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The objective of this study was to assess the accuracy of measuring surface water elevation changes of large multi-channel inland river systems using data from multiple altimetry satellite sensors and different retracking methods.
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These satellites not only measure surface water by photographs but, thanks to precise measurements of the effect of bodies of water on the atmosphere, can even calculate the amount of water in the aquifer below them.The main reason for the depletion turns out to be that more water is being taken out of the underground aquifer, mainly by farmers.
In 2006 the maximum measured surface water concentration was 0.38 μg/L for atrazine and 0.37 μg/L for hydroxyatrazine, and underground levels, 0.14 μg/L for atrazine, 0.38 μg/L for hydroxyatrazine, and 0.32 μg/L for desethylatrazine.
Extent of surface modification was physically evaluated by observing both its color changes with digital camera and morphological changes with scanning electron microscopy as well as by measuring surface tension with water contact angle.
The apparent discrepancy between the gravimetric thickness of roughly 6 nm by QCM and the clearly lower optical thickness of only 60% results from the different measurement principles: While QCM-D also measures surface-bound water, ellipsometry only detects adsorbed protein in its dry state [ 25, 27].
Measured EE2 surface water concentrations in the United States, United Kingdom, The Netherlands, and Germany range from 0.5 to 15 ng/L [ 7], and it has been frequently measured in United States streams [ 9].
As the figure indicates, the 68% of the values of the reported mixtures fell into Group I, 19% fell into Group II, 6% fell into Group IIIA and 6% into Group IIIB. Figure 4 MCR/HI plot of MCR versus HI for ecological effects of mixtures of chemicals measured in surface water or WwTP effluents [[9]].
Therefore, LCOHs measured in surface water and sediments are from natural in situ synthesis or terrestrial runoff sources not detergents.
Instantaneous stream discharge (Q) was measured during surface water sampling immediately downstream of transect E using acoustic Doppler.
However, the peak concentrations that have been measured in surface water are much higher, as is also expected to be the case after intentional water poisoning.
CNS was estimated from PFAA concentrations measured in surface water samples collected at three stations along the southern coast of Norway in 2007 (Table S11 in Supporting Information).
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