ライフサイエンスコーパス: biomonitor

1 ever, few industrial chemicals are routinely biomonitored.

2 ose that have been observed in limited human biomonitoring.

3 at current environmental exposures by human biomonitoring.

4 anding applications in transient implantable biomonitoring.

5 ital technologies that support device-driven biomonitoring.

6 be most effectively performed through human biomonitoring.

7 and has potential for applications in human biomonitoring.

8 ylation when selecting penguin chicks for Hg biomonitoring.

9 ding additional data, or as low priority for biomonitoring.

10 itional research, and 11 as low priority for biomonitoring.

11 anding morpho-taxonomic approaches in future biomonitoring.

12 ast carcinogens in breast cancer studies and biomonitoring.

13 Thirty-six were recommended for biomonitoring, 108 deferred pending additional research,

14 heric Hg(0) as the main source of Hg in most biomonitors (67 +/- 13% to 88 +/- 13%), except for Usnea

15 , there is a critical need for education and biomonitoring across the globe.

16 This assay provides a new approach for biomonitoring alachlor levels in experimental animals an

17 We show here that active biomonitoring allows the establishment of multisubstance

18 ve assessments of POP pollution derived from biomonitoring among multiple tissues.

19 Contamination with target analytes during biomonitoring analysis could result from solvents and re

20 tabolomics still underperforms in ultratrace biomonitoring analysis.

21 tepped-wedge cluster design to compare S100B biomonitoring and control groups at 11 centers in France

22 and field-deployable tool for the effective biomonitoring and diagnosis of potential exposures to ne

23 ion of specific PFOS isomers in future human biomonitoring and epidemiologic studies can provide usef

24 hort study resources are available to expand biomonitoring and epidemiology related to breast cancer

25 cal standards that will be of use for future biomonitoring and exposure assessment.

26 rspective, there are major knowledge gaps in biomonitoring and exposure data for CPs from regions oth

27 or application of the shell as a longer-term biomonitoring and forensics tool for historic exposure.

28 identify and prioritize novel chemicals for biomonitoring and health studies.

29 sampling methods should be deployed in human biomonitoring and public health surveillance studies to

30 and underscores the importance of continued biomonitoring and research efforts to elucidate current

31 For each chemical, we compiled biomonitoring and toxicity data, U.S. Environmental Prot

32 ytes, we speculated on their possible use as biomonitors and bioremediation tools.

33 ) mixtures is important for risk assessment, biomonitoring, and reporting of results to participants.

34 oral and spatial trends from Arctic wildlife biomonitoring, and suggest that the dominant PFOA source

35 completed exposure assessments, spirometry, biomonitoring, and validated mental health evaluations.

36 of European honey bees (Apis mellifera) for biomonitoring antimicrobial resistance (AMR) in urban ar

37 e not suitable for point-of-care or in-field biomonitoring applications.

38 sources, supporting the application of this biomonitoring approach.

39 DISCUSSION: Traditional and exposomic biomonitoring approaches have key advantages and disadva

40 Traditional and exposomic biomonitoring approaches have key advantages and disadva

41 y traditional and nontraditional (exposomic) biomonitoring are both critical in studies aiming to cap

42 Molecular epidemiology approaches in human biomonitoring are powerful tools that allow for verifica

43 ising method for sample preparation in human biomonitoring as it combines good recoveries with cleanu

44 Human biomonitoring assays based on liquid chromatography tand

45 owed implementation of the concepts of human biomonitoring at the community scale, opening the possib

46 and enable a noninvasive sampling method for biomonitoring BDEs in toddlers.

47 hich have not been included in U.S. national biomonitoring: benzophenone-1, triethyl phosphate, and m

48 an facilitate harmonization of environmental biomonitoring between laboratories and enable population

49 d suite of metabolites should be included in biomonitoring campaigns in order to fully characterize e

50 a keystone species and demonstrate how intI1 biomonitoring can support the surveillance of AMR.

51 It could be shown that thyroid biomonitors can work under dry conditions, which potenti

52 To address this gap and to advance QAC biomonitoring capabilities, we analyzed 19 commonly used

53 The Women FFs Biomonitoring Collaborative (WFBC) created a biological

54 To address this gap, the Women Firefighters Biomonitoring Collaborative created a biological sample

55 as humans and represent a relevant model for biomonitoring combinations of environmental pesticide ex

56 oring-I (HBM-I) values from the German Human Biomonitoring Commission.

57 tissues has posed enduring challenges in the biomonitoring community.

58 r scientific advances in analytical methods, biomonitoring, computation, and a newly articulated visi

59 lecules, for which no toxicological or human biomonitoring data are reported in the literature.

60 Human biomonitoring data collected from individuals of the sam

61 or chemical intake rates inferred from human biomonitoring data for 114 chemicals.

62 0.0001, R2=0.39) with medians inferred using biomonitoring data for 39 chemicals from the National He

63 first time a means for examining population biomonitoring data for multiple environmental chemicals

64 However, biomonitoring data for young children remain limited.

65 s study also lead to better understanding of biomonitoring data from different blood matrices, which

66 tionally used for market basket analysis, to biomonitoring data from the 2009-2010 cycle of the conti

67 We linked biomonitoring data from the New Bedford Cohort (NBC) and

68 We used biomonitoring data from the U.S. Centers for Disease Con

69 We applied our methods to PFAS biomonitoring data from the United States National Healt

70 Initial biomonitoring data have provided early indications of re

71 sed values now allow interpretation of these biomonitoring data in a public health risk context.

72 This study provides important public health biomonitoring data on isoprene exposure in the general U

73 But a lack of standardized long-term biomonitoring data prevents a deeper understanding of bi

74 Biomonitoring data reported in the National Report on Hu

75 Biomonitoring data reported in the National Report on Hu

76 Our method can provide essential biomonitoring data to establish baseline exposure levels

77 ated how FIM can be used in conjunction with biomonitoring data to narrow a large number of possible

78 Our study demonstrates that combining biomonitoring data with mechanistic modeling can identif

79 g pharmacokinetic models-in conjunction with biomonitoring data, diary information, and other related

80 ions, these results, in the context of other biomonitoring data, suggest that earlier reported declin

81 tainty in these predictions by comparison to biomonitoring data.

82 olated to the human and evaluated with human biomonitoring data.

83 provide an overview of available hazard and biomonitoring data.

84 Here we harmonized US federal biomonitoring datasets with 389 species spanning 27 year

85 ted tissue hypoxia thoroughly through online biomonitoring, determination of enzyme activity and panc

86 try (LC-MS(n)) is the most common method for biomonitoring DNA adducts, generally targeting single ex

87 As the science and biomonitoring effort progress in this area, more data se

88 Biomonitoring efforts are warranted to investigate prese

89 Biomonitoring Equivalents (BEs) and other risk assessmen

90 d analysis of the biospecimens collected for biomonitoring evaluations could compromise the reported

91 131)I, its apparent half-life in the thyroid biomonitor exceeds the physical one, thus making (131)I

92 immunoassay has been developed as a tool for biomonitoring exposures to organophosphate (OP) compound

93 able PFAS in the placenta suggests a need to biomonitor for exposure to PFAS during pregnancy.

94 ecting bird eggs is an established method of biomonitoring for specific pollution hazards.

95 Bivalves have been used as biomonitors for many pollutants, but their effectiveness

96 s a long tradition to use beached fulmars as biomonitors for marine plastic pollution.

97 ggest that aquatic invertebrates may be good biomonitors for REEs, yet there is little information on

98 through retrospective analyses of blood lead biomonitoring from the Bunker Hill Superfund Site in Ida

99 nte) birth cohort, in Sabadell, Spain, using biomonitoring, geospatial modeling, remote sensors, and

100 6 in the control group and 1152 in the S100B biomonitoring group (1235 [59.4%] boys; median age, 3.2

101 (95% CI, 47%-53%) was observed in the S100B biomonitoring group (479 [41.6%] vs 849 [91.7%]; P < .00

102 In the S100B biomonitoring group, blood sampling took place within 3

103 he control group and 112 (9.7%) in the S100B biomonitoring group.

104 and urine against previously published human biomonitoring (HBM) estimates, 4) calculate the relative

105 Human biomonitoring (HBM) often reveals statistical associatio

106 lable, fit-for-purpose next-generation human biomonitoring (HBM) workflow for analyzing >230 biomarke

107 This study aims to demonstrate the use of biomonitors (i.e., tree foliage, bark, mosses, and liche

108 er screening values, including BEs and Human Biomonitoring-I (HBM-I) values from the German Human Bio

109 le of women in the study warrants a periodic biomonitoring in attempt to identify and reduce exposure

110 Thus, we recommend improved biomonitoring in forests and croplands, and optimised su

111 Mobile biomonitoring in long-term medical diagnostics is anothe

112 rful sources of targets for therapeutics and biomonitoring in oncology.

113 f a German silicone rubber facility by human biomonitoring in plasma and urine.

114 quire electricity, making them appealing for biomonitoring in remote or resource-limited settings.

115 that aerial eDNA can be used as a source for biomonitoring in terrestrial ecosystems, specifically hi

116 ld cohort and monitored drug intake by LC-MS biomonitoring in urine.

117 The need for effective biomonitoring in wastewater has become clear due to the

118 cognition as a potentially powerful tool for biomonitoring, including early detection of aquatic inva

119 scents and 1297 adults in the European Human Biomonitoring Initiative.

120 Traditionally, marine biomonitoring involves the sorting and morphological ide

121 characterize environmental exposures through biomonitoring is key to exposome research efforts.

122 s during analysis of biological specimens in biomonitoring laboratories equipped with state-of-the-ar

123 data suggesting that heavy metal macroalgae biomonitoring may be species-specific.

124 A biomonitoring method was developed for the determination

125 Exposomic approaches differ from traditional biomonitoring methods in that they can include all expos

126 08 deferred chemicals included those lacking biomonitoring methods or toxicity data, representing an

127 ifespan, both traditional and nontraditional biomonitoring methods should be used.

128 we discuss the potential to apply innovative biomonitoring methods using high-resolution mass spectro

129 s of interest to ECHO but that have not been biomonitored nationwide and to identify gaps needing add

130 We describe the biomonitoring needs of exposome research and approaches

131 For the information obtained from biomonitoring, no association was found for ibuprofen an

132 ation of genetic tools for bioassessment and biomonitoring of aquatic ecosystems.

133 There is a clear need for continued biomonitoring of blood contaminant levels in this popula

134 Our results underline the need for wide biomonitoring of both types of ecosystems to assess the

135 heless, feces are rarely used as a matrix in biomonitoring of chemical exposures.

136 Expanded biomonitoring of emerging chemicals of concern and studi

137 Feathers have been shown to be useful in the biomonitoring of environmental contaminants, such as met

138 hromatographic test strip (ICTS) for on-site biomonitoring of exposure to cypermethrin by simultaneou

139 uggest that feces are an important matrix in biomonitoring of exposure to environmental chemicals.

140 esses the relevance of hair analysis for the biomonitoring of exposure to fast-elimination compounds

141 enzymatic inhibition and phosphorylation for biomonitoring of exposure to organophosphorus (OP) pesti

142 detect pesticides and their metabolites for biomonitoring of exposure.

143 nstrates the need for sensitive and detailed biomonitoring of harmful aeroallergens in order to inves

144 s and wearable devices that enable long-term biomonitoring of key health biomarkers which promise to

145 e algae, the study herein forms an effort in biomonitoring of metal contamination in the aforemention

146 first in-depth, comparative and prospective biomonitoring of Multiple Myeloma (MM) patients (N = 39)

147 Biomonitoring of ochratoxin A is very important.

148 ication of OP-BChE and enzyme inhibition for biomonitoring of OP and nerve agent exposures.

149 avenue for the simple, rapid, and sensitive biomonitoring of OP pesticide exposure.

150 It includes the periodical biomonitoring of PCDD/Fs body burden.

151 vice is promising for accurate point-of-care biomonitoring of pesticide exposure.

152 based assay may enable frequent longitudinal biomonitoring of PFCs and other environmental toxins usi

153 for frequent blood sampling and longitudinal biomonitoring of PFCs.

154 Biomonitoring of pollutants and their metabolites and de

155 may be a useful noninvasive matrix for human biomonitoring of specific organic contaminants, but furt

156 The long-term biomonitoring of the effects of insecticide use on the n

157 mprehensive study on the bioaccumulation and biomonitoring of the three major QAC groups and our resu

158 Based on biomonitoring of the UK Common Buzzard (Buteo buteo) col

159 Continued biomonitoring of these bisphenols in populations and fur

160 he applicability of these structures for the biomonitoring of these compounds.

161 cursors) suggest that for general population biomonitoring of these nonpersistent phenols, urine, not

162 ing life span, suggesting their potential as biomonitors of aging.

163 these areas, we measured 16 PAHs in lichens, biomonitors of atmospheric PAHs, along three transects e

164 Lichens have been used as biomonitors of the impacts of S for over 40 years, but t

165 Hence thyroid biomonitors offer even some quantitative information, wh

166 rtebrate biodiversity is challenging because biomonitoring often has limited spatial, temporal, and t

167 res; however, mesocosm experiments and field biomonitoring often indicate effects at relatively low m

168 Biomonitoring often requires a priori selection of compo

169 As human biomonitors, or "insectometers," we see that ACG's insec

170 for organism bioaccumulation is viable when biomonitoring organisms are not available.

171 ap Fusion mass spectrometer were employed to biomonitor PhIP in dyed hair.

172 ic progress made during the 29 years of this biomonitoring program is relevant to future, large-scale

173 itu-based effects measures recorded during a biomonitoring program on a French watershed impacted by

174 (POPs) in Californians prompted the state's biomonitoring program to conduct a study in firefighters

175 ccessful implementation of metabolomics in a biomonitoring program.

176 DNA barcoding, have the potential to enhance biomonitoring programs worldwide.

177 he precautionary principle, establishment of biomonitoring programs, and funding of community-based e

178 cost and logistical constraints to existing biomonitoring programs.

179 l for broad applications for all large-scale biomonitoring projects that rely on untargeted LC-HRMS d

180 Effect-based biomonitoring provides a cost-effective solution.

181 ng opens up new perspectives in the field of biomonitoring providing a device with acceptable stabili

182 ated flame retardants (BFRs) in toddlers for biomonitoring purposes.

183 No biomonitoring reference data have been reported to chara

184 nd the inclusion of PIOM analysis in current biomonitoring regimes and that plastics be used with cau

185 This in-depth biomonitoring report following real-world cilta-cel or i

186 Mercury (Hg) biomonitoring requires a precise understanding of the in

187 Biomonitoring results demonstrate that pregnant women in

188 ncentrations in organisms, interpretation of biomonitoring results, and assessment of toxicity.

189 soften materials and make them flexible, and biomonitoring shows widespread human exposure to a mixtu

190 ncentrations and isotopic compositions among biomonitor species.

191 and the integration of emerging techniques, biomonitoring strategies can be maximized in research to

192 PFOA reported in clinical (116 days) versus biomonitoring studies (1.3-3.9 years).

193 vitro biotransformation products for future biomonitoring studies and emphasize that it is important

194 Biomonitoring studies are conducted to assess internal d

195 Human biomonitoring studies are important for understanding ad

196 Meta-HO-TPHP could be relevant for future biomonitoring studies concerning flame retardants.

197 vides new data that can support future human biomonitoring studies focusing on HMW SPAs.

198 We will apply the method in future human biomonitoring studies for OC exposure and risk assessmen

199 ndings underline the importance of long-term biomonitoring studies for the conservation of Turkiye's

200 Human biomonitoring studies have shown that concentrations of

201 We recommend biomonitoring studies include these 6 DAPs as well as se

202 This lack of biomonitoring studies is partially due to the absence of

203 paration platform is optimal for large-scale biomonitoring studies of air pollution relevant to globa

204 tives in canned foods and consumer products, biomonitoring studies of human exposure to these compoun

205 tabolites in human urine facilitating future biomonitoring studies on QACs.

206 double the average intake levels observed in biomonitoring studies worldwide.

207 f benzene has been investigated in dozens of biomonitoring studies, mainly by studying (classical) ch

208 ereoisomer-specific HBCD exposures in future biomonitoring studies.

209 ealth safety concerns and proving useful for biomonitoring studies.

210 s in large-scale population health and human biomonitoring studies.

211 divergent half-lives from clinical trial and biomonitoring studies.

212 blood or urinary concentrations observed in biomonitoring studies.

213 ated with detected OMPs that warrant further biomonitoring studies.

214 esults and the data obtained in two previous biomonitoring studies.

215 ity; and (3) not currently measured in large biomonitoring studies.

216 t exposure to pre-PFAAs is provided by human biomonitoring studies?

217 epresents the first comprehensive macroalgae biomonitoring study of metal contamination from the coas

218 This human biomonitoring study presents the first body burden data

219 several for the first time in a U.S. urinary biomonitoring study.

220 -health impact relationships from the NHANES biomonitoring survey studies.

221 Given that human biomonitoring surveys show per- and polyfluoroalkyl subs

222 Biomonitoring surveys, such as the NHANES (National Heal

223 This review discusses emerging biomonitoring technologies for diagnosing and managing c

224 The challenge is to prioritize chemicals for biomonitoring that may present health risk concerns.

225 c aromatic hydrocarbon exposure relevant for biomonitoring the deleterious health impacts from tobacc

226 s are shown to cause harm and; (d) improving biomonitoring through developing ecologically relevant m

227 Further biomonitoring to ascertain current trends and determinan

228 es and, therefore, an ideal method for human biomonitoring to be combined with in vitro bioassays.

229 or the 11 neutral PFAS, followed by possible biomonitoring to experimentally verify dermal absorption

230 in diverse scientific fields from ecological biomonitoring to wastewater surveillance of viruses.

231 formation that guides the use of bivalves as biomonitors to evaluate PFAS contamination in aquatic en

232 se data, we recommended chemicals either for biomonitoring, to be deferred pending additional data, o

233 uggesting potential use of snail shells as a biomonitoring tool for metal contamination.

234 dy uses bird eggs of seven wild species as a biomonitoring tool for sunscreens occurrence.

235 luid that has not been used extensively as a biomonitoring tool in epidemiological studies.

236 to evaluate the utility of microarrays as a biomonitoring tool in field studies.

237 ing of COI could be a powerful and efficient biomonitoring tool to protect local aquatic ecosystems.

238 To test this new biomonitoring tool, we investigated Cu isotope variation

239 To test this new biomonitoring tool, we investigated Cu isotope variation

240 he importance of developing avian tissues as biomonitoring tools for assessing local risk of mercury

241 Here, two potential nonlethal biomonitoring tools for the assessment of PAH toxicity a

242 Small organisms can be used as biomonitoring tools to assess chemicals in the environme

243 g its potential for developing environmental biomonitoring tools, as it can provide an a priori asses

244 cation of DNA barcoding and metagenomics for biomonitoring using benthic macroinvertebrates.

245 analytes not currently included in the U.S. biomonitoring were detected in >=90% of samples: benzoph

246 ed piezoresistive textile (CF p-textile) for biomonitoring which is biocompatible, biodegradable, and

247 are hitherto subject to little or no routine biomonitoring, which would be essential for identificati

248 Current methodologies for biomonitoring wild populations are invasive and mostly l

249 tility of research that integrates data from biomonitoring with direct, long-term observation of enda

250 barcoding as a powerful tool for crocodylian biomonitoring within fragile and diverse ecosystems, par

251 the management of pediatric minor HT, S100B biomonitoring yielded a reduction in the number of CCT s