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1 f low DO on the nitrification performance of activated sludge.
2 metabolites formed during biodegradation in activated sludge.
3 eactor with mixed liquor from a conventional activated sludge.
4 reactor with mixed liquor from a nitrifying activated sludge.
5 terial community encountered in conventional activated sludge.
6 d plant pathogens to degradative capacity of activated sludge.
7 ibute to pharmaceutical biotransformation in activated sludge.
8 level differences in resistance gene fate in activated sludge.
9 STP (treating 4000 m(3)/day) operating with activated sludge.
10 mA and mfmB) found in isolated bacteria from activated sludge.
11 urface agitation and fine bubble aeration of activated sludge.
12 ated bioavailability differences in soil and activated sludge.
13 energy and had lower life cycle impacts than activated sludge.
14 ng biological processes such as conventional activated sludge.
15 actors with three concentrations of the same activated sludge.
16 rozil-degrader, was previously isolated from activated sludge.
17 onia monooxygenase gene (amoA) in nitrifying activated sludge.
18 digestion in treatment of oil refinery waste activated sludge.
19 icropollutant biotransformation reactions in activated sludge.
20 t TEA-soy sizes were easily biodegradable in activated sludge.
23 nity proteomics has thus far been applied to activated sludge, acid mine drainage biofilms, freshwate
24 the experimentally determined half-lives in activated sludge against average soil half-lives of the
25 h the DNA viral communities in the influent, activated sludge, anaerobic digester, and effluent of a
27 mpounds dosed at 1-2 mg C per L into diluted activated sludge and freshwater lake communities at star
29 efficient biotransformation experiments with activated sludge and mixtures of chemicals to predict so
31 ight control micropollutants in both regular activated sludge and sludge where the protozoa had been
32 was undertaken in 7 WWTPs (utilizing mainly activated sludge and trickling filters technologies) and
33 n of a parallel sewer based (SB) system with activated sludge, and a fecal sludge management (FSM) sy
34 d metatranscriptomic analyses of raw sewage, activated sludge, and effluent samples from WWTPs across
37 tment using freeze-dried, heat-treated (FDH) activated sludge (AS) has been recently proposed for pre
40 municipal wastewater treatment plant (WWTP) activated sludge (AS) processes can occur through biodeg
41 f the largest biotechnological applications, activated sludge (AS) systems in wastewater treatment pl
42 in the other 11 WWTPs employing conventional activated sludge (AS) with abundances ranging from 0.02%
43 ading BACs were developed from sewage (SEW), activated sludge (AS), soil (SOIL) and sea sediment (SEA
44 eering strategies for their out-selection in activated sludge (AS), which is desirable to promote ene
45 study emphasized the potential of nitrifying activated sludge bacteria for breaking down an environme
46 tabolites, which were produced by nitrifying activated sludge bacteria in a small-scale laboratory ba
49 of the global diversity and biogeography of activated sludge bacterial communities within a theoreti
50 obium sp. BiD32 was previously isolated from activated sludge based on its ability to degrade BPA.
52 nd DRO biotransformation with representative activated sludge batch incubations and identified releva
53 and paper mill (PPM) effluent, (13)C-labeled activated sludge biomass (ASB) and phytoplankton (PHY) w
55 of bacterial colonization into an ecosystem (activated sludge bioreactor) was measured through a dist
56 of these MAGs, however, were detected in the activated sludge bioreactors or anaerobic digesters.
57 in the untreated wastewaster compared to the activated sludge bioreactors or the anaerobic digesters
58 enomes (MAGs) from the untreated wastewater, activated sludge bioreactors, and anaerobic digesters fr
59 , F:M, and carbon-to-nitrogen ratio, C:N) on activated sludge bioreactors, focusing on the stability
62 s(-1)) in the IFAS reactors compared to the activated sludge, by the end of the treatment the EfOM c
65 he influent and effluent of the conventional activated sludge (CAS) process at a WWTP over 14 consecu
66 er microbial communities within conventional activated sludge (CAS) systems can perform hundreds of b
67 ent plants (WWTPs) by upgrading conventional activated sludge (CAS) to biological nutrient removal (B
68 ilot sized biological reactors (conventional activated sludge, CAS; nitrifying activated sludge, NAS;
69 y-biological processes covering Complete-Mix Activated Sludge (CMAS), oxidation ditch, and trickling
70 t lower than that of the full-scale domestic activated sludge cohabitating ammonium oxidizing bacteri
71 atory behavior in six AGS size fractions and activated sludge collected from full-scale municipal was
73 oxidation products previously reported from activated sludge communities and concluded that in the p
74 onjugative transfer of the RP4 plasmid among activated sludge communities at environmentally relevant
75 ic understanding of the microbial ecology of activated sludge communities by revealing seasonal succe
76 nhanced biological phosphorus removal (EBPR) activated sludge communities located across North Americ
81 0.9 days for 5-methyl-1H-benzotriazole with activated sludge confirmed their known partial persisten
82 However, biodegradation experiments with activated sludge demonstrated that LMG is resistant to d
83 acterial community composition differed from activated sludge, demonstrating that laboratory enrichme
84 linked to higher Epistylis abundance, while activated sludge, dominated by Vorticella, resembled sma
85 staining methods were applied to a municipal activated sludge during pilot scale PHA accumulation in
86 ation applications in soil, groundwater, and activated sludge environments, exhibiting enhanced degra
89 of our technique on a new project analyzing activated sludge from a lab-scale bioreactor seeded by a
90 ays during individual batch experiments with activated sludge from a pilot-scale facility treating mu
91 (DiOHCBZ), was investigated in contact with activated sludge from a wastewater treatment plant (WWTP
92 (PHAs) can be produced with municipal waste activated sludge from biological wastewater treatment pr
93 to obtain a comprehensive P mass-balance of activated sludge from four enhanced biological phosphate
97 identified a PHA polymerase (CapPhaEC) from activated sludge from wastewater treatment that demonstr
98 riptomic data obtained from experiments with activated sludge grown at different solid retention time
100 Current knowledge on Pb toxicity to the activated sludge has been limited to short-term (</=24 h
101 ession in a full-scale integrated fixed film activated sludge (IFAS) municipal wastewater treatment f
102 l activated sludge and integrated fixed-film activated sludge (IFAS) processes was performed in this
103 zation of a full-scale integrated fixed film activated sludge (IFAS) system where comammox and anammo
104 a lineage I) were successfully enriched from activated sludge in a sequencing batch reactor by mainta
106 imilar urease genes in Nitrospira lenta from activated sludge, in metagenomes from soils and freshwat
107 ong-term low DO enriched both AOB and NOB in activated sludge, increasing the sludge nitrification ca
108 stantial toxicity was observed in either the activated sludge inhibition test or the seedling germina
109 Photogranules were batch-cultivated with the activated sludge inoculum under three photosynthetic pho
110 actor to maximize PHA content when municipal activated sludge is directly used for PHA accumulation.
112 acterium wenxiniae LQY-18(T) , isolated from activated sludge, is resistant to trivalent MAs(III) and
114 each specific environmental matrix (compost, activated sludge, marine environments, etc.) that can us
117 pective, these results suggest that soil and activated sludge microbial communities, although certain
121 -analyses with global datasets associate the activated sludge microbiomes most closely to freshwater
122 nce as preferential degradation of (S)-FL in activated sludge microcosms leads to the enrichment of F
123 ed directly using the Microbial Database for Activated Sludge (MiDAS) and indirectly by predicting co
124 were calculated for 1 month operation of the activated sludge model (ASM) in a Lab-scale in three ser
125 al efficiency predictions (obtained with the Activated Sludge Model for Xenobiotics (ASM-X)) with rep
127 use of this model for denitrification in the activated sludge model, which can easily be integrated i
128 on through electron competition is proposed [Activated Sludge Model-Electron Competition (ASM-EC)].
130 nventional activated sludge, CAS; nitrifying activated sludge, NAS; and biological nutrient removal,
133 ated filamentous bacteria were isolated from activated sludge of a commercial wastewater treatment pl
135 as soils or sediments from experiments with activated sludge outperformed three widely used in silic
137 ilter plant and 3.95 and 3.73 mg N/L for the activated sludge plant, indicating that photodegradation
141 h were exposed directly to either secondary (activated sludge process (ASP)), tertiary (sand filtrate
143 were compared to the full-scale conventional activated sludge process established at the same site.
144 rickling filter/solids contact process to an activated sludge process on the removal of endocrine-dis
145 bon footprint throughout an energy-intensive activated sludge process with integrated energy recovery
146 ources (municipal wastewater influent to the activated sludge process, centrate from the sludge dryin
148 ter is typically treated by the conventional activated sludge process, which suffers from an ineffici
151 biokinetic coefficients in the complete-mix activated sludge processes were calculated for 1 month o
152 tate meaningful insights for advancements of activated sludge processes where systematic observations
153 in wastewater treatment, specifically during activated sludge processing and biofilm systems are revi
155 attained biomass PHA content with different activated sludge ranged from 0.18 to 0.42 gPHA/gVSS, and
156 o simultaneously extract clean water from an activated sludge reactor for nonpotable (or environmenta
157 in WWTPs, experiments with laboratory-scale activated sludge reactors and pristine and citrate-funct
159 electroactive biofilm was developed from an activated sludge sample (inoculum), acetate as electron
160 we analyze the antibiotic resistomes of 226 activated sludge samples from 142 WWTPs across six conti
162 16S ribosomal RNA gene sequences from ~1,200 activated sludge samples taken from 269 WWTPs in 23 coun
163 ation products of the reference compounds in activated sludge samples were consistent with the report
166 enolol and MDMA), treatment technology used (activated sludge showed higher stereoselectivity than tr
167 n was relatively constant and independent of activated sludge source, with an average value of 0.58 +
171 atment plant biomass, lab-scale conventional activated sludge systems (CAS) were continuously fed wit
172 d (3 times lower footprint than conventional activated sludge systems because of neglecting the secon
174 t removal of polar, ionizable organic MPs in activated sludge systems is less likely an effect of pH-
175 rated to occur and play an important role in activated sludge systems under both aerobic and anoxic c
178 s examined in aerobic batch experiments with activated sludge taken from the nitrification zone of a
179 ion from five other sensors installed in the activated sludge tank: NH(4)(+), pH, ORP, DO, and TSS.
181 he FO stream, water is drawn by osmosis from activated sludge through an FO membrane into a draw solu
183 ulation assays were performed with different activated sludge to determine (1) the maximum biomass PH
184 included the conversion from a carbonaceous activated sludge to nitrifying activated sludge treatmen
185 y efficient biotransformation experiments in activated sludge to soil half-lives, which are obtained
186 ermophila, protozoa that are utilized during activated sludge treatment ((R)-FL is 30x more toxic tha
187 ocessed by a UV-disinfection plant following activated sludge treatment and studied the fate of these
188 Removal of micropollutants (MPs) during activated sludge treatment can mainly be attributed to b
190 ess for polar organic micropollutants during activated sludge treatment is biotransformation, which o
195 perties and a generic mass balance model for activated sludge treatment to comprehensively detect API
199 rDNA) and rRNA gene expression of taxa in an activated-sludge-treatment plant (sequencing batch membr
200 roduced water holding; however, conventional activated sludge treatments are intolerant of high salin
201 ctivities and the enzymatic expression of an activated sludge under aerobic heterotrophic conditions.
207 cally enhance the aerobic digestion of waste activated sludge (WAS) in short-time aerobic digestion (
211 N) in final effluent of trickling filter and activated sludge wastewater treatment plants (WWTPs) was
212 are a normal and necessary component of the activated sludge wastewater treatment process, but the o
214 anaerobic digestion (HRAS+AD), conventional activated sludge with anaerobic digestion (CAS+AD), and
215 cycle environmental emissions than high rate activated sludge with anaerobic digestion (HRAS+AD), con
218 entralised systems, especially decentralized activated sludge WWTPs; and (v) N(2)O may be mitigated b