Exact(2)
From the work of Niedermayer et al. (2012), it is possible to quantitatively predict the accumulated fraction of filaments where depolymerization has been paused as a consequence of exposure to light.
Instead, the culture at 19% O2 during Phase II of tissues pre-formed at 5% O2 during Phase I differently modulated the synthesis of the two extracellular matrix molecules: while a decreased accumulation (2.3-fold) and an increased released (2.6-fold) was measured for collagen, only a reduction of the accumulated fraction was demonstrated for proteoglycan (8.6-fold).
Similar(58)
Therefore, understanding the impact that water accumulated fractions may have on the development of native species is particularly relevant for this disaster.
Following previously accepted mixing procedures, we created water accumulated fractions (WAF) of Macondo oil with autoclaved E3 embryo medium [ 40, 123].
Water accumulated fractions (WAF) of the Macondo crude oil were vortex mixed in embryo medium at a 1 10 dilution in accordance with conventional methods [ 40].
Embryos were exposed to water accumulated fractions (WAFs) made from crude oil sampled from the riser insertion tube attached to the Macondo well during the 2010 oil spill.
We have adopted zebrafish, Danio rerio, as a model to test whether water accumulated fractions (WAF) of the Deepwater Horizon oil could impact specific embryonic developmental processes.
However, as compared to 19% oxygen (Phase I and Phase II), the released fractions of these newly synthesized macromolecules by pellets cultured at 5% O2 (Phase I and Phase II) were markedly and statistically significantly lower (2.0- and 2.9-fold respectively for collagen and proteoglycan), while the accumulated fractions were higher (2.1- and 6.6-fold respectively for collagen and proteoglycan).
It was estimated that one preferential flow column (PFC) at site A, and four at site B, contributed, respectively to 11%and58%8% of the accumulated leached fraction and to more than 80% of the maximum observed standard deviation (SD) in the field-scale concentration and mass flux of pesticides at two sites.
In cells treated with MG231 and WA, the ERα protein was lost from Triton-insoluble fraction and accumulated in the Triton-insoluble fraction, indicating that WA caused ERα protein aggregation and then induced proteasome-dependent ERα protein degradation.
Completely different Sr2 + distribution was found in contaminated soil samples, where it was accumulated in exchangeable fraction, regardless of soil type, contamination level and aging time.
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