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1

Young, Jay A. "Lead(II) Oxide." Journal of Chemical Education 83, no. 10 (2006): 1457. http://dx.doi.org/10.1021/ed083p1457.

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2

Basirun, Wan Jeffrey, Idris Mohamed Saeed, Hanieh Ghadimi, et al. "Lead Corrosion and Formation of Lead Oxides from a Lead-air Cell in Methanesulfonic Acid." Journal of New Materials for Electrochemical Systems 19, no. 4 (2017): 217–22. http://dx.doi.org/10.14447/jnmes.v19i4.278.

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The corrosion of lead in methanesulfonic acid solution in the presence of a MnO2 air cathode in a primary lead-air cell is in-vestigated. The highest power density of the lead-air cell is 2.8 mW cm-2. X-ray photoelectron spectroscopy and powder X-ray diffraction results demonstrate the formation of lead (II) oxide and lead (IV) dioxide on the air cathode after continuous discharge. Field emission scanning electron microscopy image shows that the surface coverage of lead (II) oxide and lead (IV) dioxide on the air cathode is only partial and will allow oxygen reduction.
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3

Gayduk, O. V. "DETERMINATION OF LEAD OXIDE IN MIXTURE WITH LEAD FLUORIDE." METHODS AND OBJECTS OF CHEMICAL ANALYSIS 9, no. 3 (2014): 118–20. http://dx.doi.org/10.17721/moca.2014.118-120.

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4

Ranjbar, Maryam, Ömer Çelik, S. Heydar Mahmoudi Najafi, Shabnam Sheshmani, and Neda Akbari Mobarakeh. "Synthesis of Lead(II) Minoxidil Coordination Polymer: A New Precursor for Lead(II) Oxide and Lead(II) Hydroxyl Bromide." Journal of Inorganic and Organometallic Polymers and Materials 22, no. 4 (2011): 837–44. http://dx.doi.org/10.1007/s10904-011-9648-6.

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5

Sue, Kiwamu, Yukiya Hakuta, Richard L. Smith, Tadafumi Adschiri, and Kunio Arai. "Solubility of Lead(II) Oxide and Copper(II) Oxide in Subcritical and Supercritical Water." Journal of Chemical & Engineering Data 44, no. 6 (1999): 1422–26. http://dx.doi.org/10.1021/je9901029.

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6

Kemmitt, Tim, Liliane G. Hubert-Pfalzgraf, Graeme J. Gainsford, and Philippe Richard. "Cost efficient preparation of lead aminoalkoxides directly from lead(II) oxide." Inorganic Chemistry Communications 8, no. 12 (2005): 1149–53. http://dx.doi.org/10.1016/j.inoche.2005.09.021.

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7

Nepal, Ranjan, and Raja Ram Pradhananga. "Lead Oxide-Graphite Composite Electrode for pH Measurement." Nepal Journal of Science and Technology 15, no. 1 (2015): 61–66. http://dx.doi.org/10.3126/njst.v15i1.12015.

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Lead oxide-graphite composite electrode for pH measurement had been fabricated with different percentage of PbO2 in the composite. The proportions of lead oxide affected the sensitivity of the electrode. The electrode composed of 50% lead oxide and 50% graphite gave reproducible result and behaved in Nernstian manner with a potential gradient of -58.8±0.3 mV per unit change in pH. Metal ions such as iron (II), iron (III) and lead (II) interfered in the measurement of pH, while silver (I), copper (II), oxidizing agents such as dichromate and permanganate do not interfere. In absence of interfer
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KELLER, H. L., and R. LANGER. "ChemInform Abstract: HgPb2O2Cl2, a “Perforated” Lead(II) Oxide." ChemInform 25, no. 40 (2010): no. http://dx.doi.org/10.1002/chin.199440009.

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Kokozay, Vladimir, and Alexander Sienkiewicz. "DIRECT SYNTHESIS OF LEAD(II) COMPLEXES WITH TRIETHANOLAMINE USING LEAD(II) OXIDE AS STARTING MATERIAL." Journal of Coordination Chemistry 30, no. 3-4 (1993): 245–51. http://dx.doi.org/10.1080/00958979308022756.

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10

Krivovichev, Sergey V., and Peter C. Burns. "Crystal chemistry of lead oxide chlorides. II. Crystal structure of Pb7O4(OH)4Cl2." European Journal of Mineralogy 14, no. 1 (2002): 135–39. http://dx.doi.org/10.1127/0935-1221/2002/0014-0135.

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11

Ilginis, Arminas, and Egidijus Griškonis. "Modification of Graphite Felt with Lead (II) Formate and Acetate—An Approach for Preparation of Lightweight Electrodes for a Lead-Acid Battery." Processes 8, no. 10 (2020): 1248. http://dx.doi.org/10.3390/pr8101248.

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Lead-acid battery (LAB) weight is a major downside stopping it from being adapted to electric/hybrid vehicles. Lead grids constitute up to 50% of LAB electrode’s weight and it only ensures electric connection to electrochemically active material and provides structural integrity. Using graphite felt (GF) as a current collector can reduce the electrode’s weight while increasing the surface area. Modification of GF with lead (II) oxide using impregnation and calcination techniques and lead (II) formate and acetate as precursors was conducted to produce composite electrodes. It was found that lea
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12

Motitswe, Moeng Geluk, Kassim Olasunkanmi Badmus, and Lindiwe Khotseng. "Application of Reduced Graphene Oxide-Zinc Oxide Nanocomposite in the Removal of Pb(II) and Cd(II) Contaminated Wastewater." Applied Nano 5, no. 3 (2024): 162–89. http://dx.doi.org/10.3390/applnano5030012.

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Toxic metal wastewater is a challenge for exposed terrestrial and aquatic environments, as well as the recyclability of the water, prompting inputs for the development of promising treatment methods. Consequently, the rGO/ZnONP nanocomposite was synthesized at room temperature for four hours and was tested for the adsorption of cadmium and lead in wastewater. The optimized nanocomposite had the lowest band gap energy (2.69 eV), and functional group interactions were at 516, 1220, 1732, 3009, and 3460 cm−1. The nanocomposite showed good ZnO nanoparticle size distribution and separation on rGO s
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13

Sreekala, G., Beevi A. Fathima, and B. Beena. "Adsorption of Lead (Ii) Ions by Ecofriendly Copper Oxide Nanoparticles." Oriental Journal of Chemistry 35, no. 6 (2019): 1731–36. http://dx.doi.org/10.13005/ojc/350615.

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The present investigation is on the application of green synthesized CuO nanoparticles for elimination of lead (II) from waste water. Nano CuO was prepared from aqueous copper acetate solution and aqueous leaf extract of Simarouba glauca plant. The prepared nano CuO was characterized by XRD, FT-IR, UV, SEM and TEM. The nano CuO synthesized by this method was spherical in shape with particle size nearly 20 nm. The adsorption of lead (II) ions on nano CuO under various parameters such as amount of catalyst, concentration of metal ion and pH were studied using batch adsorption experiments. Experi
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Uzunoğlu, Zeynep, Demet Yilmaz, and Yusuf Şahin. "Determination of the saturation thickness and albedo factors for mercury(II) oxide and lead(II) oxide." Instrumentation Science & Technology 45, no. 1 (2016): 111–21. http://dx.doi.org/10.1080/10739149.2016.1199032.

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15

NAITO, Hiroyuki, Sigemi SATO, Hiroshi OKAYASU, and Eiichi NARITA. "Studies on production of active lead(II) oxide. IV." NIPPON KAGAKU KAISHI, no. 11 (1989): 1839–47. http://dx.doi.org/10.1246/nikkashi.1989.1839.

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16

Duffy, J. A. "The absorption edge of lead(II) in oxide systems." physica status solidi (a) 88, no. 1 (1985): K55—K57. http://dx.doi.org/10.1002/pssa.2210880158.

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17

Han, Kyoung R., Hee Jin Koo, and Chang Sup Lim. "Novel Route to Lead-Based Ferroelectric Compounds via Tetragonal Lead(II) Oxide Intermediates." Journal of the American Ceramic Society 83, no. 9 (2004): 2214–18. http://dx.doi.org/10.1111/j.1151-2916.2000.tb01537.x.

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18

Aliakbari, Azam, Ezzatollah Najafi, Mostafa M. Amini, and Seik Weng Ng. "Structure and photoluminescence properties of lead(II) oxide nanoparticles synthesized from a new lead(II) coordination polymer." Monatshefte für Chemie - Chemical Monthly 145, no. 8 (2014): 1277–85. http://dx.doi.org/10.1007/s00706-014-1202-0.

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19

Lo, Po Sang, and Chun Ki Yeung. "Graphene Oxide PMMA Solid on the Absorption of Lead Ion." Materials Science Forum 896 (March 2017): 32–39. http://dx.doi.org/10.4028/www.scientific.net/msf.896.32.

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GO-PMMA solid was used to test its ability on absorbing the lead ion obtained from standard solution. Samples of the test solution were collected at 0 min, 10 min, 30 min, 50 min and 70 min. The results analyzed from ICP reveal that GO-PMMA solid could absorb lead (II) ion sup to 68.6%, which is 65.8% higher than the control setup, i.e. PMMA solid, at room temperature and pressure. The dry mass of GO-PMMA solid is around 119.82g and the mass after testing is around 124.21g. The ability of absorption could be easily refreshed by washing with ethanol and distillated water (80/20 v/v) several tim
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20

Kireeti, Kota V. M. K., Chandrakanth G., Mahesh M. Kadam, and Neetu Jha. "A sodium modified reduced graphene oxide–Fe3O4 nanocomposite for efficient lead(ii) adsorption." RSC Advances 6, no. 88 (2016): 84825–36. http://dx.doi.org/10.1039/c6ra15364j.

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A simple, cost-effective and facile route was employed to synthesize a hydrophobic sodium modified reduced graphene oxide-magnetic iron oxide (SMGI) nanocomposite for the removal of Pb(ii) from aqueous solutions via adsorption.
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Mashentseva, Anastassiya A., Nurzhigit Seitzhapar, Murat Barsbay, et al. "Adsorption isotherms and kinetics for Pb(ii) ion removal from aqueous solutions with biogenic metal oxide nanoparticles." RSC Advances 13, no. 38 (2023): 26839–50. http://dx.doi.org/10.1039/d3ra05347d.

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This study investigates the sorption removal of lead(ii) ions using zinc oxide (ZnO) and copper(ii) oxide (CuO) nanoparticles synthesized through a wet combustion synthesis with the aid of plant extract from Serratula coronata L.
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22

SONAWALE, S. B., Y. V. GHALSASI, and A. P. ARGEKAR. "Extraction of Lead (II) and Copper (II) from Salicylate Media by Tributylphosphine Oxide." Analytical Sciences 17, no. 2 (2001): 285–89. http://dx.doi.org/10.2116/analsci.17.285.

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23

Gören, Hatice Kübra, Öner Canavar, and Uğur Tan. "Mitigating Salinity Stress in Cotton (Gossypium hirsutum L.) with K-humate and Iron Oxide Nanoparticles." Türk Tarım ve Doğa Bilimleri Dergisi 11, no. 4 (2024): 1275–83. http://dx.doi.org/10.30910/turkjans.1511172.

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Salinity stress poses a major challenge to plant growth and development, causing problems like osmotic stress, ion toxicity, and nutrient imbalances. These issues lead to reduced photosynthesis and early aging of plants. In this study, we explored the potential of potassium humate (Kh) and iron oxide nanoparticles (Fe (II,III) oxide-NPs) to help cotton plants (Gossypium hirsitum L.) cope with saline conditions. We examined various growth parameters such as plant height, leaf number, fresh and dry weights of leaves and roots, leaf area, chlorophyll content (SPAD values), and relative water cont
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24

Aslani, Alireza, and Ali Morsali. "Sonochemical synthesis of nano-sized metal-organic lead(II) polymer: A precursor for the preparation of nano-structured lead(II) iodide and lead(II) oxide." Inorganica Chimica Acta 362, no. 14 (2009): 5012–16. http://dx.doi.org/10.1016/j.ica.2009.08.011.

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25

Pershin, P. S., A. A. Katayev, N. I. Shurov, P. A. Arkhipov, and Yu P. Zaikov. "LEAD OXIDE (II) DISSOLUTION RATE IN EQUIMOLAR KCL–PBCL2 MELT." Izvestiya Vuzov. Tsvetnaya Metallurgiya (Proceedings of Higher Schools. Nonferrous Metallurgy), no. 2 (February 23, 2015): 3. http://dx.doi.org/10.17073/0021-3438-2013-2-3-8.

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26

Liang, Mengyu, Huaming Guo, and Wei Xiu. "Mechanisms of arsenite oxidation and arsenate adsorption by a poorly crystalline manganese oxide in the presence of low molecular weight organic acids." E3S Web of Conferences 98 (2019): 04009. http://dx.doi.org/10.1051/e3sconf/20199804009.

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Manganese oxides are considered as one of the effective oxides capable of oxidizing arsenite and reduce the toxicity of arsenic. Since low molecular weight organic acids (LMWOAs) commonly found in nature can act as reducing and chelating agents for manganese oxides, it is particularly important to investigate how these organic acids with different numbers of carboxyl groups like citrate and EDTA affect oxidation and adsorption of arsenic by manganese oxides. In this study, low As(V) adsorption on manganese oxide is slightly enhanced by citrate and EDTA, which results from the increase in activ
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27

E. Sultan, Alaa, Hussein I.Abdullah, and Abdul qadier H. Niama. "Adsorption Study of Ni (II) and Pb (II) by Silver oxide Nanoparticles." Journal of Kufa for Chemical Sciences 2, no. 10 (2023): 218–30. http://dx.doi.org/10.36329/jkcm/2023/v2.i10.11021.

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In the present work, silver oxide nanoparticles (Ag2O-NPs) were used as an adsorption surface for removing nickel and lead ions from aqueous solutions, the surface properties were studied using various techniques like Fourier-transform infrared spectroscopy (FTIR) spectra shown the functional groups present in the synthesis silver oxides nanoparticles, X-ray diffraction (XRD) confirmed the crystalline nature of Ag2O-NPs with a crystallite size 38.69 nm, field emission scanning-electron-microscopy(FE-SEM) images showed that the Ag2O-NPs has spherical shape, and the presence of elemental silver
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28

Balela, Mary Donnabelle L., Clarisse Mancera, Bianca Patricia Reyes, and Ma Christine Reyes. "Anodization of Zirconia Nanotubes for Lead (II) Adsorption." Materials Science Forum 939 (November 2018): 113–19. http://dx.doi.org/10.4028/www.scientific.net/msf.939.113.

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Zirconia (ZrO2) nanotubes were prepared by anodization of zirconium (Zr) foil in a glycerol-formamide electrolyte containing ammonium fluoride. The effects of anodizing voltage and temperature on the pore diameter and thickness of the resulting nanotube array were studied. ZrO2 nanotubes with larger pore diameter were formed at higher anodizing voltage and temperature. Additinally, the thickness of the oxide layer was also increased. The applicability of the ZrO2 nanotubes for adsorption of heavy metals in aqueous solution was evaluated using Pb (II) as the model ions. Generally, the uptake of
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Gustafsson, Jon Petter, Charlotta Tiberg, Abubaker Edkymish, and Dan Berggren Kleja. "Modelling lead(II) sorption to ferrihydrite and soil organic matter." Environmental Chemistry 8, no. 5 (2011): 485. http://dx.doi.org/10.1071/en11025.

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Environmental contextLead(II) is a toxic metal pollutant with many anthropogenic sources. We show that lead(II) is bound more strongly to soil surfaces than previously understood. This knowledge may lead to better models for lead(II) dissolution from the soils, which will improve risk assessments for this metal. AbstractLead(II) adsorption to soil organic matter and iron (hydr)oxides is strong, and may control the geochemical behaviour of this metal. Here, we report the adsorption of Pb2+ (i) to 2-line ferrihydrite, and (ii) to a mor layer. The results showed that ferrihydrite has heterogeneou
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Pineda Huitron, Rosa Maria, Pavel Ernesto Ramírez López, Esa Vuorinen, Pooria Nazen Jalali, Leonardo Pelcastre, and Maija Kärkkäinen. "Scale Formation on HSLA Steel during Continuous Casting Part II: The Effect of Surface Conditions." Metals 10, no. 9 (2020): 1245. http://dx.doi.org/10.3390/met10091245.

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The present research addresses the effect of surface condition on oxide scale formation at high temperatures such as those experienced during secondary cooling in Continuous Casting. Tests were carried out in clean, as-cast and surfaces covered with casting powder to replicate the oxidation/re-oxidation after the mould. Specimens oxidized at 1000, 1100 and 1200 °C under dry air and water-vapour conditions revealed that the oxide scale formation is strongly influenced by temperature, environmental and surface conditions. The oxide scale thickness increases with temperature alterations in the su
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31

Pratima, Rani Sardar. "Simultaneous removal of lead and cadmium ions by nickel oxide nanoparticles." Indian Journal of Science and Technology 14, no. 28 (2021): 2327–36. https://doi.org/10.17485/IJST/v14i28.1407.

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Abstract <strong>Objectives:</strong>&nbsp;To study the simultaneous removal of metal ions to understand the dynamics of the adsorption process for the assessment of the actual potential of an adsorbent in real-life applications.&nbsp;<strong>Methods:</strong>&nbsp;A one-step hydrothermal method was employed for the synthesis of nanomaterial. The hydrothermal treatment was performed at 110o C for 3 hours and calcined at 300o C for 2 hr to complete the nickel oxide nanoparticle synthesis. A systematic study of metal ion adsorption onto the nickel oxide nanoparticle was conducted to evaluate the
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Ricco, Raffaele, Kristina Konstas, Mark J. Styles, et al. "Lead(ii) uptake by aluminium based magnetic framework composites (MFCs) in water." Journal of Materials Chemistry A 3, no. 39 (2015): 19822–31. http://dx.doi.org/10.1039/c5ta04154f.

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33

Ramazani, Ali, Shima Hamidi, and Ali Morsali. "A novel mixed-ligands holodirected two-dimensional lead(II) coordination polymer as precursor for preparation lead(II) oxide nanoparticles." Journal of Molecular Liquids 157, no. 1 (2010): 73–77. http://dx.doi.org/10.1016/j.molliq.2010.08.012.

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34

Morsali, Ali, and Akram Panjehpour. "Ultrasonic-assisted synthesis of nano-structured lead(II) coordination polymers as precursors for preparation of lead(II) oxide nanoparticles." Inorganica Chimica Acta 391 (August 2012): 210–17. http://dx.doi.org/10.1016/j.ica.2012.04.024.

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35

Gordon-Nuñez, Franklin, Katherine Vaca-Escobar, Milton Villacís-García, et al. "Applicability of Goethite/Reduced Graphene Oxide Nanocomposites to Remove Lead from Wastewater." Nanomaterials 9, no. 11 (2019): 1580. http://dx.doi.org/10.3390/nano9111580.

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Lead ion in drinking water is one of the most dangerous metals. It affects several systems, such as the nervous, gastrointestinal, reproductive, renal, and cardiovascular systems. Adsorption process is used as a technology that can solve this problem through suitable composites. The adsorption of lead (Pb(II)) on graphene oxide (GO) and on two goethite (α-FeOOH)/reduced graphene oxide (rGO) composites (composite 1: 0.10 g GO: 22.22 g α-FeOOH and composite 2: 0.10 g GO: 5.56 g α-FeOOH), in aqueous medium, was studied. The GO was synthesized from a commercial pencil lead. Composites 1 and 2 were
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Zhu, Shan Shan, Fu Tao Hu, Dao Dong Pan, Wei Lian Xu, and Ning Gan. "Determination of Ultra Trace of Heavy Metals in Water by ICP-AES Based on Magnetic Enrichment." Advanced Materials Research 487 (March 2012): 658–62. http://dx.doi.org/10.4028/www.scientific.net/amr.487.658.

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A new method has been established for the pre-enrichment of trace heavy metals(lead(II), cadmium(II), chromium(VI) and nickel(II)) by magnetic iron oxide(core) / zirconium dioxide(shell) and determined by inductively coupled plasma atomic emission spectrometry (ICP-AES) in water samples. The factors affecting the separation and pre-enrichment of analytes such as amounts of magnetic iron oxide / zirconium dioxide, elution time and interfering ions were studied. The detection limits of the method (3σ) were 13.5ng/mL, 1.01ng/mL, 2.94ng/mL and 3.31mg/L respectively for lead(II), cadmium(II), chrom
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Liu, Sen, Ziying Wang, Tianyi Han, Teng Fei, and Tong Zhang. "Mesoporous Magnesium Oxide Nanosheet Electrocatalysts for the Detection of Lead(II)." ACS Applied Nano Materials 2, no. 5 (2019): 2606–11. http://dx.doi.org/10.1021/acsanm.9b00600.

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Egirani, Davidson E., Nanfe R. Poyi, and Napoleon Wessey. "Synthesis of a copper(II) oxide–montmorillonite composite for lead removal." International Journal of Minerals, Metallurgy, and Materials 26, no. 7 (2019): 803–10. http://dx.doi.org/10.1007/s12613-019-1788-7.

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Darwish, A. A. A., E. F. M. El-Zaidia, M. M. El-Nahass, T. A. Hanafy, and A. A. Al-Zubaidi. "Dielectric and electrical conductivity studies of bulk lead (II) oxide (PbO)." Journal of Alloys and Compounds 589 (March 2014): 393–98. http://dx.doi.org/10.1016/j.jallcom.2013.11.218.

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Tátrai, Erzsébet, Miklós Náray, Márta Brózik, Zoltán Adamis, and György Ungváry. "Combined pulmonary toxicity of diethyldithiocarbamate and lead (II) oxide in rats." Journal of Applied Toxicology 18, no. 1 (1998): 33–38. http://dx.doi.org/10.1002/(sici)1099-1263(199801/02)18:1<33::aid-jat467>3.0.co;2-x.

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Chukwuemeka-okorie, H. O., J. U. Ani, S. C. Agbo, et al. "Adsorptive performance of green synthesized zinc oxide nanoparticles for the removal of cadmium (II) and lead (II) ions." IOP Conference Series: Earth and Environmental Science 1178, no. 1 (2023): 012021. http://dx.doi.org/10.1088/1755-1315/1178/1/012021.

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Abstract This study has Zinc oxide (ZnO) nanoparticles (NPs) synthesized from the leaf extract of Costus Afers via a green approach. The synthesized zinc oxide nanoparticle (ZnO NPs) showed excellent adsorption capabilities towards Cd (II) and Pb (II) ions. ZnO NPs were characterized by Fourier Transform Infrared (FT-IR), Scanning Electron Microscopy (SEM), and X-ray Diffraction (XRD). The formation of ZnO NPs was confirmed by the absorption band at 825cm−1 and 747cm−1. The XRD and SEM analysis show the high purity and hexagonal structure of ZnO NPs with a crystallite size of 83.56 nm. A batch
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Liu, Cong, Dongxiang Zhang, Liting Zhao, et al. "Synthesis of a thiacalix[4]arenetetrasulfonate-functionalized reduced graphene oxide adsorbent for the removal of lead(ii) and cadmium(ii) from aqueous solutions." RSC Advances 6, no. 114 (2016): 113352–65. http://dx.doi.org/10.1039/c6ra24353c.

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A thiacalix[4]arenetetrasulfonate-functionalized reduced graphene oxide (TCAS–rGO) adsorbent was synthesized and used as an adsorbent for the removal of lead(ii) and cadmium(ii) from aqueous solutions.
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Lingamdinne, Lakshmi Prasanna, Janardhan Reddy Koduru, and Rama Rao Karri. "Green Synthesis of Iron Oxide Nanoparticles for Lead Removal from Aqueous Solutions." Key Engineering Materials 805 (June 2019): 122–27. http://dx.doi.org/10.4028/www.scientific.net/kem.805.122.

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Pb(II) being carcinogenic and one of the heavy metals which always pose a severe threat to human health. Adsorption is a commonly used method for the removal of heavy metal ions as this process possess high efficiency, easy to handle and cost-effective. Iron oxide based nanomaterial were found to be more attractive for the removal of heavy metals from the aqueous solution because of their size, high surface area, and magnetic. Therefore, in this research study, iron oxide nanoparticles modified with tangerine peel extract (T-Fe3O4) and utilized to carry batch adsorption experiments for the rem
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Hassan, Payam B., Rezan O. Rasheed, and Kiomars Zargoosh. "Cadmium and Lead Removal from Aqueous Solution Using Magnetite Nanoparticles Biofabricated from Portulaca oleracea Leaf Extract." Journal of Nanomaterials 2022 (August 16, 2022): 1–18. http://dx.doi.org/10.1155/2022/1024554.

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Magnetic nanoparticles of iron oxide (Fe3O4 NPs) were prepared using a biosynthetic method to investigate their potential use as an adsorbent for adsorption of Pb(II) and Cd(II) from the aqueous solution. The present study for the first time used the magnetite nanoparticles from leaf extract of Portulaca oleracea for the removal of Pb(II) and Cd(II) metal ions. Characterizations for the prepared Fe3O4 NPs (PO-Fe3O4MNPs) were achieved by using X-ray diffraction (XRD), field emission scanning electron microscope (FESEM), energy-dispersive X-ray spectroscopy (EDX), transmittance electron microsco
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Sundaram, R., and K. S. Nagaraja. "Electrical and humidity sensing properties of lead(II) tungstate–tungsten(VI) oxide and zinc(II) tungstate–tungsten(VI) oxide composites." Materials Research Bulletin 39, no. 4-5 (2004): 581–90. http://dx.doi.org/10.1016/j.materresbull.2003.12.014.

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Mbuyazi, Thandi B., and Peter A. Ajibade. "Bis(4-methylpiperidine-1-carbodithioato)-lead(II) and Bis(4-benzylpiperidine-1-carbodithioato)-lead(II) as Precursors for Lead Sulphide Nano Photocatalysts for the Degradation of Rhodamine B." Molecules 26, no. 23 (2021): 7251. http://dx.doi.org/10.3390/molecules26237251.

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Abstract:
Bis(4-methylpiperidine-1-carbodithioato)-lead(II) and bis(4-benzylpiperidine-1-carbodithioato)-lead(II) were prepared and their molecular structures elucidated using single crystal X-ray crystallography and spectroscopic techniques. The compounds were used as precursors for the preparation of lead sulphide nano photocatalysts for the degradation of rhodamine B. The single crystal structures of the lead(II) dithiocarbamate complexes show mononuclear lead(II) compounds in which each lead(II) ion coordinates two dithiocarbamato anions in a distorted tetrahedral geometry. The compounds were thermo
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ALAMRY, KHALID, SHER KHAN, ELHAM BIFARI, and ABDULLAH ASIRI. "CELLULOSE ACETATE/COPPER (II) OXIDE NANOCOMPOSITE FOR SELECTIVE DETECTION AND EXTRACTION OF LEAD (II) IONS." Cellulose Chemistry and Technology 54, no. 5-6 (2020): 591–600. http://dx.doi.org/10.35812/cellulosechemtechnol.2020.54.59.

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48

Han, Runping, Zhu Lu, Weihua Zou, Wang Daotong, Jie Shi, and Yang Jiujun. "Removal of copper(II) and lead(II) from aqueous solution by manganese oxide coated sand." Journal of Hazardous Materials 137, no. 1 (2006): 480–88. http://dx.doi.org/10.1016/j.jhazmat.2006.02.018.

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Han, Runping, Weihua Zou, Zongpei Zhang, Jie Shi, and Jiujun Yang. "Removal of copper(II) and lead(II) from aqueous solution by manganese oxide coated sand." Journal of Hazardous Materials 137, no. 1 (2006): 384–95. http://dx.doi.org/10.1016/j.jhazmat.2006.02.021.

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Akbas, Mehmet A., Michael A. McCoy, and William E. Lee. "Microstructural Evolution during Pressureless Sintering of Lead Lanthanum Zirconate Titanate Ceramics with Excess Lead(II) Oxide." Journal of the American Ceramic Society 78, no. 9 (1995): 2417–24. http://dx.doi.org/10.1111/j.1151-2916.1995.tb08679.x.

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