ≈10% across all four wells). B varies outward: W1 B = 2057 m to W3 B = 940 m, flagged by NAD type-curve crossing before any fitting. smax at W3 (0.143 m) and W4 (0.129 m) define the leakage-controlled sustainable-yield ceiling. |
| Approximately homogeneous T (≈790–930 m2/d); B increases outward | Vekol Valley | NAD confirms leaky regime; ob1 reaches full convergence, while ob2 reaches 93% convergence. At ob2, B is constrained primarily by s(t) and ΔA/Δt curvature rather than by the A(t)/t asymptote | Use T ≈ 870 m2/d; from ob1 well established (11.05 m); ob2 (9.26 m) confirmed at 93% convergence |
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Avcı, C.B. Cumulative Drawdown as a Primary State Variable: The Absement Method for Leaky-Aquifer Pumping-Test Analysis. Water 2026, 18, 1638. https://doi.org/10.3390/w18131638
Avcı CB. Cumulative Drawdown as a Primary State Variable: The Absement Method for Leaky-Aquifer Pumping-Test Analysis. Water. 2026; 18(13):1638. https://doi.org/10.3390/w18131638
Chicago/Turabian StyleAvcı, Cem B. 2026. "Cumulative Drawdown as a Primary State Variable: The Absement Method for Leaky-Aquifer Pumping-Test Analysis" Water 18, no. 13: 1638. https://doi.org/10.3390/w18131638
APA StyleAvcı, C. B. (2026). Cumulative Drawdown as a Primary State Variable: The Absement Method for Leaky-Aquifer Pumping-Test Analysis. Water, 18(13), 1638. https://doi.org/10.3390/w18131638

