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1 ing regimes (fully, moderately, and nonmixed microcosms).
2 crocosms and least consistent for raw runoff microcosms.
3 in a fully factorial design to create simple microcosms.
4  integrons in wastewater solids-amended soil microcosms.
5 se, and inorganic nitrogen (N) leaching from microcosms.
6 on dynamics disappeared in the High-variance microcosms.
7 ed in several ecotoxicological studies using microcosms.
8  less variable in High- than Normal-variance microcosms.
9 (Avena fatua) over two seasons in greenhouse microcosms.
10 e been demonstrated in simplified laboratory microcosms.
11 erating predictions that were tested in soil microcosms.
12 ns) exhibited biphasic decay patterns in all microcosms.
13 of Pinus sylvestris needles decomposition in microcosms.
14 ocosms yielded the same product as in the BL microcosms.
15 rmation in microbially active and sterilized microcosms.
16 mation product of MON was identified in soil microcosms.
17 ve dehalogenation in methanogenic laboratory microcosms.
18 tributed significantly in BL-fertilized soil microcosms.
19 as slower in the oleate and EVO than ethanol microcosms.
20  order of magnitude greater than that in the microcosms.
21 crobeloides maximus when recovered from soil microcosms.
22 outh Louisiana crude oil (SLC) in laboratory microcosms.
23 unities assembled in synthetic pitcher plant microcosms.
24 VP) coated Ag nanoparticles (NPs) in aquatic microcosms.
25 icrocosms and 0.024 y(-1) in lactate-amended microcosms.
26 tions using multi-trophic level experimental microcosms.
27 PCB 61 both in sediment and in sediment-free microcosms.
28 e greater for abiotic microcosms than biotic microcosms.
29 ed on the kinetics measured in sediment-free microcosms.
30 ding materials were determined in laboratory microcosms.
31 rs and the soil pore structure in plant-soil microcosms.
32 fficients in diffusion-dominated intact core microcosms.
33 gradation was faster in the columns than the microcosms.
34  obtained for the Dehalogenimonas-containing microcosms (1.89 +/- 0.02) and very different from those
35 per thousand) and Dehalogenimonas-containing microcosms (-23 +/- 2 per thousand and -12.0 +/- 0.8 per
36                                    In anoxic microcosms, 300 mug/L cis- and 150 mug/L trans-4-MCHM de
37 level without significant differences in the microcosm after 40 days of incubation.
38 on gas formation were decreased in unamended microcosms after ~25 days, to an average of 0.0008 y(-1)
39        After 2 h of exposure in experimental microcosms, AgNP and AgNO3 inhibited respiration and pho
40 and reductive capacities for the intact core microcosms aligned well with results from a previous mic
41  mL(-1) achieved complete DCM degradation in microcosms amended with 10 mM bicarbonate.
42                                           In microcosms amended with alginate particles and the profi
43 the fate of the compounds in soil and medium microcosms amended with an aqueous film-forming foam (AF
44                                              Microcosms amended with isotopically labeled ammonium an
45  earthworms (Eisenia fetida) exposed to soil microcosms amended with zwitterionic fluorotelomers and
46                                              Microcosm and column experiments were conducted utilizin
47                                           In microcosm and field experiments, GAC-PEDS captured over
48  between the AMF and the PSB by conducting a microcosm and two Petri plate experiments.
49 e were estimated as 0.019 y(-1) in unamended microcosms and 0.024 y(-1) in lactate-amended microcosms
50 ties of soil-entrapped N2O and N2 in biochar microcosms and a biochar-induced increase in typical and
51                                          The microcosms and enrichment cultures also reduced sulfate,
52  Rates of Sb(V) reduction in anoxic sediment microcosms and enrichment cultures were enhanced by amen
53                           In both laboratory microcosms and field mesocosms, MeHg concentrations in k
54  redox conditions using sediment-groundwater microcosms and flow-through columns.
55 was observed in nitrate- and sulfate-amended microcosms and in microcosms established to promote meth
56 the plant pathogen Ralstonia solanacearum in microcosms and in tomato plant rhizosphere.
57 , bromodeoxyuridine (BrdU), was added to the microcosms and incorporated into the DNA of actively rep
58 cates, most consistent for compost-augmented microcosms and least consistent for raw runoff microcosm
59  carpio) eDNA was evaluated using lake water microcosms and quantitative PCR for a Common Carp-specif
60 hlorobenzene and benzene was observed in the microcosms and was further confirmed by shifts in the ca
61 were grown from dental plaque inoculum (oral microcosms) and were obtained from six systemically heal
62 e degradation was not observed in the second microcosm, and this correlated with negligible relative
63 perfluoroalkyl chains was determined in soil microcosms, and biotransformation pathways were proposed
64 aneously to the sediment and water column of microcosms, and Hg species were monitored in amphipods a
65 e take-all pathogen in abstract experimental microcosms, and show that increased bacterial genotypic
66 aeal and bacterial ammonia oxidation in soil microcosms, and specifically inhibited AOB growth, activ
67                                    We used a microcosm approach to examine the single and combined ef
68                               We used a soil microcosm approach to expose A. maximus populations grow
69                          Here, we used a gut microcosm approach to quantify the effect of three human
70  identification were performed on a sediment microcosm approach.
71     Sequence analysis of etnE genes from the microcosms as well phylogenetic typing of the isolates s
72 t experimental methods (trenching, girdling, microcosms), as well as considering different temporal a
73 vestigated IPA biodegradation in BL and soil microcosms, as a process affecting the fate of IPAs in t
74      Amendments were tested in four separate microcosm assays using Hg-contaminated sediments from tw
75                                              Microcosm assays with (14)C-labeled dioxane showed that
76 from experimentally manipulated multitrophic microcosm assemblages, demonstrate that bacterial social
77                         MON was stable in BL microcosms at 24-72% water content (water/wet litter, w/
78 The majority of lactate- and H(2)-containing microcosms at 30 degrees C were dominated by strictly an
79 led the artificial intelligence problem in a microcosm because learning algorithms must act autonomou
80 ts on dentin bond strength and dental plaque microcosm biofilms for the first time.
81 um disks were contaminated with multispecies microcosm biofilms grown from in vivo peri-implant plaqu
82  eDNA was found to be distributed throughout microcosm biofilms, and was particularly abundant in the
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 re lower (ca. 1.20) than those of the biotic microcosms (ca. 1.80).
86 ival in fluctuating conditions and how these microcosms can yield insights into microscale microbial
87 vant environment, we established simple soil microcosm communities comprising two species of common s
88 se results indicate that the photo-oxidation microcosm comprehensively represents ketone/aldehyde-for
89                                              Microcosms consisting of sediment in artificial groundwa
90 re harvested over a 16-week time series from microcosms containing Gloeophyllum trabeum, Fomitopsis p
91 )C-phenyl-sulfamethazine in small pond water microcosms containing intact sediment and pond water.
92   Compared to plant-free control microcosms, microcosms containing iron plaques successfully stimulat
93 ater invasive alga, Prymnesium parvum, using microcosms containing natural freshwater microbial assem
94                      We addressed this using microcosms containing OAI sediments incubated under fluc
95                                              Microcosms containing Scots pine (Pinus sylvestris) seed
96  observed rate of dechlorination in sediment microcosms could be predicted within a factor of 2 based
97              In predator-prey (rotifer-alga) microcosms, cyclical changes in predator abundance gener
98     We present the first use of experimental microcosm data to exhaustively test the accuracy of one
99                 Correlation strength for all microcosms decayed sharply from strong correlation to un
100                               River sediment microcosms demonstrated that CFC-113 was subject to micr
101 cts in the field, whereas the biodegradation microcosm does not.
102                        A biodegradation-only microcosm enables independent determination as to which
103 e in Georgia (United States), and in aerobic microcosms (epsilon = -3.0 per thousand +/- 0.3 per thou
104 microbial degradation of ethene in anaerobic microcosms (epsilon = -6.7 per thousand +/- 0.4 per thou
105 with an undisturbed surface layer and a Gust microcosm erosion chamber to erode the surface of the co
106 at incorporated (13)C-labeled aniline in the microcosms established to promote methanogenic condition
107 trate- and sulfate-amended microcosms and in microcosms established to promote methanogenic condition
108 on to achieve CF detoxification using anoxic microcosms established with aquifer material from a CF-c
109                                           In microcosms established with freshwater sediment, HCA was
110                                              Microcosms established with soil and aquifer materials f
111 a common-garden experiment and in laboratory microcosms evaluating the influence of key root traits o
112 samples at different time points from a soil microcosm experiment conducted under denitrifying condit
113                                          Our microcosm experiment demonstrated that increased detriti
114 ife-history experiment and a multigeneration microcosm experiment during which individuals and microc
115         We conducted a seasonal survey and a microcosm experiment in an impacted and a reference tida
116 roduction was subsequently demonstrated in a microcosm experiment in compost, in which we observed ch
117 lysis of single cells (n = 34) from the same microcosm experiment revealed no (15)N2 uptake.
118                Here we report results from a microcosm experiment that evaluated how the quantity and
119                    We performed a laboratory microcosm experiment to investigate how temperature vari
120                            Here we conduct a microcosm experiment to quantify how interactions among
121            We conducted a field survey and a microcosm experiment to test the influence of changes in
122                                         In a microcosm experiment under controlled conditions, we the
123 We screened 35 plant-endophyte pairings in a microcosm experiment under well-watered and drought cond
124                            Here we conduct a microcosm experiment with laboratory protist community s
125 tions are thereby validated against a 3-week microcosm experiment, in which eight marine diatoms syst
126  the flour beetle (Tribolium castaneum) in a microcosm experiment, we disentangled the genetic and de
127 cted creek water was clearly observed in the microcosm experiment.
128 e determined their abilities to coexist in a microcosm experiment.
129 was further assessed in a 12-week laboratory microcosm experiment.
130                                              Microcosm experiments and field sampling suggest that th
131                      We performed controlled microcosm experiments and reanalyzed published pot exper
132 ian aquifer sediments was investigated using microcosm experiments and substrate amendments.
133 n natural waters by combining biogeochemical microcosm experiments and X-ray absorption spectroscopy.
134 nated riparian soil, we performed laboratory microcosm experiments at 5, 14, and 23 degrees C.
135                       We conducted anaerobic microcosm experiments containing the B25 bentonite and a
136                                              Microcosm experiments demonstrated that the constitutive
137                                 We conducted microcosm experiments in which floating acid mine draina
138                   This was also confirmed in microcosm experiments in which we quantified the biotic
139                                              Microcosm experiments provide a framework within which t
140            The addition of hematite to these microcosm experiments resulted in significant microbial
141                  Applying this new method in microcosm experiments revealed that bioirrigation enhanc
142 on processes, was investigated in laboratory microcosm experiments simulating an open-water unit proc
143                            Here, we describe microcosm experiments that investigate the biogeochemica
144 racterized its composition, and used 100-day microcosm experiments to determine the effect of in situ
145  and (18)O-labeled nitrite were added to the microcosm experiments to study the effect of putative ba
146 we provide evidence based on community-level microcosm experiments to support the hypothesis that som
147                                   Laboratory microcosm experiments were conducted to determine the de
148  reflooding, batch incubations and unplanted microcosm experiments were conducted with two paddy soil
149 iouptake, and passive sampler (PE) uptake in microcosm experiments with a freshwater worm, Lumbriculu
150                                    We set up microcosm experiments with fertilized, wet soil in which
151                                           In microcosm experiments, biotransformation rates increased
152                           In these deepwater microcosm experiments, dispersants did not enhance heter
153              With a combination of field and microcosm experiments, we show that mixotrophs in the Sp
154 nic matter and soil patch in two independent microcosm experiments.
155 ystem of the Pearl River Estuary and in soil microcosm experiments.
156 ds (n = 3-11), but not those from laboratory microcosms exposed to fluorotelomer-based AFFFs.
157  soil surface communities on pasture soil in microcosms exposed to light or dark conditions, focusing
158 presence of dispersants, suggesting that the microcosm findings are broadly applicable across marine
159 es from a wide range of soils were tested in microcosms for their ability to degrade the IM, 3-nitro-
160                                           In microcosms from contaminated canal sediments, a bacteria
161                                           In microcosms from heavily contaminated aquifer sediments,
162             We experimented with biofilms in microcosms grown under a gradient of light intensities (
163               In control and Normal-variance microcosms, hosts and parasitoids exhibited distinct pop
164                                          The microcosms imitated clean flow through a fracture next t
165 -defective tomato genotype rmc were grown in microcosms in a glasshouse experiment manipulating both
166 ants were applied to sets of triplicate soil microcosms in two independent experiments.
167                       Here, we constructed a microcosm incubation to investigate the effects of two c
168                           Here, we performed microcosm incubations using sandy soil from an agricultu
169  in oleate- and EVO- than in ethanol-amended microcosms, indicating that acetate-utilizing methanogen
170  consisting of bacterial liquid cultures and microcosms inoculated with FWI soils, using a dual nonta
171 arametrize and evaluate the model, including microcosm lab experiments, lake field observations/budge
172                                              Microcosm (laboratory-based) burial experiments have bee
173             We exposed multi-trophic protist microcosm landscapes with one predator, two competing pr
174 al degradation of (S)-FL in activated sludge microcosms leads to the enrichment of FL with 30x more t
175 st) on metacommunity assembly, using protist microcosm metacommunities that varied in predator identi
176               Compared to plant-free control microcosms, microcosms containing iron plaques successfu
177 ddress this, we developed a laboratory model microcosm mimicking air-water interfaces in soil.
178                       A photo-oxidation-only microcosm mimics solar irradiation of crude oil in the e
179               We established cocultures in a microcosm model system to determine the mechanism and su
180                                      Using a microcosm model system, we investigated whether the memb
181                   However, in the respective microcosms, no significant metabolic activity occurred,
182                                      In situ microcosm nutrient dilution bioassays and mesocosm nutri
183       Using a microfluidic platform allowing microcosm observations of a droplet passing through a ba
184               The motion of electrons in the microcosm occurs on a time scale set by the atomic unit
185 e posit that the modern airplane is a social microcosm of class-based society, and that the increasin
186 52 million-years ago) of China documenting a microcosm of ecological associations involving a polypha
187 logic Research (SER) membership-a reflection/microcosm of society.
188           The cellular proteome is a complex microcosm of structural and regulatory networks that req
189                                              Microcosms offer a useful model system to test the effec
190     Oral biofilms were modelled as in vitro "microcosms" on glass coverslips inoculated with the natu
191 he heterotrophic degrader communities in our microcosms; one group of steady state communities was en
192 tion of FTACPs was evaluated in a soil-plant microcosm over 5.5 months in the absence/presence of was
193 ion of Arctic peat soil microbiota in anoxic microcosms over a temperature gradient from 1 to 30 degr
194 biotransformation of FtTAoS occurred in live microcosms over approximately 40 days and produced 4:2,
195 nd without root hairs, were grown for 8 d in microcosms packed with sandy loam soil at 1.2 g cm(-3) d
196 sfenvalerate (0.11 mug/L) during the initial microcosm part.
197 ribe sulfate dependent ethene consumption in microcosms prepared with sediments from a freshwater can
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 Addition of 2-(14)C-acetate to Stibnite Mine microcosms resulted in the production of (14)CO2 coupled
203 derived oil slick corroborated the deepwater microcosm results as inhibition of hydrocarbon turnover
204 c, PCA analyses) of in situ and experimental microcosm results identified a temperature-driven season
205 pread fungus Paxillus involutus in monoxenic microcosms, revealing preferential allocation by the fun
206                          Supporting this, in microcosms, roots with lower specific root area (m(2) g(
207  of fluorescence microscopy, we screened the microcosm sediments for the presence of active strain CJ
208          When we examined the carbon-amended microcosm sediments stained with both a strain CJ2-speci
209                                           In microcosm sediments, Ea was somewhat lower for anammox c
210 al stanol ratios) in freshwater and seawater microcosms seeded with human wastewater.
211 s to the crude oil and dispersant in on-ship microcosms set up immediately after water collection.
212 days of exposure to 0.05 and 0.5 muM AgNP in microcosms shifted bacterial community structure but had
213 dels to understand the predation dynamics in microcosms simulating aquatic environments.
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                                              Microcosm studies indicated that NO3(-) removal was main
218    In addition to that, our analysis of four microcosm studies on the hydrolysis of the individual en
219 how large discrepancy between the laboratory microcosm studies used to parameterize the CLM4 litter d
220                          Chronic Pb exposure microcosm studies were carried out on two different peri
221                                   Greenhouse microcosm studies were conducted using native plants (Sp
222 etatranscriptomic approach, nutrient-amended microcosm studies were used to track the global metaboli
223 oval coupled to NO2(-) and NO3(-) removal in microcosm studies, suggested that anammox may have been
224 hout the presence of sediment in bench-scale microcosm studies.
225                     Correlative imaging of a microcosm study shows that the majority (75%) of bacteri
226 een these factors, we conducted a controlled microcosm study tracking bacterial assembly in cleared s
227 ms aligned well with results from a previous microcosm study using crushed sandstone from the same si
228 bal observational study with an experimental microcosm study, we provide evidence that soil biodivers
229 a from genomes, cultures, field studies, and microcosms suggest that no single factor discriminates b
230 urface and in bulk soil in the light exposed microcosms suggesting that light can influence phototrop
231 icantly lower for salt and nutrient addition microcosms, suggesting deterministic selective pressures
232 O microcosms versus 10-20 days in the oleate microcosms, suggesting that triglyceride hydrolysis was
233  further elucidated in a separate greenhouse microcosm supplemented with high concentrations of 6:2 d
234 biotransformation of DNAN in soil and sludge microcosms supplemented with uniformly ring-labeled (14)
235                                Multiple soil microcosms supplied with different organic substrates we
236    Both amendments had only small impacts on microcosm surface water, sediment and pore water chemist
237 derived from the Axton Cross Superfund (ACS) microcosms sustained PCE dechlorination to cDCE as a fin
238                                A two-chamber microcosm system was employed to create a root-free soil
239 o visualize patterns of root colonization in microcosm systems containing Picea abies or Pinus sylves
240  trophic structure in 210 natural freshwater microcosms (tank bromeliads) across Central and South Am
241                                 We conducted microcosm tests and biogeochemical modeling to study U(V
242                           In our groundwater microcosm tests, when all three substrates were present,
243      The decay rates are greater for abiotic microcosms than biotic microcosms.
244 l processes, we constructed transparent soil microcosms that enable the visualization of microbes via
245                                              Microcosms that received 6% (v/v) of the CF-to-DCM-dechl
246 ons and detoxification were also observed in microcosms that received both inocula simultaneously.
247           The study involved sediment slurry microcosms that represented a spectrum of salinities in
248 were assessed using a numerical model of the microcosms that were calibrated to monitoring data.
249 acterize the microbial communities of indoor microcosms that were either exposed to each pesticide al
250  substrates, thermophilic bacteria dominated microcosms that were incubated at 60 degrees C.
251 his end, active chlorobenzene-dechlorinating microcosms that were producing benzene were inoculated w
252 ment in replicate nutrient-cycling microbial microcosms that were set up identically and allowed to d
253     Methanogenesis was observed in duplicate microcosms that were unamended, amended with sulfate or
254 etoclastic methanogenesis for oleate and EVO microcosms, the model approximately matched observed sul
255         Upon irradiation in a photooxidation microcosm, thin films of the asphalt binder produce abun
256 relying on private wells, making it a useful microcosm to study challenges to maintaining private-wel
257 evant for these organisms, we subjected soil microcosms to a heat disturbance and followed the commun
258 romodeoxyuridine (BrdU) was added to all the microcosms to label newly synthesized DNAs.
259        Here we combine theory and laboratory microcosms to predict how simple microbial communities w
260                              We exposed soil microcosms to weekly bursts of (60)Co gamma radiation ov
261 ten to levels similar to that of the control microcosms to which no wastewater solids had been applie
262 comparison of field and photo-oxidation-only microcosm transformation products reveal remarkable simi
263  mosquito species and the water samples from microcosms treated with each of the pesticides, separate
264 ng rounds, each consisting of >/=5 replicate microcosm treatments, for one commercial FTP in one soil
265                                          The microcosm trials indicated that the persistence of BacH
266 ere we explore this question with laboratory microcosms, using cocultures of two bacterial species, P
267 centration peaked in 100-120 days in the EVO microcosms versus 10-20 days in the oleate microcosms, s
268                           Material from this microcosm was transferred into growth medium with ethene
269                           Here, a greenhouse microcosm was used to investigate the fate of endogenous
270 that the persistence of BacH and BacR in the microcosms was not significantly different from the pers
271 ls confirmed that stability in High-variance microcosms was sufficient to prevent extinction.
272 ed 96% of Se (supplied as selenate) from the microcosm water column within 72 h, with up to 61% being
273                       Using invertebrates in microcosms, we characterise phenotypic, population and e
274                                     From our microcosms, we estimated methane oxidation rates of up t
275 PA transformations, coastal bacterioplankton microcosms were amended with a single PA model compound,
276                                 Although all microcosms were amended with the same amount of C (12 mg
277 ormation rates of test compounds measured in microcosms were compared with attenuation rates measured
278                        Two landfill leachate microcosms were constructed to specifically assess those
279                    Multiple replicate closed microcosms were constructed using pond sediment and wate
280                                              Microcosms were constructed with groundwater from the Ca
281 lysis (DFA) scaling exponents of the abiotic microcosms were lower (ca. 1.20) than those of the bioti
282    The DeltaG(m) relaxation edges for biotic microcosms were lower, indicating less remaining free en
283 cosm experiment during which individuals and microcosms were maintained at a mean temperature of 26 d
284                                              Microcosms were subjected to a factorial design with two
285                              Host-parasitoid microcosms were subjected to two treatments: Normal and
286                                              Microcosms were used to elucidate biodegradation inhibit
287 adation of MON and SAL in nonfertilized soil microcosms, whereas biodegradation contributed significa
288                     We designed a laboratory microcosm with passive dosing of phenanthrene (PHE) to a
289 tudy design that combined 2 L sediment/water microcosms with 14 day bioaccumulation assays.
290                              Using semibatch microcosms with a Superfund site soil and groundwater, w
291          NTO was nonbiodegradable in aerobic microcosms with all soil inocula.
292  a silt loam sediment were used to establish microcosms with alpha- and beta-isomers of E2 or TB spik
293 ial Fe(II) oxidation using a series of batch microcosms with bacteriogenic iron oxides (BIOS).
294         Hence, we conducted dedicated bottle-microcosms with eastern Mediterranean Sea water that wer
295                                           In microcosms with minimal microbial activity (indicated by
296 eria by adding sterile alginate particles to microcosms with seawater from coastal California, a habi
297  Additionally, the presence of plants in the microcosms (with and without sediments) reduced both the
298 ibe a late Permian fossil wood-boring beetle microcosm, with the oldest known example of complex tunn
299   ARGs and intI1 quantities declined in most microcosms, with statistically significant (P < 0.05) ha
300                SAL biotransformation in soil microcosms yielded the same product as in the BL microco

 
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