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The following scenarios were modelled: Scenario 1 Reduced discretionary salt intake; Scenario 2 Reduced sodium in bread; Scenario 3 Reduced discretionary salt intake combined with reduced sodium in bread (combined Scenarios 1 & 2); Scenario 4 Reduced sodium in all processed foods; Scenario 5 Reduced sodium in all processed foods and reduced discretionary salt intake (combined scenarios 1 & 4).
The proposed model is intended to be adequately protective for consumer's health, as it considers a conservative food intake scenario, as well as various sources of contaminant exposure.
Therefore, two additional calculations were done, one with a PFFn of 10% and the other with a low intake scenario of dietary supplements (i.e., 400 µg for adults).
Based on the average dust intake scenario, food intake is the most important contributor to total intake (mean, 67%; range, 23 93%).
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As for folic acid, this will be a temporary policy for only a couple of years and it was thought that the PFFn of 15% and the high-intake scenario from dietary supplements are rather conservative estimates.
Therefore, we used two realistic high-intake scenarios of dietary supplements based on the limited Dutch dietary supplement data available: one for adults (≥18 years old) and one for children (1 17 years old).
Combining HBCD intake via both dust and diet, individual exposures ranged from 4 to 20 ng/day (average dust ingestion scenario) and from 5 to 42 ng/day (high dust ingestion scenario) (Table 3).
Under an average dust ingestion scenario, diet is the major pathway, whereas under a high dust ingestion scenario, intake via dust and diet are roughly equal in importance.
Specifically relevant to the assessment of phytonutrient intake are scenario uncertainties that may arise from the presence of phytonutrients in food additives and supplements that have not been taken into account and could have an impact on the intakes of certain sub-populations or individuals.
Scenario E combines the lower intakes of scenario D with higher outflows (other than retirement).
Emissions reductions in NA will result in significant decreases in MeHg intake, especially under scenario 1 and in faster responding ecosystems like ecosystem A. For scenario 2, emissions controls outside NA are as important as NA controls.
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