ライフサイエンスコーパス: bioremediation

1 s and this process has been employed in soil bioremediation.

2 egraders asserting its importance for use in bioremediation.

3 ggesting that it has great potential for PCB bioremediation.

4 of these mechanisms for element recovery or bioremediation.

5 ts possible utility in energy production and bioremediation.

6 lications for optimizing chlorinated solvent bioremediation.

7 tu or in-reactor applications of cometabolic bioremediation.

8 many halogenated compounds and are used for bioremediation.

9 by natural or engineered processes, such as bioremediation.

10 tial application in metal biorecovery and/or bioremediation.

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

12 AHs, which constitutes a major bottleneck in bioremediation.

13 n terms of risks and effective coupling with bioremediation.

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

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

16 I)-induced enhancement and benefit of Cr(VI) bioremediation.

17 pplications in bioenergy, bioproduction, and bioremediation.

18 for Se and Te immobilization, biorecovery or bioremediation.

19 structural or hydrodynamic properties during bioremediation.

20 biomass growth during stimulated subsurface bioremediation.

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

22 minated soil when evaluating the efficacy of bioremediation.

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

24 nd animals, food matrices, and environmental bioremediation.

25 in bioenergy production and in environmental bioremediation.

26 rocarbons with applications in environmental bioremediation.

27 ular approaches are being applied to enhance bioremediation.

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

29 g conditions associated with pathogenesis or bioremediation.

30 an imperative prerequisite for informed EDTA bioremediation.

31 will improve their effectiveness in chromate bioremediation.

32 use in synthesis of chiral intermediates and bioremediation.

33 unds used in fields ranging from medicine to bioremediation.

34 nickel, suggesting potential application in bioremediation.

35 e environment and to be efficient agents for bioremediation.

36 are potentially useful for biocatalysis and bioremediation.

37 s and has potential uses in chemotherapy and bioremediation.

38 se, biogeochemical cycling, agriculture, and bioremediation.

39 e, forming adsorption-biodegradation coupled bioremediation.

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

41 rophic bacteria with SQR and PDO for sulfide bioremediation.

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

43 rol phosphorus bioavailability and influence bioremediation.

44 ntial of this microalga for applications for bioremediation.

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

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

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

48 Additionally, engineered bioremediation activities also exhibit a biotic signatur

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

50 eating acute organophosphate toxicity and as bioremediation agents.

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

67 n research to elucidate the level of natural bioremediation and the exploitation of bacterial degrada

68 the Devosia spp. for conferring adaptation, bioremediation and the potential to utilize a wide range

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

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

71 ns to the ever-emerging fields of bioenergy, bioremediation, and biosensing.

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

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

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

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

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

77 lanetary sciences, environmental monitoring, bioremediation, and the nuclear fuel cycle.

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

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

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

81 e already a strong presence in various other bioremediation applications.

82 are promising developments for future marine bioremediation applications.

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

84 peraccumulators are promising candidates for bioremediation applications.

85 y relevant to industrial biotechnologies and bioremediation applications.

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

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

88 may provide an untapped potential for future bioremediation approaches.

89 Bioremediation at chlorinated solvent sites often leads

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

91 al dechlorinating communities for successful bioremediation at field sites.

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

93 ng brings into question the effectiveness of bioremediation because NCU(IV) species are expected to b

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

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

96 Diverse processes-e.g. bioremediation, biofertilization, and microbial drug del

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

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

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

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

101 ss indigenous soil microbial communities for bioremediation by flooding local populations with catabo

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

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

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

105 ing of organisms with improved nutrition and bioremediation capacity.

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

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

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

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

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

111 he fields of biofuels, wastewater treatment, bioremediation, desalination, and biosensing.

112 Bioremediation differs from other industrial biotechnolo

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

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

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

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

117 chloroform and chloroethenes often confounds bioremediation efforts.

118 role in mobilizing U, potentially affecting bioremediation efforts.

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

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

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

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

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

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

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

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

127 answer to the long-standing question of why bioremediation frequently stalls at cis-DCE.

128 The bioremediation fungi has received attention and reported

129 Advances in bioremediation harness molecular, genetic, microbiology,

130 Trichloroethene (TCE) bioremediation has been demonstrated at field sites usin

131 Uranium (U) in situ bioremediation has been investigated as a cost-effective

132 Bioremediation has historically been approached as a 'bl

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

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

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

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

137 red natural attenuation (MNA) and engineered bioremediation have been recognized as effective and cos

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

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

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

141 nsidered a prime biocatalyst for groundwater bioremediation in DWTPs.

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

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

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

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

146 Bioremediation is a low-cost approach for crude oil spil

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

148 Bioremediation is an accepted technology for cleanup of

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

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

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

152 Bioremediation is one of the commonly applied remediatio

153 a putative nitrilase, enzyme used in nitrile bioremediation, is here reported for the first time for

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

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

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

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

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

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

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

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

162 Bioremediation of alkaline tailings, based on fermentati

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

164 -hydroxylating Rieske oxygenases involved in bioremediation of aromatic pollutants in the environment

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

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

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

168 Bioremediation of chlorinated ethenes via anaerobic redu

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

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

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

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

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

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

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

176 nding of molecular mechanism involved in the bioremediation of EDTA and the metabolism of secondary a

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

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

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

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

181 Bioremediation of groundwater contaminated with chlorina

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

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

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

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

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

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

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

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

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

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

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

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

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

195 Bioremediation of organic pollutant contaminated soil in

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

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

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

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

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

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

202 g and critical analysis of the literature on bioremediation of products from the oil sand and shale (

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

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

205 Bioremediation of sediments contaminated with commercial

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

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

208 our understanding of natural attenuation and bioremediation of the explosive NTO.

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

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

211 tive candidate for further studies involving bioremediation of these radionuclides.

212 ry and engineering of pathways important for bioremediation of toxic and radioactive metals and under

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

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

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

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

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

218 During subsurface bioremediation of uranium-contaminated sites, indigenous

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

220 Bioremediation of vinyl chloride (VC) contamination in g

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

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

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

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

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

226 rom aqueous solutions such as those found in bioremediation or biomining processes.

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

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

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

230 tified as a promising strategy for improving bioremediation performance.

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

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

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

234 toxins and are best characterized for their bioremediation potential.

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

236 l spill conditions, and in improving current bioremediation practices.

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

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

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

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

241 Although both bioremediation processes significantly removed PAHs from

242 and to better define optimal conditions for bioremediation processes.

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

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

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

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

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

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

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

250 Its use in bioremediation requires knowledge of its BAM-catabolic p

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

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

253 icroorganisms and formation of UO2 solids in bioremediation sites.

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

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

256 used by arsenic and can inform the design of bioremediation strategies at co-contaminated sites.

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

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

259 ts into the environmental fate and potential bioremediation strategies of these notorious contaminant

260 oss short distances and may lead to improved bioremediation strategies or advance biogeochemical mode

261 We evaluated which bioremediation strategies were most effective for degrad

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

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

264 ts has prompted the development of effective bioremediation strategies.

265 d detoxification reactant may improve future bioremediation strategies.

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

267 uranium phosphate precipitation was a viable bioremediation strategy.

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

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

270 h organic content as a naturally sustainable bioremediation system.

271 However, compared to bacteria-based bioremediation systems, plant life cycle is long and gro

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

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

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

275 Bioremediation, the exploitation of biological catalysts

276 ovel application of Bayesian optimization in bioremediation, this experimental design approach has pr

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

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

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

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

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

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

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

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

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

286 entrations of degrader organisms reported in bioremediation trials.

287 Bioremediation uses soil microorganisms to degrade polyc

288 To quantify in situ bioremediation using compound specific isotope analysis

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

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

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

292 In situ bioremediation via the generation of microbially reducin

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

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

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

296 Fe(0) is often used during TCE bioremediation with Dehalococcoides mccartyi to establis

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

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

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

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