The distribution and phylogenetic affiliations of poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV)-degrading denitrifying bacteria in activated sludge were studied by a polyphasic approach including cultureindependent biomarker and molecular analyses as well as cultivation methods. A total of 23 strains of PHBV-degrading denitrifiers were isolated from activated sludges from different sewage treatment plants. 16S ribosomal DNA (rDNA) sequence comparisons showed that 20 of the isolates were identified as members of the family Comamonadaceae, a major group of -Proteobacteria. When the sludges from different plants were acclimated with PHBV under denitrifying conditions in laboratory scale reactors, the nitrate removal rate increased linearly during the first 4 weeks and reached 20 mg NO 3 ؊ -N h ؊1 g of dry sludge ؊1 at the steady state. The bacterial-community change in the laboratory scale sludges during the acclimation was monitored by rRNA-targeted fluorescence in situ hybridization and quinone profiling. Both approaches showed that the population of -Proteobacteria in the laboratory sludges increased sharply during acclimation regardless of their origins. 16S rDNA clone libraries were constructed from two different acclimated sludges, and a total of 37 clones from the libraries were phylogenetically analyzed. Most of the 16S rDNA clones were grouped with members of the family Comamonadaceae. The results of our polyphasic approach indicate that -Proteobacteria, especially members of the family Comamonadaceae, are primary PHBV-degrading denitrifiers in activated sludge. Our data provide useful information for the development of a new nitrogen removal system with solid biopolymer as an electron donor.Biological denitrification is an important process for nitrogen removal in wastewater treatment. Published reports suggest that 10 to 90% of bacteria in the activated-sludge system are capable of denitrification (16,33,44). However, the system is often confronted with the problem that the efficiency of nitrogen removal decreases due to low availability of organic matter as the reducing power for denitrification. To overcome this problem, a simple organic compound, such as methanol or acetate, is added intentionally as an electron donor to the denitrification process (16). In recent years, a new biotechnology of nitrogen removal using solid biopolymer as the electron donor has been developed (7). This type of nitrogen removal process, called here the solid-phase denitrification process, may have some advantages, e.g., a constant supply of reducing power, no secondary organic pollution, and ease of operation. A promising solid substrate for denitrification is the bacterial polyester poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV) (6, 30, 40, 52), which serves as the source of biodegradable plastic (4,17,34,50). The biodegradability of PHBV in natural environments has been extensively studied, and a number of PHBV-degrading bacteria have been isolated and characterized (1, 11, 38, 39, 41-43, 45, 55). The asso...