Every reference with a DOI in the deposited reference list resolved to a known
work in Crossref or DataCite at the dated check, and none carried a retraction,
withdrawal, or removal notice.
The 79 checked references that resolve
resolves10.1016/j.seppur.2008.04.014Comparison of liquid–liquid extraction studies on platinum(IV) from acidic solutions using bis(2,4,4-trimethylpentyl) monothiophosphinic acid
resolves10.1039/b926440jStrategies for controlling biofouling in membrane filtration systems: challenges and opportunities
resolves10.1021/ie901886cSynthesis of Carbonaceous Poly(furfuryl alcohol) Membrane for Water Desalination
resolves10.1021/ie101827ySimulation of a Membrane Bioreactor System for Wastewater Organic Removal: Biological Treatment and Cake Layer−Membrane Filtration
resolves10.1021/cm050813sFacile Synthesis and Highly Reactive Silver Ion Adsorption of Novel Microparticles of Sulfodiphenylamine and Diaminonaphthalene Copolymers
resolves10.1039/b926455hInvestigation of the effects of ion and water interaction on structure and chemistry of silicalite MFI type zeolite for its potential use as a seawater desalination membrane
resolves10.1021/jp904570zSynthesis of Boehmite Hollow Core/Shell and Hollow Microspheres via Sodium Tartrate-Mediated Phase Transformation and Their Enhanced Adsorption Performance in Water Treatment
resolves10.1039/b925619aNew organic–inorganic hybrid microporous organosilica having high metal ion adsorption capacity
resolves10.1063/1.1530740Highly effective metal vapor absorbents based on carbon nanotubes
resolves10.1021/es048287dSorption of <sup>243</sup>Am(III) to Multiwall Carbon Nanotubes
resolves10.1021/es052208wAdsorption of Polycyclic Aromatic Hydrocarbons by Carbon Nanomaterials
resolves10.1002/jctb.1626Removal of nickel(II) from aqueous solution by carbon nanotubes
resolves10.1002/jctb.2073Acid modified bamboo‐type carbon nanotubes and cup‐stacked‐type carbon nanofibres as adsorbent materials: cadmium removal from aqueous solution
resolves10.1021/es104047dMutual Effects of Pb(II) and Humic Acid Adsorption on Multiwalled Carbon Nanotubes/Polyacrylamide Composites from Aqueous Solutions
resolves10.1002/app.35666Poly(vinyl alcohol)‐based MWCNT hydrogel for lead ion removal from contaminated water
resolves10.1002/cssc.201100163Carbon Nanotube‐Based Metal‐Ion Catchers as Supramolecular Depolluting Materials
resolves10.1039/c2jm16584hFe nanoparticle-functionalized multi-walled carbon nanotubes: one-pot synthesis and their applications in magnetic removal of heavy metal ions
resolves10.1007/s00396-011-2379-yA facile approach to synthesize poly(4-vinylpyridine)/multi-walled carbon nanotubes nanocomposites: highly water-dispersible carbon nanotubes decorated with gold nanoparticles
resolves10.1080/00222341003784956A Simple and Facile Approach to Synthesize Water-Soluble Multiwalled Carbon Nanotubes Wrapped by Poly(4-Vinylpyridine)
resolves10.1002/pola.24746Poly[(sodium sulfamate/carboxylate)isoprene‐<i>b</i>‐2‐vinyl pyridine] block polyampholytes: Synthesis and self‐assembly in aqueous media
resolves10.1002/masy.200690114Characterization of Plasma‐Polymerized 4‐vinyl Pyridine with Silver Nanoparticles on Poly(ethylene terephthalate) Film for Anti‐Microbial Properties
resolves10.1016/j.colsurfa.2006.12.037One-step synthesis of biocompatible gold nanoparticles using gallic acid in the presence of poly-(N-vinyl-2-pyrrolidone)
resolves10.1039/c1jm10470eMagnetically separable porous graphitic carbon with large surface area as excellent adsorbents for metal ions and dye
resolves10.2166/wst.2011.270Removal of Pb(II) and Cu(II) from aqueous solution using multiwalled carbon nanotubes/iron oxide magnetic composites
resolves10.1021/ma048692pGrafting of Poly(4-vinylpyridine) to Single-Walled Carbon Nanotubes and Assembly of Multilayer Films
resolves10.1002/chem.200500933Versatile Coordination Chemistry towards Multifunctional Carbon Nanotube Nanohybrids
resolves10.1021/ac050358jTime-Dependent Study of the Exfoliation Process of Carbon Nanotubes in Aqueous Dispersions by Using UV−Visible Spectroscopy
resolves10.1021/cm047866eNoncovalent and Nonspecific Molecular Interactions of Polymers with Multiwalled Carbon Nanotubes
resolves10.1088/0957-4484/17/15/012The quantitative characterization of the concentration and dispersion of multi-walled carbon nanotubes in suspension by spectrophotometry
resolves10.1016/j.carbon.2009.01.007Carbon-encapsulated magnetic nanoparticles as separable and mobile sorbents of heavy metal ions from aqueous solutions
resolves10.1016/j.talanta.2007.10.039Effect of oxidation of activated carbon on its enrichment efficiency of metal ions: Comparison with oxidized and non-oxidized multi-walled carbon nanotubes
resolves10.1016/j.colsurfa.2010.03.047Comparative study of heavy metal ions sorption onto activated carbon, carbon nanotubes, and carbon-encapsulated magnetic nanoparticles
resolves10.1021/jo051091rHighly Selective Colorimetric and Electrochemical Pb<sup>2+</sup> Detection Based on TTF-π-Pyridine Derivatives
resolves10.1021/ja051075bA Highly Selective Fluorescent Chemosensor for Pb
<sup>2+</sup>
resolves10.1021/ic50222a040Enhanced stability of ternary complexes in solution through the participation of heteroaromatic N bases. Comparison of the coordination tendency of pyridine, imidazole, ammonia, acetate, and hydrogen phosphate toward metal ion nitrilotriacetate complexes
The 27 references without a DOI — listed, not checked
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no DOI — not checkedhttp://www.fairfaxcounty.gov/nvswcd/newsletter/heavymetal.htm.
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no DOI — not checkedIonic Interactions in Natural and Synthetic Macromolecules
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no DOI — not checkedThe m‐MWCNTs for this study were produced in our laboratory by using a floating‐catalyst CVD technique according to a slight modification of the synthetic conditions reported in Ref. [17b]. Full details of the synthesis and physicochemical properties of the m‐MWCNTs will be reported in a forthcoming paper;
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no DOI — not checkedThe solution of m‐PVPy‐CNTs was prepared according a previously described general procedure:c=0.5 mg per 3 mL deionised water; the absorbance of this solution at 500 nm is 0.25 as displayed in Figure 6 b–d for which normalisation was not performed and the spectra are displayed as collected.
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no DOI — not checkedNotably the decontaminated water was analysed by using UV/Vis spectroscopy and SEM coupled with energy dispersive X‐ray (EDX) spectroscopy to ensure that no m‐PVPy‐CNTs or free PVPy had themselves contaminated the water and no trace of the materials were found in the depolluted solutions (Figures S9 and S10).
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