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1 hlordane (2150 ng/g) and DDx (118 ng/g) that was amended with 0, 500, 1000, or 5000 mg/kg MWCNT or C6
2 To this end, a nonpolluted agricultural soil was amended with 0.5, 2, and 5% of the following four am
5 reviously exposed (to triclosan) communities were amended with 5, 50, and 500 mg/kg of triclosan, cor
6 r a period of conditioning with groundwater, were amended with a mixture of groundwater, soluble U(VI
7 mations, coastal bacterioplankton microcosms were amended with a single PA model compound, i.e. putre
8 2)O) and ammonia (NH(3)) emissions when soil was amended with anaerobically digested dairy manure slu
10 After 3000 days, methanogenic communities were amended with benzoate resulting in methanogenesis r
15 drinking water source), and this groundwater was amended with either tin or silicate corrosion inhibi
19 lum from a seawater-compensated ballast tank was amended with fuel from the same ship or with refiner
23 ast, over time the Bacteria communities that were amended with lower concentrations of triclosan (5 m
27 iodegraded oil reservoirs, oil sands samples were amended with nutrients and electron acceptors, but
28 soils (sandy soil and sandy clay loam) that were amended with sewage sludge or poultry manure and cr
31 5-7.2) containing 25-129 mg kg(-1) As, which was amended with sparingly-soluble phosphate rock (PR-so
35 f acidification stress, an 11.8-ha watershed was amended with wollastonite, a calcium silicate minera