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dc.contributor.authorHerrera Loaiza, Natalia Andrea-
dc.contributor.authorRobledo Restrepo, Sara María-
dc.contributor.authorOrtiz Trujillo, Isabel Cristina-
dc.contributor.authorEcheverri López, Luis Fernando-
dc.contributor.authorHerrera Mazo, Carolina-
dc.contributor.authorOrozco Jiménez, Luz Yaneth-
dc.contributor.authorAgudelo Echavarría, Diana María-
dc.date.accessioned2024-11-05T20:30:44Z-
dc.date.available2024-11-05T20:30:44Z-
dc.date.issued2018-
dc.identifier.citationHerrera N, Herrera C, Ortíz I, Orozco L, Robledo S, Agudelo D, Echeverri F. Genotoxicity and cytotoxicity of three microcystin-LR containing cyanobacterial samples from Antioquia, Colombia. Toxicon. 2018 Nov;154:50-59. doi: 10.1016/j.toxicon.2018.09.011.spa
dc.identifier.issn0041-0101-
dc.identifier.urihttps://hdl.handle.net/10495/43184-
dc.description.abstractABSTRACT: The presence of cyanobacterial blooms and cyanotoxins in water presents a global problem due to the deterioration of ecosystems and the possibility of poisoning in human and animals. Microcystin LR is the most widely distributed cyanotoxin and liver cells are its main target. In the present study, HepG2 cells were used to determine DNA damage of three crude extracts of cyanobacterial blooms containing MC-LR, through comet assay. The results show that all extracts at a concentration of 500 μg mL−1 caused low damage in hepatocytes exposed for 24 h, but produced total mortality even at low concentrations at 48 h. Moreover, balloons corresponding to cell apoptosis were found. Through HPLC/MS, MC-LR was detected in all samples of cyanobacterial blooms at concentrations of (5,65 μg ml−1) in sample 1, (1,24 μg ml−1) in sample 2 and (57,29 μg ml−1) in sample 3. In addition, in all samples high molecular weights peaks were detected, that may correspond to other microcystins. Besides, the cytotoxic effect of a cyanobacterial bloom and some of its chromatographic fractions from the crude extracts were evaluated in U-937, J774, Hela and Vero cell lines, using the enzymatic micromethod (MTT). The highest toxicity was detected in U-937 cells (LC50 = 29.7 μg mL−1) and Vero cells (LC50 = 39.7 μg mL-1). Based on these results, it is important to remark that genotoxic and cytotoxicity assays are valuable methods to predict potential biological risks in waters contaminated with blooms of cyanobacteria, since chemical analysis can only describe the presence of cyanotoxins, but not their biological effects.spa
dc.format.extent10 páginasspa
dc.format.mimetypeapplication/pdfspa
dc.language.isoengspa
dc.publisherElsevierspa
dc.type.hasversioninfo:eu-repo/semantics/publishedVersionspa
dc.rightsinfo:eu-repo/semantics/openAccessspa
dc.rights.urihttp://creativecommons.org/licenses/by-nc-nd/2.5/co/*
dc.titleGenotoxicity and cytotoxicity of three microcystin-LR containing cyanobacterial samples from Antioquia, Colombiaspa
dc.typeinfo:eu-repo/semantics/articlespa
dc.publisher.groupGrupo de Investigación en Gestión y Modelación Ambiental (GAIA)spa
dc.publisher.groupPrograma de Estudio y Control de Enfermedades Tropicales (PECET)spa
dc.publisher.groupQuímica Orgánica de Productos Naturalesspa
dc.identifier.doi10.1016/j.toxicon.2018.09.011-
oaire.versionhttp://purl.org/coar/version/c_970fb48d4fbd8a85spa
dc.rights.accessrightshttp://purl.org/coar/access_right/c_abf2spa
dc.identifier.eissn1879-3150-
oaire.citationtitleToxiconspa
oaire.citationstartpage50spa
oaire.citationendpage59spa
oaire.citationvolume154spa
dc.rights.creativecommonshttps://creativecommons.org/licenses/by-nc-nd/4.0/spa
oaire.fundernameColombia. Ministerio de Ciencia, Tecnología e Innovación - MinCienciasspa
oaire.fundernameEmpresas Públicas de Medellín (Colombia)spa
dc.publisher.placeOxford, Inglaterraspa
dc.type.coarhttp://purl.org/coar/resource_type/c_2df8fbb1spa
dc.type.redcolhttps://purl.org/redcol/resource_type/ARTspa
dc.type.localArtículo de investigaciónspa
dc.subject.decsCianobacterias-
dc.subject.decsCyanobacteria-
dc.subject.decsCompuestos de Bencilo-
dc.subject.decsBenzyl Compounds-
dc.subject.decsCélulas Cultivadas-
dc.subject.decsCells, Cultured-
dc.subject.decsChlorocebus aethiops-
dc.subject.decsColombia-
dc.subject.decsEnsayo Cometa-
dc.subject.decsDaño del ADN-
dc.subject.decsDNA Damage-
dc.subject.decsMonitoreo del Ambiente-
dc.subject.decsEnvironmental Monitoring-
dc.subject.decsCélulas Hep G2-
dc.subject.decsHep G2 Cells-
dc.subject.decsToxinas Marinas-
dc.subject.decsMarine Toxins-
dc.subject.decsMicrocistinas-
dc.subject.decsMicrocystins-
dc.subject.decsPruebas de Mutagenicidad - métodos-
dc.subject.decsMutagenicity Tests - methods-
dc.subject.decsPirazinas-
dc.subject.decsPyrazines-
dc.subject.decsCélulas U937-
dc.subject.decsU937 Cells-
dc.subject.decsCélulas Vero-
dc.subject.decsVero Cells-
dc.subject.agrovocGenotoxicidad-
dc.subject.agrovocGenotoxicity-
dc.subject.agrovocurihttp://aims.fao.org/aos/agrovoc/c_36150-
dc.description.researchgroupidCOL0015099spa
dc.description.researchgroupidCOL0009832spa
dc.description.researchgroupidCOL0015339spa
oaire.awardnumberMinCiencias FP44842-049-2016spa
oaire.awardnumberEPM 29990832845spa
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D000458-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D001593-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D002478-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D002522-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D003105-
dc.subject.meshuriComet Assay-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D020552-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D004249-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D004784-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D056945-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D008387-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D052998-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D009152-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D011719-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D020298-
dc.subject.meshurihttps://id.nlm.nih.gov/mesh/D014709-
dc.relation.ispartofjournalabbrevToxiconspa
oaire.funderidentifier.rorRoR:03fd5ne08-
oaire.funderidentifier.rorRoR:0532s7j62-
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