Computational study of interactions between ionized glyphosate and carbon nanotube: An alternative for mitigating environmental contamination
Pith reviewed 2026-05-18 20:15 UTC · model grok-4.3
The pith
Ionized glyphosate binds more strongly to carbon nanotubes than the neutral form.
A machine-rendered reading of the paper's core claim, the machinery that carries it, and where it could break.
Core claim
The central claim is that glyphosate in the G1, G3, G4, and G5 ionized forms exhibits stronger interactions with carbon nanotubes than the neutral G2 form, as shown by higher adsorption energies and greater electronic coupling in GFN2-xTB calculations. Topological analysis identifies a combination of covalent, non-covalent, and partially covalent contacts, while molecular dynamics supports the stability of these complexes. The CNT+G5 system in particular displays moderate interaction strength suitable for material recycling.
What carries the argument
The five protonation states of glyphosate (G1 to G5) at different pH ranges and the adsorption energies plus electronic coupling they produce when placed on a carbon nanotube surface.
If this is right
- Carbon nanotubes could remove ionized glyphosate from water across most pH ranges encountered in the environment.
- The neutral form at pH near 2-3 would adsorb less efficiently and might require different conditions or materials.
- Moderate binding in the G5 complex would allow the nanotubes to be regenerated and reused after capturing the pesticide.
- The observed electronic coupling opens the possibility of using the same systems for detection as well as removal.
Where Pith is reading between the lines
- If the binding differences hold, nanotube-based filters could be engineered to treat agricultural runoff at typical soil pH levels.
- The same computational approach might be tested on other charged organic contaminants to broaden remediation options.
- Running the same structures with higher-level quantum methods would provide a concrete check on whether the semi-empirical trends survive.
Load-bearing premise
The GFN2-xTB semi-empirical method supplies sufficiently accurate adsorption energies and interaction types for these ionized systems.
What would settle it
Laboratory measurement of the quantity of glyphosate adsorbed onto carbon nanotubes at fixed pH values, followed by direct comparison of the experimental uptake or binding strength to the computed values.
read the original abstract
The extensive use of glyphosate in agriculture has raised environmental concerns due to its adverse effects on plants, animals, microorganisms, and humans. This study investigates the interactions between ionized glyphosate and single-walled carbon nanotubes (CNT) using computational simulations through semi-empirical tight-binding methods (GFN2-xTB) implemented in the xTB software. The analysis focused on different glyphosate ionization states corresponding to various pH levels: G1 (pH < 2), G2 (pH ~ 2-3), G3 (pH ~ 4-6), G4 (pH ~ 7-10), and G5 (pH > 10.6). Results revealed that glyphosate in G1, G3, G4, and G5 forms exhibited stronger interactions with CNT, demonstrating higher adsorption energies and greater electronic coupling. The neutral state (G2) showed lower affinity, indicating that molecular protonation significantly influences adsorption. Topological analysis and molecular dynamics confirmed the presence of covalent, non-covalent, and partially covalent interactions, while the CNT+G5 system demonstrated moderate interactions suitable for material recycling. These findings suggest that carbon nanotubes, with their extraordinary properties such as nanocapillarity, porosity, and extensive surface area, show promise for environmental monitoring and remediation of glyphosate contamination.
Editorial analysis
A structured set of objections, weighed in public.
Referee Report
Summary. This manuscript reports a computational investigation of the adsorption interactions between five ionized forms of glyphosate (G1 at pH < 2, G2 at pH ~2-3, G3 at pH ~4-6, G4 at pH ~7-10, and G5 at pH >10.6) and single-walled carbon nanotubes using the GFN2-xTB semi-empirical tight-binding method. The central claim is that the G1, G3, G4, and G5 forms display stronger adsorption energies and greater electronic coupling than the neutral G2 form, with topological analysis and molecular dynamics confirming covalent, non-covalent, and partially covalent interactions; the CNT+G5 system is highlighted for moderate interactions suitable for material recycling, suggesting CNT utility for environmental remediation of glyphosate.
Significance. If the reported adsorption energy ordering and interaction types hold, the work offers timely computational insights into pH-dependent glyphosate-CNT binding relevant to agricultural pollution mitigation. The efficient screening of multiple protonation states via GFN2-xTB is a methodological strength for exploring large systems. The suggestion of CNT+G5 for recycling adds practical value. However, the absence of any benchmarking or experimental cross-validation limits the quantitative reliability and broader impact for remediation applications.
major comments (1)
- [Abstract and Results] Abstract and Results: the claim that G1, G3, G4, and G5 forms exhibit stronger interactions (higher adsorption energies and greater electronic coupling) rests entirely on GFN2-xTB outputs without reported benchmarking against DFT, higher-level ab initio methods, or experimental adsorption isotherms; this is load-bearing because GFN2-xTB performance on charged adsorbates and dispersion on extended π-systems is known to be variable, directly affecting the reliability of the relative affinities and remediation conclusions.
minor comments (2)
- [Abstract] The abstract and main text do not report error bars, convergence criteria, or basis-set/system-size checks for the GFN2-xTB adsorption energies, which would strengthen the quantitative claims.
- [Results] Clarify the precise definition of 'electronic coupling' and how it is quantified from the calculations (e.g., via charge transfer or orbital overlap metrics).
Simulated Author's Rebuttal
We thank the referee for their constructive review and for recognizing the timely relevance of pH-dependent glyphosate adsorption on carbon nanotubes as well as the efficiency of screening multiple protonation states with GFN2-xTB. We address the single major comment below.
read point-by-point responses
-
Referee: [Abstract and Results] Abstract and Results: the claim that G1, G3, G4, and G5 forms exhibit stronger interactions (higher adsorption energies and greater electronic coupling) rests entirely on GFN2-xTB outputs without reported benchmarking against DFT, higher-level ab initio methods, or experimental adsorption isotherms; this is load-bearing because GFN2-xTB performance on charged adsorbates and dispersion on extended π-systems is known to be variable, directly affecting the reliability of the relative affinities and remediation conclusions.
Authors: We agree that the manuscript does not report explicit benchmarking of GFN2-xTB results against DFT, higher-level methods, or experimental isotherms, and that this constitutes a limitation for the quantitative strength of the absolute adsorption energies. The method was chosen because it enables efficient exploration of five distinct ionization states on an extended nanotube model, a task that remains prohibitive for routine DFT on systems of this size. Existing literature validations of GFN2-xTB for dispersion-dominated adsorption on carbon nanostructures and for charged organic species support its use for identifying relative trends across protonation states. In the revised manuscript we will add a concise subsection (likely in Computational Details) that (i) cites relevant benchmark studies on GFN2-xTB performance for similar CNT–organic and charged adsorbate systems, (ii) explicitly states the expected accuracy range for relative energies, and (iii) qualifies the remediation conclusions accordingly. This textual revision will directly address the referee’s concern without requiring new high-level calculations at this stage. revision: yes
Circularity Check
No significant circularity; results are direct outputs from standard GFN2-xTB computations
full rationale
The paper's central results—adsorption energies, electronic coupling, and interaction classifications for the five glyphosate ionization states (G1–G5) on CNT—are obtained by direct application of the GFN2-xTB semi-empirical method to optimized geometries, followed by standard topological and molecular-dynamics post-processing. No parameters are fitted to the adsorption data, no target quantities are defined in terms of themselves, and no load-bearing self-citations or imported uniqueness theorems appear in the derivation. The ordering of affinities and the remediation implications therefore follow from the method's Hamiltonian and the chosen molecular models rather than from any circular reduction to the paper's own inputs.
Axiom & Free-Parameter Ledger
axioms (2)
- domain assumption GFN2-xTB semi-empirical method yields reliable relative adsorption energies for organic molecules on carbon nanostructures
- domain assumption Ionization states G1-G5 accurately represent glyphosate protonation at the stated pH ranges
Reference graph
Works this paper leans on
-
[1]
D. Feng, A. Soric, O. Boutin, Treatment technologies and degradation pathways of glyphosate: A critical review, Sci. Total Environ. 742 (2020) 140559 (2020). doi:10.1016/j.scitotenv.2020.140559
-
[2]
M. Tudi, H. Daniel Ruan, L. Wang, J. Lyu, R. Sadler, D. Connell, C. Chu, D. T. Phung, Agriculture development, pesticide application and its impact on the environment, Int. J. Environ. Res. Public. Health 18 (2021) 1112 (2021). doi:10.3390/ijerph18031112
-
[3]
F. P . Carvalho, Pesticides, environment, and food safety, Food Energy Secur. 6 (2017) 48–60 (2017).doi:10.1002/fes3.108
-
[4]
L. K. V . Gomes, L. H. V . Gomes, J. C. M. Amaral, P . P . Vidal, I. T. d. S. Gomes, A. M. d. J. Chaves Neto, A. F. G. Neto, Molecular dynamics of carbon nanotube with fipronil and glyphosate pesticides, The Journal of Engineering and Exact Sciences 9 (2023) 16128–01e (2023). doi:10.18540/jcecvl9iss6pp16128-01e
-
[5]
P . J. Espinoza-Montero, C. Vega-Verduga, P . Alulema-Pullupaxi, L. Fernández, J. L. Paz, Technologies employed in the treatment of water contaminated with glyphosate: A review, Molecules 25 (2020) 5550 (2020). doi:10.3390/molecules25235550
-
[6]
C. Jayasumana, S. Gunatilake, P . Senanayake, Glyphosate, hard water and nephrotoxic metals: are they the culprits behind the epidemic of chronic kidney disease of unknown etiology in Sri Lanka?, Int. J. Environ. Res. Public. Health 11 (2014) 2125–2147 (2014). doi:10.3390/ijerph110202125
-
[7]
K. F. Mendes, R. N. de Sousa, A. F. S. Laube, Current approaches to pesticide use and glyphosate-resistant weeds in Brazilian agriculture, in: J. Moudrý, K. F. Mendes, J. Bernas, R. da Silva Teixeira, R. N. de Sousa (Eds.), Multifunctionality and Impacts of Organic and Conventional Agriculture, IntechOpen, Rijeka, 2020, Ch. 1 (2020). doi:10.5772/intechope...
-
[8]
E. Haque, J. W. Jun, S. H. Jhung, Adsorptive removal of methyl orange and methylene blue from aqueous solution with a metal-organic framework material, iron terephthalate (MOF-235), J. Hazard. Mater. 185 (2011) 507–511 (2011). doi:10.1016/j.jhazmat.2010.09. 035
-
[9]
Q. Yang, J. Wang, X. Chen, W. Yang, H. Pei, N. Hu, Z. Li, Y. Suo, T. Li, J. Wang, The simultaneous detection and removal of organophosphorus pesticides by a novel Zr-MOF based smart adsorbent, J. Mater. Chem.A 6 (2018) 2184–2192 (2018). doi:10.1039/ C7TA08399H
work page 2018
-
[10]
L. Gaberell, C. Hoinkes, Highly hazardous profits. how Syngenta makes billions by selling toxic pesticides, Tech. rep., PUBLIC EYE (2019)
work page 2019
-
[11]
B. Arora, P . Attri, Carbon nanotubes (CNTs): A potential nanomaterial for water purification, J. Compos. Sci. 4 (2020) 135 (2020). doi:10.3390/jcs4030135
-
[12]
J. Jampílek, K. Králová, Carbon nanomaterials for agri-food and environmental applications, Elsevier, 2020, Ch. 17 - Potential of nanoscale carbon-based materials for remediation of pesticide-contaminated environment, pp. 359–399 (2020). doi:10.1016/ B978-0-12-819786-8.00017-7
work page 2020
-
[13]
G. Rahman, Z. Najaf, A. Mehmood, S. Bilal, A. Shah, S. Mian, G. Ali, An overview of the recent progress in the synthesis and applications of carbon nanotubes, C 5 (2019) 3 (2019). doi:10.3390/c5010003
-
[14]
A. Aligayev, F. Raziq, U. Jabbarli, N. Rzayev, L. Qiao, Chapter 17 - Morphology and topography of nanotubes, in: Y. Al-Douri (Ed.), Graphene, Nanotubes and Quantum Dots-Based Nanotechnology, Woodhead Publishing Series in Electronic and Optical Materials, Woodhead Publishing, 2022, pp. 355–420 (2022). doi:https://doi.org/10.1016/B978-0-323-85457-3.00019-0 ...
-
[15]
J. Peng, Y. He, C. Zhou, S. Su, B. Lai, The carbon nanotubes-based materials and their applications for organic pollutant removal: A critical review, Chinese Chem. Lett. 32 (2021) 1626–1636 (2021). doi:10.1016/j.cclet.2020.10.026
-
[16]
K. Sen, S. Chattoraj, Intelligent environmental data monitoring for pollution management, Elsevier, 2021, Ch. A comprehensive review of glyphosate adsorption with factors influencing mechanism: Kinetics, isotherms, thermodynamics study, pp. 93–125 (2021). doi:10.1016/B978-0-12-819671-7.00005-1
-
[17]
E. J. Barreiro, C. R. Rodrigues, M. G. a. Albuquerque, C. M. R. d. Sant’Anna, R. B. d. Alencastro, Molecular modeling: a tool for rational drug design in medicinal chemistry, Química Nova 20 (1997) 300–310 (1997). doi:10.1590/S0100-40421997000300011
-
[18]
E. J. Barreiro, C. A. M. Fraga, A. L. P . Miranda, C. R. Rodrigues, Medicinal chemistry of N-acylhydrazones: novel lead- compounds of analgesic, antiinflammatory and antithrombotic drugs, Química Nova 25 (2002) 129–148 (2002). doi:10.1590/ S0100-40422002000100022
work page 2002
-
[19]
C. Bannwarth, E. Caldeweyher, S. Ehlert, A. Hansen, P . Pracht, J. Seibert, S. Spicher, S. Grimme, Extended tight-binding quantum chemistry methods, WIREs Comput. Mol. Sci. 11 (2020) e1493 (2020). doi:10.1002/wcms.1493. Silva et al. 11
-
[20]
H. B. Schlegel, Geometry optimization, WIREs Comput. Mol. Sci. 1 (2011) 790–809 (2011). doi:10.1002/wcms.34
-
[21]
C. Aguiar, I. Camps, Exploring the potential of boron-nitride nanobelts in environmental applications: Greenhouse gases capture, Surfaces and Interfaces 52 (2024) 104874 (2024). doi:10.1016/j.surfin.2024.104874
-
[22]
G. A. D. Herath, L. S. Poh, W. J. Ng, Statistical optimization of glyphosate adsorption by biochar and activated carbon with response surface methodology, Chemosphere 227 (2019) 533–540 (2019). doi:10.1016/j.chemosphere.2019.04.078
-
[23]
C. Plett, S. Grimme, Automated and efficient generation of general molecular aggregate structures, Angew. Chem. Int. Ed. 62 (2022). doi:10.1002/anie.202214477
-
[24]
Rauk, Orbital interaction theory of organic chemistry, 2nd Edition, Wiley, 2000 (2000)
A. Rauk, Orbital interaction theory of organic chemistry, 2nd Edition, Wiley, 2000 (2000). doi:10.1002/0471220418
-
[25]
T. A. Albright, J. K. Burdett, M.-H. Whangbo, Orbital interactions in chemistry, 2nd Edition, Wiley, 2013 (2013). doi:10.1002/ 0471220418
work page 2013
-
[26]
J. T. Kohn, N. Gildemeister, S. Grimme, D. Fazzi, A. Hansen, Efficient calculation of electronic coupling integrals with the dimer projection method via a density matrix tight-binding potential, J. Chem. Phys. 159 (2023) 144106 (2023). doi:10.1063/5.0167484
-
[27]
T. Lu, F. Chen, Multiwfn: A multifunctional wavefunction analyzer, J. Comput. Chem. 33 (2012) 580–592 (2012). doi:10.1002/jcc. 22885
work page doi:10.1002/jcc 2012
-
[28]
Lu, A comprehensive electron wavefunction analysis toolbox for chemists, Multiwfn, J
T. Lu, A comprehensive electron wavefunction analysis toolbox for chemists, Multiwfn, J. Chem. Phys. 161 (2024) 082503 (2024). doi:10.1063/5.0216272
-
[29]
R. F. W. Bader, Atoms in molecules: a quantum theory, International series of monographs on chemistry, Clarendon Press, Oxford, 1994 (1994)
work page 1994
-
[30]
D. Koch, M. Pavanello, X. Shao, M. Ihara, P . W. Ayers, C. F. Matta, S. Jenkins, S. Manzhos, The analysis of electron densities: from basics to emergent applications, Chem. Rev. 124 (2024) 12661–12737 (2024). doi:10.1021/acs.chemrev.4c00297
-
[31]
I. Fedorov, Topological analysis of electron density in graphene/benzene and graphene/hBN, Materials 18 (2025) 1790 (2025). doi:10.3390/ma18081790
-
[32]
J. M. Martínez, L. Martínez, Packing optimization for automated generation of complex system’s initial configurations for molecular dynamics and docking, J. Comput. Chem. 24 (2003) 819–825 (2003). doi:10.1002/jcc.10216
-
[33]
S. Spicher, S. Grimme, Robust atomistic modeling of materials, organometallic, and biochemical systems, Angewandte Chemie International Edition 59 (2020) 15665–15673 (2020). doi:10.1002/anie.202004239
- [34]
-
[35]
V . Meunier, A. G. Souza Filho, E. B. Barros, M. S. Dresselhaus, Physical properties of low-dimensionalsp2-based carbon nanostructures, Rev. Mod. Phys. 88 (2016) 025005 (2016). doi:10.1103/RevModPhys.88.025005
-
[36]
M. S. Ribeiro, A. L. Pascoini, W. G. Knupp, I. Camps, Effects of surface functionalization on the electronic and structural properties of carbon nanotubes: A computational approach, Appl. Surf. Sci. 426 (2017) 781–787 (2017). doi:10.1016/j.apsusc.2017.07.162
-
[37]
G. L. Miessler, P . J. Fischer, D. A. Tarr, Inorganic chemistry, 5th Edition, Pearson, 2014 (2014)
work page 2014
-
[38]
A. C. Reber, S. N. Khanna, Superatoms: electronic and geometric effects on reactivity, Accounts Chem. Res. 50 (2017) 255–263 (2017). doi:10.1021/acs.accounts.6b00464
-
[39]
S. Zavareh, Z. Farrokhzad, F. Darvishi, Modification of zeolite 4A for use as an adsorbent for glyphosate and as an antibacterial agent for water, Ecotoxicology and Environmental Safety 155 (2018) 1–8 (2018). doi:10.1016/j.ecoenv.2018.02.043
-
[40]
R. Krishnamoorthy, B. Govindan, F. Banat, V . Sagadevan, M. Purushothaman, P . L. Show, Date pits activated carbon for divalent lead ions removal, J. Biosci. Bioeng. 128 (2019) 88–97 (2019). doi:10.1016/j.jbiosc.2018.12.011
-
[41]
J. C. Diel, D. S. P . Franco, I. d. S. Nunes, H. A. Pereira, K. S. Moreira, T. A. de L. Burgo, E. L. Foletto, G. L. Dotto, Carbon nanotubes impregnated with metallic nanoparticles and their application as an adsorbent for the glyphosate removal in an aqueous matrix, J. Environ. Chem. Eng. 9 (2021) 105178 (2021). doi:10.1016/j.jece.2021.105178
-
[42]
J. F. Van der Maelen, Topological analysis of the electron density in the carbonyl complexes M(CO)8(M = Ca, Sr, Ba), Organometallics 39 (2019) 132–141 (2019). doi:10.1021/acs.organomet.9b00699
-
[43]
C. F. Matta, R. J. Boyd, The Quantum Theory of Atoms in Molecules: From Solid State to DNA and Drug Design, John Wiley & Sons, 2007 (2007). 12 Interactions between ionized glyphosate and carbon nanotube
work page 2007
-
[44]
J. A. Cabeza, J. F. Van der Maelen, S. García-Granda, Topological analysis of the electron density in the N-heterocyclic carbene triruthenium cluster [ Ru3(µ − H)2(µ3 − MeImCH )(CO)9] (Me2 Im = 1,3-dimethylimidazol-2-ylidene), Organometallics 28 (2009) 3666–3672 (2009). doi:10.1021/om9000617
-
[45]
K. Koumpouras, J. A. Larsson, Distinguishing between chemical bonding and physical binding using electron localization function (ELF), J. Phys. Condens. Matter 32 (2020) 315502 (2020). doi:10.1088/1361-648X/ab7fd8
-
[46]
H. Khartabil, A. Rajamani, C. Lefebvre, J. Pilmé, E. Hénon, A 30-year journey towards an accelerated scheme for visualizing ELF basins in molecules, J. Comput. Chem. 46 (2025) e70146 (2025). doi:10.1002/jcc.70146
-
[47]
M. Michalski, A. J. Gordon, S. Berski, Topological analysis of the electron localisation function (ELF) applied to the electronic structure of oxaziridine: the nature of N-O bond, Struct. Chem. 30 (2019) 2181–2189 (2019). doi:10.1007/s11224-019-01407-9
-
[48]
D. D. Nguyen, Z. Cang, G.-W. Wei, A review of mathematical representations of biomolecular data, Phys. Chem. Chem. Phys. 22 (2020) 4343–4367 (2020). doi:10.1039/C9CP06554G
-
[49]
H. Cheng, A. C. Cooper, G. P . Pez, M. K. Kostov, P . Piotrowski, S. J. Stuart, Molecular dynamics simulations on the effects of diameter and chirality on hydrogen adsorption in single walled carbon nanotubes, J. Phys. Chem. B 109 (2005) 3780–3786 (2005). doi:10.1021/jp045358m
-
[50]
H. T. Silva, L. C. S. Faria, T. A. Aversi-Ferreira, I. Camps, (DATASET+VIDEOS) Computational study of interactions between ionized glyphosate and carbon nanotube: An alternative for mitigating environmental contamination. doi:10.5281/zenodo.16994309
discussion (0)
Sign in with ORCID, Apple, or X to comment. Anyone can read and Pith papers without signing in.