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1 roductive coastal waters are correlated with methanotrophic activity and biomass.
2 hese compounds indicate episodes of vigorous methanotrophic activity in methane-laden water masses.
3  Overall, this study shows the importance of methanotrophic activity near the water table to attenuat
4 ne observed in the chamber are attributed to methanotrophic activity, which was highest in the capill
5 on of methylocystabactin is widespread among methanotrophic alphaproteobacteria and that it can be us
6 ophic methanogenesis may have evolved from a methanotrophic ancestor.
7 axonomic distribution of HpnR extends beyond methanotrophic and acetic acid bacteria.
8 pose that these sea spiders farm and feed on methanotrophic and methylotrophic bacteria, expanding th
9 philaceae, suggesting an interaction between methanotrophic and methylotrophic microorganisms that al
10                                 For example, methanotrophic and nitrogen-fixing bacteria may benefit
11 er genes specific to methanogenic, anaerobic methanotrophic and short-chain alkane-oxidizing archaea,
12 longing to potential methanogenic, anaerobic methanotrophic and short-chain alkane-oxidizing archaea.
13 by tight linkages between methane-utilizing (methanotrophic) and nonmethanotrophic bacteria.
14 g a syntrophic partnership between anaerobic methanotrophic (ANME) archaea and sulfate-reducing bacte
15                                    Anaerobic methanotrophic (ANME) archaea obtain energy from the bre
16                                    Anaerobic methanotrophic archaea (ANME) and sulfate-reducing bacte
17  carbon isolated from consortia of anaerobic methanotrophic archaea (ANME) and sulfate-reducing bacte
18                  We show that both anaerobic methanotrophic archaea (ANME) and sulphate-reducing bact
19 2 biosynthesis was present in both anaerobic methanotrophic archaea (ANME) and sulphate-reducing bact
20                                    Anaerobic methanotrophic archaea (ANME) consume methane in marine
21 rmed by multicellular consortia of anaerobic methanotrophic archaea (ANME) in obligate syntrophic par
22 erobic oxidation of CH(4) (AOM) by anaerobic methanotrophic archaea (ANME) of ANME-2d, which proposes
23 cesses leading to the evolution of anaerobic methanotrophic archaea (ANME) remain unclear.
24 rocess is mediated by consortia of anaerobic methanotrophic archaea (ANME) that live in syntrophy wit
25 ted group of microorganisms called anaerobic methanotrophic archaea (ANME).
26 creased abundance of aggregates of anaerobic methanotrophic archaea (ANME-2) and sulfate-reducing bac
27            Yet only one association, between methanotrophic archaea and sulphate-reducing bacteria, h
28 rge multi-haem cytochromes in the genomes of methanotrophic archaea and the demonstration of redox-de
29 h likely competed for nitrate with anaerobic methanotrophic archaea and the gammaproteobacterial MBAE
30 c oxidation of methane to CO(2) in anaerobic methanotrophic archaea and the oxidation of short-chain
31 llaneous Crenarchaeotal Group, whereas known methanotrophic Archaea are not detectable.
32  comprised exclusively of putative anaerobic methanotrophic archaea of which ANME-1 was the sole arch
33                             Methanogenic and methanotrophic archaea play important roles in the globa
34                             Methanogenic and methanotrophic archaea produce and consume the greenhous
35 lative sequence abundance of ANME (anaerobic methanotrophic archaea), as well as aerobic Methylococca
36 found in strictly anaerobic methanogenic and methanotrophic archaea, catalyzes the reversible product
37 naerobic oxidation of methane to methanol by methanotrophic archaea.
38 is potent greenhouse gas in methanogenic and methanotrophic archaea.
39 t to anaerobic methane oxidation observed in methanotrophic archaea.
40                           In nature, aerobic methanotrophic bacteria and anaerobic archaea are able t
41 s a small copper-binding peptide produced by methanotrophic bacteria and is intimately involved in bo
42 the soluble methane oxidation complex of the methanotrophic bacteria and the aromatic hydroxylation c
43 in living foraminifera occurs via feeding on methanotrophic bacteria and/or incorporation of ambient
44                 It is generally assumed that methanotrophic bacteria are mostly active at the oxic-an
45           Copper is critically important for methanotrophic bacteria because their primary metabolic
46 of methane monooxygenase (MMO) isolated from methanotrophic bacteria catalyzes the O2-dependent conve
47 cave-adapted shrimp suggest that carbon from methanotrophic bacteria comprises 21% of their diet, on
48 f potential biotechnological applications of methanotrophic bacteria has not been comprehensively dis
49 on discharge, was consumed quantitatively by methanotrophic bacteria in Gulf of Mexico deep waters ov
50                                              Methanotrophic bacteria oxidize methane to methanol in t
51                                   In nature, methanotrophic bacteria perform this reaction under ambi
52                                              Methanotrophic bacteria play a key role in limiting meth
53                                              Methanotrophic bacteria represent a potential route to m
54 d Methylomicrobium albus BG8, two species of methanotrophic bacteria that are of interest for monitor
55 odified peptide natural products released by methanotrophic bacteria under conditions of copper scarc
56                                              Methanotrophic bacteria use methane, a potent greenhouse
57 acile conversion of methane into methanol in methanotrophic bacteria with high efficiency under ambie
58 tify novel emulsifier peptides from seaweed, methanotrophic bacteria, and potatoes.
59 pare salmon feeds based on protein from soy, methanotrophic bacteria, and yeast ingredients.
60 ntings harbored significantly greater plant, methanotrophic bacteria, arthropod, and bird diversity t
61 take of (13)C into fatty acids indicative of methanotrophic bacteria, associated with increasing copy
62  Biofiltration, whereby CH(4) is oxidized by methanotrophic bacteria, is a potentially effective stra
63 genase (MMO) systems have been identified in methanotrophic bacteria, namely, a soluble or cytoplasmi
64 pendent conversion of methane to methanol in methanotrophic bacteria, thereby preventing the atmosphe
65 hat in the soluble methane monooxygenases of methanotrophic bacteria, to which AMO exhibits a signifi
66 ange and is primarily regulated in Nature by methanotrophic bacteria, which consume methane gas as th
67 ered the abundance of methanogens along with methanotrophic bacteria, which may have reduced CH4 cycl
68 ature, and is an enzyme complex expressed by methanotrophic bacteria.
69  first enzyme in the C1 metabolic pathway in methanotrophic bacteria.
70 ions and without significant intervention of methanotrophic bacteria.
71 yzes the oxidation of methane to methanol in methanotrophic bacteria.
72 oenzyme that oxidizes methane to methanol in methanotrophic bacteria.
73 oenzyme that converts methane to methanol in methanotrophic bacteria.
74 sed during thaw and subsequently consumed by methanotrophic bacteria.
75  suggesting that Cu-Mb uptake is specific to methanotrophic bacteria.
76 nd a residual microbial community containing methanotrophic bacteria.
77 lyze the oxidation of methane to methanol in methanotrophic bacteria.
78 rst step in the primary catabolic pathway of methanotrophic bacteria.
79 er, the first step of carbon assimilation in methanotrophic bacteria.
80 s are methane monooxygenases (MMOs) found in methanotrophic bacteria; however, these enzymes are not
81 s work opens the door to develop an array of methanotrophic bacterial strain-engineering strategies c
82  Delta(14)-sterol reductase (MaSR1) from the methanotrophic bacterium Methylomicrobium alcaliphilum 2
83  recent identification of a novel, tractable methanotrophic bacterium, Methylomicrobium buryatense, w
84                             Our discovery of methanotrophic biofilms in sediment pockets closely asso
85 e effects of sulfide stress on the anaerobic methanotrophic biofilter have not been well explored.
86       Here, we show that the linkage between methanotrophic carbon cycling and N2 fixation may consti
87           Here, we surveyed methanogenic and methanotrophic communities associated with floating Micr
88  this mud volcano system has shaped distinct methanotrophic communities due to availability of electr
89 tudy, we investigated vertical variations in methanotrophic communities in sediments of the mud volca
90 ents, and molecular diversity surveys reveal methanotrophic communities within protolithic nodules an
91 olic functioning of these globally important methanotrophic consortia.
92                                      Using a methanotrophic enrichment culture incubated under differ
93            Here, we demonstrate that type II methanotrophic enrichments can mediate step two by coupl
94 otrophs than the other seven lakes, with the methanotrophic genera Methyloparacoccus, Crenothrix, and
95 communities and of specific methanogenic and methanotrophic guilds.
96                      These data indicate the methanotrophic-mediated production of MB can significant
97 MC09 is a mesophilic, halotolerant, aerobic, methanotrophic member of the Gammaproteobacteria, isolat
98 ceae and Methanosaetaceae, with co-occurring methanotrophic Methanoperedenaceae and Methylomirabilace
99 eir raw water and very high abundance of the methanotrophic Methylococcaceae.
100 e formation in the energy saving pathways of methanotrophic microbes.
101  knowledge gap regarding this inconsistency, methanotrophic microbiomes were enriched from paddy soil
102                                              Methanotrophic microorganisms in methane seeps use metha
103 ernatively, CH(4) oxidation (consumption) by methanotrophic microorganisms may attenuate emissions.
104                 We enriched and cultivated a methanotrophic Mycobacterium from an extremely acidic bi
105  structure of active methanotrophs and their methanotrophic pathways revealed by DNA-SIP metagenomics
106 r, this recent work only focused on a type I methanotrophic pMMO, while previous observations of the
107 n kinetics in soil infer the activity of two methanotrophic populations: one that is only active at h
108 nal wall biofilms showed the highest initial methanotrophic potential under oxic conditions compared
109 ty alpha diversity, may influence a sample's methanotrophic potential, but these factors did not demo
110 izing microbial communities with substantial methanotrophic potential.
111 o a lack of cultured representative deep-sea methanotrophic prokaryotes.
112 re detected in all of the methylotrophic and methanotrophic proteobacteria tested that assimilate for
113     During prolonged incubations the maximum methanotrophic rate increased to 8.08 mmol g(DW) (-1) d(
114 an are likely to be met by a similarly rapid methanotrophic response.
115     This study provides new understanding of methanotrophic responses to methane starvation and recov
116 y microbial community composition may affect methanotrophic responses to potential large-scale seaflo
117            We report here that some existing methanotrophic strains grow well at 500 ppm methane, and

 
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