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These small biological compounds, four different nucleotide bases, can be photocatalytically and photoelectrocatalytically degradable, and the degradation efficiencies of PEC method were found to be higher than those of PC method for all compounds investigated.
Both flushing arrangements may result in similar TCE degradation efficiencies of 35%to42%2% estimated by the ratio of TCE degraded/ TCE degraded + TCE remained in effluent) and degradation byproduct chloride generation rates of 4.9 to 7.6 mg Cl− per soil column pore volume.
The photocatalytic degradation efficiencies of AgI-BiOI/PAN after 210 min light irradiation was 98.5%.
The degradation efficiencies of the 20CBD and ACC electrodes after 6 h were 96% and 82.5%, respectively.
Co-occurring with electricity generation, the degradation efficiencies of phenol in all the MFCs reached above 95% within 60 h.
The La-doped TiO2 nanotube array electrode showed much higher degradation efficiencies (99.33%) than the undoped TiO2 nanotube array electrode (70.16%) under the same condition.
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The maximum experimental degradation efficiency was 95.07%.
Performing the experiment at 32 °C did not increase the degradation efficiency.
We fused wildtype mAID to the C terminus of Venus and quantified degradation efficiency by life cell imaging.
A quadratic model was built to predict degradation efficiency.
Increasing initial RR180 dye concentration resulted in decreasing degradation efficiency.
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