Salisbury biochar did not affect the mobility or speciation of lead in kaolin in a short-term laboratory study.
Salisbury biochar (produced from British broadleaf hardwood) with two different particle sizes (≤2mm and ≤0.15mm) was applied on a kaolin with three different lead (Pb(2+)) contamination levels (50mg/kg, 300mg/kg and 1000mg/kg) at the dosage of 1% in w/w. The short-term impact of biochar on the mobility and speciation of Pb(2+) in the kaolin was investigated using attenuation periods of 1, 7 and 28 days. The leachability and extractability of Pb(2+) in carbonic acid leaching and EDTA extraction tests as well as the speciation of Pb(2+) in soils were not significantly affected by biochar treatment during all periods. The insignificant effects of biochar on Pb(2+) immobilisation were most likely attributed to the high adsorption capacity of Pb(2+) on the kaolin and biochar failed to competitively adsorb Pb(2+) against kaolin. The kaolin immobilised Pb(2+) primarily through cation exchange, which represents the readily bioavailable fractions of Pb(2+) in soils and may still pose environmental risks. This paper suggests the inefficiency of biochar treament on heavy-metal contaminated clay-rich soils. Therefore a laboratory treatablity study with respect to the soil type may be crucial when large-scale biochar applications in heavy-metal associated soil remediation are evaluated.
['Shen|Zhengtao|Z|', 'McMillan|Oliver|O|', 'Jin|Fei|F|', 'Al-Tabbaa|Abir|A|']
D000327:Adsorption D002412:Cations D002606:Charcoal D004492:Edetic Acid D052918:Environmental Restoration and Remediation D006863:Hydrogen-Ion Concentration D007616:Kaolin D007854:Lead D008670:Metals D019216:Metals, Heavy D012987:Soil D012989:Soil Pollutants
Biochar Speciation Lead Kaolin Immobilise