2018
DOI: 10.1016/j.chemosphere.2017.10.067
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Response of ammonia oxidizing archaea and bacteria to decabromodiphenyl ether and copper contamination in river sediments

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Cited by 32 publications
(5 citation statements)
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“…191 Concentration dependent inhibitory effects of deca-BDE (1000−100 000 ng/g dry soil/sediment) on nitrification by ammonia oxidizing bacteria (AOB; that is, Nitrosospira, Nitrosomonas) and archaea (AOA; that is, Nitrosopumilus, Nitrosophaera) have been consistently reported in sediment and soil microbiomes. 198−200 Additionally, deca-BDE and copper exhibit synergic inhibition of nitrification, 200 which is noteworthy as cocontamination of heavy metals and deca-BDE is common in wastewater. 101,204 Exposure to TCEP and TCPP were also shown to decrease ammonia removal in a constructed wetland treating wastewater.…”
Section: Effects Of Hfrs On Biological Treatment Systemsmentioning
confidence: 99%
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“…191 Concentration dependent inhibitory effects of deca-BDE (1000−100 000 ng/g dry soil/sediment) on nitrification by ammonia oxidizing bacteria (AOB; that is, Nitrosospira, Nitrosomonas) and archaea (AOA; that is, Nitrosopumilus, Nitrosophaera) have been consistently reported in sediment and soil microbiomes. 198−200 Additionally, deca-BDE and copper exhibit synergic inhibition of nitrification, 200 which is noteworthy as cocontamination of heavy metals and deca-BDE is common in wastewater. 101,204 Exposure to TCEP and TCPP were also shown to decrease ammonia removal in a constructed wetland treating wastewater.…”
Section: Effects Of Hfrs On Biological Treatment Systemsmentioning
confidence: 99%
“…The effects of some HFRs (e.g., TBBPA, PBDEs, and DBDPE) on microbiomes are well documented and can be categorized based on their effects on (i) the entire microbial community, where exposure to HFRs can alter microbial composition (usually decreasing microbial diversity) and interactions of the microbiome via environmental filtering; ,, (ii) individual microbial cells, where the integrity and function of cell membrane can be compromised by accumulation of these lipophilic pollutants, which directly affects cell viability; ,,, (iii) enzymatic activity and, therefore, activity of metabolic pathways can be altered by HFRs. , The ultimate effects of HFRs and related transformation products depend on a combination of these effects. Because there are few studies investigating the direct effects of HFRs on biological wastewater treatment systems and sludge anaerobic digesters, this review discusses demonstrated and putative effects of HFRs on biological nitrogen removal (i.e., nitrification, denitrification, and anaerobic ammonia oxidation) and methanogenesis by integrating the available information from both biological treatment systems ,,, and other environmental matrices. , …”
Section: Effects Of Hfrs On Biological Treatment Systemsmentioning
confidence: 99%
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“…Firstly, NO 3 − generation through nitrification may have been inhibited. Wang et al [55] showed that ammonia monooxygenase enzyme activity in river sediments decreased by ca. 25% and 59% under Cu concentrations of 50 and 100 mg −1 , respectively, after 60 days of incubation, with similar changes in amoA gene abundance (ca.…”
Section: Cycling Of Nitrogen Species Under Increasing Copper Concentr...mentioning
confidence: 99%
“…Physiochemical factors can influence the abundance and diversity of AOA and AOB microbes in several vital processes, including river N cycling ecosystems (Jiang et al, 2016;Wang et al, 2018). For instance, oxygen availability (Gleeson et al, 2010), phosphorus (Herfort et al, 2007), sulfide (Burgin et al, 2012), pH (Li et al, 2015a), soil type (Huang et al, 2011), NH + 4 -N, and NO 3 -N (Li et al, 2012) have been classified as significant parameters that affect the distribution and diversity of ammonia-oxidizing communities in different ecosystems (Behrendt et al, 2017).…”
Section: Introductionmentioning
confidence: 99%