~ Pergamon 0043-1354(94)00177-4 War. Res. Vol. 29, No. 2, pp. 571-578, 1995 Copyright ~) 1995 Elsevier Science Ltd Printed in Great Britain. All rights reserved 0043-1354/95 $7.00 + 0.00 SULFIDE PRODUCT INHIBITION OF DESULFOVIBRIO DESULFURICANS IN BATCH AND CONTINUOUS CULTURES S. OKABE*~, P. H. NIELSEN~, W. L. JONES and W. G. CHARACKLIS Center for Biofilm Engineering, 409 Cobleigh Hall, Montana State University, Bozeman, MT 59717, U.S.A. (First received September 1993; accepted in revised form June 1994) Abstract--Sulfide product inhibition kinetics for growth and activity of Desulfovibrio desulfuricans was investigated in batch and continuous cultures at pH = 7.0. A non-competitive inhibition model adequately described sulfide product inhibition kinetics. Inhibition coefficient (K,) for maximum specific growth rate (/~hx) was 251 mg 1-1 S in a batch experiment. Cell yield determined in a chemostat was reduced in half by a sulfide concentration fabout 250 mg 1-1 S, which was very close to the K i value for the batch growth. Maximum specific growth rate (/z ~h x) and cell yield (Yc/e~c) were strongly inhibited by high levels of sulfide concentrations, whereas pecific lactate utilization rate increased with increasing sulfide concentrations. The results indicated an increase in the relative energy needed for maintenance to overcome sulfide inhibition and uncoupling rowth from energy production. However, D. desulfuricans tosome extent could recover from the shock of high sulfide concentrations. Stoichiometry for catabolic reactions (energy producing) did not change at high sulfide concentrations, while anabolic reactions (cellular synthesis) were strongly inhibited by high sulfide concentrations. These results uggested that separation of sulfide product inhibition into growth (cell yield) and activity (substrate utilization rate) was important o incorporate the sulfide product inhibition kinetics in a variety of applications. Key words--DesulJbvibrio desulfuricans, ulfide product inhibition, non-competitive inhibition kinetics, activity, cell yield, specific growth rate NOMENCLATURE D = dilution rate (t ~) i = total sulfide concentration (M~ 1-3) Ki = inhibition coefficient (M s 1-3) KLa ¢ = half-saturation coefficient for lactate (M s 1-3) m = maintenance oefficient (M s M~ 1 t - 1 ) S = effluent lactate concentration (Ms 1-3) TS = total sulfide (Mi 1-3) Y~n[~a c = intrinsic ell yield coefficient on lactate (M,. M( I ) Yc:Lac = observed cell yield coefficient on lactate (M,. M~ I ) /~ = specific growth rate (t - i ) /2ma x: maximum specific growth rate in the absence of sulfide (t i ) /~ = maximum specific growth rate in the presence of sulfide (t - i ) INTRODUCTION Sulfate reducing bacteria (SRB) cause serious prob- lems in sanitary sewer systems and industrial water systems because of production of highly toxic and corrosive hydrogen sulfide gas. The corrosion of *Present address: Department of Civil and Environmental Engineering, Miyazaki University, Miyazaki, Japan. i'Author to whom all correspondence should be addressed. :~Present address: Environmental Engineering Laboratory, Aalborg University, DK-9000 Aalborg, Denmark. concrete sewers occurs as a result of hydrogen sulfide production from sulfate-rich sewage by the activities of SRB (Mori et al., 1992). Furthermore, problems are well known in the oil industry where SRB cause serious corrosion of installations, plugging of for- mations, and contamination of petroleum with H2S (souring). In these industries, mathematical models have been developed for predicting and controlling SRB activity. A range of environmental factors affects the growth and activity of SRB and other bacteria in these systems, and a more quantitative knowledge of the significance of those environmental factors is needed for improving the mathematical models. One important factor is sulfide, a metabolic product from sulfate reduction, which has been re- ported inhibiting SRB growth and activity. Very high sulfide concentrations have, for example, been found throughout a petroleum formation with concen- trations up to 1000 mg I-~ H2S in the produced water (Subcasky, 1991), and may appear in anaerobic treat- ments of sulfate-rich wastewater (Hilton and Archer, 1988). Therefore, sulfide product inhibition may be expected to some extent in these industrial water systems. Several studies of sulfide inhibition have been performed on anaerobic wastewater treatment, 571 572 S. OKABE et al. ~- ~.~ ~ ~ =~ - _ ~ . . NNO ~ b~ =N~-N ¢~ r.) .< r.; 0 0 0 ._ .~ ~.=..~ . - ~ . t . . - e~ rr ~ ,,,, 'r ~ I ¢~- ~V~ ~ ~ I t< t< ¢< O~ o'~ oq ~t3 g ~g g .~-~ --~ ~ ~ ~ ..= especially on methane producing bacteria (Karhad- kar et aL, 1986; Koster et al., 1986; Hilton and Archer, 1988; Rinzema and Lettinga, 1988; Hilton and Oleskiewicz, 1989; Oleszkiewicz et aL, 1989; McCartney and Oleszkiewicz, 1991). The overall effect of sulfide on microbial sulfate reduction has been described qualitatively by several authors (Post- gate, 1984; Klemps et al., 1985; Shimada, 1987; Hilton and Oleskiewicz, 1989; Min and Zinder, 1990; McCartney and Oleszkiewicz, 1991; Reis et al., 1991; Okabe el al., 1992; Reis et al., 1992). The relevant literature is summarized in Table 1. However, no quantitative SRB sulfide product inhibition datum has been reported. Most of the data listed in Table ! are obtained from the batch experiment, inwhich pH, sulfide concentration, and limiting substrate cannot be maintained at the same levels over many gener- ations. Therefore, batch culture data reported in the literature must be interpreted cautiously. Sulfide toxicity is strongly dependent on pH, because the chemical equilibrium of sulfide species is pH depen- dent. At pH 8 most of total sulfide (TS) is in the HS- form, while at pH 6 most is in the n2s form. Molecu- lar hydrogen sulfide (H2S) has been found to be the major toxic form of sulfide because H2S can pass through the cell membrane (Speece, 1983; Reis et al., 1991). The distinction between growth and activity becomes very important when the environmental conditions become xtreme and energy consumption shifts from growth to maintenance (Hunik et al., 1990). Thus, it is speculated that under high sulfide conditions, the growth-associated H2S production will decrease, whereas total H2S production will remain relatively constant because the decrease in growth is counter balanced by increased nongrowth- associated H 2 S production caused by increased main- tenance nergy requirement. The goal of this paper is to describe quantitatively effects of sulfide on activity and growth of SRB, here exemplified by Desulfovibrio desulfuricans. The dis- tinction between growth and activity was clearly made in this study; growth was defined as biomass (cell) production rate and activity was defined as substrate utilization rate (e.g. lactate). THEORETICAL B A C K G R O U N D In this study, it is assumed that sulfide is a non- competitive inhibitor, which decreases maximum specific growth rate (#max) but does not alter half- saturation coefficient (KLan). Non-competitive inhi- bition kinetics for lactate-limited cultures can be described as follows (Aiba et al., 1973) /Jmax SKi = (I) (Kt~ + S)(K, + i) where i =sulfide concentration (M~l-3), K i= inhibition coefficient (Mil-3), S=eff luent lactate Sulfide product inhibition kinetics 573 concentration (M~ 1-3), and/~ = specific growth rate ( t - ' ) . For S>>KL~c (e.g. in a batch culture), equation (1) can be simplified and linearized by plotting "" ~,h 1/12 max against i 1 1 i + - - (2 ) inh •max Ki Pm~,, /-tm~,, where irih - - #m~- maximum specific growth rate in the presence of sulfide (t - j) . Thus, the x-interception of a best fit line gives -K i - However, equation (2) cannot be applied to the case of S - KL~ ¢ (i.e. in a chemostat culture). inh #m~, in a steady state chemostat at various sulfide concentrations can be determined based on a theor- etical construct extrapolated from the measured lac- tate concentration (S) to what i,h /~m~ would be based on the ratio of Kt~c to S as described rearranging equation (I) i.h _ D(KL~¢ + S) m~ - (3) S The value of KL~, has been determined previously in a similar type of experiment (Okabe et al., 1992). In this study, steady state S's were determined at a constant dilution rate (D) and various sulfide concentrations. In this way, the effect of sulfide nn inh concentration ~. . /~ can be evaluated easily instead of conducting a series of experiments to determine dependence of S on D at various sulfide concen- trations. EXPERIMENTAL MATERIALS AND METHODS Microorganisms Desulfovibrio desulfuricans (ATCC 5575) was grown in Postgate medium G (Postgate, 1984) including Na-lactate (oL-lactic acid, SIGMA, L-1375) and Na2SO4. Trace el- ements and vitamins were added. The details of medium preparation and preculture of microorganisms have been described elsewhere previously (Okabe and Characklis, 1992). Batch culture experiment Sulfide inhibition kinetics were determined in batch experiments using 500 ml Erlenmeyer flasks. Flasks were equipped with butyl rubber stoppers fitted with an injection port and a gas exchange port. 400 ml of the pH adjusted (pH = 7.0). Postgate medium G (Postgate, 1984) containing 500 mg 1- ~ of lactate and 800 mg 1 - t of sulfate was dispensed into each Erlenmeyer flask and autoclaved at 121°C for 20 min. Trace elements and vitamin solutions were aseptically added after cooling. Na2S' 9H20 solution was prepared separately inan air-tight bottle. After autoclaving, the pH of the sulfide solution was adjusted to 7.0 in the air-tight bottle using a sterile syringe and sterile 1.0 N HCI and NaOH solutions. Then appropriate volumes of the sulfide solution were added to the autoclaved culture medium to obtain the designed total sulfide concentrations (0, 70, 220, 350, 700mgl -~ S). After addition of sulfide solution, the pH of the culture medium was remeasured and readjusted using sterile syringes. A sterile oxygen-free Na- dithionite solution was added to the sulfide-free medium to provide the required negative redox potential for growth (the final concentration of NazS204 was approximately 30 rag/l). D. desulfuricans taken from an actively growing chemostat culture was inoculated into each flask and incu- bated at 35°C. The inoculum size from the chemostat was adjusted to obtain an initial cell count of approximately I × 10 7 cells ml -I. Continuous culture experiment The effect of sulfide on the activity and growth was determined in a lactate-limited chemostat operated at a constant dilution rate (D) of 0.20 h -~. The chemostat was equipped with a butyl rubber wall growth scraper continu- ously rotated by an electric motor to prevent wall growth. Constant pH (+0.1 unit) and temperature (_.+0.5°C) were maintained using a pH control system with sterile 1.0 N HCI and NaOH solutions and thermoregulator, respectively. Various concentrations of sulfide solutions with pH roughly adjusted to 7.5, were separately prepared and autoclaved, then fed to the chemostat by a peristaltic pump and speed controller (Cole-Parmer, Chicago, IU). A fine pH adjust- ment was conducted in the chemostat. Na-dithionite (Na2 $2 O4) was added to the sulfide-free medium to provide the required negative redox potential. Redox potential was monitored continuously using a redox probe (Orion) with a saturated calomel reference lectrode during the course of the experiments. The reported redox potential was standarized to a hydrogen redox couple. The details of chemostat set up protocol have been described elsewhere previously (Okabe and Characklis, 1992). Analytical methods At steady state, chemostat effluent samples were obtained for the following analyses: (1) total organic arbon (TOC); (2) soluble organic arbon (SOC); (3) total bacterial counts and cell size; (4) sulfate; (5) sulfide; (6) lactate; (7) acetate. The samples for SOC, lactate, and acetate were prepared by centrifugation at20,000 g and 4°C for 20 min using stainless steel centrifuge tubes. The obtained supernatant was sub- jected to these analyses. The sample for sulfate analysis was fixed with 1% (w/v) ZnAc solution to remove sulfide species and then filtered by Sterile Acrodisc filter (pore size 0.2/~m, Gelman Science, No. 4192). Sulfate and acetate concentrations were measured using an ion chromatograph (DIONEX A1-450). Total dissolved sulfide concentration (TS, in mg l- ~ S) in the liquid phase was measured using the methylene blue method described previously by Cline (1969). Total cell number and cell size were measured using an image analyzer (Cambridge/Olympus Quantment 10) by the epifluorescence method escribed previously by Hobbie et al. (1977). Samples (variable volumes) for cell counts were obtained irectly from the chemostat, homogenized, stained with 0.02% acridine orange solution, and fixed on Nucle- pore filters (0.2ttm pore size, 25mm dia.). Cell number was reported as the mean of more than 20 measurements along the filter. Cellular carbon concentration was deter- mined converting cell size determined by an epifluorescence technique to cellular carbon using various factors (Okabe and Characklis, 1992). The details of the rest of the chemical analytical methods have been described elsewhere pre- viously (Okabe and Characklis, 1992). RESULTS Batch experiments Maximum specific growth rate in the presence of sulfide (/1 ~h ) of D. desulfuricans was determined from the cell doubling times (td) at various total sulfide concentrations in batch cultures containing excess substrates (Fig. 1). The initial growth rates at various sulfide concentrations were determined by linear in- terpolation of the data in Fig. 1 because total sulfide concentration, substrate concentrations (i.e. lactate and sulfate), and the pH of culture medium changed 574 S. OKABE et al. 1.0E+09: ~. 1.0E+08 E ~ 1.0E+07 1'o ~ a'o ,/o 5o Tlrne (hour) Initia Sulfide Concentration --=-- 0 mg/L --*-- 70 mg/L + 224 mg/L 342 mg/L --at- 693 mg/L 60 Fig. 1. Effect of sulfide on growth of D. desulfurtcans batch cultures: temperature = 35°C, pH = 7.0. in during the incubation. Cell numbers for initial sulfide concentrat ions of 0, 70, and 224 mg 1- ~ S leveled off after 30 h due to depletion of lactate. For data interpretation pH and total sulfide concentrations, doubl ing times, and corresponding maximum specific growth rates (#i,]ahx) are presented in Table 2. The maximum specific growth rates " ~,h, ~,[/max ) deter- mined in the batch cultures never exceeded 0.20 h-J at each total sulfide concentration, which was signifi- cantly lower than values of continuous culture. The inhibition coefficient for maximum specific growth rate, Ki, was determined to be 251 mgl - t S using the non-competit ive inhibit ion model [equa- tion (2)] as shown in Fig. 2. A high square of correlation coefficient (r 2) indicates that the non- competitive inhibit ion model adequately described sulfide inhibition. Continuous experiments Response to step changes in sulfide concentration. D. desulfuricans growing at a constant dilution rate (D) of 0.20 h ~ at 35°C and pH = 7.0 was continu- ously exposed to high total sulfide concentrations to examine the response to step changes in sulfide concentrat ion in terms of growth and activity. Sulfide solutions were fed continuously into the reac- tor to maintain constant otal sulfide concentrations during the experimental period. The initial total dissolved sulfide concentrations in both exper- iments were about 20 mg 1-' S. Addit ion of sulfide solutions was started at time zero. Cell concentra- tion decreased about 25% after 8 h exposure to Table 2. Results of sulfide ffect on the maximum specific growth rate of D. desulfuricans in batch cultures. Initial lactate and sulfate concentration were 500 and 800 mgl ' respectively TS (mgl IS) pH Initial End Initial End t d (h) ,u';h~ (h ') 0 81 6.96 6.90 4.0 0.17 70 161 6.95 6.82 3.5 0.20 224 303 7.30 7.06 5.5 0.13 342 390 7.00 6.95 7.0 0.10 693 729 6.95 6.80 12.0 0.058 20. A .c | !,2 ~8 E J 0 .4oo .ao0-a0o-lb0 o 16o a6o a0o Ah0 s0o e~o r00 Total Sulfide Concentration (mg-S/I.) Fig. 2. Determination of K i value in the batch culture. Theoretical plot of the reciprocal of maximum specific growth rate in the presence of sulfide ~nh (I//~m~x) as a function of sulfide concentration. K i of 251 mg 1-1 S was determined (r 2 = 0.96). 133___ 10mgl ~ S, but recovered gradually to the original level after about 40 h [Fig. 3(a)]. The activity expressed as fractional lactate util ization [(Si - S)/Si] was relatively constant during the experimental period as effluent lactate concentrat ion increased slightly only after sulfide addition. Cell concentrat ion decreased 64% by exposure to 212_ 23 mgl -~ S. However, it recovered and approached a steady 14 8 ~8 (a) Ca~ll Number 4 Lactate Cone. 2 -20 0 20 40 60 80 Time (hour) 30 2o ~ q,l 0 ~ lO0 14 10 8 ~ 4 2 -20 (b) Cell Number 20 40 60 80 Time (hour) 40 30 ;~ o 2o ~ I00 ~ Fig. 3. Typical response of cell concentration and effluent lactate concentration to exposure to (a) 133+10mgl - IS and (b) 212_23mgl -IS: D=0.20h -I, temperature= 35~'C, pH = 7.0. Error bars represent he standard eviation of mean (n = 2). Sulfide product state value, which was about 55% of the original cell concentration. A spike increase in effluent lactate concentration was observed after sulfide addition. Afterwards the effluent lactate concen- tration stabilized in the range of 0-5.0 mgl -~ even though the cell concentration was reduced by 45%. The culture approached steady state after about 40 h in both cases. Therefore, all samples in later exper- iments were taken at about 40h after the sulfide concentration was changed. Standard deviations of duplicate measurements of all cell counts were within 20% of their respective mean values, which indicating that the accuracy of cell count is reliable. Redox potential was below -180 mV during both experiments. Effect of sulfide on cell yield. Cell yield was deter- mined in a chemostat at various sulfide concen- trations (Fig. 4). The cell yield was maximum at 108 mgl -~ S, after that it decreased with increasing sulfide concentration. The cell yield was reduced in half at about 250mgl-~S (Fig. 4). The effluent lactate concentration, however, remained relatively constant with increasing total sulfide concentration up to 332 mg 1- I S and increased to only 22.2 mg l- at 437mgl ~S (Fig. 4), indicating that activity ex- pressed as fractional actate utilization [ (S i - S)/Si] was not affected in this range of sulfide concentration. These results uggested that specific lactate utilization rate increased when D. desulfurieans grew in high sulfide concentrations. Effect of sulfide on growth rate. Maximum specific - inh x growth rates U~m,x) were determined at various sul- fide concentrations u ing equation (3) with the efflu- ent lactate concentrations and gLa c of 2.35 mgl (Okabe and Characklis, 1992) (Table 3). The maxi- mum specific growth rate in the presence of sulfide (/li,~hx) decreased from 0.33 h -1 at low levels of TS to 0.21 h -~ at high levels of TS. /t~x determined in the chemostat was higher than the one determined in the batch study at a corresponding sulfide concentration. 0.05 0.04 0.03 0.02 _ 0.01 0 5O v i i i , i 100 200 300 400 Total Sulfide Concentration (sg-S/L) 40 30 20 10 500 Fig. 4. Effect of sulfide concentration on cell yield and effluent lactate concentration: D = 0.20 h L tempera- ture = 35°C. Error bars represent the standard eviation of mean (n = 2). inhibition kinetics 575 Table 3. The effect of sulfide on the maximum specific growth rate in a chemostat (mean + SD) Effluent lactate TS (mgl IS) concentration i,h (h t) ,Umal 26.1 + 1.0 3.6_+0.2 0.33 108.2 + 3.8 4.3 + 0.1 0.31 157.9_+ 19.0 6.1 _+0.3 0.26 259.1 -+ 16.9 6.7-+0.8 0.24 284.4 -+ 7.1 7.6 -+ 0.2 0.25 332.0 -+ 8.6 5.7 ± 0.1 0.26 378.5-+ 13.0 9.8_+0.1 0.22 437.5 ± 7.8 22.2 _+ 0.4 0.21 Stoichiometry. Stoichiometry of sulfate reduction was determined at each sulfide concentration to elucidate whether the presence of sulfide results in an alteration of the metabolic pathway(s) for sulfate reduction. The stiochiometric ratios for catabolic (energy producing) reactions uch as lactate oxidized to sulfate reduced, CO 2 produced, and acetate pro- duced were independent of sulfide concentration (Table 4). The ranges of 0.42-0.51 for SO~-/lactate, 0.81-0.94 for acetate/lactate, and 1.01-1.12 for CO2/lactate approached the theoretical ratios of 0.47, 0.94, and 0.94, respectively (Okabe and Characklis, 1992). However, the stoichometric ratio for anabolic (cell synthesis) reactions, cell/lactate (i.e., cell yield), decreased with increasing total sulfide concentrations. DISCUSSION Effects of sulfide on cell yield and specific lactate utilization It was very important o separate the effect of sulfide inhibition into an effect on cell yield (growth) and on lactate utilization rate (activity) for a correct interpretation of experimental data. Cell yield de- creased ramatically from 0.036 (g cell)(g lactate)- at low levels of TS to 0.011 (g cell)(g lactate) ~ at 437mg1-~S, while fractional lactate utilization (shown as effluent lactate concentration i Fig. 4) decreased at TS of only 437 mg 1 -l S. This decrease in cell yield may have been a result of a large part of the energy source being used for maintenance and uncoupling growth from energy production. Cell yield is known to be dependent on ~, the maintenance coefficient (m), and the intrinsic cell Table 4. Steady state stoichiometry of the continuous culture of D. desulturicans exposed to various total sulfide concentrations at a constant dilution rate of 0.20 h ~ (mean ± SD) Stoichiometric ratio (M/M) Total sulfide (mgl t S) SO] /Lac Ac/Lac. CO2/Lac. Cell/Lac. 26.1 -+ 1.0 0.42 0.85 1.03 0.148 108.2 ___ 3.8 0.50 0.81 1.08 tL 174 157.9 -+ 19.0 0.49 0.84 1.05 0.128 259.1 + 16.9 0.46 0.88 1.12 0.083 284.4 + 7.1 0.51 0.91 1.01 0.067 332.0 + 8.6 0.51 0.88 1.08 0.076 378.5 -+ 13.0 0.48 0.83 1.09 0.065 437.5 + 7.8 0.47 0.94 1.01 0.043 576 S. OKABE et al. 12 10. 8 8- 8 "~ 2- 0 • , 0 5O 1(~ 1,~ 200 250 300 3~ 400 450 Total Sulfide Concentration (rag-S/L) Fig. 5. Effect of sulfide concentration on maintenance coefficient (m). The maintenance oefficient was calculated based on equation (4) using i,t, _ Y~/L~¢ --0.03 g cell (g lactate)- l (Okabe et al., 1992). yield intr (Yc/LJ and is expressed as follows (Bulthuis, 1989; Characklis, 1990) 1 m 1 - - =- + int------V-" (4) Yc/Lac D Yc/Lac The maintenance nergy was calculated using the observed cell yield (Yc/~c) in this study and the intrinsic cell yield of ~ntr Yc/Lac = 0.03 g cell (g lactate)- l measured in a similar type of experiment without sulfide inhibition (Okabe et al., 1992) (Fig. 5). The calculated maintenance oefficient increased ra- matically at total sulfide concentrations above 200 mg 1 -~ S. A similar effect of sulfide has been observed in other types of bacteria. Mountfort and Asher (1979) reported that the biomass yield, the specific growth rate, and the intracellular levels of adenosine tri- phosphate (ATP) decreased with increasing sulfide level when Methanosarcina barkeri strain DM was grown in a batch system with methanol as carbon and energy source. Furthermore, they observed an increase in specific methane production rate. They concluded that the decrease in biomass yield resulted from an increase in the maintenance coefficient and uncoupling rowth from energy production. Hobson and Millis (1990) also reported that the maintenance energy requirements for a mixed culture grown in a two-stage chemostat with phenolics increased with increasing sulfide concentration, possibly due to the need to repair damaged cell membranes. Although data derived from batch culture exper- iments are often problematic, a degree of sulfide inhibition on cell yield in the chemostat agreed reasonably with the inhibition coefficient for #~nhmax (K~-----251 mgl -~ S) determined in the batch study, which is dependent on cell yield. The cell yield determined in the chemostat was reduced 50% at a sulfide concentration near 250 rag/l, even though K~ could not be determined in the chemostat study because equation (2) could not be used since the chemostat culture was lactate limited (S--KL,~). This degree of sulfide inhibition on cell yield also agreed with the result of the recovery from sulfide shock which showed that the cell number was re- duced to 55% of the original value by exposure to 212_ 23 mgl - t S [Fig. 3 (b)]. These results indicate that separation of sulfide inhibition into growth (cell yield) and activity (substrate utilization rate) is essen- tial to interpret experimental data correctly. Effect of sulfide on specific growth rate The maximum specific growth rates in the presence of sulfide (#~x) determined in the batch culture were significantly lower than the continuous culture data at each corresponding sulfide concentration. In our previous studies (unpublished ata), lower growth rates have been observed frequently in batch cultures, which is a normal observation for most SRB (Okabe and Characklis, 1992). This discrepancy of the values inh of/~max between the batch and the continuous exper- iment is attributed to several factors. Firstly, inh #ma~ for the continuous experiment was determined from the measured lactate concentration to what inh g~ would be based on the ratio of KL,¢ to S [equation (3)], which is yield independent. In contrast, ~nh #m~ for the batch experiment was determined by directly measuring the increase in cells, which is yield dependent. Specific growth rate (#) is directly proportional to the lactate utilization rate unless maintenance nergy require- ment and intrinsic cell yield change [equation (4)]. If maintenance energy requirement increases due to sulfide inhibition, specific lactate utilization conse- quently increases. As a result of the increase in maintenance energy requirement, or in other words, the increase in specific lactate utilization, lactate concentration i the chemostat remained relatively constant and low, even though cell concentration decreases. Thus, specific growth rate determined in the chemostat under sulfide inhibition was higher than that observed in the batch experiment. Secondly, the discrepancy is in part attributed to the selection of less susceptible microorganisms to high sulfide concentrations and the recovery from sulfide shock in the continuous culture as demon- strated in Fig. 3(a) and (b). Another contributing factor for the low cell yield could be that death and lysis rates may increase at high sulfide levels. Final ly, sulfide precipitates Fe in the batch exper- iment, so that Fe and other trace nutrients (not the carbon and energy source) may become the rate limiting factor. Moreover, pH, sulfide concentration, and limiting factor cannot be maintained at the same levels over many generations. If sulfide concentration changes as they grow, the pH shifts, or vice versa, another stress is imposed on the population which also requires more maintenance energy. Effect of sulfide on stoichiometry The stoichiometric ratios for catabolic reactions in this study did not change at high levels of TS. Thus, the same amount of energy (ATP) was generated Sulfide product from substrate-level-phosphorylation nd electron transport system (i.e. reduction of sulfate to sulfide). However, lower cell yields were observed in this study at high levels of sulfide, suggesting an increase in maintenance energy and uncoupling rowth from energy production. Minor changes in the anabolic products would not have been detected in this study because of the precision of the analytical methods used in this study. Effect of wall growth Hill and Robinson (1975) reported that a possible wall growth in a chemostat culture exerts significant effects on the cell concentration a d substrate utiliz- ation. Thus, the possible wall growth increases specific substrate utilization rate as a result of the decrease in suspended cell concentration. To evaluate the effect of wall growth on experimental results obtained in this study, the concentration of cells attached to the possible surfaces in the reactor system during an experimental period (about 2 weeks) was measured. The total numbers of attached cells were measured using the epifiuorescence t ch- nique at the end of the experiment and found to be 2.4 x 104 cells cm -2, which is approximately 10% of an average total suspended cell concentration for the reactor with surface area of 613 cm 2. Thus, the effect of wall growth was regarded as insignificant in this experiment. Implication in sulfide inhibition model The kinetics of D. desulfuricans growth on lactate as a function of sulfide concentration are presented in Fig. 6 based on experimentally determined rate coefficients (Okabe and Characklis, 1992; Okabe et al., 1992) including the inhibition coefficient of 251 mgl ~S determined in the batch experiment. These results suggest hat under high sulfide con- centrations uch as in the petroleum formation [0-1000mgl -t H2S (Subcasky, 1991)] and waste- water treatment systems (Hilton and Archer, 1988), sulfide inhibition kinetics should be considered in inhibition kinetics 577 biological sulfide production models. Although other nutritional and physical conditions are suitable for SRB growth, SRB growth may be strongly inhibited by high sulfide concentrations. Furthermore, unless a change in specific sulfate reduction rate with increas- ing sulfide concentrations is taken into account, it is not possible to estimate the resulting sulfide pro- duction from growth rate data only. For instance, if SRB growth is monitored as change in total SRB cell count, it may underestimate H2S production under inhibitory levels of sulfide concentration because the specific H2S production rate may be elevated at higher sulfide levels even through bacterial growth rate and biomass production rate decreased by sulfide inhibition. CONCLUSIONS Effects of sulfide on growth and activity of D. desulfuricans were quantitatively investigated in this paper. It can be concluded that separation of sulfide inhibition into cell yield (growth) and activity (lactate utilization rate) must be emphasized based on the following specific conclusions: 1. Cell yield and maximum specific growth rate decreased with increasing sulfide concentrations, whereas pecific lactate utilization rate increased. 2. Inhibition coefficient (Ki) for maximum specific growth rate was 251 mg I ~ S in the batch experiment. 3. Cell yield determined in the chemostat was reduced in half by a sulfide concentration f approxi- mately 250 mg 1- ~ S, which was very closed to the K~ value determined in the batch culture. 4. D. desulfuricans growing in the chemostat could recover from the shock of high sulfide concentrations. 5. A non-competitive inhibition model adequately described sulfide inhibition of D. desulfuricans in the batch experiment. Acknowledgements--The authors gratefully acknowledge support from the cooperative agreement ECD-8907039 between Montana State University and the National Science Foundation and from the Center Industrial Associates, 0.4 0.35 0.3 0.25 0,2 0.15 • g 0. 1 m 0.05 1:0 I:50 1:100 I:150 1:200 I =250 110 ;0 3'0 ;0 50 Lactate Concentration (mg/L) 60 Fig. 6. Results of model simulation. Inhibition coeffi- cient (K~) was determined from experimental data: K~ = 251 mg 1 -J S,/lm, ~ = 0.34 h- 1 KL~¢ = 2.35 mg 1- i (Okabe and Characklis, 1992; Okabe et al., 1992). REFERENCES Aiba S., Humprey A. E. and Mills N. F. (1973) In: Biochemical Engineering, 2nd edn, p. 97. Academic Press, New York. Bulthuis B. A., Koningstein G. M., Stouthamer A. H. and Van Verseveld H. W. (1989) A comparison between aerobic growth of Bacillus licheniformis in continuous culture and partial-recycling fermentor, with contri- butions to the discussion on maintenance energy demand. Arch. Microbiol. 152, 499-507. Characklis W. G. (1990) Kinetics of microbial transform- ations. In: Biofilms (Edited by Characklis W. G. and Marshall K. C.) Wiley, New York. Cline J. D. (1969) Spectrophotometric determination of hydrogen sulfide in natural waters. Limnol. Oceanog. 14, 454-458. Hill G. A. and Robinson C. W. (1975) Substrate inhibition kinetics: phenol degradation by Pseudomonas putida. Biotechnol. Bioengng 17, 1599-1615. 578 S. OKABE et al. Hilton B. L. and Oleskiewicz J. A. (1989) Sulfide-induced inhibition of anaerobic digestion. J Environ. Engng 114, 1377-139 I. Hilton M. G. and Archer D. B. (1988) Anaerobic diges- tion of a sulfate-rich molasses wastewater: Inhibition of hydrogen sulfide production. Biotechnol. Bioengng 31, 885-888. Hobbie J. E., Daley R. J. and Jasper S. (1977) Use of nucleopore filters for counting bacteria by fluorescence microscopy. Appl. Envir. Microbiol. 33, 1225-1228. Hobson M. J. and Millis N. F. (1990) Chemostat studies of a mixed culture growing on phenolics. J. Wat. Pollut. Control Fed. 62, 684-4591. Hunik J. H., Hamelers H. V. M. and Koster I. W. (1990) Growth-rate inhibition of acetoclastic methanogens by ammonia and pH in poultry manure digestion. Biol. Wastes 32, 285-297. Karhadkar P. P., Audic J. M., Faup G. M. and Khanna P. (1986) Sulfide and sulfate inhibition of methanogenisis. Wat. Res. 21, 1061-1066. Klemps R., Cypionka H., Widdel F. and Pfenning N. (1985) Growth with hydrogen, and further physiological charac- teristics of Desulfotomaculum species. Arch. Microbiol. 143, 203-208. Koster I. W., Rinzema A., De Vegt A. L. and Lettinga G. (1986) Sulfide inhibition of the methanogenic activity of granular sludge at various pH-levels. War. Res. 20, 1561-1567. Lehninger A. L. (1982) Enzymes. In Principles of Biochem- istry (Edited by Lehninger A. L.), pp. 207-247. Worth, New York. McCartney D. M. and Oleszkiewicz J. A. (1991) Sulfide inhibition of anaerobic degradation of lactate and acetate. Wat. Res. 25, 203-209. Min H. and Zinder S, H. (1990) Isolation and characteriz- ation of a thermophilic sulfate-reducing bacterium Desul- fotomaculum thermoacetoxidans sp. nov. Arch. Microbiol. 153, 399-404. Mori T., Nonaka T., Tazaki K., Koga M., Hikosaka Y. and Noda S. (1992) Interactions of nutrients, moisture, and pH on microbial corrosion of concrete sewer pipes. War. Res. 26, 29-37. Mountfort D. O. and Asher R. A. (1979) Effect of inorganic sulfide on the growth and metabolism of Methanosarcina barkeri strain DM. Appl. Envir. Microbiol. 37, 670-475. Okabe S. and Characklis W. G. (1992) Effects of tempera- ture and phosphorous concentration microbial sulfate reduction by Desulfovibrio desulfuricans. Biotechnol. Bio- engng 39, 1031 1042. Okabe S., Nielsen P. H. and Characklis W. G. (1992) Factors affecting microbial sulfate reduction by Desul- fovibrio desulfur&ans in continuous culture: limiting nutri- ents and sulfide concentration. Biotechnol. Bioengng 40, 725-734. Oleszkiewicz J. A., Marstaller T. and McCartney D. M. (1989) Effects of pH on sulfide toxicity to anaerobic processes. Envir. Technol. Lett. 10, 815-822. Postgate J. R. (1984) In Sulfate-Reducing Bacteria, 2nd edn. Cambridge Univ. Press. Reis M. A., Almeida J. S., Lemos P. C. and Carrondo J. T. (1992) Effect of hydrogen sulfide on growth of sulfate reducing bacteria. Biotechnol. Bioengng 40, 593-600. Reis M. A., Lemos P. C., Almeida J. S. and Carrondo J. T. (1991) Evidence for the intrinsic toxicity of H2S to sulphate-reducing bacteria. Appl. Microbiol. Bioteehnol. 36, 145-147. Rinzema A. and Lettinga G. (1988) The effect of sulphide on the anaerobic degradation of propionate. Envir. Tech - nol. Left. 9, 83-88. Shimada K. (1987) Removal of heavy metals from mine wastewater using sulfate-reducing bacteria. J. War. Waste, Jpn 31, 52-56. Speece R. E. (1983) Anaerobic biotechnology for indus- trial wastewater treatment. Envir. Sci. Technol. 17, 416A-427A. Subcasky W. (1991) Personal communication.