Bioavailability of Soil Copper from Different Sources: Integrating Chemical Approaches with Biological Indicators
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Cited by (10)
Contrasting effects of siderophores pyoverdine and desferrioxamine B on the mobility of iron, aluminum, and copper in Cu-contaminated soils
2022, GeodermaCitation Excerpt :Copper contamination is particularly high in old vineyards (Komarek et al., 2010; Mackie et al., 2012) and in old orchards (Zhou et al., 2011; Wang et al., 2015) where the concentration of Cu in the topsoil (0–20 cm) can reach several hundred mg kg−1 soil. Soil Cu contamination in vineyard and orchard soils, although moderate compared to that of Cu-polluted soils located near Cu mines (Zotti et al., 2014), Cu smelting factories (Wang et al., 2014) or at wood preservation sites (Kolbas et al., 2020), has consequences for the functioning and the sustainability of these ecosystems since it has chronic effects on the dynamics of soil populations. Karimi et al. (2021) performed a meta-analysis of Cu ecotoxicity and reported that Cu harms soil microorganisms at concentrations above 200 kg Cu ha−1 (Cu of 67 mg kg−1 soil), which is currently the level found in many vineyard and orchard topsoils.
Copper accumulation in agricultural soils: Risks for the food chain and soil microbial populations
2020, Science of the Total EnvironmentCitation Excerpt :Moreover, we must take into account the plant uptake regulation of an essential nutrient such as copper (Chaignon et al., 2003) and the release of the removed elements from the soil solid constituents to the soil solution (Maderova et al., 2011; Wang et al., 2014). The integration of chemical methods with biological assays in the evaluation of bioavailability can be useful to assess consequences for the environment of metal-contaminated soils (Wang et al., 2014). In a survey conducted in the plain area of the Campania region (southern Italy), surrounding the site where the experiments presented in this paper were performed, no significant correlations were found between the Cu content in the edible parts of crops (maximum value: 11.4 mg kg−1 f.w.) and total (maximum value: 570 mg kg−1 d.w.) or bioavailable (maximum value: 13.8 mg kg−1 d.w.) Cu soil content (Agrelli et al., 2017).
Temporal variability in Cu speciation, phytotoxicity, and soil microbial activity of Cu-polluted soils as affected by elevated temperature
2018, ChemosphereCitation Excerpt :JH-Soil, GX-Soil, and RZ-Soil represented the three main anthropogenic scorces for soil Cu pollution, namely mining tails, mineral smelting, and agricultural practices of Cu-containing pesticides, respectively. The pollution history of these soils was detailed in Wang et al. (2014), and the sampling positions for JH-Soil and GX-Soil were 32°04ʹ N, 119°05ʹ E and 28°20ʹ N, 117°14ʹ E, respectively. According to China Soil Classification System, JH-Soil, GX-Soil, and RZ-Soil were yellow-brown soil, red soil, and brown soil, respectively, and were further categorized as Stagnic Anthrosols, Udic Ferrosols, and Udic Luvisols based on the Universal Soil Classification System, respectively.
Contamination of urban soils in a historical mining town of northern Chile
2024, Environmental Earth SciencesEvaluation of Atrichum undulatum as an effective indicator of lead pollution in soil
2021, Journal of Environmental Biology
Supported by the National Natural Science Foundation of China (No. 41101305).