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1 r 19-24 days, depending on the origin of the sludge.
2 cal processes such as conventional activated sludge.
3 ita per year or 15 USD per metric ton of dry sludge.
4 he majority becoming entrained in the sewage sludge.
5 sanitation technology and treatment of fecal sludge.
6 measuring SCCPs, MCCPs, and LCCPs in sewage sludge.
7 or obtaining maximum information from sewage sludge.
8 , 15 (30%) cholelithiasis and 3 (6%) biliary sludge.
9 ral organic micropollutants (OMPs) in sewage sludge.
10 that CPs were reported in Australian sewage sludge.
11 f sample preparation on the HRMS analysis of sludge.
12 ed up to 55% of incoming organic matter into sludge.
13 ader, was previously isolated from activated sludge.
14 xygenase gene (amoA) in nitrifying activated sludge.
15 r biological treatment is a major industrial sludge.
16 h three concentrations of the same activated sludge.
17 ewer system largely accumulate in the sewage sludge.
18 in treatment of oil refinery waste activated sludge.
19 raw and potable waters and 52% (SD 13%) for sludge.
20 hat are bound to the organic fraction of the sludge.
21 Cr) with a combined value of US $280/ton of sludge.
22 Barite is the main carrier of Ra-226 in the sludge.
23 row in aggregates like biofilms and granular sludge.
24 sizes were easily biodegradable in activated sludge.
25 on US agricultural soils contained in sewage sludge.
26 phorus rich wastes like municipal wastewater sludge.
27 a control, (2) Ag-NP sludge, and (3) AgNO(3) sludge.
28 r on trees fertilized with dehydrated sewage sludge.
29 ant biotransformation reactions in activated sludge.
30 y for enhanced resource recovery from sewage sludge.
31 ailability differences in soil and activated sludge.
32 sh, diatomaceous earth, and municipal sewage sludge.
33 eactors for 28 d to produce three batches of sludge: (1) a control, (2) Ag-NP sludge, and (3) AgNO(3)
34 samples, while the values for blast furnace sludge (-26.9 +/- 1.5 per thousand), commercial cyanides
35 erences to centralized STTs (e.g., activated sludge, 37%) were more frequent than decentralized STTs
39 rsus dissolved) added to the digested sewage sludge affects the fate of the metals during incineratio
40 imentally determined half-lives in activated sludge against average soil half-lives of the same chemi
43 In this study, intact anaerobic granular sludge (AGS), which is a spherical and dense microbial a
44 e fate of silver nanoparticles (Ag-NPs) in a sludge-amended soil cultivated with monocot (Wheat) and
45 ns: 64% for cucumber and 69% for zucchini in sludge-amended soil, and by 52% for cucumber and 51% for
47 showed that Ag2S was the main species in the sludge and amended soil before and after plant culture.
50 anules >1.0 mm), influent wastewater, excess sludge and effluent of a full-scale AGS plant were chara
51 entrations of 69 elements in digested sewage sludge and effluent samples from 64 municipal wastewater
52 sites from the colloidal mixture of waste Si sludge and graphene oxide (GO) at the same time by ultra
53 aching behavior of Ra-226 in the impoundment sludge and its implications for waste management strateg
54 recovery of aluminum from coagulated primary sludge and its reuse potential as secondary coagulant we
55 biotransformation experiments with activated sludge and mixtures of chemicals to predict soil half-li
57 ding of these components in anammox granular sludge and previously in other nonpathogenic bacteria po
59 limited transport, low deattachment from the sludge and reduced mobility through the column were foun
60 Polyhydroxyalkanoates (PHAs) from activated sludge and renewable organic material can become an alte
61 ol micropollutants in both regular activated sludge and sludge where the protozoa had been inactivate
64 the release of particulate plastic from the sludge, and (ii) the accumulation and mobility of plasti
65 ge environmental matrices (soils, sediments, sludge, and biomass) at sample scales exceeding those us
66 common polymers quantified in raw water and sludge, and polystyrene and acrylonitrile butadiene styr
68 Other phosphorus recovery methods, including sludge application to agricultural land or recovering ph
70 ntified uPFCA and HPFCA homologous series in sludge-applied agricultural soils and fodder grasses for
71 via more realistic exposure pathways (e.g., sludge) are underestimated when extrapolated from studie
73 reveal the potential of mesophilic anaerobic sludges as seed material for sulfur-reducing bioprocesse
76 er 11 WWTPs employing conventional activated sludge (AS) with abundances ranging from 0.02% to 7.0%.
77 were developed from sewage (SEW), activated sludge (AS), soil (SOIL) and sea sediment (SEA) samples.
78 Thermo-chemically treated municipal sewage sludge, as well as diatomaceous earth, did not release s
80 ydrothermal treatment (HT) of PHA-containing sludge at 300 and 375 degrees C was demonstrated to be e
83 d AgNO(3), which were added with the control sludge, at two concentrations (1 and 10 mg Ag kg(-1) dry
84 secondary treatment as off-gas and as solid sludge (averaged 2.08 kg fossil-CO2-emission-potential m
85 analyses revealed that the global activated sludge bacterial communities contain ~1 billion bacteria
86 ntrast to macroorganism diversity, activated sludge bacterial communities show no latitudinal gradien
87 obal diversity and biogeography of activated sludge bacterial communities within a theoretical ecolog
89 s previously observed in an upflow anaerobic sludge bed (UASB) reactor treating source separated blac
90 al colonization into an ecosystem (activated sludge bioreactor) was measured through a disturbance gr
91 carbon-to-nitrogen ratio, C:N) on activated sludge bioreactors, focusing on the stability of nitrifi
94 derived from pastures fertilized with sewage sludge (biosolids): a common global agricultural practic
95 of brilliant red X-3B in an upflow anaerobic sludge blanket (UASB) reactor, and examined the effects
96 six 10 L leach beds and an upflow anaerobic sludge blanket reactor treating the leachate, was operat
97 ing the particle-bound aluminum from primary sludge by acidification (HCl or H2SO4), followed by sepa
102 (WWTPs) by upgrading conventional activated sludge (CAS) to biological nutrient removal (BNR) proces
103 an that of the full-scale domestic activated sludge cohabitating ammonium oxidizing bacteria (AOB) (0
105 ent, suspended particulate matter (SPM), and sludge collected from two WWTPs (denoted as WWTP(A) and
106 anding of the microbial ecology of activated sludge communities by revealing seasonal succession patt
108 nctly different behavior in the noninhibited sludge compared to the inhibited one: (i) more removal f
109 l suitability of seven products (wastewater, sludge, compost, urine, ammonium sulfate, ammonium struv
111 igestion system, the residual SMX and NOR in sludge declined from 10.2 +/- 1.5% to 1.1 +/- 1.2% and f
112 r, biodegradation experiments with activated sludge demonstrated that LMG is resistant to degradation
114 uggest that P speciation and availability in sludge-derived chars are tunable by varying treatment te
117 through the use of three laboratory aerobic sludge digesters, each continuously operated for over 30
118 owever has not been established in anaerobic sludge digestion as well as in bioelectrochemical system
119 n removal from partially nitrified anaerobic sludge digestion liquor through the use of a membrane bi
122 amo, and anammox with methane from anaerobic sludge digestion or a mainstream anaerobic membrane bior
125 characterize anaerobic wastewater treatment sludge enrichments performing DPO coupled to CO2 reducti
126 nto conventional chemical phosphorus removal sludge (FePO4) to achieve FeS precipitation for phosphor
127 f 37), and 54% (20 of 37) revealed a dilated sludge-filled gallbladder, suggestive of bile stasis.
128 tigated anionic polymers in anammox granular sludge, focussing on sialic acids and sulfated glycosami
130 udy shows that the EPS of anaerobic granular sludge form the organic layer present on the BioSeNPs sy
131 n efficiency, this study sampled 35 digester sludge from different reactors at multiple time points t
134 d a PHA polymerase (CapPhaEC) from activated sludge from wastewater treatment that demonstrates a hig
136 grees C could act as a good heat carrier for sludge gasification and the increasing CO2 concentration
137 hods have been commercially limited by toxic sludge generation, incomplete removal, high capital and
140 gh nutrient loading by lowering aeration and sludge handling demands while increasing methane availab
143 nt knowledge on Pb toxicity to the activated sludge has been limited to short-term (</=24 h) toxicity
145 B isolated from wastewater treatment surplus sludge, have a cognate CBM48 domain and are feruloyl est
148 I) were successfully enriched from activated sludge in a sequencing batch reactor by maintaining sust
150 -CoV-2) RNA concentrations in primary sewage sludge in the New Haven, Connecticut, USA, metropolitan
151 nwhile, three strains were isolated from the sludge in the UASB reactors and identified by 16 S rRNA
153 ase genes in Nitrospira lenta from activated sludge, in metagenomes from soils and freshwater habitat
154 s in bioremediation of pivalic acid found in sludge, in stereospecific synthesis of C5 carboxylic aci
155 values as high as 0.8 were found for sewage sludge incinerated at 800 degrees C in a synthetic flue
156 he transformation of Cu and Zn during sewage sludge incineration and evaluate whether the form of Cu
157 Thus, the behavior of Ag-NP during sewage sludge incineration is essential for a comprehensive lif
158 ormation of Ag(0)-NP from Ag2S during sewage sludge incineration, as demonstrated in this study, need
159 ss the transformation of Ag-NP during sewage sludge incineration, we spiked metallic Ag(0)-NP to a pi
160 (ii) micro-organisms from methane-acclimated sludge (including Paracoccus denitrificans) to facilitat
162 nificantly reduce waste volume and transform sludge into valuable products such as pyrochar and hydro
165 y was to evaluate the current need for fecal sludge management (FSM) in LMICs by region, urban/rural
169 ids treated, with a significant reduction of sludge mass (80% reduction of wet sludge volume) and con
172 hese results suggest that soil and activated sludge microbial communities, although certainly differe
173 with global datasets associate the activated sludge microbiomes most closely to freshwater population
174 ferential degradation of (S)-FL in activated sludge microcosms leads to the enrichment of FL with 30x
175 tudied biotransformation of DNAN in soil and sludge microcosms supplemented with uniformly ring-label
177 reduced Gordonia host levels in a wastewater sludge model by approximately 10-fold as compared to non
178 ncy predictions (obtained with the Activated Sludge Model for Xenobiotics (ASM-X)) with representativ
180 s model for denitrification in the activated sludge model, which can easily be integrated in existing
182 At current modeled levels, neither activated sludge nor biofilm systems can achieve complete removal
183 entous bacteria were isolated from activated sludge of a commercial wastewater treatment plan and ide
185 e (III) being acquired from the waste ferric sludge of drinking water treatment process, to enable ma
188 g human and animal waste (e.g., urine, fecal sludge, or grey water) is a critical step in reducing th
190 d with nano-Ag (NM300 K at 1.8 and 7.0 mg/kg sludge per dm soil) and nano-CeO(2) (NM212 at 10 and 50
196 int throughout an energy-intensive activated sludge process with integrated energy recovery facilitie
197 ically treated by the conventional activated sludge process, which suffers from an inefficient overal
199 ter treatment, specifically during activated sludge processing and biofilm systems are reviewed and c
200 noates (PHA) are a key constituent of excess sludge produced by Aerobic Sewage Sludge Treatment plant
204 conversion technology for converting primary sludge (PS) at the anode and producing hydrogen peroxide
205 ferrous oxide and a Ce-rich waste industrial sludge recovered from an optical polishing activity.
206 can also promote electricity production and sludge reduction efficiency of SMFC, as the maximum powe
207 nd safe) of a complex matrix, such as sewage sludge, regarding their impacts on the chemical signatur
209 e limits, thus eliminating the need for iron sludge removal, which is one of the major drawbacks of c
210 e found to accumulate as fragments in sewage sludge, resulting in an estimated accumulation of 24 000
211 chemical composition analysis of impoundment sludge revealed that Barite is the main carrier of Ra-22
212 tive biofilm was developed from an activated sludge sample (inoculum), acetate as electron donor and
216 mal RNA gene sequences from ~1,200 activated sludge samples taken from 269 WWTPs in 23 countries on 6
217 of aging on P species, representative SS and sludge samples were taken from a wastewater treatment pl
220 Microbial communities grown from activated sludge seeds using different dissolved organic matter so
222 o relieve the environmental issues of sewage sludge (SS) disposal and greenhouse gas (GHG) emission i
223 ntea trees fertilized with dehydrated sewage sludge; such a better ecological indices in fertilized t
224 ccur and play an important role in activated sludge systems under both aerobic and anoxic conditions
226 o the aquatic environment, they also produce sludge that requires disposal, similar to reservoir sedi
227 sazurin reduction by nickel spiked anaerobic sludge, the concentration of nickel(II) on anaerobic dig
229 sequently, the potential of anaerobic biogas sludge to hydrolyze the synthetic compostable polyester
230 the conversion from a carbonaceous activated sludge to nitrifying activated sludge treatment process.
231 d ZnSO(4) into anaerobically digested sewage sludge to reach Cu and Zn concentrations of ~2500 and ~3
232 t biotransformation experiments in activated sludge to soil half-lives, which are obtained from much
233 nd Hordeum vulgare, after exposure to sewage sludge treated with nano-Ag (NM300 K at 1.8 and 7.0 mg/k
234 protozoa that are utilized during activated sludge treatment ((R)-FL is 30x more toxic than (S)-FL;
235 that CEPT with anaerobic digestion (AD) for sludge treatment achieves energy self-sufficiency, but i
236 a UV-disinfection plant following activated sludge treatment and studied the fate of these microorga
237 ull-scale as well as reactor-scale activated sludge treatment effectively removes the observed effect
238 lar organic micropollutants during activated sludge treatment is biotransformation, which often leads
244 is study highlights the potential for sewage sludge treatment processes to affect the risk of MP poll
245 d a generic mass balance model for activated sludge treatment to comprehensively detect APIs with rel
246 h for attaining the nitrite pathway based on sludge treatment using free ammonia (FA, i.e., NH3).
247 established by free nitrous acid (FNA)-based sludge treatment was not higher but much lower than that
248 overcome NOB adaptation through alternating sludge treatment with free nitrous acid (FNA) and free a
250 rRNA gene expression of taxa in an activated-sludge-treatment plant (sequencing batch membrane biorea
252 of ~2500 and ~3700 mg/kg and maintained the sludge under mesophilic, anaerobic conditions for 24 h.
253 hydrothermal treatments of municipal sewage sludge using complementary chemical extraction and nucle
254 during sequential HT-AD treatment of sewage sludge using sequential chemical extraction, X-ray diffr
257 l culture occurring in methanogenic granular sludge was able to biocatalyze the reduction of both Te
260 spiked with metal-doped plastic, the excess sludge was dewatered, ensuring realistic associations be
263 ; p < 0.001] were substantially greater, and sludge was evident in the majority of patients (71% vs 0
269 nce the aerobic digestion of waste activated sludge (WAS) in short-time aerobic digestion (STAD) syst
270 Aerobic sludge digestion of waste activated sludge (WAS) is widely used as a stabilization option in
271 % of high-purity silicon (Si) is consumed as sludge waste consisting of Si, silicon carbide (SiC) par
273 mal and necessary component of the activated sludge wastewater treatment process, but the overgrowth
277 CCPs, MCCPs, and LCCPs) in Australian sewage sludge, we applied and further validated a recently deve
278 indicators, SARS-CoV-2 RNA concentrations in sludge were 0-2 d ahead of SARS-CoV-2 positive test resu
280 hat 82% of microbial populations in the feed sludge were digested in comparison with less than 50% ca
283 be largely mitigated if 30% of the returned sludge were returned to the Second Step to reduce its bi
284 locations, precious metal concentrations in sludge were similar to those in profitable mining ores,
285 dy, hepatomegaly, cholelithiasis and biliary sludge were the most common hepatobiliary ultrasound fin
289 each isomer were added separately to sewage sludge which provided the electron-donating substrate an
291 g dw) were detected in the Australian sewage sludge, which were comparable with the LCCPs concentrati
292 ties of P as a response to manure and sewage sludge with a range of P capture and hygienization treat
293 mentation of heat-treated anaerobic digester sludge with Clostridium kluyveri (AS + Ck) on caproic ac
294 lectron shuttles (confirmed by replacing the sludge with humic acids), and (iii) Geobacter sulfurredu
295 ding to results here presented, HT of excess sludge with moderate (13%) PHA content can produce about
296 rococcus faecalis, and fresh mixed anaerobic sludge, with or without 10 mg L(-1) spiked pentachloroph
297 Two of these CE1s, wastewater treatment sludge (wts) Fae1A and wtsFae1B isolated from wastewater
300 tracted from selenite fed anaerobic granular sludge, yielded stable colloidal spherical selenium nano