Arthrobacter aurescens strain TC1 was isolated without enrichment by plating atrazine-contaminated soil directly onto atrazine-clearing plates. A. aurescens TC1 grew in liquid medium with atrazine as the sole source of nitrogen, carbon, and energy, consuming up to 3,000 mg of atrazine per liter. A. aurescens TC1 is metabolically diverse and grew on a wider range of s-triazine compounds than any bacterium previously characterized. The 23 s-triazine substrates serving as the sole nitrogen source included the herbicides ametryn, atratone, cyanazine, prometryn, and simazine. Moreover, atrazine substrate analogs containing fluorine, mercaptan, and cyano groups in place of the chlorine substituent were also growth substrates. Analogs containing hydrogen, azido, and amino functionalities in place of chlorine were not growth substrates. A. aurescens TC1 also metabolized compounds containing chlorine plus N-ethyl, N-propyl, N-butyl, N-s-butyl, N-isobutyl, or N-t-butyl substituents on the s-triazine ring. Atrazine was metabolized to alkylamines and cyanuric acid, the latter accumulating stoichiometrically. Ethylamine and isopropylamine each served as the source of carbon and nitrogen for growth. PCR experiments identified genes with high sequence identity to atzB and atzC, but not to atzA, from Pseudomonas sp. strain ADP.s-Triazine rings are common scaffolds for the synthesis of industrial chemicals; they are found in pesticides, plastic resins, dyes, and explosives (20). s-Triazine herbicides are widely used in modern agriculture, where they kill susceptible plants by coordinating to the quinone-binding protein in photosystem II, thereby inhibiting photosynthetic electron transfer (19). Atrazine (2-chloro-4-ethylamino-6-isopropylamino-1,3,5-s-triazine) is one of the most widely used herbicides in the United States for the control of broadleaf weeds in corn, sorghum, and sugarcane (1). Other s-triazine herbicides include ametryn, atratone, cyanazine, prometryn, and simazine.The fate of s-triazine compounds in the environment depends on the metabolic activities of soil microorganisms (7,14). Since 1994, a number of laboratories have independently isolated, by enrichment culture, several genera of gram-negative bacteria capable of atrazine dechlorination (4,16,22,31,33,35,36,38). Subsequent to dechlorination, metabolism of hydroxyatrazine liberates nitrogen to sustain bacterial growth. More recently, gram-positive bacteria from the genera Nocardioides (32) and Arthrobacter (22) have been shown to grow on atrazine, the former using atrazine as the sole source of carbon and nitrogen for growth. Streptomyces strain PS1/5 was also shown to metabolize several s-triazine herbicides in the presence of additional carbon and nitrogen in the growth medium (29).It is now established that bacteria metabolize melamine and the triazine herbicides such as atrazine via enzyme-catalyzed hydrolytic reactions (6,11,12,35). The enzymatic basis of atrazine mineralization has been most extensively studied in Pseudomonas sp. strain ADP (3,8,16,17...