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The algorithm includes occurrence of nosocomial infections, attributable mortality, costs and efficacy of infection control and how antibiotic-resistant bacteria affect total number of infections: do infections with antibiotic-resistant bacteria replace infections caused by susceptible bacteria (replacement scenario) or occur in addition to them (addition scenario).
The main objective of the replacement scenario analysis is to assess the potential reduction in future GHG emissions by replacing the use of reinforced concrete with EWPs.
The data were generally consistent with the hypothesis, though some biomechanical advantages were identified for each configuration; specifics and exceptions are discussed, along with reasons for a general recommendation for the use of an external mouse, or mouse and keyboard (without number pad) when using a notebook computer for an extended period of time, as in a desktop replacement scenario.
Obviously, both scenarios will coexist, excluding the possibility of a "100% additional" or "100% replacement" scenario.
Using €20,0000 per life year gained as a threshold, completely preventing MRSA would be cost-effective in the replacement scenario if attributable mortality of MRSA is ≥21%.
In the replacement scenario, the costs per life year gained range from €45,9122 to € 6590 for attributable mortality rates ranging from 10% to 50%.
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As part of the Integrated Carbon Metrics project, which comprehensively quantifies embodied GHG emissions related to the built environment in Australia, this contribution evaluates construction material replacement scenarios at the economy-wide scale.
Howard Gardiner endorses Zenon Pylyshyn's criticisms of Searle's view of the relation of brain and intentionality, as supposing that intentionality is somehow a stuff "secreted by the brain", and Pylyshyn's own counter-thought experiment in which one's neurons are replaced one by one with integrated circuit workalikes (see also Chalmers (1996), for exploration of neuron replacement scenarios).
More specifically, for all 1-year fish replacement scenarios, decreases in PCB-153 concentrations were < 10% across the three relevant exposure periods.
In fact, by the mid- to late 1980s, the estimated percent reductions in prenatal exposures for all 5-year replacement scenarios dropped below reductions estimated when steady-state emissions were assumed.
Childhood PCB-153 exposure reductions are also not depicted because of a much less pronounced impact of maternal fish replacement scenarios on this end point, given the competing influence of childhood diets during the 8.5 years following weaning.
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