To understand the energy conversion activities of the anaerobic sulfate-reducing bacteria, it is necessary to identify the components involved in electron flow. The importance of the abundant type I tetraheme cytochrome c 3 (TpIc 3 ) as an electron carrier during sulfate respiration was questioned by the previous isolation of a null mutation in the gene encoding TpIc 3 , cycA, in Desulfovibrio alaskensis G20. Whereas respiratory growth of the CycA mutant with lactate and sulfate was little affected, growth with pyruvate and sulfate was significantly impaired. We have explored the phenotype of the CycA mutant through physiological tests and transcriptomic and proteomic analyses. Data reported here show that electrons from pyruvate oxidation do not reach adenylyl sulfate reductase, the enzyme catalyzing the first redox reaction during sulfate reduction, in the absence of either CycA or the type I cytochrome c 3 :menaquinone oxidoreductase transmembrane complex, QrcABCD. In contrast to the wild type, the CycA and QrcA mutants did not grow with H 2 or formate and sulfate as the electron acceptor. Transcriptomic and proteomic analyses of the CycA mutant showed that transcripts and enzymes for the pathway from pyruvate to succinate were strongly decreased in the CycA mutant regardless of the growth mode. Neither the CycA nor the QrcA mutant grew on fumarate alone, consistent with the omics results and a redox regulation of gene expression. We conclude that TpIc 3 and the Qrc complex are D. alaskensis components essential for the transfer of electrons released in the periplasm to reach the cytoplasmic adenylyl sulfate reductase and present a model that may explain the CycA phenotype through confurcation of electrons. E nvironmental impacts of the sulfate-reducing bacteria (SRB), such as the formation of toxic sulfide and corrosion of metals, stem from SRB sulfate respiration and from vigorous metal metabolism, including both reduction and oxidation. The involvement of these bacteria in microbially influenced metal corrosion (1, 2) and their possible application for the remediation of toxic metal-contaminated environments (3, 4) have driven a systems biology investigation of their metabolism. To predict or control metabolic capabilities for beneficial environmental purposes, the bioenergetic pathways of the SRB need to be elucidated in more detail.Typically, SRB of the genus Desulfovibrio use H 2 , organic acid substrates, formate, or short-chain alcohols as electron donors for sulfate reduction, a process that occurs in the cytoplasm and is mediated by soluble enzymes. With hydrogen as the source of electrons, at an environmentally relevant partial pressure of 10 Pa (reduction potential [E=] ϭ Ϫ300 mV) (5), the first two-electron reduction of sulfate to sulfite (E 0 = ϭ Ϫ516 mV) cannot be accomplished without an additional energy input. Sulfate is activated at the expense of two ATP equivalents through the activity of sulfate adenylyltransferase (equation 1), producing adenosine phosphosulfate (APS), which increases th...