Thirteen strains of bacteria able to grow on phenanthrene were isolated from soil; they included fluorescent and non-fluorescent pseudomonads, vibrios and unidentified bacteria. Two of the pseudomonads, like Aeromonas sp. ~4 5~1 , also grew on naphthalene. In all strains, growth on phenanthrene induced the enzyme responsible for the conversion of 1-hydroxy-2-naphthoate to 2-carboxybenzaldehyde, NAD-dependent 2-carboxybenzaldehyde dehydrogenase and protocatechuate oxygenase, but not salicylate hydroxylase, catechol oxygenase or NAD(P)H-dependent 1-hydroxy-2-naphthoate hydroxylase. Growth on naphthalene induced salicylate hydroxylase and catechol oxygenase. It is suggested that the catabolism of phenanthrene occurs via protocatechuate in all these bacteria, and that the pathways for degradation of phenanthrene and naphthalene are separate.
I N T R O D U C T I O NWith the development of the petroleum industry, there has been an increase in the amount of polyaromatic hydrocarbons released into the environment. As part of a study of the mechanism of degradation of hydrocarbons by micro-organisms, we have examined the catabolism of phenanthrene by bacteria. The enzymic steps involved in the conversion of phenanthrene to 1 -hydroxy-2-naphthoate by a soil pseudomonad were elucidated by Evans, Fernley & Griffiths (1965). The naphthoate was then presumed to be oxidatively decarboxylated to 1,2-dihydroxynaphthalene which would be further degraded through the naphthalene-catabolizing pathway described by Davies & Evans (1964). However, Aeromonas sp. ~4 5~1 , which was isolated from soil by Kiyohara, Nagao & Nomi (1976), did not convert 1-hydroxy-2-naphthoate to 1,2-dihydroxynaphthalene but instead metabolized it to 2-carboxybenzaldehyde which was then oxidized to o-phthalate, by an NAD-dependent dehydrogenase, and finally to protocatechuate (Fig. 1). The cleavage of the naphthoate (Kiyohara & Nagao, 1977) involves the fission of the bond between the carbon atoms bearing the hydroxyl and carboxyl groups by an intradiol type of dioxygenase which acts in a similar way to gentisate oxidase (EC 1 ,13.1.4) (Sugiyama et al., 1958).The work described in the present paper shows that the protocatechuate pathway is the only pathway for degradation of phenanthrene in 13 independent isolates of soil bacteria. The relationship between the pathways for degradation of phenanthrene and naphthalene is also described.
METHODSBacteriaZ strains and media. Bacteria able to grow on phenanthrene were isolated from soil by enrichment culture in phenanthrene/salts medium, followed by plating on Pseudomonas F agar (Difco). The salts medium contained (yo, w/v, in tap water): (NH&HP04, 0-5; KH2P04, 0.15; Na,HPO,. 12H20, 0.15; MgS04. 7H20, 0.02; NaCI, 0.05; the pH was 7-3 without adjustment. Phenanthrene (0.3 %, w/v) was added to the medium before autoclaving at 120 "C for 15 min. The phenanthrene was melted by the heat but was finely dispersed by vigorously shaking the flasks after cooling. Naphthalene, which was crystallized from