REVIEW 2 major objections 4 minor 68 references
A flow-kick model of dryland vegetation patterns: the impact of rainfall variability on resilience
T0 review · 2 major / 4 minor · reviewed 2026-08-10 · deepseek-v4-flash
Pith's one-line read Rainfall randomness narrows the window for banded vegetation patterns.
desk verdict Solid stochastic extension of the flow-kick dryland model; direction of the result is convincing, but the headline MAP=34.8 threshold rests on an unvalidated Lyapunov-exponent estimate. read the letter →
The pith
A machine-rendered reading of the paper's core claim, the machinery that carries it, and where it could break.
The reading
What carries the argument
The load-bearing object is the kick-flow stability map $M_k[w_0,b_0,h_0,\tau_d]=\Psi_k\,\Omega_k$, whose product over successive random storms gives the maximal Lyapunov exponent $\lambda_k$ from Eq. (20). The kick factor $\Omega_k$ contains the positive feedbacks that concentrate storm water: infiltration-enhancement and flow-speed-reduction terms, with the overland travel distance $\ell_0=\nu(b)h_0/\iota(b)$ setting the resonance wavelengths $k_n^*=n\pi/\ell_0$. The flow factor $\Psi_k$ integrates the slow reaction-diffusion system linearized about the post-kick uniform state. The paper uses the sign of $\lambda_k$ as the pattern-forming instability criterion, and in the periodic case it reduces to Floquet theory.
What would settle it
Run both ramped simulation protocols with a different long random sequence (for example $10^6$ cycles instead of $10^5$) and check whether the zero crossing of the maximal Lyapunov exponent still lands at $\mathrm{MAP}=34.8$ cm/year in both the $H_0$-fixed and $T_d$-fixed paths; if the onset shifts by more than a few cm/year, the fixed-onset claim is falsified.
Extended reading notes
Core claim
The paper's central claim is that random variability in storm timing and storm depth, at the same mean annual precipitation as a periodic reference, shrinks the region in rainfall-parameter space where dryland vegetation patterns can establish and persist. Under periodic rainfall the uniform vegetation state loses stability to banded patterns at $\mathrm{MAP}=52.4$ cm/year when $H_0=1$ cm and at $75.4$ cm/year when $T_d=15$ days; under exponentially distributed storms and interstorm times the same instability occurs at $\mathrm{MAP}=34.8$ cm/year in both protocols, and the lower transcritical threshold below which the uniform state collapses moves to higher precipitation. Simulations confirm the narrowed interval and show that random rainfall lowers time-averaged biomass, destroys the resonance-tongue structure of the linear instability, and moves pattern collapse to higher mean rainfall, so variability acts as an extra stressor even when mean rainfall is fixed.
Load-bearing premise
The load-bearing premise is that the numerically estimated maximal Lyapunov exponent of the random storm sequence--computed from one sequence of $10^5$ cycles with rescaling every $100$ cycles--marks the true onset of pattern formation; the paper itself notes that negative Lyapunov exponents do not always imply stability, and the check covers only two paths in the $(H_0,T_d)$ plane.
Editorial extensions
If this is right
- Under random rainfall the uniform vegetation state is stable over a wider range of low and high mean precipitation than under periodic rainfall, so patterns appear only in a narrower band of $\mathrm{MAP}$.
- The linear instability's resonance tongues, tied to the distance surface water travels, disappear with randomness; simulations then show simple traveling bands migrating uphill.
- The lower collapse boundary (transcritical point) rises, and the bistable region where patterns and bare soil coexist shrinks; patterns persist below it only for a finite stochastic lifetime.
- The random pattern-onset boundary is insensitive to whether $\mathrm{MAP}$ is set by changing storm depth or interstorm time, sitting near $\mathrm{MAP}=34.8$ cm/year.
- Random rainfall lowers the time-averaged biomass of both uniform and patterned states compared with periodic rainfall at the same mean annual precipitation.
Reading between the lines
- Because the model draws storm depths and waiting times from exponential distributions, the near-universal onset at $\mathrm{MAP}=34.8$ cm/year may be specific to those distributions; testing gamma-distributed storms or correlated storm clusters would show whether the threshold depends on the shape of the variability.
- The finding that linear predictions match nonlinear simulations only when randomness is added suggests a time-averaged or effective-parameter model might reproduce the random behavior with much cheaper computation--an avenue the paper does not pursue.
- If this result carries to real hillslopes, monitoring changes in rainfall variability, not just mean annual precipitation, could help forecast where banded vegetation will disappear; remote sensing of band widths and migration speeds might serve as an early indicator.
- The paper's periodic-boundary setup omits water loss through runoff; including open boundaries could further shrink or shift the random-rainfall window, likely strengthening the reported effect.
Editorial analysis
A structured set of objections, weighed in public.
Referee Report
Summary. The paper studies a flow-kick model of banded vegetation on gentle hillslopes, in which rainstorms are instantaneous kicks to soil water and the dry intervals are governed by a two-component reaction-diffusion system. It compares idealized periodic rainfall with random rainfall (exponentially distributed storm depths and inter-storm times) at the same mean annual precipitation. The main claims are that randomness shifts the transcritical collapse threshold upward, lowers the MAP at which the uniform vegetation state becomes unstable to spatial perturbations, and narrows the MAP interval over which patterns exist, thereby reducing the resilience of pattern-forming dryland ecosystems. Quantitative anchors are the random-rainfall pattern onset at MAP = 34.8 cm/year versus periodic onsets of 52.4 cm/year (H0 = 1 cm) and 75.4 cm/year (Td = 15 days) along the two parameter paths studied.
Significance. The question addressed is timely and the flow-kick framework is well matched to it. If the quantitative thresholds hold, the paper delivers a clear, falsifiable prediction: increased rainfall variability with unchanged mean precipitation reduces the resilience of banded vegetation. Strengths of the manuscript include an exact analytic transcritical threshold for random kick strength with a proved q-Pochhammer identity (Appendix B), a transparent Lyapunov-exponent formulation for the random kick-flow map (Section 4.2), and an extensive battery of ramped simulations with an explicit state-classification protocol (Section 5.2). The authors also honestly flag the limitation that negative Lyapunov exponents do not in general imply stability (Section 6, citing Leonov and Kuznetsov). The main quantitative claim, however, currently rests on a single-sequence Lyapunov estimator and on only two validated simulation paths, so the headline number 34.8 cm/year and the associated invariance statement need additional support before the strongest version of the resilience conclusion can be accepted.
major comments (2)
- [Section 4.2, Eq. (21)] The maximal Lyapunov exponent for the random kick-flow map is approximated from a single sequence of n = 10^5 cycles with rescaling every m = 100 iterations, and the paper reports no convergence study in n or m, no seed-to-seed variability, and no confidence interval. Because the zero crossing of this estimator sets the random-rainfall pattern onset at MAP = 34.8 cm/year (Figures 6 and 8), a finite-time bias or slow convergence in the estimator would directly move the paper's headline number. I recommend adding a convergence study (e.g., the inferred onset as a function of n for n = 10^4, 10^5, 10^6 and of the rescaling interval m), repeating the calculation over several independent random sequences, and reporting a bootstrap or inter-quantile range for the inferred MAP. The uncertainty should be stated next to the 34.8 cm/year value.
- [Section 5.1 and Figure 8] The statement that with random rainfall 'the onset of the pattern forming instability always occurs at this MAP, independent of the particular choice of H0 and Td associated with it' is an extrapolation from two one-parameter paths (H0 = 1 cm with Td varied, and Td = 15 days with H0 varied) together with the threshold curve in Figure 7(a), which is computed with the same Lyapunov estimator. Two validated paths do not establish invariance across the (H0, Td) plane, and Section 6 itself notes that negative Lyapunov exponents do not imply stability, so the linear zero crossing is not by itself a rigorous onset. I recommend either testing additional (H0, Td) paths or explicitly softening the claim to the tested paths and adjusting the abstract and conclusion to state the uncertainty in the universal value.
minor comments (4)
- [Throughout] There are several typographical errors: 'Lyaponuv' should be 'Lyapunov' (Sections 4.2 and 6), 'trails' should be 'trials' (Section 2.5 and Figure 12), 'obeserved' should be 'observed' (Section 5.2), 'purpler dotted' should be 'purple dotted' (Section 4.3), and 'initialed' should be 'initialized' (Section 2.5).
- [Figure 8(c)] The text describing Figure 8(c) refers to the second distribution as 'magenta', while the caption says 'purple'; please make the color names consistent.
- [Section 2.4 and Section 3] The notation h0 and τd is used both for dimensionless variables and for dimensioned quantities, and the formula MAP = 3.65 h0/τd mixes these conventions. Clarify the units in the sentence preceding Eq. (3) and in the dimensionless map (13).
- [Section 3, Eq. (17)] For the fully random case and for random-timing-only case, the expectation in Eq. (17) is evaluated numerically over 10^6 cycles; reporting the sensitivity of the inferred threshold to the number of cycles would make the lower-boundary results easier to assess.
Circularity Check
No significant circularity: the random-versus-periodic rainfall comparison is a new computation that does not reduce to the model inputs or to prior results.
full rationale
Walked the derivation chain. Section 3 derives the transcritical threshold from the linearized uniform flow (Eqs. 14-17) and validates it against direct flow-kick cycle averages; Section 4 constructs the kick-flow stability map and computes maximal Lyapunov exponents for both periodic and random rainfall; Section 5 checks the predicted onset and wavenumbers with ramped nonlinear simulations. No predicted quantity is defined in terms of the output it claims to explain. The random-rainfall instability onset at MAP~34.8 cm/year is a computed zero crossing of the Lyapunov-exponent estimator, not a fitted parameter, and the claimed H0/Td independence is an observed alignment of the computed threshold with a constant-MAP line rather than an imposed constraint. The only notable self-citation is use of the kick sensitivity formula J_k and the resonance/wavelength picture from Gandhi et al. [26]; that prior work derives the formula from the stated hydrological PDE and does not contain the random-rainfall result, so it is independent support rather than load-bearing circularity. The Section 6 caveat about negative Lyapunov exponents and Perron effects, together with the two-path simulation validation, bears on numerical reliability and extrapolation strength, not on whether the derivation is circular.
Assumptions & free parameters
free parameters (3)
- State classification threshold B_epsilon =
0.02 kg/m^2
- Lyapunov exponent estimation length n and rescaling interval m =
n = 10^5, m = 10^2
- Ramped simulation step size and dwell time =
0.1 cm/year every 25 to 100 years
assumptions (4)
- domain assumption Storm arrival times follow a Poisson process and storm depths are exponentially distributed (Section 2.3)
- domain assumption The kick is computed as the quasi-steady state of the surface water PDE (2) with infiltration rate and flow speed depending on biomass via (8), and with flow speed independent of water depth
- domain assumption The linearized kick contribution J_k in Eq. (19) is taken from Gandhi et al. [26] without re-derivation
- domain assumption Periodic boundary conditions are used on a 1D domain representing a mid-slope section (Section 2.5 and limitations in Section 6)
Cite this review
Pith. "Pith review of A flow-kick model of dryland vegetation patterns: the impact of rainfall variability on resilience." pith.science (2026). https://pith.science/paper/NA5O5RJI
@misc{pith2026250101569,
author = {Pith},
title = {Pith review of: A flow-kick model of dryland vegetation patterns: the impact of rainfall variability on resilience},
year = {2026},
howpublished = {\url{https://pith.science/paper/NA5O5RJI}},
note = {Machine review of arXiv:2501.01569}
}
read the original abstract
In many drylands around the globe, vegetation self-organizes into regular spatial patterns in response to aridity stress. We consider the regularly-spaced vegetation bands, on gentle hill-slopes, that survive low rainfall conditions by harvesting additional stormwater from upslope low-infiltration bare zones. We are interested in the robustness of this pattern formation survival mechanism to changes in rainfall variability. For this, we use a flow-kick modeling framework that treats storms as instantaneous kicks to the soil water. The positive feedbacks in the storm-level hydrology, that act to concentrate water within the vegetation bands, are captured through the spatial profiles of the soil water kicks. Between storms, the soil water and vegetation, modeled by a two-component reaction-diffusion system, evolve together. We use a combination of linear stability analysis and numerical simulation to compare predictions of idealized periodic rainfall, with no variability, to predictions when there is randomness in the timing and magnitude of water input from storms. We show that including these random elements leads to a decrease in the parameter range over which patterns appear. This suggests that an increase in storm variability, even with the same mean annual rainfall, may negatively impact the resilience of these pattern-forming dryland ecosystems.
Figures
Figures from the paper (14 more)
Reference graph
Works this paper leans on
-
[1]
F. T. Maestre, B. M. Benito, M. Berdugo, L. Concostrina-Zubiri, M. Delgado-Baquerizo, D. J. Eldridge, E. Guirado, N. Gross, S. K´ efi, Y. Le Bagousse-Pinguet, R. Ochoa-Hueso, and Soliveres. S. Biogeography of global drylands. New Phytologist, 231(2):540–558, 2021
work page 2021
-
[2]
F. T. Maestre, D. J. Eldridge, S. Soliveres, S. K´ efi, M. Delgado-Baquerizo, M. A. Bowker, P. Garc ´ ıa-Palacios, J. Gait´ an, A. Gallardo, R. L´ azaro, and M. Berdugo. Structure and func- tioning of dryland ecosystems in a changing world.Annu. Rev. Ecol. Evol. Syst., 47(1):215–237, 2016
work page 2016
-
[3]
J.-C. Menaut and B. Walker. Banded vegetation patterning in arid and semiarid environ- ments: ecological processes and consequences for management , volume 149. Springer Science & Business Media, 2001
work page 2001
-
[4]
V. Deblauwe, N. Barbier, P. Couteron, O. Lejeune, and J. Bogaert. The global biogeography of semi-arid periodic vegetation patterns. Glob. Ecol. Biogeogr., 17(6):715–723, 2008
work page 2008
- [5]
-
[6]
W. A. Macfadyen. Vegetation patterns in the semi-desert plains of British Somaliland. Geogr. J., 116(4/6):199–211, 1950
work page 1950
-
[7]
J. E. G. W. Greenwood. The development of vegetation patterns in somaliland protectorate. Geogr. J., pages 465–473, 1957
work page 1957
-
[8]
C. F. Hemming. Vegetation arcs in somaliland. J. Ecol., pages 57–67, 1965
work page 1965
Show all 68 references
-
[9]
Deblauwe, P
V. Deblauwe, P. Couteron, J. Bogaert, and N. Barbier. Determinants and dynamics of banded vegetation pattern migration in arid climates. Ecol. Monogr., 82(1):3–21, 2012
2012
-
[10]
G. G. Penny, K. E. Daniels, and S. E. Thompson. Local properties of patterned vegetation: quantifying endogenous and exogenous effects. Phil. Trans. R. Soc. A , 371(2004):20120359, 2013
2004
-
[11]
Gowda, S
K. Gowda, S. Iams, and M. Silber. Signatures of human impact on self-organized vegetation in the Horn of Africa. Sci. Rep., 8:3622, 2018
2018
-
[12]
Bastiaansen, O
R. Bastiaansen, O. Ja ¨ ıbi, V. Deblauwe, M. B. Eppinga, K. Siteur, E. Siero, S. Mermoz, A. Bou- vet, A. Doelman, and M. Rietkerk. Multistability of model and real dryland ecosystems through spatial self-organization. Proc. Natl. Acad. Sci. , 115(44):11256–11261, 2018
2018
-
[13]
C. A. Klausmeier. Regular and irregular patterns in semiarid vegetation. Science, 284(5421):1826–1828, 1999
1999
-
[14]
Lejeune, P
O. Lejeune, P. Couteron, and R. Lefever. Short range co-operativity competing with long range inhibition explains vegetation patterns. Acta Oecologica, 20(3):171–183, 1999
1999
-
[15]
Rietkerk, M
M. Rietkerk, M. C. Boerlijst, F. van Langevelde, R. HilleRisLambers, J. van de Koppel, L. Ku- mar, H. H. T. Prins, and A. M. de Roos. Self-organization of vegetation in arid ecosystems. Amer. Nat., 160(4):524–530, 2002. 37
2002
-
[16]
Gilad, J
E. Gilad, J. von Hardenberg, A. Provenzale, M. Shachak, and E. Meron. Ecosystem engineers: from pattern formation to habitat creation. Phys. Rev. Lett. , 93(9):098105, 2004
2004
-
[17]
Bastiaansen, A
R. Bastiaansen, A. Doelman, M. B. Eppinga, and M. Rietkerk. The effect of climate change on the resilience of ecosystems with adaptive spatial pattern formation.Ecol. Lett., 23(3):414–429, 2020
2020
-
[18]
Rietkerk, S
M. Rietkerk, S. C. Dekker, P. C. de Ruiter, and J. van de Koppel. Self-organized patchiness and catastrophic shifts in ecosystems. Science, 305(5692):1926–1929, 2004
1926
-
[19]
E. Meron. Nonlinear physics of ecosystems . CRC Press Boca Raton, FL, 2015
2015
-
[20]
Martinez-Garcia, C
R. Martinez-Garcia, C. Cabal, J. M. Calabrese, E. Hern´ andez-Garc ´ ıa, C. E. Tarnita, C. L´ opez, and J. A. Bonachela. Integrating theory and experiments to link local mechanisms and ecosystem-level consequences of vegetation patterns in drylands. Chaos, Solitons & Fractals ...
2023
-
[21]
Noy-Meir
I. Noy-Meir. Desert ecosystems: environment and producers. Annu. Rev. Ecol. Evol. Syst. , 4(1):25–51, 1973
1973
-
[22]
Airbus, CNES/Airbus, Landsat/Copernicus, Maxar Technologies, USDA/FPAC/GEO
Google Map. Airbus, CNES/Airbus, Landsat/Copernicus, Maxar Technologies, USDA/FPAC/GEO. Accessed Dec. 30, 2024
2024
-
[23]
Cooperative observer network (COOP) data
National Oceanic and Atmospheric Administration (NOAA). Cooperative observer network (COOP) data. Accessed via NOAA National Centers for Environmental Information website, 2024
2024
-
[24]
Masson-Delmotte, P
V. Masson-Delmotte, P. Zhai, A. Pirani, S. L. Connors, C. C. B. Pell, A. G. Hope, A. C. Allen, M. Tignor, and E. Poloczanska. Climate Change 2021: The Physical Science Basis. Contribution of Working Group I to the Sixth Assessment Report of the Intergovernmental Panel on Clima...
2021
-
[25]
F. T. Maestre, R. Salguero-G´ omez, and J. L. Quero. It is getting hotter in here: determining and projecting the impacts of global environmental change on drylands, 2012
2012
-
[26]
Gandhi, L
P. Gandhi, L. Liu, and M. Silber. A pulsed-precipitation model of dryland vegetation pattern formation. SIAM J. Appl. Dyn. Syst. , 22:657, 2023
2023
-
[27]
von Hardenberg, E
J. von Hardenberg, E. Meron, M. Shachak, and Y. Zarmi. Diversity of vegetation patterns and desertification. Phys. Rev. Lett. , 87(19):198101, 2001
2001
-
[28]
Siteur, E
K. Siteur, E. Siero, M. B Eppinga, J. D. M. Rademacher, A. Doelman, and M. Rietkerk. Beyond Turing: The response of patterned ecosystems to environmental change. Ecol. Complex. , 20:81–96, 2014
2014
-
[29]
Gowda, Y
K. Gowda, Y. Chen, S. Iams, and M. Silber. Assessing the robustness of spatial pattern sequences in a dryland vegetation model. Proc. R. Soc. A , 472(2187):20150893, 2016
2016
-
[30]
Meyer, A
K. Meyer, A. Hoyer-Leitzel, S. Iams, I. Klasky, V. Lee, S. Ligtenberg, E. Bussmann, and M. L. Zeeman. Quantifying resilience to recurrent ecosystem disturbances using flow–kick dynamics. Nature Sustain., 1(11):671–678, 2018
2018
-
[31]
J. A. Sherratt. An analysis of vegetation stripe formation in semi-arid landscapes. J. Math. Biol., 51(2):183–197, 2005. 38
2005
-
[32]
van der Stelt, A
S. van der Stelt, A. Doelman, G. Hek, and J. D. M. Rademacher. Rise and fall of periodic patterns for a generalized Klausmeier–Gray–Scott model. J. Nonlin. Sci. , 23(1):39–95, 2013
2013
-
[33]
Striped pattern selection by advective reaction-diffusion systems: Resilience of banded vege- tation on slopes
E Siero, Arjen Doelman, MB Eppinga, Jens DM Rademacher, M Rietkerk, and K Siteur. Striped pattern selection by advective reaction-diffusion systems: Resilience of banded vege- tation on slopes. Chaos, 25(3):036411, 2015
2015
-
[34]
Carter and A
P. Carter and A. Doelman. Traveling stripes in the Klausmeier model of vegetation pattern formation. SIAM J Appl. Math. , 78(6):3213–3237, 2018
2018
-
[35]
D’Odorico, F
P. D’Odorico, F. Laio, and L. Ridolfi. Vegetation patterns induced by random climate fluctu- ations. Geophys. Res. Lett., 33(19), 2006
2006
-
[36]
Ursino and S
N. Ursino and S. Contarini. Stability of banded vegetation patterns under seasonal rainfall and limited soil moisture storage capacity. Adv. Water Resour. , 29(10):1556–1564, 2006
2006
-
[37]
Guttal and C
V. Guttal and C. Jayaprakash. Self-organization and productivity in semi-arid ecosystems: Implications of seasonality in rainfall. J. Theor. Biol. , 248(3):490–500, 2007
2007
-
[38]
A. G. Konings, S. C. Dekker, M. Rietkerk, and G. G. Katul. Drought sensitivity of patterned vegetation determined by rainfall-land surface feedbacks. J. Geophys. Res. G: Biogeosciences, 116(G4), 2011
2011
-
[39]
Siteur, M
K. Siteur, M. B. Eppinga, D. Karssenberg, M. Baudena, M. F. P. Bierkens, and M. Rietkerk. How will increases in rainfall intensity affect semiarid ecosystems? Water Resour. Res. , 50(7):5980–6001, 2014
2014
-
[40]
Gandhi, S
P. Gandhi, S. Bonetti, S. Iams, A. Porporato, and M. Silber. A fast–slow model of banded vegetation pattern formation in drylands. Physica D, 410:132534, 2020
2020
-
[41]
L. F. Gordillo and P. E. Greenwood. Intermittent precipitation-dependent interactions, en- compassing allee effect, may yield vegetation patterns in a transitional parameter range. Bull. Math. Biol. , 85(10):86, 2023
2023
-
[42]
O. V. Crompton and S. E. Thompson. Sensitivity of dryland vegetation patterns to storm characteristics. Ecohydrology, 14(2):e2269, 2021
2021
-
[43]
Crompton, A
O. Crompton, A. Sytsma, and S. Thompson. Emulation of the saint venant equations enables rapid and accurate predictions of infiltration and overland flow velocity on spatially heteroge- neous surfaces. Water Resour. Res. , 55(8):7108–7129, 2019
2019
-
[44]
A. Y. Kletter, J. Von Hardenberg, E. Meron, and A. Provenzale. Patterned vegetation and rainfall intermittency. J. Theor. Biol. , 256(4):574–583, 2009
2009
-
[45]
Yizhaq, S
H. Yizhaq, S. Sela, T. Svoray, S. Assouline, and G. Bel. Effects of heterogeneous soil-water diffusivity on vegetation pattern formation. Water Resour. Res. , 50(7):5743–5758, 2014
2014
-
[46]
Yizhaq, I
H. Yizhaq, I. Stavi, Mo. Shachak, and G. Bel. Geodiversity increases ecosystem durability to prolonged droughts. Ecol. Complex., 31:96–103, 2017
2017
-
[47]
Hamster, P
C. Hamster, P. van Heijster, and E. Siero. Blurring the busse balloon: Patterns in a stochastic klausmeier model. arXiv preprint arXiv:2411.13238 , 2024. 39
2024 arXiv
-
[48]
Rodriguez-Iturbe, D
I. Rodriguez-Iturbe, D. R. Cox, and V. Isham. Some models for rainfall based on stochastic point processes. Proc. R. Soc. Lond. A: Math. Phys. Sci. , 410(1839):269–288, 1987
1987
-
[49]
L. F. Shampine and M. W. Reichelt. The Matlab ODE suite. SIAM J. Sci. Comput. , 18(1):1– 22, 1997
1997
-
[50]
J. D. Meiss. Differential Dynamical Systems . SIAM, 2007
2007
-
[51]
K. J. Meyer, H. Fusco, C. Smith, and A. Hoyer-Leitzel. Continuation of fixed points and bifurcations from ode to flow-kick disturbance models. SIAM J. Appl. Dyn. Syst. , 23(4):2983– 3012, 2024
2024
-
[52]
Rietkerk, R
M. Rietkerk, R. Bastiaansen, S. Banerjee, J. van de Koppel, M. Baudena, and A. Doel- man. Evasion of tipping in complex systems through spatial pattern formation. Science, 374(6564):eabj0359, 2021
2021
-
[53]
N. J. Middleton and D. S. G. Thomas. World atlas of desertification. Publication Office of the European Union, 1992
1992
-
[54]
D’Odorico and A
P. D’Odorico and A. Bhattachan. Hydrologic variability in dryland regions: impacts on ecosys- tem dynamics and food security. Phi. Trans. R. Soc. B , 367(1606):3145–3157, 2012
2012
-
[55]
L. A. Gherardi and O. E. Sala. Effect of interannual precipitation variability on dryland productivity: A global synthesis. Glob. Change Biol. , 25(1):269–276, 2019
2019
-
[56]
G. A. Leonov and N. V. Kuznetsov. Time-varying linearization and the perron effects. Int. J. Bifurcat. Chaos, 17(04):1079–1107, 2007
2007
-
[57]
Butler and N
T. Butler and N. Goldenfeld. Robust ecological pattern formation induced by demographic noise. Phys. Rev. E , 80(3):030902, 2009
2009
-
[58]
Karig, K
D. Karig, K. M. Martini, T. Lu, N. A. DeLateur, N. Goldenfeld, and R. Weiss. Stochastic turing patterns in a synthetic bacterial population. Proc. Natl. Acad. Sci., 115(26):6572–6577, 2018
2018
-
[59]
Crompton, G
O. Crompton, G. G. Katul, and S. Thompson. Resistance formulations in shallow overland flow along a hillslope covered with patchy vegetation. Water Resour. Res., 56(5):e2020WR027194, 2020
2020
-
[60]
B. K. Bera, O. Tzuk, J. J. R. Bennett, and E. Meron. Linking spatial self-organization to community assembly and biodiversity. Elife, 10:e73819, 2021
2021
-
[61]
J. J. R. Bennett, B. K. Bera, M. Ferr´ e, H. Yizhaq, S. Getzin, and E. Meron. Phenotypic plasticity: A missing element in the theory of vegetation pattern formation. Proc. Natl. Acad. Sci., 120(50):e2311528120, 2023
2023
-
[62]
Hoyer-Leitzel and S
A. Hoyer-Leitzel and S. Iams. Impulsive fire disturbance in a savanna model: Tree–grass coexistence states, multiple stable system states, and resilience. Bull. Math. Biol. , 83(11):113, 2021
2021
-
[63]
M. L. Zeeman, K. Meyer, E. Bussmann, A. Hoyer-Leitzel, S. Iams, I. J. Klasky, V. Lee, and S. Ligtenberg. Resilience of socially valued properties of natural systems to repeated disturbance: A framework to support value-laden management decisions. Nat. Resour. Model., 31(3):e12...
2018
-
[64]
Patel and P
S. Patel and P. De Leenheer. On the spectral radius properties of a key matrix in periodic impulse control. Syst. Control Lett. , 187:105781, 2024
2024
-
[65]
E. H. Colombo, C. L´ opez, and E. Hern´ andez-Garc ´ ıa. Pulsed interaction signals as a route to biological pattern formation. Phys. Rev. Lett. , 130(5):058401, 2023
2023
-
[66]
E. H. Colombo, R. Martinez-Garcia, J. M. Calabrese, C. L´ opez, and E. Hern´ andez-Garc ´ ıa. Pulsed interactions unify reaction–diffusion and spatial nonlocal models for biological pattern formation. J. Stat. Mech.: Theory Exp. , 2024(3):034001, 2024
2024
-
[67]
Hoyer-Leitzel, S
A. Hoyer-Leitzel, S. M. Iams, A. J. Haslam-Hyde, M. L. Zeeman, and N. H. Fefferman. An immuno-epidemiological model for transient immune protection: A case study for viral respi- ratory infections. Infect. Dis. Model. , 8(3):855–864, 2023
2023
-
[68]
Gasper and M
G. Gasper and M. Rahman. Basic Hypergeometric Series , volume 96. Cambridge university press, 2011. 41
2011
Reviewed August 10, 2026 · model on record in the stance chip above.
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