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1 rs was determined by measurement of original Aroclors.
2       Three represent relatively unweathered Aroclors.
3 easured in the sediment were not detected in Aroclors.
4  East Chicago, IN and five original Monsanto Aroclors.
5 sent in above-trace quantities in commercial Aroclors.
6 ater than trace concentrations in commercial Aroclors.
7 levels in sediments and less than 0.0025% in Aroclors.
8              We investigated how exposure to Aroclor 1016 and Aroclor 1254, as well as a newly charac
9  and in the original commercial PCB mixtures Aroclors 1016, 1242, 1248, and 1254.
10 duced deletions in vivo in the mouse embryo; Aroclor 1221 and Aroclor 1260 induced deletions in yeast
11                         In this study, TCDD, Aroclor 1221, and Aroclor 1260 induced deletions in vivo
12 es strongly resembled the OH-PCB profiles of Aroclors 1221, 1242, 1248, and 1254, yet 25% of OH-PCBs
13 PLA2 that are linked to different functions: Aroclor 1242 activates a calcium-independent PLA2 that r
14                      These data suggest that Aroclor 1242 and A23187 activate distinct isoforms of PL
15                                         Both Aroclor 1242 and A23187 caused release of [3H]AA; howeve
16 AA release and O2- production in response to Aroclor 1242 were inhibited by bromoenol lactone (BEL),
17 hat are activated by the neutrophil stimuli, Aroclor 1242, a mixture of polychlorinated biphenyls, an
18  AA release, but did not alter AA release in Aroclor 1242-stimulated neutrophils.
19 re at both Camden and New Brunswick resemble Aroclor 1242.
20  PLA2 activity was significantly enhanced by Aroclor 1242.
21  O2- production was seen only in response to Aroclor 1242.
22 adioactivity recovered from cells exposed to Aroclor 1242.
23 d placental anti-angiogenesis in response to Aroclor 1254 (A-1254), a mixture of polychlorinated biph
24  or 6 mg/kg/day of a commercial PCB mixture, Aroclor 1254 (A1254) by gavage from gestational day (GD)
25                                              Aroclor 1254 (A1254) interferes with normal dendritic gr
26 stribution patterns indicate historic use of Aroclor 1254 as well as modern sources of non-Aroclor co
27              In vivo or in vitro exposure to Aroclor 1254 coupled with IL-10 deficiency significantly
28                                       PB and Aroclor 1254 significantly enhanced malondialdehyde and
29                           Here, we show that Aroclor 1254, a mixture of structurally distinct PCBs, c
30 e effects of ecologically relevant levels of Aroclor 1254, a polychlorinated biphenyl (PCB) mixture,
31 nvestigated how exposure to Aroclor 1016 and Aroclor 1254, as well as a newly characterized non-Arocl
32 tive stress were influenced mainly by PB and Aroclor 1254, indicative of an oxidative damage response
33 rs (beta-naphthoflavone, phenobarbital (PB), Aroclor 1254, isoniazid, pregnenolone 16alpha-carbonitri
34 ent of PCB congeners in factors, relative to Aroclor 1254, suggested biotransformation (via cytochrom
35                                              Aroclor 1254-treated IL-10(-/-) mice demonstrated increa
36 repared from the livers of rats treated with Aroclor 1254.
37 -phase PCBs from a solid material containing Aroclor 1254.
38 ow), 0.70 (intermediate), or 1.05 (high) mug Aroclor 1254/g-body weight by gavage from 1 through 18 d
39 nated most hexa- and heptachlorobiphenyls in Aroclor 1260 (50 mug/mL) leading to losses of 51% and 20
40  high molecular weight formulations, such as Aroclor 1260 and PCBs 206, 208, and 209 produced during
41 he highly chlorinated commercial PCB mixture Aroclor 1260 for organohalide respiration.
42       In this study, TCDD, Aroclor 1221, and Aroclor 1260 induced deletions in vivo in the mouse embr
43 n vivo in the mouse embryo; Aroclor 1221 and Aroclor 1260 induced deletions in yeast.
44  responsible for extensive dechlorination of Aroclor 1260, and finally to the identification of a Deh
45 D14 dechlorinated the commercial PCB mixture-Aroclor 1260-mainly by removing flanked para- and doubly
46 rcial polychlorinated biphenyl (PCB) mixture Aroclor 1260.
47 at links its growth to the dechlorination of Aroclor 1260.
48 B-209, which was manufactured at the site in Aroclor 1270 and 1271, was the most abundant congener in
49          We hypothesized that there are both Aroclor and non-Aroclor sources within a single school a
50 d Harbor sediments but less than 1.2% in the Aroclors and 3.3% in any other sediments.
51 ons of sediments are different from those of Aroclors and are different according to sites.
52 ic chemicals with both legacy sources (e.g., Aroclors) and new sources (e.g., unintentional contamina
53 of the five resolved factors resemble low MW Aroclors, and declined from 1996 to 2007.
54  to report levels of OH-PCBs in sediment and Aroclors, and our discovery is significant because it is
55  highly weathered as to be unrecognizable as Aroclors, and thus have probably resided in the river fo
56  factors were probably originally related to Aroclors, but they are so highly weathered as to be unre
57                                      The non-Aroclor congener 3,3'-dichlorobiphenyl (PCB 11) has been
58          We hypothesized that additional non-Aroclor congeners are present in serum.
59 roclor 1254 as well as modern sources of non-Aroclor congeners associated with paint pigments and sur
60  L laboratory mesocosms containing weathered Aroclor-contaminated sediment from Baltimore Harbor, MD,
61 ilized Aroclors (gaseous PCBs) and unaltered Aroclors (dissolved PCBs) dominate in some samples, ongo
62 d factors that better resembled the original Aroclor formulations.
63 between schools and indicated the sources as Aroclors from building materials and individual PCBs ass
64 rization indicated that although volatilized Aroclors (gaseous PCBs) and unaltered Aroclors (dissolve
65 ociations of PCB congener distributions with Aroclors in most foods and found manufacturing byproduct
66 se commercial mixtures of PCBs, analogous to Aroclors in the United States) is reduced from 20- or 50
67 f non-Aroclor PCB congeners (</=0.20 wt % in Aroclor) in human serum collected from urban and rural a
68 ediment anywhere that PCB contamination from Aroclors is present.
69 r 1254, as well as a newly characterized non-Aroclor mixture that resembles the PCB profile found in
70 ons of polychlorinated biphenyls (PCBs) from Aroclor mixtures present in building materials explain t
71            We have previously shown that non-Aroclor PCB 11 is prevalent in indoor and outdoor air an
72 olescents have significantly lower total non-Aroclor PCB concentrations than mothers in East Chicago
73         Here we report the prevalence of non-Aroclor PCB congeners (</=0.20 wt % in Aroclor) in human
74                             A list of 70 non-Aroclor PCB congeners was determined by measurement of o
75     There are significant differences in non-Aroclor PCBs between East Chicago community and Columbus
76                                          Non-Aroclor PCBs represent an average of 10% (and up to 50%)
77                  Two were related to the non-Aroclor sources of diarylide yellow pigments and titaniu
78  PCBs) dominate in some samples, ongoing non-Aroclor sources such as paints/pigments (PCB 11) and coa
79 thesized that there are both Aroclor and non-Aroclor sources within a single school and that PCB conc
80  exhibited congener patterns consistent with Aroclor weathering, suggesting potential PCB metabolism
81                                              Aroclors with an intermediate weight percent of chlorine
82 with high potency (EC50=1.4 microM), whereas Aroclors with either high or low chlorine composition sh