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1 ing could meaningfully contribute to overall body burden.
2 s accounted for only 1.2-2.5% of their total body burden.
3 ese polychaetes to account for >90% of their body burden.
4 ppears to be more influential than remaining body burden.
5 not accurately reflect medium- to long-term body burden.
6 ation of lipophilic POPs will increase total body burden.
7 udes the periodical biomonitoring of PCDD/Fs body burden.
8 s in relation to both recent exposure and Hg body burden.
9 matodes without increasing the C. elegans Cu-body burden.
10 ing a trip can be small compared to baseline body burdens.
11 udies of persons with high prediagnosis TCDD body burdens.
13 level combining evolutionary ecotoxicology, body burden analysis and testing for exposure to mutagen
14 icantly reduced tumor incidence, lower tumor body burden and a significant delay in the latency perio
17 from multiple microenvironments to PentaBDE body burden, and to explore the role of handwipes as a m
18 and cognition were found associated with Hg body burden as compared with those associated with recen
19 is-level and excess-toxicity doses (critical body burdens) as well as chemical activities A(50) (at t
21 estimated body burdens that were similar to body burdens associated with developmental neurotoxicity
22 can use concentrations in food to determine body burdens based on individual or population character
23 re conditions, ENM transformation, dose, and body burden be used in interpreting biological and compu
24 estrial Folsomia candida due to steady-state body-burdens being below equilibrium partitioning levels
25 d 2,4,6-TBP in order to study differences in body burden between healthy and sick cats diagnosed with
26 del, confirmed these positive effects on the body burdens but suggested lower effects of migration, o
29 gration and opportunistic feeding on seabird body burdens can be similar to that of an increase of on
32 human biomonitoring study presents the first body burden data for TCC from exposures occurring during
35 mug/kgww, while the measured nanoparticulate body burden for D. magna exposed to Ag ENPs was 59 +/- 5
36 global inventory of individual microplastic body burden for invertebrate species inhabiting marine s
38 rtments is becoming more frequent, the whole-body burden (i.e., internal concentrations) in nontarget
40 ld supply only approximately 30% of the MeHg body burden in C. hyperboreus and, thus, transformation
42 most important factor in predicting PentaBDE body burden in North Americans, and potential exposure p
43 icient male mice, with only 13% of the 203Hg body burden in the kidneys of GGT-deficient mice versus
44 ows the bio-accumulation of cadmium to yield body burdens in excess of 1/1000th of total dry body wei
45 i) increased sequestration of the surfactant body burden into membranes and other body tissues, resul
48 valence of 16% for Anniston overall; the PCB body burden of 35 major congeners ranged from 0.11 to 17
49 ndrocyte or osteoblast-like cell; high total body burden of calcium and phosphorus due to abnormal bo
52 that dietary intake contributed the most to body burden of CPs in this cohort, contributing a median
55 areas, research is lacking to determine the body burden of inhaled PCBs and consequent health effect
60 onstrated that inhalation contributed to the body burden of mostly tri- to hexachlorobiphenyls and pr
61 tigraphy is a means of quantifying the total-body burden of OA for systemic biomarker validation.
65 for riparian predators, showed an increased body burden of pharmaceuticals and endocrine disruptors.
66 recisely quantify and characterize the whole-body burden of replication-competent HIV in individuals
67 ion between risk of non-Hodgkin lymphoma and body burden of selected organochlorines in the general p
71 trially dosed mesocosm), and relatively high body burdens of Ag (0.5-3.3 mug Ag/g wet weight) were fo
72 f the United Kingdom and investigate whether body burdens of contamination vary according to species,
73 uggest that lifestyle factors are related to body burdens of HBCD and that domestic electronics may b
74 rates Crayfish (Orcoescties spp.) had larger body burdens of SDPAs and BZT-UVs compared to pelagic fi
76 10 mug L(-1), accumulated fluoxetine with a body burden over 270 times greater than exposure concent
77 icantly associated with lung tissue asbestos body burden (P < 0.03), and significantly predicted surv
78 g worms experiencing up to 130 times greater body burden ratios and increased magnitudes of effects t
79 tion (e.g., peak concentration and the whole-body burden recovery after a spill), then the nonsteady-
80 hest combined exposures, with some estimated body burdens that were similar to body burdens associate
82 ts for PCB-153, we simulated cross-sectional body burden versus BMI trends (CBBTs), as well as popula
87 to be more sensitive toward PtNPs and higher body burdens were measured in this species, possibly due
88 ong-chain PFAAs substantially increase human body burdens, which remain elevated for many years after