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. 2023 Jul 12;9(7):e18191. doi: 10.1016/j.heliyon.2023.e18191

Table 3.

Soil quality and urban planning.

Impacts
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    Accumulation of toxic metal-rich wastes (i.e. tailings) from mining activities in urban and peri-urban areas [70,71].

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    Dispersion of toxic metals from mine tailings without proper safe closure measures [72].

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    Mining accounted for ∼10% of the total GDP in 2018 (over 30% in some regions, up to 53% in the Antofagasta region) [73].

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    Natural and anthropogenic soil enrichment with toxic metals and metalloids [70,74,75].

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    Mine tailings: 85% of 764 tailings in Chile are either inactive or abandoned [76].

Causes
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    Absence of regulations establishing substance concentration threshold values by soil use, as in Canada [77] and Brazil [78].

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    Urban planning legislation does not consider soil quality and health impacts of mine tailings [70].

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    Urban planning legislation does not explicitly consider public exposure to metals in soil risk assessments [79].

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    Local background not defined for the establishment of soil quality guidelines [70]

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    Urban planning legislation is vague in the definition of “risk areas” (i.e. Article N°2.1.17) [66].

Current plans for action
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    Polymetals Health Initiative of the Arica and Parinacota region as a local policy [80].

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    Guide for the management of soils with the potential presence of pollutants [81].

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    New soil bill aiming at protecting and restoring soils. Limiting urban development in contaminated areas is currently being discussed [82].