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Fig. 1 Emission of monoterpenes from P. violacea flowers exposed to different light/dark conditions.
The insets show the PL intensity ratio R of the E 1 emission to the E 0 emission (R = E 1 emission/E 0 emission × 100%%) as a function of the excitation laser intensity.
Figure 1 Emission curves for tebuconazole, copper, DOC and TN from parallel TS-2 and OECD 313 experiments.
Therefore, the intensity of the E 1 emission increased slower than that of the E 0 emission.
With the content of Gd increases, the intensity of 5 D 0 → 7 F 1 emission increases.
Fig. 1 Emission of active substances from treated articles during rain events; data from BAM field experiments on paint B and an impregnated textile.
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This study included locomotives that are currently in the NCDOT fleet, which are certified to meet the EPA Tier 0+ and Tier 1+ emission standards.
All locomotives were remanufactured within the last 4 years to meet the Tier 0+ and Tier 1+ emission standards for the F59PH and F59PHI locomotives, respectively.
This phenomenon can be used to examine suitability of APTES coverage on glass surfaces since YOYO-1 emission can be distinguished by its glass adsorbed versus DNA-bound forms.
The figures of merit of the Spectrophone were very good, with limits of quantification of 70 μg L-1 for absorption and 60 μg L-1 emission modes, respectively, and high linearity (R2 > 0.9995).
The most stringent PM thresholds (Euro 5, Euro 6), however, allow 5 mg PM km−1 emission resulting in a radiative effect of 3.9 g CO2 equivalents km−1.
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