Risk element sorption/desorption characteristics of dry olive residue: a technique for the potential immobilization of risk elements in contaminated soils
Jazyk angličtina Země Německo Médium print-electronic
Typ dokumentu časopisecké články
PubMed
27557964
DOI
10.1007/s11356-016-7488-1
PII: 10.1007/s11356-016-7488-1
Knihovny.cz E-zdroje
- Klíčová slova
- Dry olive residue, Fungal pretreatment, Risk elements, Sorption,
- MeSH
- adsorpce MeSH
- biotransformace MeSH
- houby metabolismus MeSH
- kadmium chemie metabolismus MeSH
- látky znečišťující půdu chemie metabolismus MeSH
- odpadní produkty analýza MeSH
- Olea chemie metabolismus MeSH
- olovo chemie metabolismus MeSH
- půda chemie MeSH
- půdní mikrobiologie MeSH
- zinek chemie metabolismus MeSH
- Publikační typ
- časopisecké články MeSH
- Geografické názvy
- Středomoří MeSH
- Názvy látek
- kadmium MeSH
- látky znečišťující půdu MeSH
- odpadní produkty MeSH
- olovo MeSH
- půda MeSH
- zinek MeSH
Olive oil production is one of the most relevant agroindustrial activities in the Mediterranean region and generates a huge amount of both solid and semi-solid wastes, the uncontrolled disposal of which might lead to serious environmental problems. Due to its organic matter and mineral nutrient content, the waste material can be applied to agricultural soil as a fertilizer. However, due to its high organic matter content, dry olive residue (DOR), commonly called "alperujo," has the potential to immobilize risk elements in contaminated soils. The main objective of this study was to assess the possible effect of DOR on sorption of risk elements such as cadmium (Cd), lead (Pb), and zinc (Zn) in the soil. A set of batch sorption experiments were carried out to assess the ability of DOR to adsorb Cd, Pb, and Zn where the effect of the preceding biotransformation of DOR by four species of fungi: Penicillium chrysogenum, Coriolopsis floccosa, Bjerkhandera adusta, and Chondrostereum purpureum was compared. The Freundlich and Langmuir sorption isotherms were calculated to assess the sorption characteristics of both transformed and non-transformed DOR. The results showed good potential sorption capacity of DOR, especially for Pb and to a lesser extent for Cd and Zn. Better sorption characteristics were reported for the biotransformed DOR samples, which are expected to show higher humification of the organic matter. However, the desorption experiments showed weakness and instability of the DOR-bound elements, especially in the case of Zn. Thus, future research should aim to verify the DOR sorption pattern in contaminated soil as well as the potential stabilization of the DOR element bounds where the increase of the pH levels of the DOR samples needs to be taken into account.
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