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1 neous (nonanalyte) substances (e.g., ions of heavy metals).
2 phase extraction of Co(II) as an example of heavy metals.
3 n identified as hyperaccumulators of several heavy metals.
4 the dopant or the ionizing reagent to ionize heavy metals.
5 roved to be useful for the analysis of mixed heavy metals.
6 n environmentally sustainable alternative to heavy metals.
7 o conventional ones for on-site detection of heavy metals.
8 cal parameters, tHg, MeHg and bacterio-toxic heavy metals.
9 netic objects, such as bio-macromolecules or heavy metals.
10 r hazardous chemicals and pollutants such as heavy metals.
11 rate, hydrocarbons, chlorinated solvents and heavy metals.
12 rticles are an essential carrier for aqueous heavy metals.
13 play a critical role in animal responses to heavy metals.
14 detecting and responding to toxic levels of heavy metals.
15 of soils and groundwaters contaminated with heavy metals.
16 n on mineral surfaces can immobilize aqueous heavy metals.
17 t levels, anoxia, and high concentrations of heavy metals.
18 ay improve green technologies for removal of heavy metals.
19 mulated and actual tap water contaminated by heavy metals.
20 ontributes to the toxic action of individual heavy metals.
21 rabidopsis (Arabidopsis thaliana) exposed to heavy metals.
22 ction pressures on siderophore production by heavy metals - a detoxifying effect of siderophores, and
25 provides the restricted factors of PAHs and heavy metal acropetal translocation by maize when they c
27 from the spin-orbit coupling of non-magnetic heavy metals allow electrical switching of perpendicular
28 ble in situ EC-XRF instrumentation will make heavy metal analysis at the source a very realistic poss
30 nds on the microbial Kingdom and the type of heavy metal and that consortia are significantly more re
31 ild requiring no oxidant and no excess toxic heavy metal and the reagent [(13/14)CN]-NCTS is a stable
32 grown in hydroponic medium supplemented with heavy metals and compared with those grown in a referenc
33 es have investigated the association between heavy metals and hearing loss in a general population th
34 robial expression of genes for resistance to heavy metals and metalloids is usually transcriptionally
37 tained substantially lower concentrations of heavy metals and organic contaminants in their tissues t
40 h the cobalt layer is sandwiched between two heavy metals and so provides additive interfacial Dzyalo
42 ical contaminants, (insecticide residues and heavy metals), and natural toxic substances (nitrate, ni
45 water that contain high levels of salinity, heavy metals, and naturally occurring radioactive materi
47 er for agricultural irrigation are salinity, heavy metals, and pathogens, which cause adverse effects
53 study aimed to determine bioavailability of heavy metal (As, Cd, Cu, Cr, Co, Al, Fe, Zn and Pb) conc
55 dimmer and are relatively rare, as, without heavy-metal atoms, spin-orbit coupling is less efficient
58 s population1 identified the metal-pump gene Heavy Metal ATPase4 as the major genetic determinant for
59 l components in the spectra influencing soil heavy metal bioavailability were identified and used in
61 cence resonance energy transfer (FRET)-based heavy metal biosensor for the quantification of bioavail
62 Cd(2+) uptake by measuring the amount of the heavy metals both in growth medium and in plant tissues
64 these electrodes, including the detection of heavy metals by absorptive stripping voltammetry, are al
65 e to gamma-radiation in combination with the heavy metal cadmium (Cd), using the MIXTOX approach.
66 hat treatment of Arabidopsis leaves with the heavy metal cadmium produces time course-dependent chang
67 transports divalent metal cations, including heavy metal cadmium, the accumulation of which has been
69 , copper (Cu), zinc (Zn), chromium (Cr)) and heavy metals (cadmium (Cd), lead (Pb) and nickel (Ni)) i
71 versal and robust in magnetic junctions with heavy metal caps across the 5d transition metals and tha
72 ficient functionality to enable adsorbent of heavy metals (Cd(2+), Co(2+), Cu(2+), Hg(2+), Ni(2+), an
73 otal and bioaccessible of trace elements and heavy metals (Cd, Cr, Cu, Co, Al, Zn, As, Pb and Fe) in
75 ments (manganese, iron, copper and zinc) and heavy metals (chromium, cadmium, lead and nickel) were d
76 showed significantly high concentrations of heavy metals, compared to those in the control group.
77 ly significant correlations between PM10 and heavy metal compounds (other heavy metals (r = 0.43, p =
78 est (0.015+/-0.001 mg/kg) bioavailability of heavy metal concentration in 22 varieties of cooked rice
80 ediction models were applied to estimate the heavy metal concentrations in wheat grains in the mid-Ya
81 information on the antioxidant activity and heavy metal concentrations of Polyporus sulphureus, Macr
85 Little is known about the bioavailability of heavy metal contamination and its health risks after ric
86 (based on spectroscopy) for the detection of heavy metal contamination are often very expensive, tedi
88 ring through rapid and specific detection of heavy metal contamination in potable water is of paramou
90 s changed significantly across a gradient of heavy metal contamination, and the relative abundances w
94 However, unrefined magnetite could have high heavy metal contents (e.g., Cr, Zn, Ni, Sn, etc.) and th
98 onal RecA expression to respond to genotoxic heavy metals (Cr>Cd approximately Pb), and polluted ash
102 e extent to which the atomic coefficients of heavy metal d orbitals contribute to the one-electron ex
105 demonstrated glucose assay, immunoassay, and heavy metal detection on well-spot C-microPAD and latera
107 s reviewed from one agent in each class, for heavy metal drugs (cisplatin), targeted agents (imatinib
108 irs through produced sulfide and precipitate heavy metals, either as sulfides or by alteration of the
114 are derived for the spin-orbit torques in a heavy metal/ferromagnet bilayer geometry, showing in gen
115 based on the spin-orbit torque switching in heavy metal/ferromagnet structures have been proposed wi
116 c devices, currently accessible in ultrathin heavy metal/ferromagnetic bilayers and multilayers with
117 asurements is established by investigating a heavy-metal/ferromagnetic-metal device (Ta/CoFeB/MgO).
118 As an in-plane charge current flows in a heavy metal film with spin-orbit coupling, it produces a
120 III) chloride (FeTPP) catalyst by colloidal, heavy metal-free CuInS2/ZnS quantum dots (QDs) to reduce
121 hlight recent advances in the development of heavy-metal-free nanocrystals within the context of spec
123 Many areas have been heavily contaminated by heavy metals from industry and are not suitable for food
124 cyclic aromatic hydrocarbons (PAHs) and five heavy metals from soils to maize at the farmlands with i
125 tical report on the potential health risk of heavy metals from the leather industries in Pakistan bas
131 growing body of evidence has suggested that heavy metals have ototoxic effects, yet few epidemiologi
133 as "free" layers in SHO are in contact with heavy metals having large spin-orbital interaction, and,
134 tate further dissection of the mechanisms of heavy metal (HM) accumulation/tolerance in plants and th
135 nd insert a thin layer of Cu to separate the heavy metal (HM) from the FM to avoid the proximity cont
136 emissions of five precedent-controlled toxic heavy metals (HMs), including mercury (Hg), arsenic (As)
137 growing support for a potential link between heavy metal homeostasis and host switching and reveals p
138 wn as Thlaspi caerulescens), an extremophile heavy metal hyperaccumulator model plant in the Brassica
141 made by printing indicators for detection of heavy metals in chemical symbols of the metals in a styl
143 out to determine the concentrations of some heavy metals in dairy products, collected from five indu
144 r can identify the existence of a variety of heavy metals in drinking water, and the four-electrode s
145 aeopollution through geochemical analyses of heavy metals in four renowned archaeological caves of th
146 easy solutions to field-based monitoring of heavy metals in industrial wastewater discharges and in
148 fractionation of endogen elements and toxic heavy metals in living organisms for biomedical applicat
149 is study was to increase the accumulation of heavy metals in plant foods by the external application
155 stitching were the principal contributors of heavy metals in the biological entities of the workers.
156 for the quantification of bioavailable free heavy metals in the cytoplasm of the microalga Chlamydom
157 CMAs play an important role for the fate of heavy metals in the environment, particularly in systems
160 have substantial buffering capacity for free heavy metals in their cytosol, even at high external met
164 es and sensors are used for the detection of heavy metals include spectroscopy and chromatographic me
166 to 10microgml(-1), as well as several other heavy metals, including arsenic, mercury and lead at sim
167 ain elevated levels of biogenic elements and heavy metals, including C (and organic carbon), N, S, Al
170 NP stimulated ROS production, expression of heavy metal-inducible and stress-inducible genes, stress
174 rstand that the inclusion of bioavailability heavy metal into HRA produces a more realistic estimatio
176 u(II) from water was observed at a low Fe-to-heavy metal ion ratio (Fe/M(II) = 2:1) while a removal e
177 ing principle into the field of self-powered heavy-metal-ion detection and removal using the triboele
178 r is taken as a sustainable power source for heavy-metal-ion removal by recycling the kinetic energy
182 rmance is best for the low concentrations of heavy metal ions and its sensitivity decreases with the
187 imultaneous determination of trace levels of heavy metal ions by anodic stripping voltammetry (ASV).
188 imultaneous determination of trace levels of heavy metal ions by anodic stripping voltammetry (ASV).
190 has a great potential to efficiently remove heavy metal ions from wastewaters in the presence of org
192 ance (SPR) based sensor for the detection of heavy metal ions in the drinking water is designed.
193 tection signals generated due to presence of heavy metal ions in the solution matrix like current, po
194 report the presence and the safety level of heavy metal ions in water simultaneously and by text mes
195 probes are fabricated and characterised for heavy metal ions out of these pyrrole/chitosan/ITO/Ag co
196 ctrochemical biosensors for the detection of heavy metal ions such as Hg(2+), Ag(+), Cu(2+) and Pb(2+
197 ous electrochemical detection techniques for heavy metal ions those are user friendly, low cost, prov
198 simple preconcentration and determination of heavy metal ions using methodology based on DMSPE and TX
199 ecent trends in electrochemical detection of heavy metal ions with various types of sensing platforms
200 paration and preconcentration method of some heavy metal ions, Cd(II), Cu(II), Ni(II), Pb(II) and Zn(
202 of sensitive and selective discrimination of heavy metal ions, including lanthanide and actinide salt
210 -state enzymatic glucose oxidase reaction by heavy metals ions such as Ag(+), produced a quantitative
212 the first nonhelical DNA structure driven by heavy-metal ions, thus further contributing to the struc
214 alent chromium (CrVI), one of the more toxic heavy metals, is widely used in more than 50 industries
216 butions of the damping and the IDMI from the heavy metal layer on the magnetization reversal and prov
217 s at the interface between ferromagnetic and heavy metal layers with strong spin-orbit coupling, but
219 f 16 ice cores quantifying substantial toxic heavy metal lead pollution at South Pole and throughout
221 used to examine changes in feeding ecology, heavy metal levels associated with life history events a
223 ytochelatins, which help in sequestration of heavy metal(loid)s inside the cell vacuole to alleviate
228 These results show that the investigated heavy metals modulate Fe deficiency responses at differe
229 mycin, alcohols of ethanol and n-butanol and heavy metals of Cu(2+) and Cr(6+), were analyzed and 31
230 rigation, this study revealed the effects of heavy metals on PAHs uptake in terms of co-contamination
231 e impact of high loads of Hg, MeHg and other heavy metals on the dental clinic wastewater microbiome,
233 f oil spills, removal of dyes, extraction of heavy metals or toxic anions, and the detection or remov
236 th plant systems appeared to have few common heavy-metal pathway regulators addressing mineral toxici
237 mization of contaminant inputs, reduction of heavy metal phytoavailability in soil with liming or oth
238 recognized medicinal use in the treatment of heavy metal poisonings as well as having potency for red
240 cteria (SRB) are widely used for attenuating heavy metal pollution by means of sulfide generation.
247 IED) and correlations of PM10 with SO2, NOx, heavy metals, polychlorinated dibenzo-p-dioxins/furan (P
249 n mass spectrometry can detect certain toxic heavy metals present in water, using surfactant-metal co
251 monstrate theoretically that a bi-layer of a heavy metal (Pt) and a bi-axial antiferromagnetic (AFM)
252 etween PM10 and heavy metal compounds (other heavy metals (r = 0.43, p = <0.001)), PAHs (r = 0.20, p
255 threatened by noxious contaminants, of which heavy metals represents an area of growing concern.
260 trategy of C. elegans populations exposed to heavy metals resulting in an evolutionary pressure acros
261 This produced the IMS spectra of several heavy-metal salts, including CdCl2, ZnSO4, NiCl2, HgSO4,
263 he grids and improved the homogeneity of the heavy metal stain needed to enhance visualization of bio
265 ns for cell culture, transfection, fixation, heavy-metal staining, embedding in resin, and EM imaging
266 medium (methylcellulose) before introducing heavy metal stains for visualization in small air-dried
267 g an oxidative stress (hydrogen peroxide), a heavy metal stress (arsenite) and an amino acid analogue
272 n was conducted to survey the levels of some heavy metals such as cadmium, lead, chromium, nickel and
273 rinking water can be ex-post contaminated by heavy metals such as Cu(2+) from house fittings (e.g., w
274 capable of immobilizing large quantities of heavy metals, such as nickel, via sorption processes.
276 vironmental chemicals such as pesticides and heavy metals that may be anthropogenic or dietary or fro
277 herapies; nutritional therapy; chelation and heavy metal therapy; and biological and pharmacological
279 only emphasizes the importance of assessing heavy metal toxicities at multiple levels but also provi
281 ause phytochelatins (PC) protect plants from heavy metal toxicity, strategies directed at manipulatin
282 e that soil carbonates critically influenced heavy metal transfer from soil to plants and presented a
283 that soil carbonates play a critical role in heavy metal transfer from soil to plants, implying that
284 It is well known that carbonates inhibit heavy metals transferring from soil to plants, yet the m
286 teria of accidental Hg(II) transport through heavy metal transporters with similar rates of uptake bu
288 nd categorize recent reports on detection of heavy metals using paper-based microfluidic devices on t
291 expensive method was developed for detecting heavy metals via the ion mobility spectrometry (IMS) in
294 otal and bioaccessible of trace elements and heavy metals were digested using closed-nitric acid dige
295 age of the excellent scattering intensity of heavy metals which have undergone association by metallo
296 jor importance for the toxicity reduction of heavy metals, while the influence of the organic materia
298 dary spin-charge conversion element, such as heavy metals with large spin Hall angle or multilayer la
300 the contrasting case of a magnetic-insulator/heavy-metal (YIG/Pt) heterostructure, where analogous tr
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