ENAapplication/xmlftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/076/SRR25304776/SRR25304776.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/072/SRR25304772/SRR25304772.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/079/SRR25304779/SRR25304779.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/080/SRR25304780/SRR25304780.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/077/SRR25304777/SRR25304777.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/078/SRR25304778/SRR25304778.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/074/SRR25304774/SRR25304774.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/075/SRR25304775/SRR25304775.fastq.gzftp://ftp.sra.ebi.ac.uk/vol1/fastq/SRR253/073/SRR25304773/SRR25304773.fastq.gzprimaryOK200Genomicsnortheastern universityhttps://www.ebi.ac.uk/ena/browser/view/PRJNA995376More than 80% TN removal from OSW was achieved at a COD/N of 3.TN removal load increased by 53.3% with COD/N ratio dropping from 8 to 3The abundance of aerobic denitrifying bacteria reached 42.48% and dominatedThe functional gene napA of aerobic denitrification increased by 73.6%ENAfalseEnhancement strategies of aerobic denitrification for high-rate nitrogen removal from low COD/N oil shale wastewater2023-07-182023-07-18PRJNA995376