1 EXPERIMENTAL PROCEDURES 2 Clay minerals: smectite. Smectite was extracted from bentonite (Georgia, Europe) from the 3 mine in Ozurgeti. A suspension of 20 g of bentonite in 700 mL of distilled water, containing 4 40 mL of Amberlite IR 1200 Na resin (Rohm and Haas) to facilitate dispersion, was shaken 5 for 16 hrs. The mixture was filtered and poured into 30 cm measuring cylinders, mixed for 1 6 minute and decanted (between 14 and 16 hrs). After decantation, the supernatant (the upper 7 20 cm according to Stokes’ law) corresponding to the clay fraction (particles of 2 m in 8 diameter) was recovered, transferred in small bottles and centrifuged (4,000 g, 1 h). The 9 pellets were dried at 75°C for 24 hrs. 10 TEM micrographs, X-ray and infrared spectroscopic analyses were performed and detected no 11 iron oxides at the surface of the purified clay, contrarily to quartz and carbonates which were 12 present before purification of the smectites. However, infrared spectroscopy showed the 13 possible presence of residual silica, colloidal or crystalline (Devineau et al., 2004). 14 To measure the ξ potential of the clay sample, a suspension of the smectitic material used in 15 the present study (1 g/L) was prepared in 0.01M NaCl electrolyte at pH 3.1 in an individual 16 HDPE tube, and the tube was gently shaken at 298K. At the end of the shaking period (3hs), 17 the final pH value of the sample was taken and was found to be equal to 3.9. The 18 electrophoretic mobility (EM) of the particles dispersed in the suspension was measured with 19 a Malvern NanoZS apparatus. The EM value was converted into ξ (surface) potential value by 20 using the Smolukowski equation. The ξ potential of the suspended particles was found to be 21 equal to - 41mV. The ξ measurement provided strong evidence for existence in the suspension 22 of only one type of particles, which show a negative value of surface potential at acidic pH. 23 This result is in good accordance with previously published data for smectites, which have 24 been widely reported to exhibit an overall negative charge at acidic pH (Delgado et al., 1986; 25 Horikawa et al., 1988; Zarzycki et al., 2007; Zadaka et al., 2010), unlike what is usually 1 26 observed for particles of (oxihydr)oxides of aluminum or iron (Del Nero et al, 2010). The ξ 27 potential result obtained here for the smectite rules out the existence of Fe-(oxihydr)oxides in 28 our smectite sample, either as coatings at the clay surface and/or as individual phases of Fe- 29 (oxyhydr)oxides of very small size (colloids). 30 The CEC of the smectite was determined using a hexamminecobalt trichloride solution 31 (Ciesielski and Sterckeman, 1997). The smectite preparation was sterilized by a combination 32 of heat and chemical treatments chosen to preserve the layer structures: the samples were 33 subjected to tyndallization treatment, with three cycles of heating for 2 hrs per day at 90°C, 34 followed by 15 days of incubation in chloroform (Hasnaoui et al., 2001). The smectite was 35 then rehydrated to a concentration of 20 g L-1 in distilled deionized water. 36 37 Bacterial strains and growth conditions. We used the wild-type P. aeruginosa ATCC 15692 38 strain and three siderophore mutants: PAO6297 (a pyochelin-deficient strain, (Serino et al., 39 1995)), PAO6382 (a pyoverdine-deficient strain, (Braud et al., 2009)) and PAO6383 (a 40 pyoverdine- and pyochelin-deficient strain, (Michel et al., 2007)). Bacteria were grown at 41 30°C overnight in LB broth medium at 200 rpm. For iron-depleted culture, cells were 42 harvested from a LB pre-culture (24 hrs incubation), washed twice in an iron-deficient 43 succinate medium (composition in g L-1: K2HPO4, 6.0; KH2PO4, 3.0; (NH4)2SO4, 1.0; 44 MgSO4.7H2O, 0.2; sodium succinate, 4.0; pH adjusted to 7.0 by addition of NaOH) (Meyer 45 and Abdallah, 1978) and used to inoculate fresh medium. The cultures were incubated for 48 46 hrs under shaking (200 rpm) and then centrifuged (10 min at 8,600 g) and washed twice with 47 succinate medium. Bacterial cell density was determined by measuring the optical density 48 (OD) at 600 nm. 49 Growth in the presence of smectite was performed in polycarbonate erlenmeyer flasks 50 (125 mL) in 20 mL of succinate medium supplemented with one of a series of concentrations 2 51 of smectite (0, 0.2, 1 and 10 g L-1). Each Erlenmeyer flask was inoculated with bacterial cells 52 to a final OD600 of 0.05 per mL. Controls without bacteria or without clay were included. 53 Erlenmeyer flasks were incubated at 30°C and shaken at 200 rpm for 28 hrs. Each condition 54 was replicated three times. One mL aliquots were removed after 4, 8, 24, and 28 hrs of 55 incubation and bacteria enumerated: samples were serially diluted and plated on LB agar 56 plates incubated at 30°C for 24 hrs. Results are expressed as “colony forming units” (CFU) 57 per mL. For each growth condition, the pH and the redox potential (Eh) were measured at the 58 beginning and at the end of the experiment. For the initial measurements of pH and Eh, a 59 flask from each experiment was sacrified to avoid adventitious bacteria that might be 60 associated with the electrodes. The redox potential was measured with an Ag/AgCl electrode. 61 62 Monitoring siderophore production in batch experiments. For each time point of bacterial 63 growth, 1 mL of culture was centrifuged for 10 min at 8,600 g and the amount of pyoverdine 64 in solution in the supernatant was estimated by monitoring absorbance at 400 nm 65 (Folschweiller et al., 2002). To measure pyoverdine trapped in the biofilm matrix, pyoverdine 66 was extracted using sodo-calcic glass beads in 10 mL of 200 mM Tris-HCl pH 7.0 buffer and 67 the absorbance monitored at 400 nm ( = 19 000 M-1 cm-1 for pyoverdine at pH 7). 68 Fluorescence microscopy was used to check the destruction of the biofilm. 69 The bacteria produce less pyochelin than pyoverdine and pyochelin cannot be detected 70 directly in culture supernatants without prior extraction. Due to the limited volumes of culture 71 supernatant available, this study focused only on pyoverdine. 72 73 Metal detection in bacterial batch growth experiments. P. aeruginosa cells were incubated 74 in the presence of smectite in succinate media. After 28 hrs of growth, the cultures were 75 centrifuged for 15 min at 4,500 g, and filtered through a 0.2 m pore-size membrane. The 3 76 filtrate was acidified to pH 1.0 with 70 % HNO3, and Al, Fe and Si were assayed by 77 Inductively Coupled Plasma Atomic Emission Spectrometry (ICP-AES, Liberty II, Varian, 78 Inc, Palo Alto, California). A certified solution (EU-H-2, SCP Science, Courtaboeuf, France) 79 was included in the analyses as a control for the determination step. Detection and 80 quantification limits were calculated for each batch of analysis according to Neuilly (1998) 81 (Neuilly, 1998). Quantification limits ranged from 0.67 to 1.00 µM for Al, 0.09 to 0.21 µM 82 for Fe and 7.12 to 12.46 M for Si. 83 84 Biofilm quantification. Biofilm formation in the presence or absence of smectite was tested 85 in 6-well plates (Greiner, TC-plate CELLSTAR), filled with 3 mL of succinate medium 86 supplemented with a series of concentrations of smectite (0, 0.2, 1 and 10 g L-1). Each well 87 was inoculated with bacterial cells to a final OD600 of 0.05 per ml and incubated at 30 °C for 88 28 hrs on a shaker (50 rpm). Controls without bacteria were included. Each condition was 89 repeated three times. For violet crystal treatment, culture supernatants were carefully removed 90 and the biofilm washed twice with sterile distilled water. One mL of 0.5 % crystal violet was 91 added and left in contact for 15 min at room temperature with gentle agitation. The solution 92 was removed, the biofilm was washed twice in sterile distilled water, and then the crystal 93 violet was eluted with 2 mL of ethanol. Biofilm was then quantified by measuring the 94 absorbance at 570 nm of the eluted crystal violet. 95 96 Microscopy. Smectite incubated for 28 hrs with or without bacteria in the succinate medium 97 was examined under light and epifluorescence microscope (Nikon Eclipse 50i, objective: CFI 98 Achroplan 100 x A ON 1.25 DT 0.18) connected to a numerix 12 bits DS-Fi1 camera. 99 Biofilm, stained naturally by the pyoverdine produced, was detected with a Bv2A Filter set 4 100 (excitation 400-440 nm, emission 470 nm, dichroic filter 455 long pass). Images were 101 captured using NIS imaging software elements. 102 103 Pyoverdine sorption on smectite. One g L-1 of smectite was incubated in the presence of 250 104 µM of pyoverdine in 10 mL of 2 mM MES, 725 µM Ca(NO3)2 buffer in 50 mL Falcon tubes 105 and shaken at 220 rpm. Controls without siderophore or without smectite were run in parallel. 106 Purification of pyoverdine accumulated in the culture supernatant of iron-starved growth of P. 107 aeruginosa was done by the XAD procedure, as described previously (Meyer et al, 1997). 108 Briefly, supernatant was acidified with HCl 6M (pH 6) and passed through an XAD-4 109 Amberlite column which retained the pyoverdine. After washing with 500 ml distilled water, 110 the pyoverdine was eluted with 250 ml 50% ethanol, concentrated using vacuum using 111 rotavapor and lyophilized (Meyer et al, 1997). Each treatment was replicated three times. At 112 various times (0, 1, 8, 24, 48 hrs), samples were centrifuged (8.000 g, 20 min), and the 113 supernatants were filtered (0.22 µm pore-size filters), acidified (to pH 1.0 with 70% HNO3) 114 and assayed for Fe and Al contents by ICP-AES. One mL aliquots of the supernatant 115 collected before acidification were used to measure siderophore concentrations by visible 116 light absorption (OD400 nm). 117 118 Statistical analysis. Data were analyzed using analysis of variance (ANOVA) and differences 119 among treatments were separated using Tukey’s test (Turkey, 1951), under R environment (R 120 Core Team (2012) R: A language and environment for statistical computing. R Foundation 121 for Statistical Computing, Vienna, Austria. ISBN 3-900051-07-0). 122 123 124 5 125 References 126 Braud, A., Hannauer, M., Mislin, G.L.A., and Schalk, I.J. (2009) The Pseudomonas 127 aeruginosa pyochelin-iron uptake pathway and its metal specificity. J Bacteriol 191: 5317- 128 5325. 129 Ciesielski, H., and Sterckeman, T. (1997) Determination of cation exchange capacity and 130 exchange cations in soils by means of cobalt hexamine trichloride. effects of experimental 131 conditions. 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FTIR profile of smectite (JASCO, 4100 type A, 2 cm-1 resolution) C. TEM micrograph of smectite (JEOL 2100F Cs 200KV 0.1nm resolution) 8