ライフサイエンスコーパス: microcosm

1 ing regimes (fully, moderately, and nonmixed microcosms).

2 gradation was faster in the columns than the microcosms.

3 ns) exhibited biphasic decay patterns in all microcosms.

4 ocosms yielded the same product as in the BL microcosms.

5 rmation in microbially active and sterilized microcosms.

6 mation product of MON was identified in soil microcosms.

7 ve dehalogenation in methanogenic laboratory microcosms.

8 tributed significantly in BL-fertilized soil microcosms.

9 as slower in the oleate and EVO than ethanol microcosms.

10 order of magnitude greater than that in the microcosms.

11 ding materials were determined in laboratory microcosms.

12 crobeloides maximus when recovered from soil microcosms.

13 outh Louisiana crude oil (SLC) in laboratory microcosms.

14 VP) coated Ag nanoparticles (NPs) in aquatic microcosms.

15 pattern of persistence seen in the original microcosms.

16 s (EC(50) approximately 30%) in the nonmixed microcosms.

17 rameters determined in experimental seawater microcosms.

18 ult in proliferation of AR in irrigated soil microcosms.

19 our beetle Tribolium castaneum in laboratory microcosms.

20 crocosms and least consistent for raw runoff microcosms.

21 he specialists when propagated in laboratory microcosms.

22 or-prey (rotifer-algal) cycles in laboratory microcosms.

23 integrons in wastewater solids-amended soil microcosms.

24 se, and inorganic nitrogen (N) leaching from microcosms.

25 rs and the soil pore structure in plant-soil microcosms.

26 on dynamics disappeared in the High-variance microcosms.

27 ed in several ecotoxicological studies using microcosms.

28 less variable in High- than Normal-variance microcosms.

29 (Avena fatua) over two seasons in greenhouse microcosms.

30 e been demonstrated in simplified laboratory microcosms.

31 e sequenced from duplicate bloom and control microcosms 1 day after a phytoplankton biomass peak, and

32 obtained for the Dehalogenimonas-containing microcosms (1.89 +/- 0.02) and very different from those

33 per thousand) and Dehalogenimonas-containing microcosms (-23 +/- 2 per thousand and -12.0 +/- 0.8 per

34 In anoxic microcosms, 300 mug/L cis- and 150 mug/L trans-4-MCHM de

35 ns of fungal-colonized mineral surfaces from microcosms after careful removal of the organism and bio

36 After 2 h of exposure in experimental microcosms, AgNP and AgNO3 inhibited respiration and pho

37 mL(-1) achieved complete DCM degradation in microcosms amended with 10 mM bicarbonate.

38 In microcosms amended with alginate particles and the profi

39 the fate of the compounds in soil and medium microcosms amended with an aqueous film-forming foam (AF

40 Microcosm and column experiments were conducted utilizin

41 We present evidence from four independent microcosm and field experiments demonstrating that CO(2)

42 between the AMF and the PSB by conducting a microcosm and two Petri plate experiments.

43 ties of soil-entrapped N2O and N2 in biochar microcosms and a biochar-induced increase in typical and

44 The microcosms and enrichment cultures also reduced sulfate,

45 Rates of Sb(V) reduction in anoxic sediment microcosms and enrichment cultures were enhanced by amen

46 In both laboratory microcosms and field mesocosms, MeHg concentrations in k

47 redox conditions using sediment-groundwater microcosms and flow-through columns.

48 was observed in nitrate- and sulfate-amended microcosms and in microcosms established to promote meth

49 the plant pathogen Ralstonia solanacearum in microcosms and in tomato plant rhizosphere.

50 , bromodeoxyuridine (BrdU), was added to the microcosms and incorporated into the DNA of actively rep

51 cates, most consistent for compost-augmented microcosms and least consistent for raw runoff microcosm

52 carpio) eDNA was evaluated using lake water microcosms and quantitative PCR for a Common Carp-specif

53 hlorobenzene and benzene was observed in the microcosms and was further confirmed by shifts in the ca

54 were grown from dental plaque inoculum (oral microcosms) and were obtained from six systemically heal

55 ealed extensive cellulose degradation in one microcosm, and Fibrobacter spp. and Clostridium cluster

56 RNA transcripts dominated the HMWDOM-amended microcosm, and included gene transcripts associated with

57 e degradation was not observed in the second microcosm, and this correlated with negligible relative

58 perfluoroalkyl chains was determined in soil microcosms, and biotransformation pathways were proposed

59 aneously to the sediment and water column of microcosms, and Hg species were monitored in amphipods a

60 e take-all pathogen in abstract experimental microcosms, and show that increased bacterial genotypic

61 aeal and bacterial ammonia oxidation in soil microcosms, and specifically inhibited AOB growth, activ

62 We used a microcosm approach to examine the single and combined ef

63 We used a soil microcosm approach to expose A. maximus populations grow

64 identification were performed on a sediment microcosm approach.

65 rey oscillations in rotifer-algal laboratory microcosms are qualitatively altered by the presence of

66 Sequence analysis of etnE genes from the microcosms as well phylogenetic typing of the isolates s

67 t experimental methods (trenching, girdling, microcosms), as well as considering different temporal a

68 vestigated IPA biodegradation in BL and soil microcosms, as a process affecting the fate of IPAs in t

69 Amendments were tested in four separate microcosm assays using Hg-contaminated sediments from tw

70 Microcosm assays with (14)C-labeled dioxane showed that

71 from experimentally manipulated multitrophic microcosm assemblages, demonstrate that bacterial social

72 Water samples taken from the microcosms at 24 h postdosing were used in acute toxicit

73 Cell-free supernatants obtained from microcosms at 24 hours, 180 days, and 700 days all showe

74 MON was stable in BL microcosms at 24-72% water content (water/wet litter, w/

75 observed in the case of the moderately mixed microcosms at 333 gal acre(-1) and was maintained at mod

76 experiments were conducted in respirometric microcosms at an oil loading of 333 gal acre(-1) (0.31 L

77 No toxicity was detected in all biotic microcosms at the end of the incubation period, while hi

78 led the artificial intelligence problem in a microcosm because learning algorithms must act autonomou

79 ts on dentin bond strength and dental plaque microcosm biofilms for the first time.

80 um disks were contaminated with multispecies microcosm biofilms grown from in vivo peri-implant plaqu

81 eDNA was found to be distributed throughout microcosm biofilms, and was particularly abundant in the

82 Human saliva was collected to grow microcosm biofilms.

83 els of BrdU incorporation in the PUT and SPD microcosms, but not in the CTRs.

84 uantities of ARGs and intI1 decreased in all microcosms, but thermophilic anaerobic digestion, alkali

85 vant environment, we established simple soil microcosm communities comprising two species of common s

86 Microcosms consisting of sediment in artificial groundwa

87 To address this question, we set up microcosms containing a pair of test plants, interlinked

88 re harvested over a 16-week time series from microcosms containing Gloeophyllum trabeum, Fomitopsis p

89 )C-phenyl-sulfamethazine in small pond water microcosms containing intact sediment and pond water.

90 Compared to plant-free control microcosms, microcosms containing iron plaques successfully stimulat

91 ater invasive alga, Prymnesium parvum, using microcosms containing natural freshwater microbial assem

92 ariovorax strain VC1, was isolated from soil microcosms containing NQ as the sole nitrogen source.

93 We addressed this using microcosms containing OAI sediments incubated under fluc

94 Microcosms containing Scots pine (Pinus sylvestris) seed

95 rogen-fixation activity could be detected in microcosms containing sediments from the field site wher

96 In predator-prey (rotifer-alga) microcosms, cyclical changes in predator abundance gener

97 We present the first use of experimental microcosm data to exhaustively test the accuracy of one

98 In contrast, the DOM-amended microcosm doubled in cell numbers over 27 h, and a varie

99 hyllosilicate minerals in sterile controlled microcosm environments containing only tree seedlings, m

100 e in Georgia (United States), and in aerobic microcosms (epsilon = -3.0 per thousand +/- 0.3 per thou

101 microbial degradation of ethene in anaerobic microcosms (epsilon = -6.7 per thousand +/- 0.4 per thou

102 with an undisturbed surface layer and a Gust microcosm erosion chamber to erode the surface of the co

103 at incorporated (13)C-labeled aniline in the microcosms established to promote methanogenic condition

104 trate- and sulfate-amended microcosms and in microcosms established to promote methanogenic condition

105 on to achieve CF detoxification using anoxic microcosms established with aquifer material from a CF-c

106 In microcosms established with freshwater sediment, HCA was

107 Microcosms established with soil and aquifer materials f

108 a common-garden experiment and in laboratory microcosms evaluating the influence of key root traits o

109 samples at different time points from a soil microcosm experiment conducted under denitrifying condit

110 Our microcosm experiment demonstrated that increased detriti

111 roduction was subsequently demonstrated in a microcosm experiment in compost, in which we observed ch

112 lysis of single cells (n = 34) from the same microcosm experiment revealed no (15)N2 uptake.

113 amics to predict the outcome of a laboratory microcosm experiment testing for interactions among all

114 Here we report results from a microcosm experiment that evaluated how the quantity and

115 We performed a laboratory microcosm experiment to investigate how temperature vari

116 Here we conduct a microcosm experiment to quantify how interactions among

117 We conducted a field survey and a microcosm experiment to test the influence of changes in

118 In a microcosm experiment under controlled conditions, we the

119 Here we conduct a microcosm experiment with laboratory protist community s

120 tions are thereby validated against a 3-week microcosm experiment, in which eight marine diatoms syst

121 the flour beetle (Tribolium castaneum) in a microcosm experiment, we disentangled the genetic and de

122 was further assessed in a 12-week laboratory microcosm experiment.

123 e determined their abilities to coexist in a microcosm experiment.

124 ontinuously fed dechlorinating mixed-culture microcosm experiments (n = 26), we varied respiratory su

125 Microcosm experiments and field sampling suggest that th

126 ian aquifer sediments was investigated using microcosm experiments and substrate amendments.

127 n natural waters by combining biogeochemical microcosm experiments and X-ray absorption spectroscopy.

128 nated riparian soil, we performed laboratory microcosm experiments at 5, 14, and 23 degrees C.

129 Microcosm experiments demonstrated that the constitutive

130 We conducted microcosm experiments in which floating acid mine draina

131 This was also confirmed in microcosm experiments in which we quantified the biotic

132 Microcosm experiments provide a framework within which t

133 Microcosm experiments provide a promising avenue for det

134 The addition of hematite to these microcosm experiments resulted in significant microbial

135 Applying this new method in microcosm experiments revealed that bioirrigation enhanc

136 on processes, was investigated in laboratory microcosm experiments simulating an open-water unit proc

137 Here, we describe microcosm experiments that investigate the biogeochemica

138 and (18)O-labeled nitrite were added to the microcosm experiments to study the effect of putative ba

139 we provide evidence based on community-level microcosm experiments to support the hypothesis that som

140 Laboratory microcosm experiments were conducted to determine the de

141 iouptake, and passive sampler (PE) uptake in microcosm experiments with a freshwater worm, Lumbriculu

142 We set up microcosm experiments with fertilized, wet soil in which

143 In microcosm experiments, biotransformation rates increased

144 In these deepwater microcosm experiments, dispersants did not enhance heter

145 With a combination of field and microcosm experiments, we show that mixotrophs in the Sp

146 nic matter and soil patch in two independent microcosm experiments.

147 soil surface communities on pasture soil in microcosms exposed to light or dark conditions, focusing

148 presence of dispersants, suggesting that the microcosm findings are broadly applicable across marine

149 st twenty years have shown the vulva to be a microcosm for organogenesis and a model for the integrat

150 that the study of skilled reading provides a microcosm for revealing cognitive processes, he illustra

151 es from a wide range of soils were tested in microcosms for their ability to degrade the IM, 3-nitro-

152 In microcosms from contaminated canal sediments, a bacteria

153 In microcosms from heavily contaminated aquifer sediments,

154 We experimented with biofilms in microcosms grown under a gradient of light intensities (

155 g of microbial life, results from artificial microcosms have not been validated in complex natural po

156 In control and Normal-variance microcosms, hosts and parasitoids exhibited distinct pop

157 -defective tomato genotype rmc were grown in microcosms in a glasshouse experiment manipulating both

158 ants were applied to sets of triplicate soil microcosms in two independent experiments.

159 in oleate- and EVO- than in ethanol-amended microcosms, indicating that acetate-utilizing methanogen

160 In all microcosms, intractable rigid polymers unavailable for b

161 ot described previously in the bacteriophage microcosm, involves a SaPI-encoded protein that directly

162 A microcosm iron-enrichment experiment using mixed-layer w

163 arametrize and evaluate the model, including microcosm lab experiments, lake field observations/budge

164 Microcosm (laboratory-based) burial experiments have bee

165 Higher k values were measured in the microcosms lacking the antioxidant (k = 0.0023 h(-1)), m

166 inks scale with area and species richness of microcosms, lakes and streams from community to metacomm

167 We exposed multi-trophic protist microcosm landscapes with one predator, two competing pr

168 al degradation of (S)-FL in activated sludge microcosms leads to the enrichment of FL with 30x more t

169 ore realistic environmental conditions using microcosm/mesocosm-type experiments.

170 ectivity per se shapes diversity patterns in microcosm metacommunities at different levels.

171 st) on metacommunity assembly, using protist microcosm metacommunities that varied in predator identi

172 Compared to plant-free control microcosms, microcosms containing iron plaques successfu

173 ddress this, we developed a laboratory model microcosm mimicking air-water interfaces in soil.

174 We established cocultures in a microcosm model system to determine the mechanism and su

175 Using a microcosm model system, we investigated whether the memb

176 Here we use laboratory experiments in microcosms monitoring the hydrocarbon composition of deg

177 HT concentrations and was significant in the microcosms not supplemented with the antioxidant.

178 In situ microcosm nutrient dilution bioassays and mesocosm nutri

179 The motion of electrons in the microcosm occurs on a time scale set by the atomic unit

180 e posit that the modern airplane is a social microcosm of class-based society, and that the increasin

181 52 million-years ago) of China documenting a microcosm of ecological associations involving a polypha

182 just seven cells of four different types--a microcosm of pattern formation and gamete specification

183 The cellular proteome is a complex microcosm of structural and regulatory networks that req

184 lytic herpesviral transcriptome resembles a microcosm of the host transcriptome and provides a usefu

185 rovide insight into this system, acting as a microcosm of the processes involved in reading.

186 Microcosms offer a useful model system to test the effec

187 Oral biofilms were modelled as in vitro "microcosms" on glass coverslips inoculated with the natu

188 he heterotrophic degrader communities in our microcosms; one group of steady state communities was en

189 NQ persisted in unamended microcosms or under anaerobic conditions.

190 tion of FTACPs was evaluated in a soil-plant microcosm over 5.5 months in the absence/presence of was

191 ion of Arctic peat soil microbiota in anoxic microcosms over a temperature gradient from 1 to 30 degr

192 biotransformation of FtTAoS occurred in live microcosms over approximately 40 days and produced 4:2,

193 nd without root hairs, were grown for 8 d in microcosms packed with sandy loam soil at 1.2 g cm(-3) d

194 sfenvalerate (0.11 mug/L) during the initial microcosm part.

195 ribe sulfate dependent ethene consumption in microcosms prepared with sediments from a freshwater can

196 s indicated by methane degradation assays in microcosms prepared with soil samples from different dep

197 ent-poor filter sterilized lake water (FSLW) microcosm promoted a shift to what we have defined as a

198 Microcosms provide a system in which the accuracy of est

199 Soil microcosms rapidly mineralized fullerol C, as determined

200 ed to sea and river waters in biogeochemical microcosm reactors across field-validated redox conditio

201 Successful invasion occurred in microcosms receiving high propagule pressure whereas nut

202 The lichen as a microcosm represents a structured, unique microbial habi

203 Addition of 2-(14)C-acetate to Stibnite Mine microcosms resulted in the production of (14)CO2 coupled

204 derived oil slick corroborated the deepwater microcosm results as inhibition of hydrocarbon turnover

205 c, PCA analyses) of in situ and experimental microcosm results identified a temperature-driven season

206 pread fungus Paxillus involutus in monoxenic microcosms, revealing preferential allocation by the fun

207 Supporting this, in microcosms, roots with lower specific root area (m(2) g(

208 of fluorescence microscopy, we screened the microcosm sediments for the presence of active strain CJ

209 When we examined the carbon-amended microcosm sediments stained with both a strain CJ2-speci

210 In microcosm sediments, Ea was somewhat lower for anammox c

211 al stanol ratios) in freshwater and seawater microcosms seeded with human wastewater.

212 s to the crude oil and dispersant in on-ship microcosms set up immediately after water collection.

213 days of exposure to 0.05 and 0.5 muM AgNP in microcosms shifted bacterial community structure but had

214 In microcosms simulating the SRS wetland processes, U immob

215 Methane, ethene, and VC were added to the microcosms singly or as mixtures.

216 Using microcosms spiked with fluorotelomer compounds, we found

217 c isotope analysis, molecular surveys and/or microcosm studies has demonstrated the need for multiple

218 Microcosm studies indicated that NO3(-) removal was main

219 hese simpler model experiments and the whole microcosm studies is illustrated partly by observations

220 In addition to that, our analysis of four microcosm studies on the hydrolysis of the individual en

221 sis suggests why some theoretical, field and microcosm studies present conflicting views of fragmenta

222 how large discrepancy between the laboratory microcosm studies used to parameterize the CLM4 litter d

223 Chronic Pb exposure microcosm studies were carried out on two different peri

224 Greenhouse microcosm studies were conducted using native plants (Sp

225 oval coupled to NO2(-) and NO3(-) removal in microcosm studies, suggested that anammox may have been

226 brown tide bloom prone natural seawater in a microcosm study, this treatment effectively removed the

227 a from genomes, cultures, field studies, and microcosms suggest that no single factor discriminates b

228 urface and in bulk soil in the light exposed microcosms suggesting that light can influence phototrop

229 O microcosms versus 10-20 days in the oleate microcosms, suggesting that triglyceride hydrolysis was

230 further elucidated in a separate greenhouse microcosm supplemented with high concentrations of 6:2 d

231 biotransformation of DNAN in soil and sludge microcosms supplemented with uniformly ring-labeled (14)

232 Multiple soil microcosms supplied with different organic substrates we

233 Both amendments had only small impacts on microcosm surface water, sediment and pore water chemist

234 ia densa), followed by toxicity testing with microcosm surface water.

235 derived from the Axton Cross Superfund (ACS) microcosms sustained PCE dechlorination to cDCE as a fin

236 A two-chamber microcosm system was employed to create a root-free soil

237 o visualize patterns of root colonization in microcosm systems containing Picea abies or Pinus sylves

238 We conducted microcosm tests and biogeochemical modeling to study U(V

239 In our groundwater microcosm tests, when all three substrates were present,

240 with and without the AM fungus Glomus hoi in microcosms that allowed only the fungus access to a 15N/

241 Microcosms that received 6% (v/v) of the CF-to-DCM-dechl

242 ons and detoxification were also observed in microcosms that received both inocula simultaneously.

243 The study involved sediment slurry microcosms that represented a spectrum of salinities in

244 acterize the microbial communities of indoor microcosms that were either exposed to each pesticide al

245 his end, active chlorobenzene-dechlorinating microcosms that were producing benzene were inoculated w

246 ment in replicate nutrient-cycling microbial microcosms that were set up identically and allowed to d

247 evolution in the AdhA region reflects, in a microcosm, the overall difference in genome size, with a

248 etoclastic methanogenesis for oleate and EVO microcosms, the model approximately matched observed sul

249 relying on private wells, making it a useful microcosm to study challenges to maintaining private-wel

250 evant for these organisms, we subjected soil microcosms to a heat disturbance and followed the commun

251 In this study, we used tide pool microcosms to demonstrate that the effects of real-world

252 transfer of PP of V. cholerae from original microcosms to freshly prepared FSLW resulted in the same

253 romodeoxyuridine (BrdU) was added to all the microcosms to label newly synthesized DNAs.

254 ten to levels similar to that of the control microcosms to which no wastewater solids had been applie

255 in the sediment, to cultivation in sediment microcosms, to the identification of four distinct types

256 ng rounds, each consisting of >/=5 replicate microcosm treatments, for one commercial FTP in one soil

257 The microcosm trials indicated that the persistence of BacH

258 model was calibrated using data from outdoor microcosm trials performed in March, August, and Novembe

259 There were four microcosm types: surface water; water and sediment; wate

260 centration peaked in 100-120 days in the EVO microcosms versus 10-20 days in the oleate microcosms, s

261 Material from this microcosm was transferred into growth medium with ethene

262 Here, a greenhouse microcosm was used to investigate the fate of endogenous

263 ter three weeks of bioreduction, a subset of microcosms was aerated in order to reoxidize the Fe(II)

264 that the persistence of BacH and BacR in the microcosms was not significantly different from the pers

265 ls confirmed that stability in High-variance microcosms was sufficient to prevent extinction.

266 ed 96% of Se (supplied as selenate) from the microcosm water column within 72 h, with up to 61% being

267 Using invertebrates in microcosms, we characterise phenotypic, population and e

268 rotist communities established in laboratory microcosms, we demonstrate that disturbance does not dim

269 Furthermore, using experimental microcosms, we show that microarthropods significantly i

270 Using rotifer-algal microcosms, we tracked rapid evolution resulting from te

271 PA transformations, coastal bacterioplankton microcosms were amended with a single PA model compound,

272 ormation rates of test compounds measured in microcosms were compared with attenuation rates measured

273 Two landfill leachate microcosms were constructed to specifically assess those

274 Multiple replicate closed microcosms were constructed using pond sediment and wate

275 Microcosms were constructed with groundwater from the Ca

276 Microcosms were designed with four environmental matrice

277 Soil microcosms were extracted with ethyl acetate followed by

278 ntify metabolically active BLO guilds, tidal microcosms were spiked with six (13)C-labeled bacteria a

279 Microcosms were subjected to a factorial design with two

280 Host-parasitoid microcosms were subjected to two treatments: Normal and

281 Microcosms were used to elucidate biodegradation inhibit

282 NQ was efficiently degraded in aerobic microcosms when a carbon source was added.

283 adation of MON and SAL in nonfertilized soil microcosms, whereas biodegradation contributed significa

284 We designed a laboratory microcosm with passive dosing of phenanthrene (PHE) to a

285 tudy design that combined 2 L sediment/water microcosms with 14 day bioaccumulation assays.

286 However, mineralization exceeded 67% in the microcosms with added antioxidant and did not significan

287 and were not significantly different in the microcosms with added BHT (k = 0.001 h(-1)).

288 NTO was nonbiodegradable in aerobic microcosms with all soil inocula.

289 a silt loam sediment were used to establish microcosms with alpha- and beta-isomers of E2 or TB spik

290 Hence, we conducted dedicated bottle-microcosms with eastern Mediterranean Sea water that wer

291 article (AgNP) toxicity, AgNPs were added to microcosms with freshwater sediments and two species of

292 In microcosms with minimal microbial activity (indicated by

293 about 41% of the oil was mineralized in the microcosms with no BHT.

294 eria by adding sterile alginate particles to microcosms with seawater from coastal California, a habi

295 achieve homeostasis by differentiation into microcosms with specialist functions, e.g. cell types.

296 Additionally, the presence of plants in the microcosms (with and without sediments) reduced both the

297 ibe a late Permian fossil wood-boring beetle microcosm, with the oldest known example of complex tunn

298 ARGs and intI1 quantities declined in most microcosms, with statistically significant (P < 0.05) ha

299 tent with theoretical predictions and recent microcosm work that suggest a predictable path is follow

300 SAL biotransformation in soil microcosms yielded the same product as in the BL microco