ライフサイエンスコーパス: bioremediation

1 e long-term stability of U(IV) products from bioremediation.

2 AHs, which constitutes a major bottleneck in bioremediation.

3 n terms of risks and effective coupling with bioremediation.

4 ated aromatics and may be useful for in situ bioremediation.

5 ration of PCBs and shed light on in situ PCB bioremediation.

6 pplications in bioenergy, bioproduction, and bioremediation.

7 structural or hydrodynamic properties during bioremediation.

8 biomass growth during stimulated subsurface bioremediation.

9 t has many applications, such as in chromate bioremediation.

10 minated soil when evaluating the efficacy of bioremediation.

11 t, suggesting the enzyme may be valuable for bioremediation.

12 in bioenergy production and in environmental bioremediation.

13 , S, and V all significantly decreased after bioremediation.

14 rocarbons with applications in environmental bioremediation.

15 ular approaches are being applied to enhance bioremediation.

16 la oneidensis MR-1, an important microbe for bioremediation.

17 g conditions associated with pathogenesis or bioremediation.

18 will improve their effectiveness in chromate bioremediation.

19 use in synthesis of chiral intermediates and bioremediation.

20 unds used in fields ranging from medicine to bioremediation.

21 nickel, suggesting potential application in bioremediation.

22 e environment and to be efficient agents for bioremediation.

23 are potentially useful for biocatalysis and bioremediation.

24 s and has potential uses in chemotherapy and bioremediation.

25 ise new strategies for biotransformation and bioremediation.

26 ive microbial populations or the progress of bioremediation.

27 ngineering improved microbes and enzymes for bioremediation.

28 l relevance to human health or environmental bioremediation.

29 ging as an approach to solve the problems of bioremediation.

30 rophic bacteria with SQR and PDO for sulfide bioremediation.

31 ed vegetable oil (EVO) amendment for uranium bioremediation.

32 rol phosphorus bioavailability and influence bioremediation.

33 ntial of this microalga for applications for bioremediation.

34 egraders asserting its importance for use in bioremediation.

35 e, forming adsorption-biodegradation coupled bioremediation.

36 ggesting that it has great potential for PCB bioremediation.

37 of these mechanisms for element recovery or bioremediation.

38 ts possible utility in energy production and bioremediation.

39 lications for optimizing chlorinated solvent bioremediation.

40 tu or in-reactor applications of cometabolic bioremediation.

41 many halogenated compounds and are used for bioremediation.

42 by natural or engineered processes, such as bioremediation.

43 tial application in metal biorecovery and/or bioremediation.

44 recycling(17), industrial fermentation(18), bioremediation(19) and human health(16,20).

45 to determine the compatibility with further bioremediation, a pilot scale treatment at a diesel-cont

46 t role of microbes in biofuel production and bioremediation, a thorough understanding of the impact o

47 s for generating mutant P450s with increased bioremediation abilities.

48 Additionally, engineered bioremediation activities also exhibit a biotic signatur

49 bacteria that are of interest for monitoring bioremediation activity.

50 lities and thus is of potential utility as a bioremediation agent.

51 eating acute organophosphate toxicity and as bioremediation agents.

52 rld applications in medicine, biotechnology, bioremediation and bioenergy.

53 library screening and protein engineering to bioremediation and biofuels production.

54 ing S. oneidensis as a platform organism for bioremediation and biotechnology, necessitating a comple

55 their beneficial natural product production, bioremediation and energy applications.

56 ir mechanism of action and potential uses in bioremediation and enzymatic synthesis.

57 ions in fields as varied as pest management, bioremediation and fine chemical production.

58 ne monooxygenases have enormous potential in bioremediation and for biotransformations producing bulk

59 ce in food sciences, environmental sciences, bioremediation and in understanding basic cellular proce

60 o exploit extremophiles and their enzymes in bioremediation and industry.

61 lobal biogeochemical processes and can guide bioremediation and medical treatments.

62 e environment will facilitate the control of bioremediation and other processes mediated by complex m

63 cations ranging from wastewater treatment to bioremediation and potential future use in biocatalysis

64 tions of GMOs in open systems, which include bioremediation and probiotics.

65 able isotope analysis to demonstrate in situ bioremediation and push-pull tests, in which isotopes ar

66 an important role in biogeochemical cycles, bioremediation and several bioenergy strategies, but the

67 ene transfer, with potential applications in bioremediation and synthetic biology.

68 l of Q is of great contemporary interest for bioremediation and the development of synthetic approach

69 ose potential range of applications includes bioremediation and the production of biofuels.

70 cesses that drive microbe-host interactions, bioremediation, and biogeochemistry.

71 appropriate water and fertilizer management, bioremediation, and change of land use to grow nonfood c

72 in biogeochemical metal cycling, subsurface bioremediation, and corrosion processes.

73 ing investigations of microbial communities, bioremediation, and human health.

74 es in order to address questions in ecology, bioremediation, and human health.

75 y unique role in medical, materials, energy, bioremediation, and synthetic biological research.

76 In all, culture AD14 is promising for bioremediation applications at sites cocontaminated with

77 croorganisms (GEMs) have shown potential for bioremediation applications in soil, groundwater, and ac

78 ults suggest that MerB could be utilized for bioremediation applications, but certain organolead and

79 atile bacterium with promising bioenergy and bioremediation applications, Shewanella oneidensis, in m

80 are promising developments for future marine bioremediation applications.

81 abolic potential of M. vanbaalenii PYR-1 for bioremediation applications.

82 y relevant to industrial biotechnologies and bioremediation applications.

83 s indicates enhanced performance compared to bioremediation approach that requires several months to

84 lopment of rational and effective engineered bioremediation approaches for sites contaminated with ch

85 may provide an untapped potential for future bioremediation approaches.

86 rtaining to genetically engineered microbial bioremediation are supported by laboratory-based experim

87 Bioremediation at chlorinated solvent sites often leads

88 will help facilitate the optimization of TCE-bioremediation at contaminated sites containing both TCE

89 consecutive years of acetate-enabled uranium bioremediation at the US Department of Energy's Rifle In

90 oneidensis, an important model organism for bioremediation because of its extraordinary abilities to

91 ortant for engineering applications, such as bioremediation, biocatalysis and microbial fuel cells.

92 s would create powerful new opportunities in bioremediation, bionanotechnology, and synthetic biology

93 mical processes and the potential for making bioremediation breakthroughs and illuminating the 'black

94 not only in the design of new inoculants in bioremediation but also in biodegradation assessments of

95 ent of electron acceptors as in contemporary bioremediation but also significantly shortens the remed

96 t is a widely accepted practice in oil-spill bioremediation but there is scant understanding of the s

97 urface environments as well as in subsurface bioremediation by oxidizing organic compounds with the r

98 erview is provided of the recent advances in bioremediation by utilizing rhizoremediation, protein en

99 ns like wastewater treatment, biosensors and bioremediation can be made possible with the help of MFC

100 irected evolution of a phosphotriesterase (a bioremediation catalyst) caged in GSBs and isolate a 20-

101 Live cultures can be used for bioremediation, chemical transformation (propene to prop

102 Within the context of bioremediation, chemotaxis may work to enhance bacterial

103 industrial biotechnologies in that, although bioremediation contractors must profit from the activity

104 tamination because the efficiency of in situ bioremediation depends on how effectively and rapidly U(

105 Bioremediation differs from other industrial biotechnolo

106 te, or UO2, is the preferable end-product of bioremediation due to its relatively high stability and

107 These findings suggest that anaerobic bioremediation (e.g., bioaugmentation) is a possible rem

108 organic carbon dose rates as key controls on bioremediation efficacy, and will enable future developm

109 h to fully address the competence of GEMs in bioremediation efforts is through long-term field releas

110 eductive dechlorination reaction relevant to bioremediation efforts with some of its closest homologs

111 role in mobilizing U, potentially affecting bioremediation efforts.

112 The use of enhanced in situ anaerobic bioremediation (EISB) and bioaugmentation in fractured b

113 arbon-contaminated soil with relatively high bioremediation end point were characterized by image ana

114 he role of soil microstructure on attainable bioremediation end points could be qualitatively assesse

115 -oxidizing microorganisms and their roles in bioremediation, energy recovery and global carbon cyclin

116 However, DHP fails as a bioremediation enzyme because, unlike HRP, it has an int

117 RP, DHP has been investigated as a potential bioremediation enzyme.

118 munities, to utilize microbes for bioenergy, bioremediation, etc.

119 arbon dose rates both significantly affected bioremediation extent and efficiency with lower minimum

120 Advances in bioremediation harness molecular, genetic, microbiology,

121 Bioremediation has historically been approached as a 'bl

122 as a contaminant, the potential for vanadium bioremediation has not been widely studied.

123 The use of chemotactic bacteria in bioremediation has the potential to increase access to,

124 Current research suggests that bioremediation has the potential to offer an additional

125 well as in valuable chemical production and bioremediation, has been explored.

126 hnology and many of the factors that control bioremediation have yet to be adequately understood.

127 many advantages over bacteria as agents for bioremediation; however, they typically lack the degrada

128 efforts (e.g., chemical oxidation, enhanced bioremediation) impacted dioxane attenuation.

129 taining heterogeneous information related to bioremediation in a framework that allows its query, adm

130 ides the first experimental demonstration of bioremediation in bauxite residue, identifying pH and or

131 g the margins of a selenite plume undergoing bioremediation in the presence of background sulfate.

132 ent of microbially driven pH neutralization (bioremediation) in alkaline tailings.

133 advances in our scientific understanding of bioremediation, in situ applications involving commercia

134 ium potentially important for biocontrol and bioremediation, in soil.

135 into the microbial ecology of in situ SCN(-) bioremediation involving autotrophic sulfur-oxidizing ba

136 non-specificity of conventional techniques, bioremediation is a promising alternative technology for

137 Bioremediation is an accepted technology for cleanup of

138 Microbial selenium (Se) bioremediation is based on conversion of water soluble,

139 Bioremediation is being increasingly seen as an effectiv

140 Once active bioremediation is halted, UO2 may be subsequently reoxid

141 As bacterial chromate bioremediation is limited by the toxicity of chromate, m

142 Bioremediation is one of the commonly applied remediatio

143 d that circumneutral pH, commonly applied in bioremediation, is not appropriate for gravitational sep

144 tively long history of research on oil-spill bioremediation, it remains an essentially empirical tech

145 damental questions related to global change, bioremediation, land use, human health, and ecological t

146 effective strategy for V removal, and that V bioremediation may be a viable technology.

147 tification of microorganisms associated with bioremediation may help increase accuracy that is dimini

148 to metal immobilization biotechnologies for bioremediation, metal and P biorecovery, and utilization

149 er is a key component of site assessment and bioremediation monitoring.

150 rk for studying the global properties of the bioremediation network.

151 ale membrane bioreactor (MBR) was tested for bioremediation of 1,2-dichloroethane (DCA) in groundwate

152 Bioremediation of alkaline tailings, based on fermentati

153 on due to their potential application in the bioremediation of anthropogenic polyhalogenated persiste

154 DCM to nonchlorinated products promises that bioremediation of CF plumes is feasible.

155 Subsurface biofilms are central to bioremediation of chemical contaminants in soil and grou

156 sms have several biotechnological uses, from bioremediation of chlorinated compounds, radionuclides,

157 Bioremediation of chlorinated ethenes via anaerobic redu

158 rtyi, an important bacterium involved in the bioremediation of chlorinated solvents, reveal homologou

159 ur findings is that in engineered or natural bioremediation of chloroethene-contaminated groundwater,

160 n the microbiological processes used for the bioremediation of co-mingled chlorinated solvents such a

161 BE can be degraded anaerobically which makes bioremediation of contaminated aquifers a potential solu

162 Geobacter species play important roles in bioremediation of contaminated environments and in elect

163 ntral to strategies for biocatalysis and the bioremediation of contaminated environments.

164 microalgae, showing their potential for the bioremediation of contaminated water.

165 range of biological processes, including the bioremediation of environmental contaminants.

166 ich has considerable implications toward the bioremediation of environmental pollutants.

167 cter species often play an important role in bioremediation of environments contaminated with metals

168 vestigate this possibility in the context of bioremediation of explosive residues, we generated trans

169 As methods pertinent to the intrinsic bioremediation of fuel hydrocarbons have become better e

170 analysis (CSIA) has been applied to monitor bioremediation of groundwater contaminants and provide i

171 Bioremediation of groundwater contaminated with chlorina

172 acteria play critical roles in environmental bioremediation of halogenated compounds.

173 akes it an attractive target for the in situ bioremediation of halogenated waste.

174 energy recovery in microbial fuel cells and bioremediation of heavy metals and radionuclides.

175 nonexhaustible electron acceptor for in situ bioremediation of hydrocarbon contaminated soil.

176 sphorus bioaccessibility is critical for the bioremediation of hydrocarbons in calcareous soils.

177 nsidered a potential agent for environmental bioremediation of industrial waste and a good colonizer

178 Adaptation of such pathways to the bioremediation of man-made pollutants such as polychlori

179 the importance of SRB-mediated reduction for bioremediation of metal ion contaminants, ongoing resear

180 Bioremediation of metals is still primarily a research p

181 pective use of engineered D. radiodurans for bioremediation of mixed wastes containing both radionucl

182 they can complement plant P450s and perform bioremediation of oil spills by the breakdown of alkanes

183 a useful tool for monitoring the progress of bioremediation of oil spills in the environment.

184 nding of hydrocarbon biodegradation and thus bioremediation of oil-polluted intertidal wetlands.

185 al for use in areas of biotechnology such as bioremediation of organic and inorganic pollutants and b

186 rient cycles of aquatic sediments and in the bioremediation of organic and metal contaminants in grou

187 t also suggests a strategy for promoting the bioremediation of organic contaminants in subsurface env

188 Bioremediation of organic pollutant contaminated soil in

189 s) is a common approach to achieving in situ bioremediation of organic pollutants (e.g., explosives).

190 , capable of extracting energy and promoting bioremediation of organic pollutants from sediments.

191 provide a generally applicable strategy for bioremediation of organic pollutants in soil.

192 ants makes them promising candidates for the bioremediation of organophosphorus compounds.

193 Here, we examine the potential for in situ bioremediation of OSPW AEOs by indigenous algae.

194 Study of intrinsic bioremediation of other prevalent contaminants, such as

195 s is one of the concerns associated with the bioremediation of PAH-contaminated soils.

196 vative PCM-F, have potential applications in bioremediation of pivalic acid found in sludge, in stere

197 specific synthesis, as well as catalysts for bioremediation of polluted areas.

198 rganism clearly has the potential for use in bioremediation of radioactive metals and in the generati

199 The use of white rot fungi (WRF) for bioremediation of recalcitrant trace organic contaminant

200 Bioremediation of sediments contaminated with commercial

201 have promising implications for sustainable bioremediation of sites contaminated with chlorinated be

202 taminant source) may be helpful in enhancing bioremediation of such contaminated sites.

203 results, the potential exists for intrinsic bioremediation of the oil plume in the deep-water column

204 n the product(s) of uranium reduction during bioremediation of the subsurface.

205 ing biocorrosion of metal infrastructure and bioremediation of toxic metal ions.

206 ron sulfide minerals produced during in situ bioremediation of U can serve as an oxygen scavenger to

207 ns about the long-term sustainability of the bioremediation of U-contaminated sites.

208 Despite its promise for the bioremediation of uranium contaminants, the biological m

209 llular mechanism that is of interest for the bioremediation of uranium-contaminated groundwater.

210 During subsurface bioremediation of uranium-contaminated sites, indigenous

211 UO2 is critical to the success of reductive bioremediation of uranium.

212 Bioremediation of vinyl chloride (VC) contamination in g

213 be evaluated as potential candidates for the bioremediation of wastewater and groundwater contaminate

214 gradation products and has the potential for bioremediation of xenobiotic compounds.

215 ucidation of the pathways for reduction (and bioremediation) of pollutants such as uranium (U) and ch

216 e elucidation of pathways for reduction (and bioremediation) of pollutants such as uranium and chromi

217 uide future exploitation of these enzymes in bioremediation or biocatalysis.

218 an important role in the environmental fate, bioremediation or biorecovery of Sr or other metals and

219 synthesis of novel biominerals and in metal bioremediation or biorecovery.

220 rategy used is one of engineered accelerated bioremediation or natural attenuation.

221 iated with PAH-contaminated soils and places bioremediation outcomes in a context relevant to human h

222 tified as a promising strategy for improving bioremediation performance.

223 communities, having direct implications for bioremediation potential and deposit-feeder nutrition.

224 ioaccessibility of PAHs to microorganisms or bioremediation potential in AC-amended soils.

225 ments may enhance the metabolic capacity and bioremediation potential of deposit-feeder microbial sys

226 Oxic sediments showed the greater bioremediation potential; however, the oxic-anoxic sedim

227 d biodiversity can play a direct role in the bioremediation process.

228 Applications of SIP to biodegradation and bioremediation processes are still in their infancy.

229 oved model can help to better design in situ bioremediation processes for groundwater contaminated by

230 unparalleled interest in new passive in situ bioremediation processes for sites contaminated with nuc

231 Although both bioremediation processes significantly removed PAHs from

232 and to better define optimal conditions for bioremediation processes.

233 as plant site before and after two simulated bioremediation processes: a sequencing batch bioreactor

234 es important to carbon and nutrient cycling, bioremediation, production of secondary metabolites, and

235 predicting the stability and mobility of Se bioremediation products and understanding of Se biogeoch

236 formation can be applied to improve the fuel bioremediation properties of bacteria.

237 st in the development of novel monitoring or bioremediation protocols, as well as in understanding th

238 Bioremediation provides the potential for cost-effective

239 ic fungi into soil for biological control or bioremediation purposes.

240 tral and founding community effects during a bioremediation-related organic carbon disturbance.

241 omyces enzymes in biosynthetic processes and bioremediation requires identification and engineering o

242 These findings are relevant for bioremediation scenarios that require an optimized outre

243 works in soils, extending their potential in bioremediation scenarios.

244 icroorganisms and formation of UO2 solids in bioremediation sites.

245 models may be able to predict the outcome of bioremediation strategies and aid in the development of

246 lts could guide the development of effective bioremediation strategies and efficient lignocellulosic

247 have implications for selecting 1,4-dioxane bioremediation strategies at sites where chlorinated sol

248 Chemotaxis has the potential to improve bioremediation strategies by enhancing the transport of

249 e efforts allow the design of more realistic bioremediation strategies that complement natural proces

250 production has stimulated the development of bioremediation strategies using Deinococcus radiodurans,

251 We evaluated which bioremediation strategies were most effective for degrad

252 Ultimately, bioremediation strategies, in the studies reviewed, were

253 ts has prompted the development of effective bioremediation strategies.

254 d detoxification reactant may improve future bioremediation strategies.

255 s and also to enhance the effectiveness of U bioremediation strategies.

256 demonstrate a potential algal-based in situ bioremediation strategy for OSPW AEOs and uncover a link

257 uranium phosphate precipitation was a viable bioremediation strategy.

258 neidensis is an important model organism for bioremediation studies because of its diverse respirator

259 neidensis is an important model organism for bioremediation studies because of its diverse respirator

260 potentially for the preparation of novel PAH bioremediation systems.

261 protein production, or on new biocontrol and bioremediation technologies based on Aspergillus species

262 has been a dramatic maturation of intrinsic bioremediation technologies.

263 ate in the environment and the efficiency of bioremediation technologies.

264 essential information for the development of bioremediation technology.

265 ring phases, such as the mineral products of bioremediation, that may otherwise be transported away f

266 Bioremediation, the exploitation of biological catalysts

267 enes at a contaminated field site undergoing bioremediation, this study demonstrates how CSIA of ethe

268 ngs have implications for the feasibility of bioremediation to achieve cleanup levels for PAHs in soi

269 iety of functions from sensing molecules and bioremediation to energy production and biomedicine.

270 ical potential for applications ranging from bioremediation to stereospecific synthesis of C2-C5 carb

271 ed by ToMO invites applications ranging from bioremediation to the regio- and enantiospecific oxidati

272 ion in light of its possible employment as a bioremediation tool.

273 als, biorenewable chemicals, fuel resources, bioremediation tools and general tools for recombinant t

274 ted on their possible use as biomonitors and bioremediation tools.

275 cochemical remediation technologies, in situ bioremediation treatment based on Dehalococcoides mccart

276 derstanding of the fate of pollutants during bioremediation treatments is important for establishment

277 to use this theoretical framework to select bioremediation treatments that specifically encourage th

278 entrations of degrader organisms reported in bioremediation trials.

279 Bioremediation uses soil microorganisms to degrade polyc

280 To quantify in situ bioremediation using compound specific isotope analysis

281 This study also suggests that bioremediation using microbial consortia is a valid opti

282 (often gypsum), presenting opportunities for bioremediation using microorganisms.

283 ale microbial ecology context to in situ RDX bioremediation using modern sequencing techniques that w

284 In situ bioremediation via the generation of microbially reducin

285 and agro-biotechnological processes such as bioremediation, wastewater treatment, plant growth promo

286 r laboratories working in biodegradation and bioremediation, which need to maintain and consult publi

287 in biological control of plant diseases and bioremediation, while some strains are plant pathogens o

288 gated the potential synergy between UTES and bioremediation with batch experiments to simulate the ef

289 s of the subsurface community during uranium bioremediation with environmental transcriptomic and pro

290 Bioremediation with microorganisms is an attractive alte

291 piration of PCBs and facilitates in situ PCB-bioremediation with strain JNA.

292 ly reduced in 89% of treated soils following bioremediation, with a mean degradation of 44% across th

293 lysis, biotransformation, biodegradation and bioremediation would be an invaluable tool for academic