Oladele A. Oluwayiose, Karolina Nowak, Emily Houle, Alexander Suvorov, J.Richard Pilsner
{"title":"邻苯二甲酸盐暴露于成年小鼠可改变尾状附睾小体中的非编码rna","authors":"Oladele A. Oluwayiose, Karolina Nowak, Emily Houle, Alexander Suvorov, J.Richard Pilsner","doi":"10.1016/j.envpol.2025.127227","DOIUrl":null,"url":null,"abstract":"We have previously reported associations between urinary biomarkers of anti-androgenic phthalates and small non-coding RNA (sncRNA) compositions of extracellular vesicles (EVs) in seminal plasma of men undergoing fertility treatment. To complement these findings, we assessed sncRNAs of cauda epididymosomes in mice after exposure to the anti-androgenic phthalates, Di-n-butyl phthalate (DBP), Di(2-ethylhexyl) phthalate (DEHP), and their mixture.Male mice were exposed to 2.5 mg/kg/day of DBP or DEHP and their mixture (2.5 mg/kg/day each of DBP and DEHP) for six weeks. Cauda epididymosomal RNA were isolated and subjected to sequencing to assess their non-coding RNA (ncRNA) content. Mapping of reads to transcriptomes and differential expression of normalized read counts were conducted using counts between the exposed groups relative to controls using STAR alignment tool and EdgeR (Fold change, FC ≥ 1.5 and p < 0.01), respectively.The mapped reads of epididymosomal ncRNAs were mostly piRNAs (47%), followed by tRFs (34%) and miRNAs (6%). Phthalate exposures altered a total of 79 (DBP = 47; DEHP = 11; mixture = 21) epididymosomal sncRNA biotypes (miRNA = 14, tRFs = 5 & piRNA = 60). These ncRNAs were predicted to target genes involved in various functional processes, including tissue development, olfactory perception, and potassium channel activity.This is the first study, to our knowledge, to show that exposure to phthalates in adult male mice disrupts the ncRNA profiles of cauda epididymosomes. These data suggest that cauda epididymosomes ncRNAs are responsive to environmental exposures and may have implication in the health and development of the next generation.","PeriodicalId":311,"journal":{"name":"Environmental Pollution","volume":"66 1","pages":""},"PeriodicalIF":7.3000,"publicationDate":"2025-10-10","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Phthalate exposure to adult mice alters non-coding RNAs in cauda epididymosomes\",\"authors\":\"Oladele A. Oluwayiose, Karolina Nowak, Emily Houle, Alexander Suvorov, J.Richard Pilsner\",\"doi\":\"10.1016/j.envpol.2025.127227\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"We have previously reported associations between urinary biomarkers of anti-androgenic phthalates and small non-coding RNA (sncRNA) compositions of extracellular vesicles (EVs) in seminal plasma of men undergoing fertility treatment. To complement these findings, we assessed sncRNAs of cauda epididymosomes in mice after exposure to the anti-androgenic phthalates, Di-n-butyl phthalate (DBP), Di(2-ethylhexyl) phthalate (DEHP), and their mixture.Male mice were exposed to 2.5 mg/kg/day of DBP or DEHP and their mixture (2.5 mg/kg/day each of DBP and DEHP) for six weeks. Cauda epididymosomal RNA were isolated and subjected to sequencing to assess their non-coding RNA (ncRNA) content. Mapping of reads to transcriptomes and differential expression of normalized read counts were conducted using counts between the exposed groups relative to controls using STAR alignment tool and EdgeR (Fold change, FC ≥ 1.5 and p < 0.01), respectively.The mapped reads of epididymosomal ncRNAs were mostly piRNAs (47%), followed by tRFs (34%) and miRNAs (6%). Phthalate exposures altered a total of 79 (DBP = 47; DEHP = 11; mixture = 21) epididymosomal sncRNA biotypes (miRNA = 14, tRFs = 5 & piRNA = 60). These ncRNAs were predicted to target genes involved in various functional processes, including tissue development, olfactory perception, and potassium channel activity.This is the first study, to our knowledge, to show that exposure to phthalates in adult male mice disrupts the ncRNA profiles of cauda epididymosomes. 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Phthalate exposure to adult mice alters non-coding RNAs in cauda epididymosomes
We have previously reported associations between urinary biomarkers of anti-androgenic phthalates and small non-coding RNA (sncRNA) compositions of extracellular vesicles (EVs) in seminal plasma of men undergoing fertility treatment. To complement these findings, we assessed sncRNAs of cauda epididymosomes in mice after exposure to the anti-androgenic phthalates, Di-n-butyl phthalate (DBP), Di(2-ethylhexyl) phthalate (DEHP), and their mixture.Male mice were exposed to 2.5 mg/kg/day of DBP or DEHP and their mixture (2.5 mg/kg/day each of DBP and DEHP) for six weeks. Cauda epididymosomal RNA were isolated and subjected to sequencing to assess their non-coding RNA (ncRNA) content. Mapping of reads to transcriptomes and differential expression of normalized read counts were conducted using counts between the exposed groups relative to controls using STAR alignment tool and EdgeR (Fold change, FC ≥ 1.5 and p < 0.01), respectively.The mapped reads of epididymosomal ncRNAs were mostly piRNAs (47%), followed by tRFs (34%) and miRNAs (6%). Phthalate exposures altered a total of 79 (DBP = 47; DEHP = 11; mixture = 21) epididymosomal sncRNA biotypes (miRNA = 14, tRFs = 5 & piRNA = 60). These ncRNAs were predicted to target genes involved in various functional processes, including tissue development, olfactory perception, and potassium channel activity.This is the first study, to our knowledge, to show that exposure to phthalates in adult male mice disrupts the ncRNA profiles of cauda epididymosomes. These data suggest that cauda epididymosomes ncRNAs are responsive to environmental exposures and may have implication in the health and development of the next generation.
期刊介绍:
Environmental Pollution is an international peer-reviewed journal that publishes high-quality research papers and review articles covering all aspects of environmental pollution and its impacts on ecosystems and human health.
Subject areas include, but are not limited to:
• Sources and occurrences of pollutants that are clearly defined and measured in environmental compartments, food and food-related items, and human bodies;
• Interlinks between contaminant exposure and biological, ecological, and human health effects, including those of climate change;
• Contaminants of emerging concerns (including but not limited to antibiotic resistant microorganisms or genes, microplastics/nanoplastics, electronic wastes, light, and noise) and/or their biological, ecological, or human health effects;
• Laboratory and field studies on the remediation/mitigation of environmental pollution via new techniques and with clear links to biological, ecological, or human health effects;
• Modeling of pollution processes, patterns, or trends that is of clear environmental and/or human health interest;
• New techniques that measure and examine environmental occurrences, transport, behavior, and effects of pollutants within the environment or the laboratory, provided that they can be clearly used to address problems within regional or global environmental compartments.