Research Article
Removal of Lead (II) Ions from Aqueous Solutions onto Activated Carbon Derived from Waste Biomass
Table 4
Comparison of adsorption capacities of activated carbons obtained from various lignocellulosic materials for lead (II) ions.
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Biomass |
pH | (K) | Operating conditions | Initial concentration or range (mg L−1) | Amount of adsorbent (g L−1) | Adsorption capacity (mg g−1) |
| Apricot stone [7] | 6.5 | 298.15 | — | 2.0 | 22.85 | Soybean hulls [3] | 5.0 | 296.15 | 518 | 10.0 | 39.37 | Pecan shell [8] | 4.8 | — | 104 | 0.5–10.0 | 64.2 | Coconut shell [9] | 5.6 | 298.15 | — | 2.0 | 76.66 | Palm shell [10] | 3.0 and 5.0 | 300.15 | 100–700 | 5.0 | 95.20 | Sawdust [11] | 5.0 | 300.15 | 50–1000 | 2.0 | 200.00 | Bagasse pith [12] | 4.0–8.0 | 303.15 | 100 | — | 200.00 | Coir pith waste [13] | 4.0 | — | 25–100 | — | 263.00 | Euphorbia rigida [14] | 5.0 | 313.15 | 50–200 | 0.8 | 279.72 | Soybean oil cake* | 5.5 | 298.15 | 50–500 | 0.5 | 476.2 |
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Present study.
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