Atrazine chlorohydrolase, TrzN (triazine hydrolase or atrazine chlorohydrolase 2), initiates bacterial metabolism of the herbicide atrazine by hydrolytic displacement of a chlorine substituent from the s-triazine ring. The present study describes crystal structures and reactivity of wild-type and active site mutant TrzN enzymes. The homodimer native enzyme structure, solved to 1.40 Å resolution, is a (␣) 8 barrel, characteristic of members of the amidohydrolase superfamily. TrzN uniquely positions threonine 325 in place of a conserved aspartate that ligates the metal in most mononuclear amidohydrolases superfamily members. The threonine side chain oxygen atom is 3.3 Å from the zinc atom and 2.6 Å from the oxygen atom of zinccoordinated water. Mutation of the threonine to a serine resulted in a 12-fold decrease in k cat /K m , largely due to k cat , whereas the T325D and T325E mutants had immeasurable activity. The structure and kinetics of TrzN are reminiscent of carbonic anhydrase, which uses a threonine to assist in positioning water for reaction with carbon dioxide. An isosteric substitution in the active site glutamate, E241Q, showed a large diminution in activity with ametryn, no detectable activity with atratone, and a 10-fold decrease with atrazine, when compared with wild-type TrzN. Activity with the E241Q mutant was nearly constant from pH 6.0 to 10.0, consistent with the loss of a proton-donating group. Structures for TrzN-E241Q were solved with bound ametryn and atratone to 1.93 and 1.64 Å resolution, respectively. Both structure and kinetic determinations suggest that the Glu 241 side chain provides a proton to N-1 of the s-triazine substrate to facilitate nucleophilic displacement at the adjacent C-2.There is substantial evidence that microbes rapidly evolve new enzymes to metabolize anthropogenic chemicals (1, 2). The s-triazine herbicides, such as atrazine, were first introduced into the environment 50 years ago and Ͼ2 billion pounds have been applied globally. s-Triazine compounds were initially found to be poorly biodegradable, but more rapid biodegradation is observed today (3). Many atrazine-degrading bacteria have now been isolated (4 -6). They invariably contain highly conserved genes encoding enzymes that hydrolytically displace substituents from the s-triazine ring carbon atoms to generate cyanuric acid (Fig. 1). The genes, trzN, atzA, atzB, and atzC, are found on plasmids and now are distributed globally (7, 8). These observations are consistent with the idea that a new metabolic pathway for atrazine catabolism may have evolved and spread in recent evolutionary times (9).The s-triazine herbicides, such as atrazine (2-chloro-4-isopropylamino-6-ethylamino-1,3,5-triazine) and ametryn (2-thiomethyl-4-isopropylamino-6-ethylamino-1,3,5-triazine), are metabolized readily by dedicated enzymes. The enzymes have been purified to homogeneity and shown to be inactive with structurally analogous pyrimidines and other closely related compounds (10 -13). Moreover, the enzymes are isolated from bacteria...