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Extracellular Electron Transfer of Pseudomonas Stutzeri Driven By Received: January 13, 2016 Electrochemistry Accepted: March 3, 2016 Published: May 5, 2016 The Electrochemical Society of Japan http://dx.doi.org/10.5796/electrochemistry.84.312 Communication Electrochemistry, 84(5), 312–314 (2016) Extracellular Electron Transfer of Pseudomonas stutzeri Driven by Lithotrophic and Mixotrophic Denitrification Tetsuya YAMADA,a Satoshi KAWAICHI,b Akihisa MATSUYAMA,c Minoru YOSHIDA,c Nobuhiro MATSUSHITA,d and Ryuhei NAKAMURAb,* a Department of Electronic Chemistry, Interdisciplinary Graduate School of Science and Engineering, Tokyo Institute of Technology, 4259 Midori, Nagatsuta, Yokohama 226-8503, Japan b Biofunctional Catalyst Research Team, RIKEN Center for Sustainable Resource Science, 2-1 Hirosawa, Wako, Saitama 351-0198, Japan c Chemical Genomics Research Group, RIKEN Center for Sustainable Resource Science, 2-1 Hirosawa, Wako, Saitama 351-0198, Japan d Department of Chemistry and Materials Science, Graduate School of Science and Engineering, Tokyo Institute of Technology, 4259 Midori, Nagatsuta, Yokohama 226-8503, Japan * Corresponding author: [email protected] ABSTRACT The present study investigated extracellular electron transfer (EET) of Pseudomonas stutzeri, a model organism for bacterial denitrification. Electrochemical cultivation of P. stutzeri in a lithotrophic medium with Fe2+ ions generated the clear cathodic current associated with denitrification reactions. The EET ability of P. stutzeri was greatly strengthened by the addition of acetate, which correlated with the enhanced rate of the enzymatic oxidation of Fe2+. Since the addition of acetate induced the change of cellular metabolisms from lithotrophic denitrification to mixotrophic one, the present finding suggests the effectiveness of EET monitoring as a descriptor of bacterial denitrification activity and changing metabolisms according to the environmental conditions. © The Electrochemical Society of Japan, All rights reserved. Keywords : Extracellular Electron Transfer, Denitrification, Pseudomonas stutzeri 1. Introduction Over the past century, human activity has increased the amount ¹ ¹ (A) OM of fixed nitrogen (NO3 ,NO2 ,NH3, etc.), which has led to the extensive eutrophication of fresh water and coastal zone, acid rain, Nap Nir N2 1 - - NO - NO2 NO and global warming. In particular, Haber-Bosch and fossil fuels NO3 2 Nos Periplasm N2O combustion have been the major cause of those environmental - - NO2 e problems, and their nitrogen fixation doubled the natural rate of e- - NO3 cyt c NorC terrestrial nitrogen fixation driven by microbial activity.2 Given that Complex I IM e- Q/QH Q/QH NorB increasing human population would further disrupt the nitrogen Nar cyt bc1 + - - cycle in nature, it is of utmost importance to restore and sustain the NADH NAD NO3 NO2 balance of nitrogen cycle. Considering the way to improve the CO2 Acetate / situation, decreasing the use of fertilizer in agriculture and or EET e- (from electrodes or fi fi minerals in nature) facilitating microbial denitri cation processes to return the xed (B) nitrogen to nitrogen gas are the promising approach. OM The denitrification process can be carried out by microorganisms ¹ ¹ / Fe2+ Fe3+ Nir which utilize NO3 and or NO2 as terminal electron acceptors for N - NO 2 NO2 3 - NO3 cellular bioenergetics. During the process, several metalloproteins - Nos Periplasm Nap e N2O - catalyze four successive steps of multielectron transfer reactions NO2 - NO2 fi - (Scheme 1). Demands for denitri cation differ from the situations; for NO3 cyt c NorC fi instance, the suppression of denitri cation is required in agricultural IM Q/QH Q/QH NorB ¹ Nar cyt bc1 lands, since its process competes with the uptake of NO3 by plants Fe(II):menaquinone oxidoreductase - - and thus results in the decreased efficiency of fertilizer. Contrary to NO3 NO2 this, enhancing microbial denitrification is an important target in the Scheme 1. Electron transfer models of denitrification pathway in environments where extensive eutrophication is observed. P. stutzeri. (A) Organotrophic denitrification is driven by NADH In an attempt to control the microbial denitrification depending on from inside the cell as a primary electron donor. NADH generation those different needs, we have focused on the ability of bacteria to is coupled to the oxidation of acetate. (B) Lithotrophic denitrifica- gain and release electrons from/to electrodes during the course of tion utilizes Fe2+ from outside the cell. Dotted arrows indicate the cellular metabolisms: bacterial extracellular electron transfer (EET). hypothetical electron flow. Both pathways comprise respiratory Recent advance in the field of ElectroMicrobiology4 has expanded nitrate reductase (Nar), nitrite reductase (Nir), NO reductase the concept of EET significantly not only to understand the microbial (NorBC), and N2O reductase (Nos). Furthermore, a periplasmic respiration with insoluble minerals,5 but also to control metabolic nitrate reductase (Nap) and the postulated nitrate/nitrite antiporter at pathways and even gene-expression patterns.6 For instance, the the inner membrane have been included in the models. 312 Electrochemistry, 84(5), 312–314 (2016) activity of TCA cycle and gene expression of Shewanella cells were 50 l mol 35 mo Amount of NO 6 µ regulated by changing electrode potential. It was also demonstrated / µ 30 NO - 25 200 that even cyanobacteria, which lack the ability to conduct EET, could 40 3 20 produced fi 2 15 sense the electrode potential by using arti cial redox mediators, formed / 10 2 150 and the redox state of plastoquinone and consequently the circadian 30 5 ND Amount of N 0 2+ - - 2+ 7 - Fe NO3 NO3 + Fe 3 - clock was regulated by electrode potential. These studies have NO3 consumed / and N + 4 100 encouraged us to hypothesize that the microbial denitrification 20 8,9 activity can be regulated by optimizing environmental redox states. , NH - 2 As a first step toward controlling bacterial denitrification, the 10 50 - µ NO NH4- present study investigated the EET ability of Pseudomonas stutzeri, 2 mol fi a model organism for the study of bacterial denitri cation. P. stutzeri 0 0 is characterized as its diverse and versatile bioenergetics for fi Amount of NO 0 50 100 150 200 250 denitri cation. It can utilize either organics, inorganics such as Time / h Fe2+, or both of them as an electron source for denitrification,3,10,11 ¹ which allows them to flexibly change the cellular metabolisms Figure 1. Time course of N-products and NO3 consumption by among organotrophic, lithotrophic, and mixotrophic denitrification P. stutzeri in medium containing 5 mM NaNO3 and FeSO4. Initial according to environmental conditions. Here we report the in-vivo OD600 was 0.9. Inset: N2 production by P. stutzeri for 162 h from monitoring of EET coupled with denitrification by P. stutzeri, and medium containing 5 mM of NaNO3 and FeSO4, and abiotic control demonstrate how the EET efficiency is affected by changing the with 5 mM NaNO3 and 5 mM FeSO4. culture media from lithotrophic to mixotrophic conditions. periplasmic enzymes, respectively.13 Although it is also reported 2. Experimental that P. stutzeri can perform lithotrophic denitrification reactions using extracellular Fe2+,10,11 it has been unknown how the electron Cell Preparation: P. stutzeri (JCM5965) was provided by Japan flow from Fe2+ drives denitrification, and also whether complete Collection of Microorganisms, RIKEN BRC which participates in denitrification can be possible or not (Scheme 1B). To get insight the National BioResource Project of the MEXT, Japan. Cells were into those questions, we firstly cultivated P. stutzeri in batch cultures cultured in autoclaved Lysogeny Broth medium (LB broth) and and analyzed the products of lithotrophic denitrification. incubated aerobically with shaking at 25°C. Subsequently, the The time course of the products from the cell culture cultivated culture was centrifuged at 6270 rpm for 5 min, and the pelleted cell with Fe2+ is shown in Fig. 1. No organic compounds were added in was washed with a fresh PS medium (10 mM NH4Cl, 1 mM MgCl2, the reactor as an electron donor. With increased cultivation time, both ¹ 0.5 mM CaCl2, 5 mM NaHCO3, 10 mM HEPES). This process was N2 and NO2 increased, which correlated with the consumption of ¹ + repeated 3 times. NO3 and a small increase of NH4 . The total amount of electrons ¹ Product Analysis: P. stutzeri was incubated in a deaerated PS consumed by the production of NO2 and N2 after 260 h of medium with Ar gas. We also used the modified PS mediums of cultivation was ³290 µmol, which was higher than the amount of 2+ which pH buffer was replaced by NaHPO4 and KH2PO4. The Fe added in the cell culture (200 µmol). Since this imbalance of amount of N2 production was measured by GC equipped with a stoichiometry is reproducible, we consider that organics accumulated TCD detector (GC-8A, Shimadzu). Hach kits (method no. 8192, inside the cells during preculture with LB and/or cell lysis provided ¹ ¹ 14,15 8507 and 8155) were used for the quantification of NO3 ,NO2 and surplus electrons for denitrification. The control experiments + + ¹ 2+ NH4 . For the detection of NH4 , the cells were incubated in the with the cell cultures lacking either NO3 or Fe generated less modified PS medium which lacks NH4Cl. amount of N2 (inset of Fig. 1). In addition, after cultivation of the ¹ 2+ Electrochemical measurements: A single-chamber, three-electrode cells in the presence of NO3 and Fe , the colorless cell suspension system was used for the electrochemical studies of intact
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