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Presence and leaching of PAHs in soils of high Andean grasslands affected by intentional burning

dc.contributor.authorVega Quispe, Anyela Pierina
dc.contributor.authorMerma Chacca, Donald Efrain
dc.contributor.authorColque Ayma, Elvis Jack
dc.contributor.authorGuimarães Guilherme, Luiz Roberto
dc.contributor.authorJiménez Jiménez, Paúl Andrés
dc.contributor.authorRivera Campano, Milko Raúl
dc.contributor.authorZirena Vilca, Franz
dc.contributor.authorMaldonado, Ingrid
dc.contributor.authorRamos Tejeda, José Luis
dc.date.accessioned2024-10-02T15:30:24Z
dc.date.available2024-10-02T15:30:24Z
dc.date.issued2024-05-21
dc.description.abstractShepherds intentionally burn certain high Andean grasslands to stimulate the regrowth of grass. Nevertheless, this practice results in the generation of Polycyclic Aromatic Hydrocarbons (PAHs), which contaminate and can leach into the soil and be absorbed by plants. Ultimately, this adversely affects the livestock graze on these contaminated plants. The objective of this study was to evaluate the presence of 15 PAHs at the surface, 10, 20, and 30 cm depth, immediately and three months after burning natural grasses in Somoa, Carumas-Peru, during the year 2021. UHPLC-FLD determined PAHs, and the QuEChERS method was used to extract the PAHs from soil samples. Twelve of the 15 PAHs listed by the USEPA were found. The highest concentration was found at the surface, followed by the 10, 20, and 30 cm (759,63, 157,99, 85,86, and 68,04 ng g−1, respectively). On the other hand, Acenaphthene presented higher leaching concerning the rest of the compounds, showing 1.80 ng g−1 at 0 cm, 3.86 ng g−1 at 10 cm, 3.70 ng g−1 at 20c, and 3.44 ng g−1 at 30 cm of depth. The ∑12PAHs at the surface at T1 (first collection after burning) were 669.74 ng g−1, and T2 (second collection, three months after burning) was 759.63 ng g−1; that indicates these soils are contaminated with mean values between 600 and 1000 ng g−1. Additionally, according to the Canadian soil criteria, Fluoranthene slightly exceeded the established limits (157.99 ng g−1).
dc.formatapplication/pdf
dc.identifier.doihttps://doi.org/10.1016/j.enmm.2024.100915
dc.identifier.urihttps://hdl.handle.net/20.500.14655/581
dc.language.isoeng
dc.publisherElsevier
dc.publisher.countryUS
dc.relation.ispartofurn:issn:2215-1532
dc.relation.urihttps://doi.org/10.1016/j.enmm.2024.100915
dc.rightshttps://purl.org/coar/access_right/c_abf2
dc.rights.urihttps://creativecommons.org/licenses/by-nc-nd/4.0/
dc.subjectAndean grasslands burning.en
dc.subjectOctanol–water partition coefficient (Kow).en
dc.subjectPolycyclic aromatic hydrocarbons (PAHs); QuEChERS; UHPLCen
dc.subject.ocdehttps://purl.org/pe-repo/ocde/ford#2.00.00
dc.titlePresence and leaching of PAHs in soils of high Andean grasslands affected by intentional burning
dc.typehttp://purl.org/coar/resource_type/c_6501
dc.type.versionhttp://purl.org/coar/version/c_970fb48d4fbd8a85

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