Phellinus noxius was not recovered from pieces of artificially infested wood placed in or on soil amended with urea (NH 4 ) 2 CO 3 or aqueous ammonia. High concentrations of volatile NH 3 were detected in these treatments, indicating that NH 3 generated from these chemicals was fungicidal to P. noxius . A high concentration of volatile NH 3 was detected from nonautoclaved soil amended with urea, but not from amended autoclaved soil, indicating that soil microorganisms were involved in NH 3 generation. To kill P. noxius completely required 3000 p.p.m. urea in soil. Volatile NH 3 was generated from urea in alkaline soil, but not in acidic soil. In acidic soil 1 month after urea amendment, populations of both fungi and bacteria, and the concentration of NH 4 + (but not of NH 3 in the air), were significantly greater than in the no urea treatment and in the urea treatment 3 d after amendment, indicating that NH 4 + , generated from urea in the soil enhanced the activity of soil microorganisms. In contrast, 1 month after amendment of alkaline soil, the concentration of NH 4 + in the soil and NH 3 in the air increased significantly and the populations of both fungi and bacteria decreased, indicating that NH 3 in the air inhibited activity of soil microorganisms. Similar quantities of volatile NH 3 were generated at temperatures ranging from 12 to 32°C. A large quantity of NH 3 was generated at low soil matric potentials (− 0.75 to − 0.15 MPa) while high potentials (> − 0.025 MPa) and flooded soil hindered production of volatile NH 3 . Ammonia was more effective at killing P. noxius growing in smaller pieces of wood than in larger pieces. The fungus was not recovered from wood pieces less than 3 cm in diameter. Volatile NH 3 was also lethal to six other root rotting fungi ( Ganoderma australe, G. lucidum, G. tropicum, Rigidoporus vinctus, Heterobasidion annosum, and Rosellinia necatrix ) in addition to P. noxius .
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Chang (1999) studied this question.
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