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1 itivity of parameters on the model output of toxicological activity was examined across possible rang
4 es of three proficiency tests for systematic toxicological analysis and of 103 authentic human urine
9 structure-activity relationships by linking toxicological and chemical mechanistic insights to the i
10 ight major polymer types, according to their toxicological and chemical signatures using in vitro bio
14 impact of engineered nanoparticles (NPs) in toxicological and environmental media are driven by comp
16 tends beyond sample storage for analysis, as toxicological and exposure studies conducted at room tem
18 stances across multiple media, including non-toxicological and non-chemically deleterious effects.
19 s of PoP and PoPx, further investigations in toxicological and sensory aspects of PoP and PoPx should
21 Further research included studies on GSH, toxicological aspects (the concept of "redox cycling"),
22 identified the following physicochemical and toxicological aspects as well as knowledge gaps that sho
24 o nutritional quality, shelf-life extension, toxicological aspects, legislation pertaining to food ir
26 iated with these models pose a challenge for toxicological assays to accurately report treatment outc
27 uctures of an arsenolipid is pivotal for its toxicological assessment and in understanding the arseni
28 that ATS were already viable approaches, for toxicological assessment of one or more end points in th
30 usually performed as a part of a traditional toxicological assessment; however, it often requires add
31 modified plants is explained, and aspects of toxicological assessments are discussed, especially the
32 pports further quantification approaches and toxicological assessments compared to nontarget investig
39 el (ULSD) fuel on the physical, chemical and toxicological characteristics of diesel particulate matt
40 and 4% oxygen levels on physicochemical and toxicological characteristics of particulate emissions f
42 etabolites is a sensible alternative for the toxicological characterization of parent molecules vs. m
44 r, is now detrimental as it enhances risk to toxicological compounds harbored by modern carrion resou
45 s of 56 and 29 ng/g, which are equivalent to toxicological concentrations of 123 and 18 ng WHO-TEQDL-
47 itude below the long-term daily threshold of toxicological concern (TTC) of 1.5 mug/g and the potenti
48 pecific migration limits (SML) and threshold toxicological concern (TTC) recommended values according
49 n the marine environment and OH-PBDEs are of toxicological concern and are therefore of interest to m
50 ficult to identify which compounds may be of toxicological concern and should be prioritized for furt
52 ed international guidelines, DBPs of greater toxicological concern were observed in high concentratio
55 centrations, many of them raise considerable toxicological concerns, particularly when present as com
56 n Se-Hg interactions, considers not only the toxicological consequences of Hg exposure but also the b
57 ation of action), concerns over the possible toxicological consequences of protein haptenization have
60 enated byproducts of PPCPs that have limited toxicological data and significant uncertainty with rega
61 city of oil has generally relied on existing toxicological data for a relatively few standard test sp
62 It is shown in this essay how some specific toxicological data has been misused by those aiming to d
66 g metabolites and pathways, governmental and toxicological databases, pharmacology resources, and bio
70 life-history trait interactions underlying a toxicological effect on population growth rate, should b
75 ase, coastal food webs may be at risk to the toxicological effects of increased methylmercury burdens
76 odel to characterise the pharmacological and toxicological effects of LiCl and VPA using gene express
78 nteractions between nanoparticles change the toxicological effects of single ENMs in unexpected ways.
79 hroughput examination of the therapeutic and toxicological effects of target compounds in realistic t
80 odel for studying the cellular and molecular toxicological effects on the liver after chronic exposur
82 more, evaluation of potential off-target and toxicological effects, as well as relevant in vitro ADME
83 etabolic vulnerability, as well as potential toxicological effects, inherent in the more potent prima
92 de novel insights into identifying potential toxicological end points and molecular mechanisms, often
98 tem cell-derived hepatocytes demonstrate all toxicological endpoints examined, including steatosis, a
99 ate the potential general toxicity (based on toxicological endpoints selected) and toxicokinetics of
100 er guidelines for PFAAs, including choice of toxicological endpoints, uncertainty factors, and exposu
101 was also confirmed during in vitro cellular toxicological evaluation of LCPM for the case of polyure
102 a correct identification, quantification and toxicological evaluation of the respective metabolites,
106 safety margin to the efficacious exposure in toxicological evaluations supported progression to Phase
109 ection in indoor environments and increasing toxicological evidence suggesting a potential for advers
111 transparency, efficiency, and acceptance of toxicological evidence, with benefits in terms of reduci
112 evaluated by investigating the oxidative and toxicological evolution of TiO(2) and SiO(2) nanoparticl
113 netics, degradation chemical mechanisms, and toxicological evolution of two OPFRs (2-ethylhexyl diphe
115 ure to susceptible populations; and e) using toxicological findings for risk assessment and remediati
116 United States, we have established that the toxicological footprint (TF) increased by 3.3% (88.4 Mt)
117 re-cast predefined molecular pathways into a toxicological framework and (2) provide a data-driven, u
118 ydes and possess important physiological and toxicological functions in areas such as CNS, metabolic
123 30%, <450 nm) has the potential for stronger toxicological impacts relative to those of other Cu mine
125 This investigation assessed the aquatic toxicological implications of copper oxide (CuO) nanosph
126 required to fully understand the levels and toxicological implications of the identified metabolites
130 There is a lack of publically available toxicological information for the main contaminant 4-met
135 ore this scenario, we probe the chemical and toxicological interactions of nanosilver (n-Ag) and nano
137 e formed in HepG2 cells that warrant further toxicological investigation, particularly since catechol
139 neurological manifestations was subjected to toxicological investigations but was found to have no sp
140 ication of free nanoparticle release and the toxicological investigations of the released particles f
142 of concept, our workflow was applied to the toxicological issue of the oxidation of dietary polyunsa
143 show that NgR1-Fc does not have preclinical toxicological issues in healthy animals or safety concer
144 g an oxazolidinone on the scaffold mitigated toxicological issues often seen with topoisomerase inhib
145 al tool to systematically integrate existing toxicological knowledge from a mechanistic perspective t
146 ts should strategically attempt to fill this toxicological knowledge gap so human health risk assessm
148 lls can identify potential chemical targets, toxicological liabilities and mechanisms useful for eluc
150 ividual PAHs, and we describe the paucity of toxicological literature for many of these compounds.
151 , but biological evidence is lacking and its toxicological mechanism remains unclear for the disease
152 eplete antioxidants in vivo, is a prevailing toxicological mechanism underlying the adverse health ef
156 ncy Center for the Evaluation of Alternative Toxicological Methods developed the Integrated Chemical
160 e models of ion speciation (WHAM VI) and eco-toxicological models such as the biotic ligand model (BL
162 mechanistic and cellular events underlying a toxicological outcome allows the prediction of impact of
164 covery of compound 41, which showed improved toxicological outcomes at similar exposure levels to com
168 bolic and lipidomics datasets with classical toxicological parameters we developed a hypotheses free,
171 Efforts in many countries have focused on a toxicological pathway-based vision for human health asse
173 logical processes involved in the underlying toxicological pathways can be implemented in a tiered sc
174 ve transcriptomic evaluation across multiple toxicological pathways following exposure to the SPMD ex
175 plied technology allowing many insights into toxicological pathways of environmental contaminants.
182 ngineer a pharmacophore in order to overcome toxicological problems while maintaining iron clearing e
183 Compound 27 stands out due to its favorable toxicological profile and physicochemical properties, wh
184 ss the recent knowledge regarding thebaine's toxicological profile available for the assessment of po
185 receptor agonists with a pharmacological and toxicological profile compatible with clinical developme
188 has been paid to the studies describing the toxicological profile of PtNPs with an attempt to draw c
189 on by In(NO3)3 and ITO indicating a critical toxicological profile that needs further investigation.
191 es demonstrate excellent pharmacokinetic and toxicological profiles and dramatic antitumour efficacy
192 notechnology research community and produced toxicological profiles for selected ENMs, as well as imp
193 microarrays and RNA-sequencing technologies, toxicological profiles of contaminants could be identifi
194 In this review, we summarize the in vivo toxicological profiles of different nanomaterials, inclu
195 ge of the mechanism of formation, levels and toxicological profiles of the chemical products in the a
202 /A1 to -5 have distinct in vitro and in vivo toxicological properties and that, unlike those for BoNT
203 fining the compounds to improve efficacy and toxicological properties for efficient blocking of malar
204 formation on the complex physicochemical and toxicological properties of both toner powders and print
205 pomers could improve the pharmacological and toxicological properties of drugs and provide mechanisti
207 significantly affect the physicochemical and toxicological properties of LCPM released during thermal
208 to study the phytochemical constituents and toxicological properties of seagrasses when considering
210 armacokinetic, in vivo efficacy, safety, and toxicological properties, compound 37 was selected for f
214 antioxidants to an aquatic species and imply toxicological relevance for dissipated tire rubber resid
218 that this new biosensor is suitable for lead toxicological research in vitro and in vivo, and will pa
219 ted in the United States National Center for Toxicological Research Liver Toxicity Knowledge Base (NC
220 g development stage, the National Center for Toxicological Research of the US Food and Drug Administr
222 This advance is critical for biomedical and toxicological research, as well as in fundamental studie
223 cell population in the overall governance of toxicological response following exposure to a panel of
224 ts were visualized in radar charts to assess toxicological response patterns allowing the comparison
226 SCs) enable the study of pharmacological and toxicological responses in patient-specific cardiomyocyt
228 formation System (IRIS) completed an updated toxicological review of dichloromethane in November 2011
229 onmental Protection Agency (EPA) completed a toxicological review of trichloroethylene (TCE) in Septe
233 rrogates to investigate the aqueous fate and toxicological risk of metal oxide NPs associated with wa
234 tion of toxic As species by plants suggested toxicological risk to higher organisms known to utilize
236 l value of the mushroom, as well as possible toxicological risks associated with its consumption.
238 echanisms against pathogens, incurring lower toxicological risks than conventional agrochemicals.
239 kinetic modeling aided in characterizing the toxicological role of the complex metabolism and multipl
241 on human leukaemic U937 cells and sufficient toxicological safety on normal human white blood cells w
243 bstacle to the development of cost-effective toxicological screening methods for engineered nanomater
244 t laboratories to facilitate high-throughput toxicological screening of pharmaceutical agents and tre
249 s in the aquatic environment differ in their toxicological sensitivity to the various chemicals they
250 y systems indicating activation of different toxicological signaling pathways is one of the paramount
253 aw attention to the ubiquity, diversity, and toxicological significance of fungal VOCs as well as som
255 ing, selection of appropriate in vivo model, toxicological studies (including toxin production) and d
258 nsortia, intramural research activities, and toxicological studies being conducted by the National To
259 extrapolating synergy observations from (eco)toxicological studies done at high exposure levels.
260 omaterials for various applications, in vivo toxicological studies for evaluating the potential hazar
261 ted particles (PEPs) continues to grow, most toxicological studies have not used the actual PEPs but
266 urther profiling, but, unfortunately, in GLP toxicological studies it showed liver findings in rat an
268 gn and interpretation of pharmacological and toxicological studies on the effects and disposition of
272 und dental implants and will help in guiding toxicological studies to determine the biological signif
273 ing models for assessing epidemiological and toxicological studies to reach consensus on probabilitie
274 to measure concentrations typically used in toxicological studies, and uses inexpensive, commerciall
275 are increasingly used in pharmacological and toxicological studies, but it is often overlooked that i
276 ish (Danio rerio) is a widely used model for toxicological studies, in particular those related to in
277 omedical applications, and for metabolic and toxicological studies, is a cutting-edge research topic.
286 these results, prior studies, and extensive toxicological support, the association between PM2.5 and
287 An emerging body of evidence points to the toxicological susceptibility of aquatic reptiles to Hg e
288 opment of reliable and efficient methods for toxicological testing and investigation of nano-bio inte
289 and West Virginia) that routinely performed toxicological testing on drivers involved in such crashe
291 at elevated Se concentrations are also known toxicological threats to aquatic animals, we performed a
292 s are existing for the analytes, both EFSA's toxicological threshold of concern (TTC) and sum of olig
294 tions are declining and how levels relate to toxicological thresholds and indices of health like infe
295 tant when exposure values were compared with toxicological thresholds in a risk characterization stud
296 ioaccumulation of Hg to levels that approach toxicological thresholds in at least one apex predator.
298 data on IHs with publicly available data on toxicological transcriptomics from propranolol exposure,
299 ther, for substances for which there is good toxicological understanding, a regulatory approach based