Amendment Type and Dose Effects onto Coexisting Copper, Lead, and Nickel Ions Distribution in Soil
Nema prikaza
Autori
Šljivić-Ivanović, Marija Z.Smičiklas, Ivana D.
Jović, Mihajlo D.
Dimović, Slavko
Onjia, Antonije E.
Članak u časopisu (Objavljena verzija)
,
© 2018, Springer Nature Switzerland AG
Metapodaci
Prikaz svih podataka o dokumentuApstrakt
The use of soil additives for toxic metals chemical stabilization aims to decrease in situ the pollutants’ mobility and availability. In this study, the effectiveness of rinsed red mud (RBRM) and annealed animal bones (B400) was compared in terms of Cu, Pb and Ni stabilization in two contaminated soils with contrasting properties Dystric Cambisol (CM dy) and Rendzic Leptosol (LP rz). The mobility of metals in unamended soil samples (control) and samples amended with 1% and 5% of selected additives were compared using sequential extraction protocol. The relative content of metals in readily and potentially available fractions was higher in CM dy (62% Pb, 13% Cu, and 31% Ni in exchangeable fraction) than in LP rz (< 5% of Pb, Cu, Ni in exchangeable fraction). In CM dy, both additives have caused a decrease in metal mobility with an increase of their doses. The effect of 5% sorbent addition was most pronounced related to Pb immobilization, provoking decrease of exchangeable Pb content to ...< 10%. Furthermore, B400 addition has redistributed investigated metals from the exchangeable to the residual phase more effectively than RBRM, and its effect on metal mobility decreased in the order Pb > Cu > Ni. Amending of LP rz soil had limited effects with no apparent decrease in exchangeable metal content. The effects of soil type variation, the type of additive and the additive dose onto metal mobility were compared according to ANOVA results. The content of readily and potentially available forms of metals was found to be (i) significantly correlated with all investigated variables for Pb, (ii) significantly correlated with soil type for Cu, and (iii) not in significant correlation with selected variables for Ni. Complex impacts of soil properties and treatment conditions on the mobility of co-contaminants emphasize the need for an individual approach to each case of contamination. © 2018, Springer Nature Switzerland AG.
Ključne reči:
Soil remediation / Toxic metals / Mobility / Waste valorization / Soil additives / Sequential extractionIzvor:
Water, Air, and Soil Pollution, 2018, 229, 10, 339-
DOI: 10.1007/s11270-018-3981-0
ISSN: 0049-6979; 1573-2932
WoS: 000446522400002
Scopus: 2-s2.0-85054484144
URI
http://link.springer.com/10.1007/s11270-018-3981-0https://vinar.vin.bg.ac.rs/handle/123456789/7903
Institucija/grupa
VinčaTY - JOUR AU - Šljivić-Ivanović, Marija Z. AU - Smičiklas, Ivana D. AU - Jović, Mihajlo D. AU - Dimović, Slavko AU - Onjia, Antonije E. PY - 2018 UR - http://link.springer.com/10.1007/s11270-018-3981-0 UR - https://vinar.vin.bg.ac.rs/handle/123456789/7903 AB - The use of soil additives for toxic metals chemical stabilization aims to decrease in situ the pollutants’ mobility and availability. In this study, the effectiveness of rinsed red mud (RBRM) and annealed animal bones (B400) was compared in terms of Cu, Pb and Ni stabilization in two contaminated soils with contrasting properties Dystric Cambisol (CM dy) and Rendzic Leptosol (LP rz). The mobility of metals in unamended soil samples (control) and samples amended with 1% and 5% of selected additives were compared using sequential extraction protocol. The relative content of metals in readily and potentially available fractions was higher in CM dy (62% Pb, 13% Cu, and 31% Ni in exchangeable fraction) than in LP rz (< 5% of Pb, Cu, Ni in exchangeable fraction). In CM dy, both additives have caused a decrease in metal mobility with an increase of their doses. The effect of 5% sorbent addition was most pronounced related to Pb immobilization, provoking decrease of exchangeable Pb content to < 10%. Furthermore, B400 addition has redistributed investigated metals from the exchangeable to the residual phase more effectively than RBRM, and its effect on metal mobility decreased in the order Pb > Cu > Ni. Amending of LP rz soil had limited effects with no apparent decrease in exchangeable metal content. The effects of soil type variation, the type of additive and the additive dose onto metal mobility were compared according to ANOVA results. The content of readily and potentially available forms of metals was found to be (i) significantly correlated with all investigated variables for Pb, (ii) significantly correlated with soil type for Cu, and (iii) not in significant correlation with selected variables for Ni. Complex impacts of soil properties and treatment conditions on the mobility of co-contaminants emphasize the need for an individual approach to each case of contamination. © 2018, Springer Nature Switzerland AG. T2 - Water, Air, and Soil Pollution T1 - Amendment Type and Dose Effects onto Coexisting Copper, Lead, and Nickel Ions Distribution in Soil VL - 229 IS - 10 SP - 339 DO - 10.1007/s11270-018-3981-0 ER -
@article{ author = "Šljivić-Ivanović, Marija Z. and Smičiklas, Ivana D. and Jović, Mihajlo D. and Dimović, Slavko and Onjia, Antonije E.", year = "2018", abstract = "The use of soil additives for toxic metals chemical stabilization aims to decrease in situ the pollutants’ mobility and availability. In this study, the effectiveness of rinsed red mud (RBRM) and annealed animal bones (B400) was compared in terms of Cu, Pb and Ni stabilization in two contaminated soils with contrasting properties Dystric Cambisol (CM dy) and Rendzic Leptosol (LP rz). The mobility of metals in unamended soil samples (control) and samples amended with 1% and 5% of selected additives were compared using sequential extraction protocol. The relative content of metals in readily and potentially available fractions was higher in CM dy (62% Pb, 13% Cu, and 31% Ni in exchangeable fraction) than in LP rz (< 5% of Pb, Cu, Ni in exchangeable fraction). In CM dy, both additives have caused a decrease in metal mobility with an increase of their doses. The effect of 5% sorbent addition was most pronounced related to Pb immobilization, provoking decrease of exchangeable Pb content to < 10%. Furthermore, B400 addition has redistributed investigated metals from the exchangeable to the residual phase more effectively than RBRM, and its effect on metal mobility decreased in the order Pb > Cu > Ni. Amending of LP rz soil had limited effects with no apparent decrease in exchangeable metal content. The effects of soil type variation, the type of additive and the additive dose onto metal mobility were compared according to ANOVA results. The content of readily and potentially available forms of metals was found to be (i) significantly correlated with all investigated variables for Pb, (ii) significantly correlated with soil type for Cu, and (iii) not in significant correlation with selected variables for Ni. Complex impacts of soil properties and treatment conditions on the mobility of co-contaminants emphasize the need for an individual approach to each case of contamination. © 2018, Springer Nature Switzerland AG.", journal = "Water, Air, and Soil Pollution", title = "Amendment Type and Dose Effects onto Coexisting Copper, Lead, and Nickel Ions Distribution in Soil", volume = "229", number = "10", pages = "339", doi = "10.1007/s11270-018-3981-0" }
Šljivić-Ivanović, M. Z., Smičiklas, I. D., Jović, M. D., Dimović, S.,& Onjia, A. E.. (2018). Amendment Type and Dose Effects onto Coexisting Copper, Lead, and Nickel Ions Distribution in Soil. in Water, Air, and Soil Pollution, 229(10), 339. https://doi.org/10.1007/s11270-018-3981-0
Šljivić-Ivanović MZ, Smičiklas ID, Jović MD, Dimović S, Onjia AE. Amendment Type and Dose Effects onto Coexisting Copper, Lead, and Nickel Ions Distribution in Soil. in Water, Air, and Soil Pollution. 2018;229(10):339. doi:10.1007/s11270-018-3981-0 .
Šljivić-Ivanović, Marija Z., Smičiklas, Ivana D., Jović, Mihajlo D., Dimović, Slavko, Onjia, Antonije E., "Amendment Type and Dose Effects onto Coexisting Copper, Lead, and Nickel Ions Distribution in Soil" in Water, Air, and Soil Pollution, 229, no. 10 (2018):339, https://doi.org/10.1007/s11270-018-3981-0 . .