Research articleVermicompost improves maize, millet and sorghum growth in iron mine tailings
Graphical abstract
Introduction
Mining activity has expanded throughout the world (Oladipo et al., 2016), and consequently, its negative effects on the environment have increased. In countries such as Brazil, accidents with dams have caused severe damage to the environment. Therefore, authorities are worried and are looking for new techniques to mitigate the pollution generated. In addition, many remediation programs for soils contaminated with mine tailings have been costly and inefficient for depollution. At the Aznalcóllar mine (Spain), for example, after 20 years of a remediation program in the mine overflow areas, waste pollution is still present (García-Carmona et al., 2019).
In 2015, the largest accident recorded in the mining history of Brazil, the collapse of the Fundão dam, occurred. The dam was designed to store iron mine tailings in the region of Mariana, state of Minas Gerais, Brazil, for the company Samarco S/A. With the rupture of this dam, there was an overflow of 50 million m3 of tailings, mainly consisting of iron oxide and silica, that left a trail of destruction. The tailings covered an area of 663.2 km and mixed with the soil, causing changes in soil pH, reductions in organic matter content, the leaching of chemical elements, and the addition of metals to the soil, as well as creating a thick crust due to the tailings drying (compaction), thus hindering natural revegetation and plant succession in these areas (Silva et al., 2016).
Soil recovery in environments with mine tailings is complex, and particularly in the case of the Mariana tailings, problems with compaction and heavy metals stand out. Crop species have been considered for use in decontamination processes due to their fast growth and large biomass accumulation (Vamerali et al., 2010). Additionally, many plant species of the Poaceae, Fabaceae and Brassicaceae families have high biomass yields that can compensate for the low concentration absorbed and translocated to tissues, making their performance similar or even better than that of hyperaccumulators (Vamerali et al., 2010). In addition, many of these cultivated plants show a strong increase in metal accumulation when fertilization and organic changes are applied (Sierra Aragón et al., 2019; Vamerali et al., 2010). Therefore, the use of vermicompost is justified in this case.
Regarding the physical changes in the soil generated by the tailings, this process in the soil decreases the number of macropores as a result of the high density, which results in physical resistance to the roots and reduction in aeration and the infiltration of water and nutrients; consequently, there are increases in runoff and erosive processes (Andrade et al., 2018). Fertilizer and organic matter application, as well as the planting of species with a robust root system, are among the alternatives for minimizing the effects of soil compaction.
Vermicompost is an organic amendment with high water retention capacity, porosity and nutrient availability. This compost comes from the interactions between earthworms and beneficial microorganisms for the decomposition of organic matter under vermicomposting techniques (Lazcano and Domínguez, 2011). Furthermore, the constant excretion of vermicompost by earthworm calciferous glands confers greater maturity and stability than other compost materials.
The beneficial effects of vermicompost to plant growth improvement are related to physical, chemical and biological mechanisms. The physical pathway refers to the increase in soil porosity and water retention, promoting rooting and reducing the physical limitations on plant growth caused by soil properties (Góes et al., 2011). The chemical is related to the increased nutrients availability and may affect the mobility and bioavailability of heavy metals (Huang et al., 2016; Sharma and Nagpal, 2018). Finally, the biological pathway refers to the active microbiome, which might produce humic substances and/or increase nutrients availability for plants absorption (Lazcano and Domínguez, 2011).
Species such as maize, millet and sorghum assist in soil decompaction (Calonego et al., 2011; Rivero Herrada et al., 2017) and are part of metal phytoextraction programs with cultivated plants (De Boer et al., 2018; Oladipo et al., 2016; Tavares et al., 2013; Tolentino et al., 2016; Vamerali et al., 2010). There are studies showing the use of maize, millet and sorghum plants for phytoremediation in contaminated areas. The potential of maize for extracting Cu, Zn, Pb and Cd (Xu et al., 2015), millet for extracting Cd and Ni (Asopa et al., 2017; Gupta et al., 2017), and sorghum for extracting Ni, Mn and Cr (Naeini and Rad, 2018; Padmapriya et al., 2016; Serme et al., 2015) have been described. These findings show the potential use of these plant species in the recovery of contaminated areas, and the plants can have alternative uses such as bioenergy generation.
Thus, considering the extent and severity of the disaster, the destruction of agricultural areas and the need for studies on species that can be used for the recovery of this native and agricultural environment, it was hypothesized that the addition of vermicompost to mine tailings improves tailing conditions and, consequently, the development of cultivated plants. For this reason, the objective of this study was to verify the influence of vermicompost on the morpho-physiological characteristics of maize, millet and sorghum cultivated in iron mine tailings.
Section snippets
Experimental conditions
The experiment was carried out in a greenhouse in Alfenas, MG (UTM 402117.38 East, 7627089.90 South), from December 2018 to April 2019. The minimum and maximum temperatures were 18 °C and 30 °C, respectively, and the relative humidity was approximately 78%. The light source was natural light. The experiment was carried out in 6 dm3 plastic pots using three species of field crops: maize DKB 390 (Zea mays L.), millet BRS 1502 (Pennisetum glaucum L.) and sorghum BRS 332 (Sorghum bicolor).
The
Physicochemical characterization of substrates
The vermicompost used in this study (Table 1) showed the presence of cadmium (Cd), chromium (Cr), lead (Pb), copper (Cu), iron (Fe), manganese (Mn), boron (B), zinc (Zn) sulfur (S), calcium (Ca), magnesium (Mg), organic carbon (C), nitrogen (N), potassium (K2O) and phosphorus (P2O5). The pH was alkaline (8.6), and the humidity was 21.4.
Chemical and physical analysis of the mine tailings (Table 2) showed alkaline pH (7.8) and very low magnesium (Mg), aluminum (Al) and organic matter (OM)
Discussion
The analysis of the vermicompost demonstrated the presence of macro- and micronutrients in the material used, as well as the presence of some heavy metals. The quantities of metals are within the tolerable limits for plant substrates in Brazil (300 mg kg−1 of Pb and 500 mg kg−1 of Cr) (MAPA - Ministério da Agricultura Pecuária e Abastecimento, 2016).
Regarding the chemical analysis of the tailings, it was observed that calcium (Ca) and potassium (K) levels and cation exchange capacity (CEC) were
Conclusion
Iron mine tailings showed high levels of Mn, Fe and Cr and high density and pH, which limited the growth, biomass accumulation and physiology of crop plants. The main role of vermicompost when added to iron mine tailings is to promote the growth of thick and very thick roots in crop plants, which is one of the survival strategies of species experiencing physical substrate limitation. The performance of maize plants provides evidence of their higher tolerance to cultivation in iron mine tailings
CRediT authorship contribution statement
Gisele de Fátima Esteves: Investigation, Writing - original draft, Data curation. Kamila Rezende Dázio de Souza: Data curation, Writing - review & editing, Formal analysis. Leticia Aparecida Bressanin: Data curation, Investigation. Paula Cristina Castro Andrade: Data curation. Valdir Veroneze Júnior: Data curation, Visualization. Pedro Ernesto dos Reis: Data curation, Visualization. Adriano Bortolotti da Silva: Methodology, Conceptualization, Resources. José Ricardo Mantovani: Methodology,
Acknowledgements
This paper is dedicated to the researcher Paulo César Magalhães, PhD, Embrapa Milho e Sorgo, Sete Lagoas, MG, Brazil, for the long-term merits of his studies on crop physiology. The authors would like to thank the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES), the Fundação de Amparo à Pesquisa do Estado de Minas Gerais (FAPEMIG), the Fundação de Amparo à Pesquisa e Inovação do Espírito Santo (FAPES), the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
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