ライフサイエンスコーパス: amend

1 bon (OC) amount present (either intrinsic or amended).

2 One plot was amended 16 years ago with process sand, organic matter,

3 and seeded (fully treated), another plot was amended 16 years ago with process sand, organic matter,

4 We amended a shallow fast-flowing uranium (U) contaminated

5 Their synthesis was made possible by amending a previously reported synthesis of ketomethylen

6 An important question is the capacity of the amended AC after prolonged exposure in the field.

7 ypothalamic GnRH decline, and GnRH treatment amends ageing-impaired neurogenesis and decelerates agei

8 ainfall can mobilize hormones from biosolids-amended agricultural fields, directly to surface waters

9 insights into GB1:IgG complex structure that amend and revise the current model available from studie

10 of perfluoroalkyl acids (PFAAs) in biosolids-amended and aqueous film-forming foam (AFFF)-impacted so

11 fall simulation tests were then performed on amended and control plots.

12 determine the contents of BC (BCHyPy) in the amended and control soils, while the hydrocarbon composi

13 otroph co-culture experiments under nutrient-amended and natural seawater conditions, and show that i

14 The document was amended and the prioritizations were set at a NIH-organi

15 The control and amended and/or revegetated treatments were sampled from

16 ial to near-complete genomes from an acetate-amended aquifer.

17 At the end of the experiment, all triclosan-amended Archaea communities had diverged from the contro

18 rfactants were part of a chemical mixture or amended as individual additives.

19 Seven sorbents amended at a level of 0.2 x soil total organic carbon (0

20 er (NOM) on Pu sorption, Pu(IV) and (V) were amended at environmentally relevant concentrations (10(-

21 a redox-active precipitate formed in the ZVI-amended biocathode, which sorbed to the electrode and/or

22 obacteria and fewer Bacteroidetes in the ZVI-amended biocathode.

23 Furthermore, CH4 production by the ZVI-amended biocathodes remained elevated throughout three s

24 e archaeal community in the ZVI-free and ZVI-amended biocathodes.

25 trations observed in lettuce grown in a soil amended (biosolids:soil dry weight ratio of 1:10) with P

26 ns in the pore water of the activated carbon amended caps were 3-4 orders of magnitude lower (0.04 +/

27 numbers of V(5+)-reducing cells in vanadium-amended columns compared to controls.

28 dramatic and differential shifts in the oil-amended communities that included blooms of recognized H

29 re observed in adult midges emerging from AC amended compared to unamended sediments.

30 Naphtha-amended cultures harbored a blend of these two archaeal

31 Institution-specific internal reviews should amend current protocols for antibiotic prophylaxis to re

32 blication of the IES trial, the protocol was amended (Dec 13, 2004).

33 m 5 m depth in the central North Pacific and amended duplicate 20 liter polycarbonate carboys with ni

34 or inclusion of teenagers or young adults or amended during the study period, participation rates for

35 MR of the proposed calcaripeptide B has been amended during this synthetic study.

36 collected from several full-scale biosolids-amended farm fields.

37 t edible crops grown in soils conventionally amended for nutrients with biosolids (that are not impac

38 The study was amended for patient intolerance to sunitinib (37.5 mg),

39 biotransformation, with 10% (mol/mol) of the amended FtTAoS accounted for in FtS, FtCA, and PFCA prod

40 s of Cr(H(2)O)(6)(2+), suspensions of Fe(II)-amended goethite, and suspensions of Fe(II)-amended hema

41 n a column percolated with sulfidic, nitrate amended groundwater.

42 -amended goethite, and suspensions of Fe(II)-amended hematite.

43 Transformation of amended hormones in autoclaved sediments was markedly sl

44 s can blur these distinctions, being able to amend how host cells acquire nutrients from their enviro

45 ia were promulgated in 1994 and subsequently amended in 2008 and 2011 to promote organ transplantatio

46 This statement has now been amended in all versions of the Letter.

47 n of a suite of metabolites only in the fuel-amended incubations confirmed that alkylated benzene hyd

48 he formation of marine oil snow (MOS) in oil-amended incubations was consistent with its formation du

49 The amended insulin-glucose ratio correctly identified 48 of

50 The amended insulin-glucose ratio showed improved diagnostic

51 Glucose, insulin, C-peptide, and the amended insulin-glucose ratio were measured during and a

52 Use of an "amended" insulin-glucose ratio that accounts for the nor

53 nd reflection of change over time codes were amended, integrated and collapsed as appropriate through

54 arlier, which may provide the opportunity to amend intervention strategies.

55 We propose an amended life-cycle in which wind-dispersed, insect-vecto

56 Surface-applied roxarsone-amended litter does not influence deep aquifer arsenic c

57 Due to continued soil accumulation, arsenic-amended litter use as fertilizer is thought to be unsust

58 PAH availability overall was measured in PAC-amended, live soil.

59 3 and (Cax Sr1-x )CO3 when incubated in urea-amended media and equivalent CaCl2 and SrCl2 concentrati

60 When we examined the carbon-amended microcosm sediments stained with both a strain C

61 ne loss was observed in nitrate- and sulfate-amended microcosms and in microcosms established to prom

62 s longer in oleate- and EVO- than in ethanol-amended microcosms, indicating that acetate-utilizing me

63 ent of VASP to form tetramers and provide an amended model of processive VASP-mediated actin assembly

64 noxic Fe(II)-rich nutrient solution, a U(VI) amended nutrient solution was added to the system for an

65 chronic lymphocytic leukaemia, the study was amended on Dec 9, 2009, to change cycle 1 for group B wh

66 Inclusion criteria were amended on Feb 25, 2010, to include patients with stage

67 cessibility (IVBA) of lead (Pb) in phosphate-amended Pb-contaminated soil was assessed using a variet

68 results revealed that olive fruits of OMW-RP amended plants had higher contents of polyphenols and ma

69 itrate and ammonium, were highest in topsoil-amended plots, with increases in denitrification potenti

70 Data demonstrates that carbonation in BCA-amended reactors remained limited by CO2 supply, implyin

71 ls several unexpected findings, including an amended registry of the surface on the bulk and strontiu

72 compared to those measured by depositing Pu amended resin beads on the filament.

73 .1 x 10(-3) m(2) E(-1), and the rate in MeHg amended samples was 9.3 x 10(-3) m(2) E(-1).

74 rly correlated with PBDE burdens, but sludge-amended samples were significantly delta(15)N enriched.

75 enhanced TOrC biodegradation and (2) biochar-amended sand bearing DOC-cultivated biofilms would achie

76 gher than that of E. coli K12 in all biochar-amended sand columns.

77 ort-term toxicity assays with homogenized Ni-amended sediment (i.e., standard sediment toxicity tests

78 sediment and biota, and (3) activated carbon amended sediment and biota.

79 ate was observed in any of the other oxidant-amended sediment suspensions.

80 Desorption of As from nonlactate-amended sediment was negligible with little change in se

81 1.7 mol % of 17beta-E2 formed in 17alpha-E2 amended sediments and peak concentrations of approximate

82 e physicochemistry and toxicity of anoxic Cu-amended sediments changed as they aged (i.e., naturally

83 al food supply, exposure to untreated and AC-amended sediments resulted in similar reduction of weigh

84 phthalene stimulated nitrogenase activity in amended sediments, as detected using the acetylene reduc

85 , soot, natural coastal sediments, and SWCNT-amended sediments.

86 ducing phylotypes more common in the sulfate-amended sediments.

87 of predaceous ground spiders from the sludge-amended site.

88 itation limits in vegetation from the sludge-amended site.

89 sities in the unamended in comparison to the amended sites and hierarchical clustering separated the

90 ant separation of the untreated site and the amended sites in both sampling years.

91 tering separated the unamended site from the amended sites.

92 brates with the greatest contact with sludge-amended soil (e.g., summation operator3-7PBDE of 10 300

93 BDE-209 burdens in sludge-amended soil and earthworms were 7500 +/- 2800 mug/kg TO

94 ts of crops grown in the municipal biosolids-amended soil and in the control soil were less than 25 n

95 s that influence Cu extractability in CuO NP-amended soil and suggest that a time-dependent series of

96 on of metal adsorption edges on the biosolid-amended soil and the soil sample showed that Cu, Ni, and

97 and shoots, dried ground S. pinnata, and the amended soil at post-plant, we demonstrate that Se-enric

98 Ag2S was the main species in the sludge and amended soil before and after plant culture.

99 ll increase metals retention in the biosolid-amended soil by providing reactive organic matter and ir

100 ene passive sampling devices immersed in ADB-amended soil coincident with exposed worms.

101 of silver nanoparticles (Ag-NPs) in a sludge-amended soil cultivated with monocot (Wheat) and dicot (

102 ct ratios (TERs, the bioaccessibility in the amended soil divided by the bioaccessibility in the untr

103 Biosolid-amended soil exhibited increased concentrations of diPAP

104 perfluoroalkyl acids (PFAAs) from biosolids-amended soil has been identified as a potential pathway

105 namic Plant Uptake (DPU) model and Biosolids-amended Soil Level IV (BASL4) model to predict the conce

106 s and class 1 integrons in wastewater solids-amended soil microcosms.

107 s in the tissue of plants grown in biosolids-amended soil under a number of exposure scenarios.

108 er frequency of resistant bacteria in manure-amended soil was attributable to enrichment of resident

109 pon) from an industrially impacted biosolids-amended soil, a municipal biosolids-amended soil, and a

110 grown in an industrially impacted biosolids-amended soil, a municipal biosolids-amended soil, and a

111 rol soil, an industrially impacted biosolids-amended soil, a municipal biosolids-amended soil, and tw

112 iosolids-amended soil, a municipal biosolids-amended soil, and a control soil was measured.

113 iosolids-amended soil, a municipal biosolids-amended soil, and a control soil.

114 iosolids-amended soil, a municipal biosolids-amended soil, and two AFFF-impacted soils) was measured.

115 dominant role in Ni binding in the biosolid-amended soil, it was of lesser importance for Cu and Zn.

116 ance of Pseudomonas spp. increased in manure-amended soil.

117 ion of copper, nickel and zinc in a biosolid-amended soil.

118 nd respiration rates were highest in the GAC amended soil.

119 gene copy numbers in unamended, PAC-, or GAC-amended soil.

120 Amending soil with biochar (pyrolized biomass) is sugges

121 We examined the effects of amending soil with biosolids produced from a pilot-scale

122 Amending soil with phosphoric acid or rock phosphate res

123 of -3.5) and for sul1 and sul2 in dry-stack-amended soils (logarithmic decay coefficients of -0.54 a

124 To test, we incubated nano-TiO2-amended soils across a range of water potentials for 288

125 f extractable PAHs increased markedly in the amended soils and decreased with time from 153 to 78 ng

126 emissions) originating from the surface 1 cm amended soils and decreasing with depth.

127 at cause N2O emission suppression in biochar-amended soils are still poorly understood.

128 tected in reference site samples, but sludge-amended soils contained 17 600 +/- 2330 mug/kg summation

129 the bioaccumulation of PFAAs from biosolids-amended soils depends strongly on PFAA concentrations, s

130 he first 11 days, and lower than in the salt-amended soils for at least 28 d.

131 nded soils was higher than in the micrometer-amended soils for at least the first 11 days, and lower

132 CuO-amended soils were similar, but the salt-amended soils had lower pH for at least 14 d, and higher

133 rrence and fate of nitrosamines in biosolids-amended soils in the context of crop and drinking water

134 th time (maximum -5.20), whereas in the salt-amended soils it was initially high (maximum -4.80) and

135 h reclaimed wastewater or grown in biosolids-amended soils may take up pharmaceuticals and personal c

136 detrimental effects on soil microbiology, AC-amended soils retained the potential to biodegrade PAHs,

137 The Cu2+ activity in the nano-amended soils was higher than in the micrometer-amended

138 ors (BSAFs) for worms exposed to ADB- and CB-amended soils were comparable after 28 d.

139 issolved Ca and Mg concentrations in the CuO-amended soils were similar, but the salt-amended soils h

140 In all of the phosphate amended soils, Pb RBA decreased compared to that in untr

141 In the CuO-amended soils, the log Cu2+ activity was initially low (

142 re monitored following exposure to biosolids-amended soils.

143 on nonionic detergent found in sewage sludge amended soils.

144 and following a lag (13 days) for dry-stack-amended soils.

145 he long-term stability of metals in biosolid-amended soils.

146 take of PPCPs into plants grown in biosolids-amended soils.

147 oorganisms or bioremediation potential in AC-amended soils.

148 cluding organic fragments, of the sludge and amended soils.

149 DIET may be an important consideration when amending soils with biochar and can help explain why bio

150 Amending soils with Fe(II) at field concentrations stimu

151 Amending soils with Se-hyperaccumulator plant derived so

152 race organic contaminants (TOrCs) in biochar-amended stormwater biofilters.

153 In E1-amended systems, E1 transformed to E2 with preferential

154 char functioning in fire-impacted or biochar-amended systems.

155 showed full retention of (99m)Tc in acetate amended systems.

156 We amend the canonical model and demonstrate several conseq

157 To overcome this issue, we amend the formulation in CFP, so as to account for atomi

158 parasite cultures with exogenous acetate can amend the lytic cycle of the glucose transport mutant.

159 and in reading session 3, the readers could amend the scores assigned during reading session 2.

160 ecelerating the solvent evaporation does not amend the superlattice symmetry, but improves the superl

161 ression-related toxic effects; therefore, we amended the lenalidomide dose to 25 mg per day for 5 day

162 Hence, amending the current Japan-Philippines Economic Partners

163 By amending the current model, this study advances our unde

164 When amending the model with the known three-dimensional stru

165 The change required amending the protocol at 14 sites to preserve internal v

166 We may amend these approaches to include emergency department v

167 We now amend this view by showing that inhibitory GABA-glyciner

168 In addition, exosomes can be amended through their parental cells to express a target

169 l analysis plan for the primary endpoint was amended to a combined analysis of cohorts 1 and 2 (inste

170 2008, in response to new data, the trial was amended to a prospectively stratified design, restrictin

171 erved declining event rate, the protocol was amended to a time-based analysis.

172 induction group was closed and the study was amended to a two-arm study.

173 The fluid mosaic model has recently been amended to account for the existence of membrane domains

174 On May 30, 2012, the study protocol was amended to allow crossover from control to trastuzumab e

175 The protocol was amended to allow patients in the investigator's choice g

176 On Sept 12, 2012, the study protocol was amended to allow patients with disease progression to cr

177 Subsequently, the protocol was amended to assess OS by unadjusted log-rank test after a

178 enrollment of 252 patients, the protocol was amended to continue with a three-arm design (1:1:6 ratio

179 Drug laws need to be amended to ensure the safety and effectiveness of medici

180 ibrinolytic therapy with bolus tenecteplase (amended to half dose in patients >/=75 years of age), cl

181 As such, the method of administration was amended to have a maximum infusion time of 60 minutes an

182 The protocol was subsequently amended to include a 60-week safety follow-up, to allow

183 or the trial ACOSOG Z1031B, the protocol was amended to include a tumor Ki67 determination after 2 to

184 On April 6, 2011, the protocol was amended to include three additional patients in the IGF-

185 ion of the planned accrual, the protocol was amended to introduce a third arm with rituximab alone.

186 fluency theory of aesthetic pleasure can be amended to meet the requirements of the framework.

187 OG PS of 2, any histology at first and later amended to nonsquamous only, no prior chemotherapy, and

188 Both studies were amended to remove rituximab, but two of three additional

189 days for four cycles, until the protocol was amended to six cycles.

190 rmulations, PFASs, and ethylene glycols were amended to the growth medium of a D. mccartyi-containing

191 Lag times of 37 days (sulfate amended) to more than 100 days (methanogenic) were obser

192 of an Alteromonas-like population in the DSW-amended treatment after 12 h, relative to the control.

193 bacter) were detected in the revegetated and amended treatment.

194 ammonia-oxidizing bacteria (AOB) in the DMPP-amended treatments.

195 e trial designs use interim data analysis to amend trials, and have been recognized for more than a d

196 We amended two sediments (Dow and Ocoee) with Cu, incubated

197 The decision to introduce or amend vaccination programmes is routinely based on mathe

198 and acetic acid were applied to differently amended vineyard soils.

199 Columns amended with >10% alfalfa removed significantly more sul

200 noxic slurry incubations with lake sediments amended with (13)C-labeled methane and naturally abundan

201 nts were grown in 125 mL jars of vermiculite amended with 0 or 40 mg of C(60) fullerenes.

202 eta-cyclodextrin (HPCD) extractions in soils amended with 0, 0.1, 1, and 5% (dry wt. soil) activated

203 dane (2150 ng/g) and DDx (118 ng/g) that was amended with 0, 500, 1000, or 5000 mg/kg MWCNT or C60.

204 his end, a nonpolluted agricultural soil was amended with 0.5, 2, and 5% of the following four amendm

205 ieved complete DCM degradation in microcosms amended with 10 mM bicarbonate.

206 When amended with 10 mM lactate and 0.11 mM PCE, aqueous samp

207 In the culture medium BG-11 amended with 250 muM Ca and 50 or 250 muM Sr and Ba, G.

208 Prior to planting, the jars were amended with 40 mL solution containing 100 ng/mL of p,p'

209 usly exposed (to triclosan) communities were amended with 5, 50, and 500 mg/kg of triclosan, correspo

210 standard soil toxicity tests-in three soils amended with 500 mg/kg Cu as nanometer-sized CuO (nano),

211 nts were grown in 125-mL jars of vermiculite amended with 500 or 2000 mg/L of bulk or NP Ag; ion cont

212 hworms ( Eisenia fetida ) to artificial soil amended with a Class B anaerobically digested biosolid (

213 eriod of conditioning with groundwater, were amended with a mixture of groundwater, soluble U(VI), an

214 ng Mine Humboldt Smelter Superfund site when amended with a range of compost concentrations.

215 ns, coastal bacterioplankton microcosms were amended with a single PA model compound, i.e. putrescine

216 of sediment in artificial groundwater media amended with acetate were probed by repeated injection o

217 +0.1 V vs. Ag/AgCl using domestic wastewater amended with acetate.

218 e most dramatic result was observed for caps amended with activated carbon at a dose of 2% by dry wei

219 Experiments amended with AFFF-derived PFASs and perfluoroalkyl acids

220 stribution of Ag species in marine sediments amended with AgNP-citrate, AgNP-PVP, and AgNO3 was AgCl

221 In microcosms amended with alginate particles and the proficient algin

222 late occurred under colonies growing on agar amended with all the test manganese oxides after growth

223 the compounds in soil and medium microcosms amended with an aqueous film-forming foam (AFFF) solutio

224 and ammonia (NH(3)) emissions when soil was amended with anaerobically digested dairy manure slurry

225 This study demonstrates that RC wood chips amended with antimicrobial compounds show promising appl

226 Alkaline brucite slurries were amended with BCA and supplied with 10% CO2 gas while aqu

227 articular, black carbon emissions from soils amended with biochar may counteract the negative emissio

228 remove nanoparticulate Ag from a field soil amended with biosolids contaminated with engineered silv

229 s (Falco sparverius) at an experimental site amended with biosolids for the previous 7 years.

230 Treatments consisted of soils amended with biosolids generated with (1) Ag, ZnO, and T

231 Soils were amended with biosolids to simulate 20 years of metal loa

232 sulfate reduction were found in incubations amended with camelina-JP5 [(57.2 +/- 2.2)-(80.8 +/- 8.1)

233 significant retention of Sb (89-98%) in soil amended with CFH-12 (2%) mixed with limestone (1%) compa

234 An obese-associated microbiome was amended with Christensenella minuta, a cultured member o

235 ds present in aqueous extracts from the sand amended with CuO (-27.0 mV) and ZnO (-10.0 mV) NPs was r

236 In the second experiment comparing seawater amended with cyanobacteria- and diatom-derived DOM, meta

237 t experiment comparing seawater and seawater amended with diatom-derived DOM, metatranscriptomes reve

238 sand and two agriculturally important soils amended with different concentrations of biochar, in com

239 um of salinities in an estuary and were each amended with different forms of mercuric sulfides: disso

240 Red cedar wood chips (RC) were amended with different loadings of either 3-(trihydroxys

241 trations (20, 50 and 500 mg/Kg) in sediments amended with different percentage of rice straw biochar

242 In slurries amended with dissolved and nano-HgS, mercury was mainly

243 tivity), net MeHg production in the slurries amended with dissolved Hg was greater than in slurries a

244 Silencing BtPGRP with artificial media amended with dsRNA led to reduced expression of a gene e

245 Biofilms were amended with either (15)NH4(+) or deuterium oxide ((2)H2

246 a choice between paired sugar water feeders amended with either a xenobiotic or solvent only (contro

247 nts were cultivated to full maturity in soil amended with either nCeO2 or nZnO at 0, 400, and 800 mg/

248 d by municipal secondary wastewater effluent amended with elevated Br(-) and I(-) after disinfection

249 dy U(VI) reduction in contaminated sediments amended with emulsified vegetable oil (EVO).

250 lations estimated that an infiltration basin amended with F300-AC or MCG-biochar could obtain sorptio

251 The sorption capacity of soils amended with Fe(0) (2%) increased steadily up to 72% ove

252 umulation in the heavy soil fraction in soil amended with fine-sized (<0.2 mm) compared with coarse-s

253 from a seawater-compensated ballast tank was amended with fuel from the same ship or with refinery fr

254 howed lower activity in cells grown in media amended with glucose rather than glycerol.

255 cus were grown on modified Czapek-Dox medium amended with glycerol 2-phosphate (G2P) as sole P source

256 nicus grew in 5 mM Pb(NO3)2-containing media amended with glycerol 2-phosphate (G2P) or phytic acid (

257 of Se in broccoli and carrots grown in soils amended with ground shoots of the Se-hyperaccumulator St

258 a field lysimeter containing a glass pellet amended with high-level nuclear waste for 24 years.

259 Sediment from an unpolluted site was amended with increasing levels of AC, placed in trays an

260 Furthermore, one-week bottle incubations amended with inorganic nutrients and carbon substrates (

261 ieved by injecting site groundwater (6000 L) amended with KTR9 cells (10(8) cells mL(-1)) and low car

262 rest types yielded consistent results: soils amended with leaf tissue switched faster from negative P

263 ended with stalks had a higher PE than those amended with leaf.

264 e propose an MEOR technology, in which water amended with light hydrocarbon below the solubility limi

265 Exponential decay of gull marker in sand amended with live Catellicoccus marimammalium suggested

266 ells) was performed by injecting groundwater amended with low (<1 mM fructose) or high (>15 mM fructo

267 over time the Bacteria communities that were amended with lower concentrations of triclosan (5 mg/kg

268 d ( approximately 80%) in settling particles amended with molybdate, demonstrating the prominent role

269 (Methanosaetaceae) were enriched in cultures amended with n-alkanes, whereas hydrogenotrophic methano

270 In bacteria cultures amended with nano-HgS from a 16 h-old nanoparticle stock

271 In contrast, 2-4% was methylated in cultures amended with nano-HgS that was aged for 3 days or 1 week

272 th dissolved Hg was greater than in slurries amended with nano-HgS, similar to previous experiments w

273 Two sediments (Burntwood and Raisin) were amended with Ni, equilibrated, incubated in a flow-throu

274 ed in lettuce and tomato grown in field soil amended with only a single application of biosolids (at

275 he rate and extent being greater in sediment amended with organic carbon.

276 in water-saturated Quincy sand (QS) columns amended with oxidized (OX) or unoxidized (UO) pine wood

277 ture, edible portions of crops grown in soil amended with PFAA industrially impacted biosolids were h

278 able P was low, allowing its growth on media amended with phytate as the sole source of P.

279 ies grown in continuous cultures on seawater amended with phytoplankton-derived DOM.

280 with the greatest richness achieved in soils amended with pig manure.

281 ased to the atmosphere in natural ecosystems amended with plant litters varying in quantity and quali

282 ice will respond to elevated As when soil is amended with Si-rich materials is unresolved.

283 falfa, lentil and soy in a hydroponic system amended with soluble salts, containing the same proporti

284 During 19 d of growth, plants were amended with solution containing 100 ng/mL of p,p'-DDE.

285 2) containing 25-129 mg kg(-1) As, which was amended with sparingly-soluble phosphate rock (PR-soil)

286 were spiked with stable mercury isotopes and amended with specific microbial stimulants and inhibitor

287 However, after 16 d of incubation, soils amended with stalks had a higher PE than those amended w

288 o greater microbial growth compared to soils amended with stalks.

289 ion was observed in Hg-DOM-sulfide solutions amended with sufficient l-cysteine to prevent beta-HgS(s

290 1.8 mA/cm(2)) in medium lacking chloride and amended with sulfate, nitrate, or phosphate as alternati

291 Lab-scale anaerobic digesters were amended with TCC at concentrations ranging from the back

292 community shifts were observed in digesters amended with TCC levels that did not inhibit function.

293 by conducting on-deck incubation experiments amended with tetrapeptide ala-val-phe-ala (AVFA), a frag

294 (6) E. coli luc IAC to simulated groundwater amended with the Dhc-containing consortium KB-1 yielded

295 The rates of sulfate removal in incubations amended with the refinery fuels were elevated relative t

296 ity composition was characterized from soils amended with three types of organic matter over a 30-yea

297 major global commodity crop, using farm soil amended with two high-production metal oxide MNMs (nano-

298 as removed from solution when grown in media amended with urea and 50 mM SrCl2 .

299 After incubation in media amended with urea and CaCl2 and/or SrCl2 , calcite (CaCO

300 idification stress, an 11.8-ha watershed was amended with wollastonite, a calcium silicate mineral, t