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dc.contributor.authorPeña, M.es_PE
dc.contributor.authorArana-Maestre, J.es_PE
dc.contributor.authorCruz-Gutierrez, J.es_PE
dc.contributor.editorLarrondo Petrie, M.M.es_PE
dc.contributor.editorTexier, J.es_PE
dc.contributor.editorPena, A.es_PE
dc.contributor.editorViloria, J.A.S.es_PE
dc.date.accessioned2026-02-10T15:50:21Z
dc.date.available2026-02-10T15:50:21Z
dc.date.issued2022
dc.identifier.urihttp://hdl.handle.net/20.500.14074/9576
dc.description.abstractThe present investigation was carried out in the Chonta River, located in the province of Cajamarca, department of Cajamarca-Peru. The work was based on the application of three environmental evaluation techniques that consisted of the determination of heavy metals in sediments, the realization of the Survival Test with Eisenia fetida earthworms and the application of the CERA protocol with macroinvertebrates, with the objective of evaluating the ecological status of the Chonta River in the upper a nd middle parts of the river. To meet this objective, five monitoring stations were established, four control stations (M-1, M-3, M-4, M-5) and one reference station (M-2). In mention, Station M1 sho ws impacts from mining activity. The metals analyzed in sediments were: As, Cd, Pb, Hg, Ni, Zn, Cu and Cr whose results were compared with the threshold values established with the Canadian sediment quality standards TEL values (Canadian ECA). The results obtained were as follows: When analyzed by the three techniques, the stations with the highest degree of contamination were M-1, M-4 and M-5. In addition, the average concentrations of metals in sedim ents during the 4 campaigns obtained were for Zn: 24.084 mg/kg, As: 12.15 mg/kg and Cd: 0.579 mg/kg in M-1. Station M-1 was the station with the highest concentration of almost all the metals analyzed. At this station, As and Cd exceeded the Canadian Standard for sediments in all campaigns. Also Cd was exceeded for the Canadian sediment RCTs at M-1 (first campaign: 0.974 mg/kg a nd fourth campaign: 1.017 mg/kg), M-2 (fourth campaign: 0.847 mg/kg), and M-3 (fourth campaign: 0.959 mg/kg). None of the following metals exceeded RCTs for Canadian sediments Ni, Zn, Cr, Cu, Pb, Hg. On the other hand, the survival test determined that tox ic metals do influence worm growth, the greatest weight loss was recorded at M-1 with -34.9%. Finally, the CERA protocol evaluations showed ecological qualities ranging from very poor in all the campaigns for M-1, M-4 and M-5 to poor for M-3 and fair on average for M-2.es_PE
dc.description.sponsorshipEste trabajo fue financiado por Universidad Privada del Norte, UPN.es_PE
dc.formatapplication/pdfes_PE
dc.language.isospaes_PE
dc.publisherLatin American and Caribbean Consortium of Engineering Institutions.es_PE
dc.relation.ispartofurn:isbn:978-628952070-5es_PE
dc.relation.ispartofhttps://www.scopus.com/pages/publications/85140037452es_PE
dc.relation.ispartofurn:issn:24146390es_PE
dc.rightsinfo:eu-repo/semantics/openAccesses_PE
dc.rights.urihttp://creativecommons.org/licenses/by/4.0/es_PE
dc.subjectcontaminación mineraes_PE
dc.subjectmacroinvertebradoses_PE
dc.subjectsedimentoses_PE
dc.subjectestado ecológicoes_PE
dc.subjecttest de supervivenciaes_PE
dc.subjectprotocolo CERAes_PE
dc.titleECOLOGICAL ASSESSMENT OF THE FLUVIAL ECOSYSTEM OF THE CHONTA RIVER WITH MINING INFLUENCE IN NORTHERN PERU.es_PE
dc.typeinfo:eu-repo/semantics/conferenceObjectes_PE
dc.type.versioninfo:eu-repo/semantics/publishedVersiones_PE
dc.subject.ocdehttps://purl.org/pe-repo/ocde/ford#1.05.08es_PE
dc.identifier.doihttp://dx.doi.org/10.18687/LACCEI2022.1.1.54es_PE


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