Abstract
Purpose
The difference in copper (Cu) availability between soils can be a result of different distribution of Cu forms in various size fractions of aggregates. This study aimed to determine different Cu forms in bulk soils and aggregate size fractions of some heavy metal-contaminated soils from Isfahan Province, Iran and to examine the relationship between Cu forms associated with different soil aggregates and plant indices.
Materials and methods
Bulk soil of five contaminated soils was partitioned into four aggregate size fractions (2.0 to 4.0 mm (large macro-aggregates), 0.25 to 2.0 mm (small macro-aggregates), 0.05 to 0.25 mm (micro-aggregates), and < 0.05 mm (mineral fraction)) by dry sieving. Copper was fractionated into soluble and exchangeable (F1), carbonate-bound (F2), Fe-Mn oxide-bound (F3), and organic-bound (F4) by Tessier’s method. Copper concentration and dry weight of shoots and roots of corn (corn indices) were determined in a pot experiment to assay the Cu availability in the five studied soils. Relationship between the Cu bound to different chemical fractions in different size aggregates and corn indices was assessed using cluster analysis.
Results and discussion
The results showed that the 0.25–2.0-mm fraction, with the highest mass percentage in the soils, had higher contribution to the total content of Cu in the bulk soils. Copper was mainly associated with the organic-bound and residual fractions in the bulk soils and aggregates. Principal component analysis (PCA) represented that the distribution patterns of Cu chemical fractions in different aggregates were strongly related to the soil type. The study of relationship between Cu fractions and the corn indices demonstrated that the organic-bound fraction of Cu in 2.0–4.0 mm aggregates was remarkably correlated with the Cu concentration in corn root and suggested that the organic-bound fraction of Cu in larger aggregates constitutes the chief plant-available Cu pool in the soils.
Conclusions
Soil type and aggregate size distribution were important factors controlling availability and distribution patterns of Cu fractions in studied soils. The organic-bound fraction of Cu in the larger aggregate fractions appeared to be more readily available for plant than in the smaller aggregate fractions. Therefore, soil aggregate size fractionation can be used to assess the distribution, bioavailability, and environmental hazard of Cu in soils.
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References
Acosta JA, Faz A, Kalbitz K, Jansen B, Martinez-Martinez S (2011) Heavy metal concentrations in particle size fractions from street dust of Murcia (Spain) as the basis for risk assessment. J Environ Monitor 13:3087–3096
Arias-Estévez M, Novoa-Munoz JC, Pateiro M, Lopez-Periago E (2007) Influence of aging on copper fractionation in an acid soil. Soil Sci 172:225–232
Bech J (2018) Reclamation and management of polluted soils: options and case studies. J Soils Sediments 18:2131–2135
Chapman HD, Pratt PF (1961) Methods of analysis for soils, plants, and waters. University of California, Riverside, CA
Chatenet B, Marticorena B, Gomes L, Bergametti G (1996) Assessing the actual grain-size distributions of desert soils erodible by wind. Sedimentology 43:901–911
Chen Z, Pawluk S, Juma NG (1998) Impact of variations in granular structures on carbon sequestration in two Alberta Mollisols. In: Lal R et al (eds) Soil processes and the carbon cycle. Adv. Soil Sci. CRC Press, Boca Raton, FL, pp 225–243
Chen JH, He F, Zhang XH, Sun X, Zheng JF, Zheng JW (2014) Heavy metal pollution decreases microbial abundance, diversity and activity within particle-size fractions of a paddy soil. FEMS Microbiol Ecol 87:164–181
Dankoub Z, Khademi H, Ayoubi S (2012) Magnetic susceptibility and its relationship with the concentration of selected heavy metals and soil properties in surface soils of the Isfahan region. J Environ Study 38(63):4–6
Davidson CM, Duncan AL, Littlejohn D, Ure AM, Garden LM (1998) A critical evaluation of the three-stage BCR sequential extraction procedure to assess the potential mobility and toxicity of heavy metals in industrially-contaminated land. Anal Chim Acta 363:45–55
Filgueiras AV, Lavilla I, Bendicho C (2002) Chemical sequential extraction for metal partitioning in environmental solid samples. J Environ Monitor 4:823–857
Gee GW, Bauder JW (1986) Particle size analysis. In: Klute A (ed) Methods of soil analysis. Part 1, 2nd edn. ASA and SSSA, Madison, WI, pp 404–407
Gong C, Ma L, Cheng H, Liu Y, Xu D, Li B, Liu F, Ren Y, Liu Z, Zhao C, Yang K, Nie H, Lang C (2014) Characterization of the particle size fraction associated heavy metals in tropical arable soils from Hainan Island, China. J Geochem Explor 139:109–114
Guo G, Zhang Y, Zhang C, Wang SH, Yan Z, Li F (2013) Partition and characterization of cadmium on different particle size aggregates in Chinese Phaeozem. Geoderma 200:108–113
Huang B, Li Z, Huang J, Guo L, Nie X, Wang Y, Zhang Y, Zeng G (2014) Adsorption characteristics of Cu and Zn onto various size fractions of aggregates from red paddy soil. J Hazard Mater 264:176–183
Kalbits K, Wenrich R (1998) Mobilization of heavy metals and arsenic in polluted wetland soils and its dependence on dissolved organic matter. Sci Total Environ 209:27–39
Li Z, Huang B, Huang J, Chen G, Zhang C, Nie X, Luo N, Yao H, Ma W, Zeng G (2015) Influence of removal of organic matter and iron and manganese oxides on cadmium adsorption by red paddy soil aggregates. RSC Adv 5:90588–90595
Loeppert RH, Suarez DL (1996) Carbonate and gypsum. In: Sparks DL (ed) Methods of soil analysis. Soil Science Society of America Journal, Madison, pp 437–474
Lund LJ, Betty EE, Page AL, Elliott RA (1981) Occurrence of naturally high cadmium levels in soils and its accumulation by vegetation. J Environ Qual 10:551–556
Ma LQ, Rao GN (1997) Chemical fractionation of cadmium, copper, nickel, and zinc in contaminated soils. J Environ Qual 26:259–264
Márquez CO, Garcia VJ, Cambardella CA, Schultz RC, Isenhart TM (2004) Aggregate size-stability distribution and soil stability. Soil Sci Soc Am J 68:725–726
Motaghian HR, Hosseinpur AR (2013) Copper desorption kinetics in wheat (Triticum aestivum L.) rhizosphere in some sewage sludge amended soils. Environ Earth Sci 70:1571–1580
Neu S, Müller I, Brackhage C, Galazka R, Siebielec G, Puschenreiter M, Dudel EG (2018) Trace elements bioavailability to Triticum aestivum and Dendrobaena veneta in a multielement-contaminated agricultural soil amended with drinking water treatment residues. J Soils Sediments 18:2259–2270
Pichler M, Guggenberger G, Hartmann R, Zech W (1996) Polycyclic aromatic hydrocarbons (PAHs) in different forest humus types. Environ Sci Pollut Res 3:24–31
Qian J, Shan XQ, Wang ZJ, Tu Q (1996) Distribution and plant availability of heavy metals in different particle-size fractions of soil. Sci Total Environ 187:131–141
Quenea K, Lamy I, Winterton P, Bermond A, Dumat C (2009) Interactions between metals and soil organic matter in various particle size fractions of soil contaminated with waste water. Geoderma 149:217–223
Sposito GL, Lund J, Chang AC (1982) Trace metal chemistry in arid-zone field soils amended with sewage sludge: I. Fractionation of Ni, Cu, Zn, Cd, and Pb in solid phases. Soil Sci Soc Am J 46:260–265
Sumner ME, Miller PM (1996) Cation exchange capacity and exchange coefficient. In: Sparks DL (ed) Methods of soil analysis. Soil Science Society of America Journal, Madison, pp 1201–1230
Tembo BD, Sichilongo K, Cernak J (2006) Distribution of copper, lead, cadmium and zinc concentrations in soils around Kabwe Town in Zambia. Chemosphere 63:497–501
Tessier A, Campbell PGC, Bisson M (1979) Sequential extraction procedure for the speciation of particulate trace metals. Anal Chem 51:844–851
Venditti D, Durécu S, Berthelin J (2000) A multidisciplinary approach to assess history, environmental risks, and remediation feasibility of soils contaminated by metallurgical activities. Part A: chemical and physical properties of metals and leaching ability. Arch Enviro Con Tox 38(4):411–420
Von Lutzow MV, Kogel-Knabner I, Ekschmitt K, Flessa H, Guggenberger G, Matzner E, Marschner B (2007) SOM fractionation methods: relevance to functional pools and to stabilization mechanisms. Soil Biol Biochem 39:2183–2207
Wu J, Li H, Li F, Zhang Y, Lu H, Zhuang P, Mo Q, Li Z (2016) Distribution and fractionation of cadmium in soil aggregates affected by earthworms (Eisenia fetida) and manure compost. J Soils Sediments 16:2286–2295
Xiao R, Zhang M, Yao X, Ma Z, Yu F, Bai J (2015) Heavy metal distribution in different soil aggregate size classes from restored brackish marsh, oil exploitation zone, and tidal mud flat of the Yellow River Delta. J Soils Sediments 15:1–10
Zhang MK, He ZL, Calvert DV, Stoffella PJ, Yang XE, Li YC (2003) Phosphorus and heavy metal attachment and release in sandy soil aggregate fractions. Soil Sci Soc Am J 67:1158–1167
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This study supported by funds allocated by the Vice President for research of Shahrekord University (Iran).
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Farshadirad, A., Hosseinpur, A. & Motaghian, H. Distribution and availability of copper in aggregate size fractions of some calcareous soils. J Soils Sediments 19, 1866–1874 (2019). https://doi.org/10.1007/s11368-018-2187-9
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DOI: https://doi.org/10.1007/s11368-018-2187-9