• Journal of Inorganic Materials
  • Vol. 35, Issue 3, 315 (2020)
Xudong DU1, Chengyuan TANG1, Xiaoli YANG2, Jianbo CHENG1, Yuke JIA1, and Shubin YANG1、*
Author Affiliations
  • 1School of Chemistry and Chemical Engineering, Yantai University, Yantai 264005, China
  • 2School of Environmental and Municipal Engineering, North China University of Water Resources and Electric Power, Zhengzhou 450045, China
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    DOI: 10.15541/jim20190349 Cite this Article
    Xudong DU, Chengyuan TANG, Xiaoli YANG, Jianbo CHENG, Yuke JIA, Shubin YANG. High-efficiency Biogenic Calcium Carbonate for Adsorption of Pb(II) and Methyl Orange from Wastewater[J]. Journal of Inorganic Materials, 2020, 35(3): 315 Copy Citation Text show less

    Abstract

    A low-cost oyster shell was carried to prepare biogenic calcium carbonate (bio-CaCO3) to remediate Pb(II) and methyl orange (MO) from contaminated water. The morphology, composition and structure of the material were analyzed mainly by scanning electron microscope (SEM), thermogravimetric analysis (TGA), X-ray fluorescence (XRF). The adsorption of Pb(II) and MO by bio-CaCO3 was studied by combining batch experiments and microstructure characterization. Batch sorption experiments showed that 45% MO was removed by bio-CaCO3 (msorbent/Vsolvent=0.2 g/L, [MO]initial=60 mg/L). An obviously morphology change took place after MO adsorbed onto bio-CaCO3. The maximum sorption capacity of bio-CaCO3 for Pb(II) is 1775 mg/g (pH=5.0, T=298 K), which is higher than that of the traditional nanomaterials such as bentonite and activated carbon. The Pb(II) removal mechanism is expected to be CaCO3+ Pb(II)→PbCO3, where the ΔHθ, ΔSθ and ΔGθ of Pb(II) sorption by bio-CaCO3 (pH=5.0, T=298K) are -7.64 kJ/mol, -17.92 J/(mol·K) and -2.30 kJ/mol, respectively. More regular products with quadrangular structure are formed after Pb(II) adsorption. The results highlight that the bio-CaCO3 has a high Pb(II) and MO sorption efficiency, demonstrating that it is a promising adsorbent material in environmental pollution management.
    $\eta=\frac{C_{0}-C_{e}}{C_{0}}\times100\%$

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    $Q=\frac{(C_{0}-C_{e})V}{m}$

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    $K_{d}=\frac{C_{0}-C_{e}}{C_{e}}·\frac{V}{m}$

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    $lg(q_{e}-q{t})=lgq_{e}-\frac{k_{1}t}{2.303}$

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    $\frac{t}{q_{t}}=\frac{1}{k_{2}q^{2}_{e}}+\frac{t}{q_{e}}$

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    $q_{t}=K_{di}\sqrt{t}+C_{i}$

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    $q_{e}=\frac{q_{m}K_{L}C_{e}}{1+K_{L}C_{e}}$

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    $Q_{e}=K_{F}C^{\frac{1}{n}}_{e}$

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    $lgK^{\theta}_{d}=\Delta S^{\theta}/R-\Delta H^{\theta}/RT$

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    $\Delta G^{\theta}=\Delta H^{\theta}-T\Delta S^{\theta}$

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    Xudong DU, Chengyuan TANG, Xiaoli YANG, Jianbo CHENG, Yuke JIA, Shubin YANG. High-efficiency Biogenic Calcium Carbonate for Adsorption of Pb(II) and Methyl Orange from Wastewater[J]. Journal of Inorganic Materials, 2020, 35(3): 315
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