ライフサイエンスコーパス: biodegradation

1 nsidered the rate-limiting step in polyester biodegradation.

2 (from 1.4 x 10(7) to 0 CFU/mL) and hindered biodegradation.

3 to design appropriate strategies to enhance biodegradation.

4 rC attenuation due to sorptive retention and biodegradation.

5 ved from fossil oil and largely resistant to biodegradation.

6 ertness of gold nanoparticles prevents their biodegradation.

7 that are relatively more amenable to aerobic biodegradation.

8 ties involved in oxidized biodiesel compound biodegradation.

9 competitive inhibition are used to describe biodegradation.

10 ing to increased pollutant accessibility and biodegradation.

11 ducing a compound with potential for further biodegradation.

12 enced by the petroleum contamination and its biodegradation.

13 nation with other environmental factors like biodegradation.

14 all except R-95 substantially increased PAH biodegradation.

15 -1) 1,1-DCE completely inhibited 1,4-dioxane biodegradation.

16 ensively studied, we know little of isoprene biodegradation.

17 ria in the initial steps of unsaturated LCFA biodegradation.

18 natural gases after their formation, such as biodegradation.

19 , extending anaerobic conditions may enhance biodegradation.

20 he key redox process involved in contaminant biodegradation.

21 lina-JP5 biofuel due to its relatively rapid biodegradation.

22 ace contaminants can be mitigated by aerobic biodegradation.

23 in similar quantities, we know little of its biodegradation.

24 ), most of which did not undergo significant biodegradation.

25 no information exists on the genetics of BAM biodegradation.

26 , indicating that the Gulf is primed for oil biodegradation.

27 test flumes and test EFr as an indicator of biodegradation.

28 pecial attention is given to biosorption and biodegradation.

29 ore favorable conditions for both photo- and biodegradation.

30 ionation and enantiomer fractionation during biodegradation.

31 nsidered the rate-limiting step in polyester biodegradation.

32 he known taxonomic distribution of sulfolane biodegradation.

33 does not necessarily indicate the absence of biodegradation.

34 oisture content and potentially reduces wood biodegradation.

35 rts to promote their efficient recycling and biodegradation.

36 s to identify putative pathways of sulfolane biodegradation.

37 ential of native microbes for in situ SCN(-) biodegradation, a remediation option that is less costly

38 Initially all sludge inocula showed limited biodegradation ability, but as market introduction progr

39 and CSi@CSi-Mg10 scaffolds displayed limited biodegradation, accelerated new bone ingrowth (4-12 week

40 The survival and biodegradation activity of strain LH128 were measured in

41 sformations, including aerobic and anaerobic biodegradation, alkaline hydrolysis, Fenton-like degrada

42 es include energy from aerobic and anaerobic biodegradation, anaerobic metal corrosion, ash hydration

43 egradation, IL design strategies, methods of biodegradation analysis, properties of IL/surfactant der

44 ented runoff would demonstrate enhanced TOrC biodegradation and (2) biochar-amended sand bearing DOC-

45 imary compounds in crude MCHM (1) to undergo biodegradation and (2) for sediments to serve as a long-

46 ction processes in the human body related to biodegradation and biosynthesis.

47 isotope analysis (CSIA) to track the aerobic biodegradation and biotransformation pathways of the mos

48 Despite the existence of bacteria capable of biodegradation and cometabolic transformation of HCH iso

49 valuate the different aspects of hydrocarbon biodegradation and identify the knowledge gaps in the li

50 t on the interplay of processes that control biodegradation and isotope fractionation of contaminants

51 Given their slow biodegradation and limited sorption affinities, IL catio

52 ith respect to in situ petroleum hydrocarbon biodegradation and microbial sulfate reduction.

53 aquatic microorganisms involved in polyester biodegradation and mineralization.

54 ion as a source of variability in regulatory biodegradation and persistence assessments.

55 reenland to simulate and investigate in situ biodegradation and photo-oxidation of dispersed oil drop

56 LC-MS/MS analysis as a probe to distinguish biodegradation and photodegradation.

57 Biodegradation and photolysis of dissolved organic matte

58 In contrast, CSi scaffolds exhibited fast biodegradation and retarded new bone regeneration after

59 scales and establish a potential pathway to biodegradation and sedimentations as well as substantial

60 ntidepressant fluoxetine (FLX) by photo- and biodegradation and shows similarities and differences in

61 four (14)C-labeled compounds with different biodegradation and sorption behavior were tested across

62 This study investigates BP and BZ biodegradation and subsequent carbon flow through the mi

63 itically discuss current research on plastic biodegradation and the identification of potentially pat

64 per thousand), ruling out this mechanism for biodegradation and transformation by MnO2.

65 different processes as Vitamin B12-dependent biodegradation and zerovalent metal-mediated dehalogenat

66 m is proposed by which carbamazepine resists biodegradation, and a previously unknown microbial biode

67 cations to the dentin matrix, reduced tissue biodegradation, and bridging to methacrylate resins.

68 non-immunogenic, substrates for proteolytic biodegradation, and can be decorated with pharmacologica

69 , in vivo data suggested tissue integration, biodegradation, and minimal host inflammatory responses

70 removal process in the environment is due to biodegradation, and particularly anaerobic reductive dec

71 Oil compound depletion by dissolution, biodegradation, and photo-oxidation was untangled by gas

72 attributed to the combination of adsorption, biodegradation, and photocatalysis of triclosan by algae

73 ives and computational methods of predicting biodegradation are discussed.

74 icide; the genes and enzymes responsible for biodegradation are largely unknown, the relative roles o

75 onmental factors on the rates and extents of biodegradation are not clear.

76 So, anaerobic and aerobic biodegradation are not recommended as feasible disposal

77 Sorption and biodegradation are the two major removal pathways of ant

78 nd their synergistic interactions during PCB biodegradation, are not well understood.

79 OM quality and quantity were consistent with biodegradation as an explanation for the differences.

80 The medium for the biodegradation assay contains regular organic compounds

81 fter BTS placement into the duodenum for the biodegradation assay.

82 importance of metabolite studies as part of biodegradation assays is highlighted.

83 new inoculants in bioremediation but also in biodegradation assessments of chemicals present in natur

84 potential to simultaneously contribute to VC biodegradation at these sites.

85 Important factors affecting sorption and biodegradation behavior of antibiotics are also highligh

86 Ni was observed in association with ethanol biodegradation but not with BTEX.

87 , nutrient limitation may severely delay oil biodegradation, but in the photic zone, photolytic trans

88 reduced corrinoids and Zn(0) particles; EDB biodegradation by Ancylobacter aquaticus and Sulfurospir

89 E was the strongest inhibitor of 1,4-dioxane biodegradation by bacterial pure cultures exposed to chl

90 sed enzymes might bias the assessment of HCH biodegradation by CSIA at contaminated sites.

91 Insecticide biodegradation by detoxification enzymes is a common res

92 actionation of sulfamethoxazole (SMX) during biodegradation by Microbacterium sp. strain BR1 (ipso-hy

93 ts and their mixtures on aerobic 1,4-dioxane biodegradation by Pseudonocardia dioxanivorans CB1190.

94 At low NP concentrations, RC suppressed NP biodegradation by reducing NP bioavailability, while at

95 oncentrations, moderate RC addition promoted biodegradation by reducing toxicity of NP to microbes.

96 Under some conditions biodegradation can be measured in unspiked natural water

97 ecologically relevant, and whether phenazine biodegradation can counter their effects.

98 experiments in real produced water showed a biodegradation capacity of 1.45 mg COD/gramwet-day at a

99 s, showing that bottlenecks to reach optimal biodegradation clearly exist.

100 (2) at levels relevant to in vivo Mg-implant biodegradation compared to the other indicator/Au-Pd NP

101 Here, we investigated laboratory biodegradation, consisting of bacterial liquid cultures

102 that this modified ISCO approach coupled to biodegradation could be a feasible strategy for the remo

103 ated biodegradation rate, forming adsorption-biodegradation coupled bioremediation.

104 nsive study on the effects of biochar on HOC biodegradation coupled with bioavailability and microbia

105 The importance of biodegradation data as part of the design of safer chemi

106 In Gram-negative bacteria, biodegradation depends on facilitated diffusion of the p

107 The combination of biodegradation, dissolution, and photo-oxidation deplete

108 d insights of the interaction of contaminant biodegradation, dominant redox processes, and interactio

109 Herein, triphenyltin (TPT) biodegradation efficiency and its transformation pathway

110 advanced sorbents, improved dispersants, or biodegradation enhancers.

111 ribution of pores in aggregates sampled from biodegradation experiments of a clayey, aggregated, hydr

112 However, biodegradation experiments with activated sludge demonst

113 nterestingly, the same trend was observed in biodegradation experiments.

114 RBTs are central in assessing the biodegradation fate of chemicals and inferring exposure

115 The biodegradation fluxes of the contaminants were estimated

116 ork we assess the compound-specific rates of biodegradation for 125 aliphatic, aromatic, and biomarke

117 e principal biogeochemical barrier to SCN(-) biodegradation for an autotrophic microbial consortium e

118 Third, the extent of biodegradation for any given sample was influenced by th

119 eds to be considered when deriving rates for biodegradation from field studies.

120 ites and searched for relationships among VC biodegradation gene abundance and expression and site ge

121 roach to mine for phenazine biosynthesis and biodegradation genes, applying it to >800 soil and plant

122 nents had no or only a limited effect on the biodegradation half times for three compounds when teste

123 toxicity, and potential carcinogenicity, its biodegradation has garnered significant attention.

124 t, to our knowledge, the mechanisms for ATBC biodegradation have not been identified previously and p

125 Structural features that promote/impede IL biodegradation, IL design strategies, methods of biodegr

126 or the role of Variovorax in in situ linuron biodegradation in a BPS, alongside other organisms like

127 ify microorganisms associated with sulfolane biodegradation in a contaminated subarctic aquifer.

128 irst, molecular structure served to modulate biodegradation in a predictable fashion, with the simple

129 nd soil characteristics governing mulch film biodegradation in agricultural soils.

130 thanogenesis observed was coupled to bitumen biodegradation in an unspecific manner.

131 ent additives tested significantly increased biodegradation in any of these environments.

132 e dark, exhibits pronounced enantioselective biodegradation in certain soils.

133 EFr offers the opportunity to differentiate biodegradation in complex environmental systems from abi

134 their ability to enhance PAH desorption and biodegradation in contaminated soil after treatment in a

135 w rates impose challenges for micropollutant biodegradation in DWTPs.

136 Hyporheic zones mediate vinyl chloride (VC) biodegradation in groundwater discharging into surface w

137 tanding the complicated process of petroleum biodegradation in marine environments.

138 To study hydrocarbon biodegradation in marsh sediments impacted by Macondo oi

139 y be the principal barrier to in situ SCN(-) biodegradation in mine tailing waters and also yield new

140 noninvasive monitoring of in vivo Mg-implant biodegradation in research and clinical settings with fa

141 However, understanding polymer biodegradation in soils remains a significant challenge

142 indicated that the oxic phases promoted oil biodegradation in subsequent anoxic phases by microbiall

143 prominent than suppression of co-contaminant biodegradation in subsurface locations where poly- and p

144 The model considers biomass while including biodegradation in the capillary fringe and unsaturated z

145 ndicate that bacteria capable of contaminant biodegradation in the capillary fringe can create a sink

146 res subject to fastest loss, indicating that biodegradation in the deep ocean progresses similarly to

147 All measures of biodegradation in the samples (in situ degradation estim

148 Various groups have studied the rate of oil biodegradation in the sea over many years, but with no c

149 oil was exposed to sunlight, suggesting that biodegradation (in the dark) and photodegradation (under

150 Bacterial taxa that were associated with biodegradation included Acidobacteria (groups 6, 17, and

151 Biodegradation-induced changes in (15)N/(14)N ratios (ep

152 Microcosms were used to elucidate biodegradation inhibition at varying glutaraldehyde conc

153 Concentrations of known biodegradation intermediates, including methylperfluorob

154 PE biodegradation is achieved through the combination of ab

155 lethal oiling at the surface, and microbial biodegradation is dramatically increased.

156 Assessment of micropollutant biodegradation is essential to determine the persistence

157 Biodegradation is one of the necessary conditions for th

158 centrations can accelerate the generation of biodegradation kinetic data, which are more environmenta

159 s oxygen-, substrate-, and biomass-dependent biodegradation kinetics along with diffusive transport p

160 s spiked incubation tests to provide data on biodegradation kinetics in surface waters.

161 tudy the concentration and mixture effect on biodegradation kinetics.

162 ombining electrolytic treatment with aerobic biodegradation may be a promising synergistic approach f

163 formation products in the field, whereas the biodegradation microcosm does not.

164 rmulations were also evaluated for swelling, biodegradation, moisture content, in-vitro aerodynamic p

165 l method enables accurate quantification and biodegradation monitoring of PBAT in agricultural field

166 oxygenases is frequently the initial step of biodegradation, O2 activation kinetics may also have bee

167 5), with more consistent rates and extent of biodegradation observed in the erBST.

168 alkanes and polycyclic aromatic hydrocarbons biodegradation occurred in two distinct phases, consiste

169 Hexadecane biodegradation occurred only when pores were 5 mum or la

170 s phase to the liquid phase, where pollutant biodegradation occurs.

171 ctionation during both aerobic and anaerobic biodegradation of 1,2-dichloroethane (1,2-DCA) using fiv

172 C-Cl isotope fractionation during anaerobic biodegradation of 1,2-dichloroethane (1,2-DCA) via dihal

173 onstrated that individual solvents inhibited biodegradation of 1,4-dioxane in the following order: 1,

174 In situ natural attenuation or enhanced biodegradation of 1,4-dioxane is being considered for co

175 When coupled to electrolysis, biodegradation of 1,4-dioxane was sustained even in the

176 We would like to highlight that the biodegradation of 2D materials mainly depends on the typ

177 PACs at substantially faster rates than the biodegradation of alkanes.

178 Originally discovered in a quest for biodegradation of anthropogenic organohalogens, these or

179 own as coenzyme Q) biosynthesis or microbial biodegradation of aromatic compounds, respectively.

180 microorganisms and the genes involved in the biodegradation of BACs is crucial for better understandi

181 dition of rhBMP-2 significantly affected the biodegradation of beta-TCP and BBM, accelerating the res

182 inflammation, has been shown to catalyze the biodegradation of carbon nanomaterials.

183 8 and OECD 309 are performed to simulate the biodegradation of chemicals in water-sediment systems in

184 rial enzyme catalyzing the first step in the biodegradation of cholesterol.

185 rsal, and at such concentrations the rate of biodegradation of detectable oil hydrocarbons has an app

186 n improve drinking water quality through the biodegradation of dissolved contaminants but also pose p

187 ESH were particularly effective at enhancing biodegradation of four- and five-ring PAHs, including fi

188 tory results from this study showed that the biodegradation of FPB in loamy soils gave rise to the pr

189 gelatin content, which may be related to the biodegradation of gelatin in culture media.

190 We initially cover the biodegradation of graphene family materials, followed by

191 these populations play a pivotal role in the biodegradation of high-molecular-weight PAHs and other c

192 where HCB may contribute importantly to the biodegradation of hydrocarbon contaminants in marine sur

193 e a simple proxy for long-term monitoring of biodegradation of hydrocarbons in the smear zone.

194 In modern societies, biodegradation of hydrophobic pollutants generated by in

195 ation, photodegradation, evaporation, and/or biodegradation of individual PAH compounds.

196 Thus, the anaerobic biodegradation of labile fuel components coupled with su

197 condary water quality impacts related to the biodegradation of methane.

198 othiazide and diclofenac) while reducing the biodegradation of metoprolol.

199 ng of the three fundamental steps underlying biodegradation of mulch films in agricultural soils: col

200 te, stability, toxicity, immunogenicity, and biodegradation of nanocellulose-based delivery platforms

201 In contrast, the biodegradation of nonvolatile contaminants in the vadose

202 In this paper, the effects of biochar on the biodegradation of nonylphenol (NP) were investigated usi

203 Assessing the biodegradation of organic compounds is a frequent questi

204 are theoretically conceptualized to restrict biodegradation of organic contaminants, bioavailability

205 The biodegradation of PEG-PDLA stabilized nanoemulsions was

206 Biodegradation of persistent micropollutants like pestic

207 duces biofouling and provides a platform for biodegradation of persistent organic pollutants.

208 capability of these bacterial candidates for biodegradation of plastic.

209 ic environments, there is much less known on biodegradation of polyesters in natural and artificial a

210 of biodegradation-promoting additives on the biodegradation of polyethylene (PE) and polyethylene ter

211 with KTR9 is a feasible strategy for in situ biodegradation of RDX and, at this site, is capable of a

212 Anaerobic microbial biodegradation of recalcitrant, water-insoluble substrat

213 These taxa could be related to biodegradation of shorter-chain (<=C(26)) alkanes, longe

214 ms contributed to the apparent and exclusive biodegradation of substituted and non-substituted polycy

215 able to autogenous bone graft with favorable biodegradation of the bioactive ceramic component in viv

216 crobial growth, raising the question how the biodegradation of the buried oil would proceed.

217 unterparts and clear demonstration of fungal biodegradation of the cellulose-nanofibril-based electro

218 Biodegradation of the entire device minimizes potential

219 in fish, possibly indicating attenuation by biodegradation of the fluorine-free moiety, supported by

220 This was accompanied by a biodegradation of the nanotubes approaching 40%, whereas

221 ances of nitrogenase genes (nifH), catalyzed biodegradation of the nitrogen-poor petroleum hydrocarbo

222 Biodegradation of the persistent groundwater contaminant

223 set of mass transfer limitations during slow biodegradation of the polycyclic aromatic hydrocarbon 2-

224 The ability of the plants to stimulate the biodegradation of these compounds was evaluated by measu

225 e host's actual role and if it benefits from biodegradation of this synthetic polymer.

226 Biodegradation of TOrCs in runoff was more enhanced by c

227 gen (through the photosystem II complex) and biodegradation of toxic superoxide to hydrogen peroxide

228 tic character of some of these substituents, biodegradation of trifluralin does occur, and pure cultu

229 rse biotic and abiotic stresses, and promote biodegradation of various contaminants.

230 proach can be applied to sensitively monitor biodegradation of various organic compounds under anoxic

231 Biodegradation of volatile contaminants in the capillary

232 ng of the microorganisms involved in in situ biodegradation of xenobiotics, like pesticides, in natur

233 al on enantiomers, biotic processes, such as biodegradation often result in enantiomeric fractionatio

234 A biodegradation-only microcosm enables independent determ

235 ly relevant levels to assess their impact on biodegradation outcome and intratest replicate variabili

236 onmental fate of trifluralin with a focus on biodegradation pathways and mechanisms, and we identify

237 naerobic naphthalene and 2-methylnaphthalene biodegradation pathways at PAH-contaminated field sites.

238 rganisms, where the initial steps of various biodegradation pathways include an oxidative dechlorinat

239 differentiate between aerobic and anaerobic biodegradation pathways of 1,2-DCA in the field and sugg

240 mental insights into sorption mechanisms and biodegradation pathways of different classes of antibiot

241 and characterization methods, macromolecular biodegradation pathways, and polyphosphazene-based multi

242 rates and gene expression, implying that the biodegradation performance in soils cannot be directly a

243 constructed microbial mats was evaluated for biodegradation performance, microbial community structur

244 substituent group structure and position on biodegradation potential demonstrated a significant corr

245 Notably, the oil biodegradation potential of the phytoplankton-associated

246 ferences in community compositions and their biodegradation potential were primarily associated (P <

247 tally realistic assessment of in situ SCN(-) biodegradation potential.

248 Med., and indicate strong oil biodegradation potential.

249 t HOC concentrations, which strengthened HOC biodegradation process and accelerated biodegradation ra

250 of polyesters, the key step in their overall biodegradation process.

251 s to assess crystallinity changes during the biodegradation process.

252 pollutants must be identified to understand biodegradation processes and reaction mechanisms and to

253 oplets in comparison to substantially slower biodegradation processes at oil-water interfaces highlig

254 o gain a better mechanistic understanding of biodegradation processes of polyesters in WWTPs where th

255 et traverses the plume in ~48 h, while known biodegradation processes require weeks to complete.

256 review will help to better understand their biodegradation processes, and will stimulate the chemist

257 mportant considerations for their respective biodegradation processes.

258 ining electrochemical oxidation with aerobic biodegradation produces an overadditive treatment effect

259 In addition, the biodegradation products of crude oil contaminants are co

260 compound structure disclosure for predicting biodegradation products.

261 Biodegradation-promoting additives for polymers are incr

262 In this study, we evaluated the effect of biodegradation-promoting additives on the biodegradation

263 e plastics containing any of the five tested biodegradation-promoting additives.

264 drug delivery because of their controllable biodegradation properties and perceived favorable cytoco

265 ntial implications for diverse areas such as biodegradation, quorum sensing and gut biology.

266 ne augmentation, bone microarchitecture, and biodegradation rate of additional carriers to rhBMP-2/ab

267 d HOC biodegradation process and accelerated biodegradation rate, forming adsorption-biodegradation c

268 However, the effects of dispersants on oil biodegradation rates are debated.

269 Inhibition of 1,4-dioxane biodegradation rates by chlorinated solvents was attribu

270 Three trends emerge from analysis of the biodegradation rates of 125 individual hydrocarbons in t

271 For most of the compounds, biodegradation rates slowed with increasing glutaraldehy

272 med that these HLs were substantially due to biodegradation rather than other loss processes.

273 conclude that spiking can strongly influence biodegradation, reducing the environmental relevance of

274 a publicly available quantitative structure-biodegradation relationship (QSBR) model.

275 able aromatic compounds in a high throughput biodegradation screening test (HT-BST).

276 Standard OECD biodegradation screening tests (BSTs) have not evolved a

277 Unlike previous lignin biodegradation studies, white rot fungi were used to pro

278 matory response while undergoing significant biodegradation such that only 25% of the embolic materia

279 ategory in contrast to a standard OECD Ready Biodegradation Test (RBTs, P < 0.05).

280 ng-based platform was recently developed for biodegradation testing of composed mixtures of hydrophob

281 Most biodegradation tests are conducted using single chemical

282 s were (1) to design a closed test setup for biodegradation tests in soil in which the maintaining an

283 l risk assessments of chemicals, higher-tier biodegradation tests in soil, sediment, and surface-wate

284 Biodegradation tests showed that the presence of cellulo

285 Biodegradation tests were conducted in 20 mL vials using

286 Approximately 20000 individual biodegradation tests were performed, returning analogous

287 marine environment may be essential for its biodegradation, the underlying processes have yet to be

288 This modified ISCO approach was coupled to biodegradation to further remove residual compounds by m

289 erial populations indicated that most of the biodegradation took place within the lower part of the c

290 and the impact of nutrient limitation on oil biodegradation under Arctic conditions.

291 esults showed that the influence of RC on NP biodegradation varied with different NP concentrations.

292 roles of abiotic processes vs growth-linked biodegradation vs cometabolism are unresolved, and the i

293 erobic polycyclic aromatic hydrocarbon (PAH) biodegradation was characterized by compound specific st

294 Biodegradation was evaluated in compost, anaerobic diges

295 Biodegradation was limited by low nutrient concentration

296 radation, and a previously unknown microbial biodegradation was predicted computationally.

297 has been proposed as an analog for sulfolane biodegradation, we found only a subset of the required g

298 remendous enrichment of genes related to oil biodegradation, which was consistent with the results fr

299 biodegradability of PyOM and deciphering if biodegradation will most likely proceed via cometabolism

300 r and stationary biofilms, and diffusion and biodegradation within the biofilms.