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APPLIED AND ENVIRONMENTAL MICROBIOLOGY, May 1985, p. 1101-1107 0099-2240/85/051101-07$02.00/0 Copyright © 1985, American Society for Microbiology Test Medium for the Growth of Nitrosomonas europaea CHIKASHI SATO,* JERALD L. SCHNOOR, DONALD B. McDONALD, AND JON HUEY Civil and Environmental Engineering, The University of Iowa, Iowa City, Iowa 52242 Received 10 September 1984/Accepted 31 January 1985 A mineral medium for studying the growth of Nitrosomonas europaea was developed and examined. The medium was defined in terms of chemical speciation by using chemical equilibrium computer models. The medium significantly increased the metabolic activity of the organisms compared with previously developed media, yielding a specific growth rate as high as 3.0 day-' (generation time, 5.5 h). The specific growth rate was enhanced by increasing the inoculum and was linearly correlated with the inoculum-to-total-culture volume ratio on a semilog scale. A reproducible growth rate for N. europaea was obtained with this medium under controlled experimental conditions. One of the most important features to be considered in the study of bacterial ecology is the choice of a proper medium. Ideally, studies should be carried out in a chemically defined growth medium to overcome difficulties in interpreting re- sults which result when a complex or nonchemically defined medium, such as river water or wastewater, is used. Since the genus Nitrosomonas was first described by Winogradsky in the ltatter part of the nineteenth century, a number of media have been developed and used for studying the nitrifying bacteria (1, 8, 10-12, 14-18, 20, 24, 25, 27-30, 32, 33). However, there has been confusion and contradiction about the effects of various stimulating and inhibiting factors on the growth of the nitrifying bacteria. One of the problems which often obscure the interpretation of results is the lack of a standard test medium. To obtain maximum metabolic activity, enriched media may be recommended. On the other hand, minimal media may be necessary to minimize complex effects induced by medium constituents. As a result, a point of compromise must be found in developing a standard medium. The purpose of this research was to develop a simple medium which would support high metabolic activity for Nitrosomonas europaea. In addition, an attempt was made to define the medium in terms of chemical speciation by using equilibrium computer models. The medium can be used for toxicity screening tests of various compounds. It is especially useful for investigating ionic and complexing effects. The use of computer-assisted chemical analysis for the medium also makes it possible to gain insight into the nutritional requirements of and the effects of toxic com- pounds on N. europaea. MATERIALS AND METHODS The growth medium for N. europaea was prepared as follows. A known volume of deionized, distilled water was sterilized by autoclaving and allowed to cool to room tem- perature. The medium was completed by aseptically adding nutrients in the form of concentrated stock solutions (Table 1). To prevent precipitation, the nutrient solutions, except iron, were autoclaved separately at 103 kPa (15 lb/in2) for 20 min. The iron solution was sterilized by filtration through membrane filters (0.2-p.m pore size). The molar concentra- tions of the medium constituents are given in Table 2. Var- ious amounts of (NH4)2SO4 were added as a concentrated solution depending on the nature of the investigation being * Corresponding author. carried out. The pH of the final solution was 8.5 + 0.5 and was not adjusted further. The original pure-culture strain of N. europaea ATCC 19718 was obtained from the American Type Culture Col- lection. Stock cultures were grown in medium containing 0.14 mM total ammonium in the dark at 25°C. Subcultures grown for 14 days were used to inoculate culture solutions. The size of the inoculum was 10 ml/liter of medium. No inoculum preparation was performed. Since the cultures were grown in a medium which was free of precipitates and which contained a low concentration of ammonium (in a reciprocating shaker operated at 80 oscillations per min), it seems likely that the organisms were uniformly dispersed in the culture medium. In addition, the amount of nitrite carried over to fresh medium was low (<1.4 ,uM). Mutation and subsequent variation in the nutrient requirements of the stock culture was considered unlikely (18). The culture was maintained on the proposed medium for 2 years with transfer every 14 days. To validate the proposed medium, various combinations of nutrients were prepared in 500-ml Erlenmeyer flasks. Sterile (NH4)2SO4 solution was then added to the medium at 3.57 mM. N. europaea was added to the medium at an inoculum-to-total-culture volume ratio (defined below) of 0.01. The flasks were capped with 150-ml beakers to avoid contamination but allow sufficient oxygen transfer into the medium. The initial concentrations of total ammonium and nitrite and the pH were measured immediately after mixing. Cultures were incubated in the dark at 25 + 0.25°C in a reciprocating shaker at 80 oscillations per min to provide a dissolved-oxygen concentration in excess of 2.0 mg/liter (6). TABLE 1. Nutrient stock solutions Nutrient Concn Amt (ml) used per gliter mM liter of medium Phosphate buffer" 500 10 Carbonate bufferb 600 10 CaC12 * 2H20 1.84 12.5 10 MgSO4 - 7H20 250 1,000 2 FeSO4 * 7H20 0.1 0.36 1 " 68.0 g of KH2PO4 and 87.1 g of K,HPO4 were dissolved separately in 1 liter of deionized, distilled water; the two solutions were mixed together in the proper amounts to give a pH of 8.2. b 50.4 g of NaHCO3 and 63.6 g of Na,CO3 were dissolved separately in 1 liter of deionized, distilled water; the two solutions were mixed together in the proper amounts to give pH of 8.2. 1101 Vol. 49, No. 5 on April 13, 2020 by guest http://aem.asm.org/ Downloaded from
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Page 1: Test Mediumfor the Growth of NitrosomonasTEST MEDIUM FOR N. EUROPAEA 1103 culture flasks. It can be seen (Table 4) that the results from COMICSand MINTEQwerein general agreement. Table

APPLIED AND ENVIRONMENTAL MICROBIOLOGY, May 1985, p. 1101-11070099-2240/85/051101-07$02.00/0Copyright © 1985, American Society for Microbiology

Test Medium for the Growth of Nitrosomonas europaea

CHIKASHI SATO,* JERALD L. SCHNOOR, DONALD B. McDONALD, AND JON HUEY

Civil and Environmental Engineering, The University of Iowa, Iowa City, Iowa 52242

Received 10 September 1984/Accepted 31 January 1985

A mineral medium for studying the growth of Nitrosomonas europaea was developed and examined. Themedium was defined in terms of chemical speciation by using chemical equilibrium computer models. Themedium significantly increased the metabolic activity of the organisms compared with previously developedmedia, yielding a specific growth rate as high as 3.0 day-' (generation time, 5.5 h). The specific growth ratewas enhanced by increasing the inoculum and was linearly correlated with the inoculum-to-total-culturevolume ratio on a semilog scale. A reproducible growth rate for N. europaea was obtained with this mediumunder controlled experimental conditions.

One of the most important features to be considered in thestudy of bacterial ecology is the choice of a proper medium.Ideally, studies should be carried out in a chemically definedgrowth medium to overcome difficulties in interpreting re-sults which result when a complex or nonchemically definedmedium, such as river water or wastewater, is used. Sincethe genus Nitrosomonas was first described by Winogradskyin the ltatter part of the nineteenth century, a number ofmedia have been developed and used for studying thenitrifying bacteria (1, 8, 10-12, 14-18, 20, 24, 25, 27-30, 32,33). However, there has been confusion and contradictionabout the effects of various stimulating and inhibiting factorson the growth of the nitrifying bacteria. One of the problemswhich often obscure the interpretation of results is the lackof a standard test medium. To obtain maximum metabolicactivity, enriched media may be recommended. On the otherhand, minimal media may be necessary to minimize complexeffects induced by medium constituents. As a result, a pointof compromise must be found in developing a standardmedium.The purpose of this research was to develop a simple

medium which would support high metabolic activity forNitrosomonas europaea. In addition, an attempt was madeto define the medium in terms of chemical speciation byusing equilibrium computer models. The medium can beused for toxicity screening tests of various compounds. It isespecially useful for investigating ionic and complexingeffects. The use of computer-assisted chemical analysis forthe medium also makes it possible to gain insight into thenutritional requirements of and the effects of toxic com-

pounds on N. europaea.

MATERIALS AND METHODSThe growth medium for N. europaea was prepared as

follows. A known volume of deionized, distilled water wassterilized by autoclaving and allowed to cool to room tem-perature. The medium was completed by aseptically addingnutrients in the form of concentrated stock solutions (Table1). To prevent precipitation, the nutrient solutions, exceptiron, were autoclaved separately at 103 kPa (15 lb/in2) for 20min. The iron solution was sterilized by filtration throughmembrane filters (0.2-p.m pore size). The molar concentra-tions of the medium constituents are given in Table 2. Var-ious amounts of (NH4)2SO4 were added as a concentratedsolution depending on the nature of the investigation being

* Corresponding author.

carried out. The pH of the final solution was 8.5 + 0.5 andwas not adjusted further.The original pure-culture strain of N. europaea ATCC

19718 was obtained from the American Type Culture Col-lection. Stock cultures were grown in medium containing0.14 mM total ammonium in the dark at 25°C. Subculturesgrown for 14 days were used to inoculate culture solutions.The size of the inoculum was 10 ml/liter of medium. Noinoculum preparation was performed. Since the cultureswere grown in a medium which was free of precipitates andwhich contained a low concentration of ammonium (in a

reciprocating shaker operated at 80 oscillations per min), itseems likely that the organisms were uniformly dispersed inthe culture medium. In addition, the amount of nitritecarried over to fresh medium was low (<1.4 ,uM). Mutationand subsequent variation in the nutrient requirements of thestock culture was considered unlikely (18). The culture wasmaintained on the proposed medium for 2 years with transferevery 14 days.To validate the proposed medium, various combinations

of nutrients were prepared in 500-ml Erlenmeyer flasks.Sterile (NH4)2SO4 solution was then added to the medium at3.57 mM. N. europaea was added to the medium at aninoculum-to-total-culture volume ratio (defined below) of0.01. The flasks were capped with 150-ml beakers to avoidcontamination but allow sufficient oxygen transfer into themedium. The initial concentrations of total ammonium andnitrite and the pH were measured immediately after mixing.Cultures were incubated in the dark at 25 + 0.25°C in a

reciprocating shaker at 80 oscillations per min to provide a

dissolved-oxygen concentration in excess of 2.0 mg/liter (6).

TABLE 1. Nutrient stock solutions

Nutrient Concn Amt (ml) used pergliter mM liter of medium

Phosphate buffer" 500 10Carbonate bufferb 600 10CaC12 * 2H20 1.84 12.5 10MgSO4 - 7H20 250 1,000 2FeSO4 * 7H20 0.1 0.36 1

" 68.0 g of KH2PO4 and 87.1 g of K,HPO4 were dissolved separately in 1liter of deionized, distilled water; the two solutions were mixed together in theproper amounts to give a pH of 8.2.

b 50.4 g of NaHCO3 and 63.6 g of Na,CO3 were dissolved separately in 1liter of deionized, distilled water; the two solutions were mixed together in theproper amounts to give pH of 8.2.

1101

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APPL. ENVIRON. MICROBIOL.

TABLE 2. Composition of medium

Constituent Concn (mol/liter)

MetalsK+ 9.65 x 10-3Na+ 6.06 x 10-3Ca2+ 1.25 x 10-4Mg2+ 2.00 x 10-3Fe2+ 3.60 x 10-7

LigandsC032- 6.00 x 10-3P043 5.00 x10-3C1- 2.50 x 10-4so42- 1.99 x 10-3-5.56 x 10-3NH4+b 7.14 x 10-5-9.4 x 10-3

a The S042- concentration varied with NH4+ concentration because NH4+was added as (NH4)2SO4.bThe range of total ammonium (NH3 plus NH4') concentrations tested is

shown.

The flasks were removed from the shaker every 12 to 24 h,depending on the activity of the organisms, and a smallsample was removed from each flask with sterilized pipettesfor measurement of the nitrite concentration. The effects oftotal ammonium and inoculum concentrations were investi-gated by the procedure described above, except that a seriesof media containing different total ammonium concentra-tions and different volumes of inoculum were prepared.During the present study, the amount of nitrite produced

was used as a measure of growth. This method was validatedby Engel and Alexander (8), who presented nitrite concen-tration which corresponded with viable cell counts of N.europaea (see Fig. 1, inset). Loveless and Painter (18) statedthat the greater sensitivity, simplicity, and accuracy of thenitrite determination make it a better choice than the esti-mation of cell carbon, mass, or number. They also statedthat nitrite production is a true measure of growth forNitrosomonas spp. at least up to 35.7 mM N02 . Values forthe specific growth rate were obtained by measuring theslope of the straight-line portion of each semilog plot (logNO2- concentration versus time) and converting these val-ues to the natural logarithm. The analytical proceduresfollowed the recommended standard methods (2). Nitritenitrogen was determined by the diazotization method withN-(1-naphthyl)ethylenediamine dihydrochloride. Ammonianitrogen was determined by the Nesslerization method.

RESULTS AND DISCUSSIONThe preliminary medium for N. europaea was prepared by

the directions furnished by the American Type CultureCollection. This medium was then modified by trial anderror. The final medium contains five major metals (Ca2,Mg2+, Fe2 , K+, and Na+) and six inorganic ligands (CO32-,S042-, Cl-, P043-, NH4+, and OH-). These medium con-stituents may exist as free ions, ion pairs, colloids, orprecipitates as a result of hydrolysis, hydrolytic polymeriza-tion, and oxidation-reduction reactions. These species maybe subject to adsorption to particulate matter and subse-quent sedimentation. They complex with the inorganicligands present in the medium. Therefore, defining themedium with respect to chemical speciation is important tounderstanding the nature of the medium and the nutritionalrequirements of N. europaea. Equilibrium calculations wereperformed with modified versions of the COMICS (23) andMINTEQ (9) computer models. COMICS is a relativelysimple model which accounts for only a dissolved phase,

whereas MINTEQ is one of the most sophisticated computermodels designed to calculate geochemical equilibria account-ing for both liquid and solid phases. Table 3 lists theequilibria and equilibrium constants considered in COMICS.The thermodynamic data for MINTEQ are incorporated intoits data base (9). Log activities of chemical species, calcu-lated at a total ammonium concentration of 3.57 mM at aconstant pH of 8.5, are presented in Table 4. Adsorption toa solid phase was not considered in the computationsbecause it is likely that the chemical species exist in themedium as ionic or aqueous forms and that the ammonialigands kept the metals from adsorbing strongly to the

TABLE 3. Equilibria considered with the COMICS model

Reaction log K

K+ + Cl- t KCI -1.59K+ + S042- t KS04- 0.96K+ + H+ + P043- t KHPO4- 13.39Na+ + C032- t NaCO- 1.272Na+ + C032- t Na2CO3 0.67Na+ + H+ + C032- t NaHCO3 10.08Na+ + S042 - = NaSO4- 0.722Na+ + S042- t Na2SO4 1.51Na+ + H,O ± NaOH + H+ -14.7Na+ + Cl- NaCl -1.60Mg2+ + P043- t MgPO4- 6.59Mg2+ + H+ + P0433- MgHPO4 14.8Mg2+ + 2H+ + P0433- MgH2PO4+ 21.01Mg2+ + S042-- t MgSO4 2.36Mg2+ + H20 t MgOH+ + H+ -11.42Fe2+ + H+ + P043- t FeHPO4 15.9Fe2+ + 2H+ + P043- t FeH2PO4+ 22.2Fe2+ + S042- t FeSO4 2.2Fe2+ + Cl- ± FeCI+ 0.36Fe2+ + 2Cl- ± FeCl2 0.40Na+ + H+ + P043- ± NaHPO4- 13.5Ca2+ + C032- = CaCO3 3.2Ca2+ + H+ + C032- ±T CaHC03+ 11.6Ca2+ + P043- - CaPO4- 6.5Ca2+ + H+ + P043- = CaHPO4 15.0Ca2+ + 2H + + P043 -ts CaH2PO4+ 20.9Ca2+ + H20 ±: CaOH+ + H+ 12.6Ca2+ + S0422 CaSO4 2.31Mg2+ + C0322- MgCO3 2.18Mg2+ + H+ + C032- MgHCO3+ 11.332H+ + P043- ± H2P04- 19.53Fe2+ + H20 t FeOH+ + H+ -8.3Fe2+ + 2H20 = Fe(OH)2 + 2H+ -18.9Fe2+ + 3H20 ±4 Fe(OH)3- + 3H+ -32.0Fe2+ + 4H20 t Fe(OH)42- + 4H+ -46.4Fe2+ + C032- ± FeCO3 -5.31Fe2+ + H+ + C032- = FeHCO3+ 13.05Fe2+ + P043- FePO4- 7.93H+ + C032- ± HCOj 10.32H+ + C032- = H2CO3 16.7H+ + P043- HP042- 12.323H+ P043-2 H3PO4 21.7H+ + Cl- HCI -6.1H+ + S042- HS04- 2.02H+ + S042- ± H2SO4 -1.0Ca2+ + NH3 = CaNH32+ -0.2Ca2+ + 2NH3 ± Ca(NH3)22+ -0.8Ca2+ + 3NH3 t Ca(NH3)32+ -1.6Ca2+ + 4NH3 t Ca(NH3)42+ -2.7Mg2+ + NH3 ± MgNH32+ 0.23Mg2+ + 2NH3 ± Mg(NH3)22+ -0.08Mg2+ + 3NH3ts Mg(NH3)32+ -0.34Mg2+ + 4NH3 ±= Mg(NH3)42+ -1.04H+ + NH3ts NH4+ 9.26

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TEST MEDIUM FOR N. EUROPAEA 1103

culture flasks. It can be seen (Table 4) that the results fromCOMICS and MINTEQ were in general agreement. Table 5summarizes the percent distribution of the major compo-nents as computed by MINTEQ.The medium was examined by varying the concentration

of one constituent while holding the concentration of allother medium components constant. Once the concentration

TABLE 4. Computed medium composition

aog activityChemical species

MINTEQ

NH44 -2.59K+ -2.09Ca2+ -4.53Mg2+ -3.39Na+ -2.29Fe2+ -18.01Fe3+ -19.04C032- -4.66P043- -6.55S042- -2.74Cl- -3.67HP042- -2.70H2PO4- -4.00NH3 (aq)b -3.33NH4SO4- -4.22MgOH+ -6.67MgCO3 (aq) -5.07MgHCO3+ -5.15MgSO4 (aq) -3.88MgPO4- -3.34MgH2PO44 -5.87MgHPO4 (aq) -3.21CaOH+ -8.63CaHCO3+ -6.34CaCO3 (aq) -6.03CaSO4 (aq) -4.96CaHPO4 (aq) -4.49CaPO4- -4.62CaH2PO4+ -7.12NaCO3- -5.68NaHCO3 (aq) -5.37NaSO4- -4.33NaHPO4- -4.70KS04- -3.99KHPO4- -4.50FeOH+ -19.01Fe(OH)3- -23.51FeSO4 (aq) - -18.50FeH2PO4+ -19.30Fe(OH)2 (aq) -21.58FeHPO4 (aq) -17.11FeOH2+ -12.73FeHPO4+ -16.31FeSO4+ -17.86FeC12+ -21.23FeC124 -24.26FeCI3 (aq) -28.93Fe(OH)2+ -7.71Fe(OH)3 (aq) -7.14Fe(OH)4- -6.64FeH2PO42+ -17.61Fe(SO4)2 -19.11Fe2(OH)24+ -24.03Fe3(OH)45+ -29.42HCO3- -2.83H2CO3 (aq) -4.98HS04- -9.26

a _, Computation was not performed.b aq, Aqueous.

COMICS

-2.61-2.12-4.53-3.31-2.32-8.10

-4.42-7.21-2.89-3.70-3.39-4.68-3.37

-6.23-5.55-4.90-3.84-3.93-6.51-4.22-8.63-5.85-5.75-5.11-5.24-5.24-7.84-5.47-7.48-4.49-4.53-4.05-4.44-7.90

-14.60-8.79

-10.11-10.00-7.91

-2.62-4.66-9.39

TABLE 5. Distribution of medium components

Component Species Ds

NH4+ NH4+ 85.2NH3 (aq)" 12.9NH4SO4- 1.9

K+ K+ 98.4KS04- 1.2

Ca2+ Ca2+ 42.0CaHPO4 (aq) 25.7CaPO4- 22.4CaSO4 (aq) 8.7

Mg2+ Mg2+ 35.9MgPO4- 26.2MgHPO4 (aq) 30.4MgSO4 (aq) 6.6

Na+ Na+ 98.6Fe2+ Fe2+ 17.5

FeOH+ 1.1FeHPO4 (aq) 77.7FeSO4 (aq) 3.1

Cl- Cl- 100.0P043- HP042- 72.6

H2PO4 2.3MgPO4- 10.5MgHPO4 (aq) 12.2

S042- S042- 89.8MgSO4 (aq) 3.5NaSO4 1.4KS04- 3.1NH4SO4 1.8

C032- C032- 2.2HC03- 95.8

Fe3+ Fe(OH)2' 6.3Fe(OH)3 (aq) 20.0Fe(OH)4- 73.7

aaq, Aqueous.

of one medium constituent was validated, the concentrationof another was varied. The order in which the constituentswere tested was Fe24, Mg24, Ca24, C032, and P043. Table6 shows the various combinations of nutrients and thespecific growth rates measured. The results showed that theproposed concentrations of the medium constituents shouldnot limit the growth of N. europaea and that the highestconcentration (250 mM) of CaC12 * 2H20 tested retarded itsgrowth. It was observed that high levels of phosphate (>5mM) and carbonate (>6 mM) buffers at higher pH (>8.8)caused marked precipitation in the medium. This observa-tion is in general agreement with the computed saturationindices (9). The saturation indices for calcite and dolomiteincreased from -0.3 (undersaturation) at pH 8.75 to +0.1(supersaturation) at pH 9.0 and from -0.2 at pH 8.5 to +0.6at pH 8.75, respectively. The possibility of apatite precipi-tation in the proposed medium was indicated by computa-tion, but precipitates were not observed in solution exceptafter several days. Precipitate formation did not occur in anysample during the period when growth rates were deter-mined. In this experiment, an extremely small number oforganisms were introduced into the medium so that adsorp-tion of metals onto bacterial cells was minimal in the earlystage of growth. To summarize the experimental conditions,the pH was relatively constant, precipitation and adsorptionwere minimal, and chemical speciation was approximatelyfixed in the early stage of growth. Under these conditions,the initial medium conditions can be defined by a simplechemical equilibrium model such as COMICS. In a morecomplex medium, in which the sorption characteristics of

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APPL. ENVIRON. MICROBIOL.

TABLE 6. Various compositons of the medium" and the specific growth rates measured

Phosphate Carbonate CaCI 2H.O MgSO4 7H,O FeSO4 7H,O Initial ~i (day-')Constituents varied buffer buffer (>M) (mM) (,M) pH

(MM) (MM)

Iron and calcium 20O 12 12.5 3 0.18 8.4 1.912.512.512.52525252562.562.562.562.5125125125125

0.360.901.800.180.360.901.800.180.360.901.800.180.360.901.80

8.48.48.48.48.48.48.48.58.58.48.58.48.58.58.4

1.92.02.02.12.0 (2.4)b2.22.02.02.12.02.01.82.0 (2.2)2.02.1

Magnesium and calcium

Phosphate and carbonate buffers

20

1010101010202020202030303030

12

36

12182436

1218246

121824

62.562.562.562.5125125125125125250250250250250

125

12340.512340.51234

2

0.36

0.36

8.4 2.28.4 2.28.4 2.4 (2.0)8.4 2.28.5 2.18.5 2.38.5 2.28.5 2.2 (2.0)8.4 2.08.5 1.38.5 1.88.4 1.98.4 1.88.4 1.6

8.0 2.18.3 2.3 (2.1)8.6 2.28.7 2.29.0 2.28.0 2.28.3 2.28.4 2.38.6 2.28.8 2.18.2 2.28.4 2.38.7 2.18.8 2.1

Phosphate buffer 2.55`10

6 1256' 125'6 125

" For each variation studied, the concentrations of the other constituents were held constant and are shown only in the first line for each section. For all

experiments (t = 42), r = 2.1, + 0.1 day' (standard deviation) for specific growth rate. Data from the media containing 250 ,M CaCI2 2H20 were not used tocalculate the mean or standard deviation because this high concentration retarded growth.bNumbers in parentheses indicate replicate experiment." These concentrations are proposed for the medium.

medium components onto particulate matter and bacterialcells are important, defining the medium becomes more

difficult and requires a more sophisticated model such as

MINTEQ. Because sorption trends are dependent on thecharacteristics of the metals, ligands, and particulate matterpresent in the medium (4, 34), a great deal of effort may berequired to obtain the necessary input data. Although therehas been considerable controversy over the effect of partic-ulate matter on the growth of N. europaea (7, 13), there is anadvantage to using a clear rather than a suspended medium

in simplifying measurement of the chemical equilibria of themedium.The presence of adequate concentrations of substrate and

organisms is important in obtaining a high and consistentgrowth rate. There is now an immense body of literature on

the effects of total ammonium concentration on nitrifyingbacteria (26). Substrate and product inhibitions occur at highconcentrations. Unionized ammonia and nitrous acid are

more toxic than their ionized forms (3). The levels ofsubstrate which have been reported to inhibit ammonia

22'2

0.360.36'0.36

8.3 1.98.3 2.18.0 2.1

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TEST MEDIUM FOR N. EUROPAEA 1105

2 x 1O*- I x OSE 5 x 107cn-Aj 2x1070 1 x 107

5 x 1O6

50 100 150

TIME (hours)

- ~ 1000

CELLS /ni, 500 E

I/ 300 A.J0 N 100 z*' N02-N 50I'p ~~~~z

30

20 40 60 80HOURS

200 250

FIG. 1. Nitrite formation during growth of N. europaea. The medium contained 4% inoculum and 7.8 mM total ammonium. Inset:Logarithmic p!ot of viable cells and nitrite concentration during the growth of N. europaea (reproduced from reference 8).

oxidation are >75 mM total ammonium (>2.1 mM ammonia)at pH 7.7 (19), 0.71 to 10.7 mM ammonia (3), and >0.71 mMammonia (21). The wide range of toxicities reported isprimarily due to different test conditions (i.e., Nitrosomonasspecies, medium, pH, temperature). To assess the effect oftotal ammonium, several batch experiments were conductedin which the initial concentration of total ammonium wasvaried from 0 to 263 mM (40 mM ammonia). Results fromseveral batch runs indicated that N. europaea could toleratehigh total ammonium concentrations. Growth was not inhib-ited by total ammonium concentrations of up to 71 mM (10.7mM ammonia), but a total ammonium concentration of 263mM (40 mM ammonia) reduced the specific growth ratesignificantly. The results also indicated that the specificgrowth rate was weakly dependent on the total ammoniumconcentration in the range between 1.4 and 71 mM. Theo-retical calculations indicate that the concentration of union-ized nitrous acid in the medium should not increase to thetoxic levels (16 to 200 ,uM) reported by Anthonisen et al. (3)during the period when growth rates are determined if theorganisms are grown at c7.1 mM total ammonium. At higherconcentrations, however, unionized nitrous acid may reachtoxic concentrations in the later stages of growth.

It has been shown that the number of nitrifying bacteriapresent in a system influences the nitrification rate (5, 26, 31,35). In the present experiment, an extremely small numberof organisms were introduced into the medium, and thusaccurate determination of the number of organisms wasdifficult. To simplify the technique, it was defined in terms offraction of inoculum volume (inoculum-to-total-culture vol-ume ratio), F, where F equals the inoculum volume trans-ferred (in milliliters) divided by the total culture volume (inmilliliters).To investigate the influence of inoculum volume on the

growth of N. europaea, experiments were performed withtotal ammonium concentrations between 0 and 7.8 mM (0 to110 mg/liter as N). Figure 1 shows a logarithmic plot ofnitrite formation by N. europaea (F = 0.04) in a medium

containing 7.8 mM total ammonium. The inset is a reproduc-tion of the plot of viable N. europaea cells and nitriteconcentration reported by Engel and Alexander (8), whichshows a good correspondence between nitrite formation andviable cell count during the growth of N. europaea. Theeffects of both total ammonium concentration and inoculumvolume on the specific growth rate, ,u, are shown in Fig. 2. Ina control culture containing no ammonium, no growth wasevident. The specific growth rate increased as the inoculumvolume fraction, F, was increased. At an inoculum volumefraction of 0.04 and a total ammonium concentration of 7.8mM, the specific growth rate reached 3.0 day-1 (Fig. 1). Thisis a considerably higher value than any previously reportedfor the growth of Nitrosomonas spp. (22). The data alsoindicated that the specific growth rate was less dependent onF (zero-order relationship) when F was 0.01 or higher.However, at a lower F, the specific growth rate decreasedsignificantly, indicating a pseudo-first-order relationship. Al-though it appeared that the specific growth rate was en-hanced by increasing the number of organisms, the fact thatsome of the medium from the stock culture was transferredalong with the organisms suggests that such stimulation mayhave been caused, at least in part, by substances present inthe inoculum medium. Another point of interest is that theplots of specific growth rate versus log F gave linear rela-tionships (r > 0.95) with a similar slope.To serve as a useful research tool, a successful test

medium must be capable of furnishing consistent resultsunder given experimental conditions. At a total ammoniumconcentration of 1.5 mM and an F of 0.01, the mean specificgrowth rate (standard deviation) obtained from five experi-ments was 2.1 + 0.2 day-'. This and similar media are

consistently able to yield high specific growth rates withminimal variation (Table 6). Since the use of culture mediacontaining large quantities of insoluble constituents compli-cates studies of nutrition and biochemistry in Nitrosomonasspp. (8), the proposed clear medium can be effectively usedas a test medium in studies of N. europaea. It is hoped that

10000

1000

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I-

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APPL. ENVIRON. MICROBIOL.

3

0~~~~~~~~~0

O 1- IL^mol/L NH3- N

L , 0 71a-

u) V 180,0 850*7800

0

0.00 0.01 0.02 0.03 0.04INOCULUM VOLUME FRACTION, F

FIG. 2. Effect of inoculum volume on specific growth rate, with the amount of nitrite produced used as a measure of growth.

the medium can be used for toxicity screening tests forvarious compounds, especially for ionic and complexingcompounds.

In conclusion, a medium for high metabolic activity andgrowth of N. europaea ATCC 19718 was developed andexamined for nutritional requirements. The concentrationsof the medium constituents satisfied the requirements of theorganisms. The initial condition of the medium was definedin terms of chemical speciation by using two chemicalequilibrium models. The medium significantly increased theactivity of the bacteria compared with previously developedmedia, giving a specific growth rate as high as 3.0 day-'(generation time, 5.5 h). The medium provided reproducibledata under controlled conditions. The specific growth ratewas influenced by the inoculum volume at low concentra-tions, but was less dependent on inoculum concentrationabove an inoculum-to-total-culture volume ratio (F) of 0.01.The specific growth rate was linearly correlated with theinoculum-to-total-culture volume ratio on a semilog scalewithin the range of F values tested.

ACKNOWLEDGMENTS

We thank James C. Lin for his assistance in computing thechemical speciations and Werner Stumm for advice on defining themedium via equilibrium calculations.The study was sponsored by the Office of Water Research and

Technology, the Iowa State Water Resources Research Institute,under grant A-0711A.

LITERATURE CITED1. Alexander, M., and F. E. Clark. 1965. Nitrifying bacteria, p.

1467-1483. In C. A. Black (ed.), Methods in soil analysis, part2. American Society of Agronomy, Madison, Wis.

2. American Public Health Association. 1976. Standard methods forthe examination of water and waste water, 14th ed. AmericanPublic Health Association, Inc., New York.

3. Anthonisen, A. C., R. C. Loehr, T. B. S. Prakasam, and E. G.Srinath. 1976. Inhibition of nitrification by ammonia and nitrousacid. J. Water Pollut. Control Fed. 48:835-852.

4. Davis, J. A., and J. 0. Leckie. 1978. Effect of adsorbedcomplexing ligands on trace metal uptake by hydrous oxides.Environ. Sci. Technol. 12:1309-1315.

5. DeMarco, J., J. M. Kurbiel, M. Symons, and G. Robeck. 1967.

Influence of environmental factors on the nitrogen cycle inwater. J. Am. Water Works Assoc. 59:580-592.

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8. Engel, M. S., and M. Alexander. 1958. Growth and autotrophicmetabolism ofNitrosomonas europaea. J. Bacteriol. 76:217-222.

9. Felmy, A. R., and E. A. Jenne. 1983. MINTEQ: a computerprogram for calculating aqueous geochemical equilibria. Batt-elle, Pacific Northwest Laboratories, Richland, Wash.

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13. Kholdebarin, B., and J. J. Oertli. 1977. Effect of suspendedparticles and their size on nitrification in surface water. J. WaterPollut. Control Fed. 49:1693-1697.

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15. Krummel, A., and H. Harms. 1982. Effect of organic matter ongrowth and cell yield of ammonia-oxidizing bacteria. Arch.Microbiol. 133:50-54.

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19. Lozinov, A. B., and V. A. Ermachenko. 1959. NH4' oxidationby nitrite bacteria as a function of certain factors of the medium.1. The effect of (NH4)2SO4 concentration. Microbiology (Wash-ington, D.C.) 28:674-679.

20. Meiklejohn, J. 1950. The isolation of Nitrosomonas europaea inpure culture. J. Gen. Microbiol. 4:185-190.

21. Neufeld, R. D., A. J. Hill, and D. 0. Adekoya. 1980. Phenol andfree ammonia inhibition to Nitrosomonas activity. Water Res.

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TEST MEDIUM FOR N. EUROPAEA

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nitrogen. Prog. Water Technol. 8:3-29.23. Perrin, D. D., and I. G. Sayce. 1967. Computer calculation of

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25. Salvas, P. L., and B. F. Taylor. 1984. Effect of pyridine com-

pounds on ammonia oxidation by autotrophic nitrifying bacteriaand Methylosinus trichosporium OB36. Curr. Microbiol.10:53-56.

26. Sharma, B., and R. C. Ahlert. 1977. Nitrification and nitrogenremoval. Water Res. 11:897-925.

27. Shieh, W. K., and E. J. La Motta. 1979. Effect of initial sub-strate concentration on the rate of nitrification in a batchexperiment. Biotechnol. Bioeng. 21:201-211.

28. Skinner, F. A., and N. Walker. 1961. Growth of Nitrosomonaseuropaea in batch and continuous culture. Arch. Mikrobiol.38:339-349.

29. Smith, E. D., R. M. Sweazy, D. M. Wells, M. L. Peoples, R. C.

Baskett, and R. G. Ramsey. 1977. Development of an unconven-tional approach to nitrification-denitrification. Water ResourcesCenter publication no. WRC-77-3. Texas Technological Col-lege, Lubbock, Tex.

30. Soriano, S., and N. Walker. 1968. Isolation of ammonia-oxidiz-ing autotrophic bacteria. J. Appl. Bacteriol. 31:493-497.

31. Srna, R. F., and A. Baggaley. 1975. Kinetic response of per-turbed marine nitrification systems. J. Water Pollut. ControlFed. 47:472-486.

32. Tomlinson, T. G., A. G. Boon, and C. N. A. Trotman. 1966.Inhibition of nitrification in the activated sludge process ofsewage disposal. J. Appl. Bacteriol. 29:266-291.

33. Van Ginkel, C. G., J. Tramper, K. C. A. M. Luyben, and A.Klapwijk. 1983. Characterization of Nitrosomonas europaeaimmobilized in calcium alginate. Enzyme Microb. Technol.5:297-303.

34. Vuceta, J., and J. J. Morgan. 1978. Chemical modeling of tracemetals in fresh waters: role of complexation and adsorption.Environ. Sci. Technol. 12:1303-1309.

35. Wong-Chong, G. M., and R. C. Loehr. 1975. The kinetics ofmicrobial nitrification. Water Res. 9:1099-1106.

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