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The model ZnS solutions and the vent fluid samples were amended with Cu2+ in order to determine whether metal-exchange reactions would occur.
Litter samples were amended with labile C (+ C, as sucrose), N (+ N, as NH4NO3), P (+ P, as NaH2PO4), all three inputs (+ CNP), or no inputs (CK).
Following the initial bioluminescent reading, samples were amended with 0.002% (w/v) n-decanal and the readings were continued to determine if additional aldehyde could increase light output.
Soil samples were amended with a solution of dextrose (0.5 g per L) and KNO3 (0.72 g per L) to ensure non-limiting substrate conditions and chloramphenicol (0.125 g per L) to inhibit protein synthesis.
Briefly, samples were amended with internal standards and extracted with organic solvents.
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In the lab, duplicate 5 g samples of homogenized, field-moist soil were amended with 10 mL of a solution of 0.5 g/L dextrose and 0.72 g/L potassium nitrate (KNO3) to ensure non-limiting substrate conditions, and 0.125 g/L chloramphenicol to inhibit protein synthesis.
After divergence angles were amended, extinction coefficient of samples with deferent concentrations was measured.
The filtrates were amended with nitric acid for sample preservation and were measured by ICP-MS.
In any case, no laws were amended.
This revealed ambiguities which were amended.
The cultures were amended with a sterile, deoxygenated stock solution of benzoate, resulting in an initial concentration of 13.8 mM, and regularly sampled for analysis of benzoate.
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CEO of Professional Science Editing for Scientists @ prosciediting.com