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EE2 in the range 50 200 μg/L was treated in various matrices, i.e. ultrapure water, wastewater and drinking water, and treatment efficiency was assessed as a function of photon flux, ZnO loading and addition of hydrogen peroxide.
The maximum photochemical efficiency was assessed as (FM− F0)/ FM.
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Nanoparticle exposure was assessed as follows.
Statistical significance was assessed as indicated.
Recovery (extraction efficiency) was assessed, expressed as [ mean predicted concentration)/ spiked concentration)] x 100.
The labeling efficiency was assessed and calculated as the ratio of the activity in 99mTc-BMCs to the total radioactivity (radioactivity in cells plus in discarded supernatant).
Adsorption efficiency was assessed by counting plaques, as described above.
The filament-forming efficiency was assessed by high-speed sedimentation assay as described previously (Nicholl and Quinlan, 1994).
Labeling efficiency was assessed with a 10% SDS-PAGE gel as labeled myosin displayed a distinct gel-shift.
Selection efficiency was assessed by qPCR with Y-linked genes, SRY and DDX3Y, as positive controls and β-Actin and CDYL as negative controls.
The transduction efficiency was assessed by determining the fluorescence intensity after 4 d of culture.
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