Nitrogen Fixation by the Photosynthetic Sulfur Bacterium - Europe PMC

0 downloads 0 Views 375KB Size Report
T. BERGSTEIN,'* Y. HENIS,2 AND B. Z. CAVARI'. Kinneret Limnological Laboratory, Tiberias,' and Hebrew University ofJerusalem, Faculty ofAgriculture,.
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, Feb. 1981, p. 542-544 0099-2240/81/020542-03$02.00/0

Vol. 41, No. 2

Nitrogen Fixation by the Photosynthetic Sulfur Bacterium Chlorobium phaeobacteroides from Lake Kinneret T. BERGSTEIN,'* Y. HENIS,2 AND B. Z. CAVARI' Kinneret Limnological Laboratory, Tiberias,' and Hebrew University of Jerusalem, Faculty of Agriculture, Rehovot,2 Israel

N2 fixation by Chlorobium phaeobacteroides from Lake Kinneret was dependent on ammonia concentration and light intensity. In the thermocline of Lake Kinneret, N2 fixation and photosynthesis were low. It was concluded that the bacteria do not contribute significantly to the organic nitrogen load of the lake.

It is well known that photosynthetic bacteria, like blue-green algae (cyanobacteria), can fix nitrogen (4, 8, 15, 18, 21). The nitrogen fixation activity of these bacteria has been shown to depend on light. A cell-free extract of the photosynthetic bacterium Chromatium vinosum strain D fixes nitrogen only in the light (22). Furthermore, it has been found that nitrogen fixation rises with increasing light intensity, with optimal activities for the photosynthetic bacterium Rhodospirillum rubrum and the blue-green alga Mastigocladus laminosus being at 135 x 103 erg cm-' sec-' for white incandescent light bulbs and 1 x 104 erg cm-2 sec 1 for Natur-Escent fluorescent light bulbs, respectively. (10, 13). Under higher light intensities, nitrogen fixation activity did not change. In Lake Mendota and Green Bay Lake (Wisconsin), nitrogen fixation by blue-green algae decreases with depth (14, 17, 19). A high correlation between nitrogen fixation, photosynthesis, and light intensity was found in Lake Mendota when the dominant phytoplankton was the alga Aphanisomenon sp. Nitrogen fixation and photosynthesis at the surface were maximal at a light intensity of 32,280 lx, and both decreased at midday, when light intensity was high (64,560 lx) (12). Another factor that can influence nitrogen fixation is the external concentration of ammonia. In cultures of Anabaena cylindrica, rice roots, and the photosynthetic bacterium Rhodopseudomonas palustris, the presence of ammonia in the media inhibited nitrogen fixation (2, 3, 20). However, when a cell-free extract of R. rubrum was grown in chemostat culture with a low ammonia concentration as the sole nitrogen source, nitrogen fixation activity (after removal of the ammonia) was higher than when grown without ammonia (11). Every summer between July and September, there is a bloom of the photosynthetic green sulfur bacterium Chlorobium phaeobacteroides 542

in the thermocline of Lake Kinneret (1). The aim of this study was to find out under which conditions C. phaeobacteroides can fix nitrogen and whether there is any contribution to the organic nitrogen load in the lake. The bacterium C. phaeobacteroides, isolated from Lake Kinneret, was grown as previously described (1) but without ammonia in the medium. Nitrogen fixation was determined by an adaptation of the acetylene ethylene reduction technique (16) as follows. In field and laboratory experiments, 100-ml bottles containing 50 ml of C. phaeobacteroides culture were flushed with a mixture of argon-acetylene (90:10) and incubated for various times at different depths in the lake, or under different light intensities in the laboratory. Gas samples were taken, and the ethylene content was determined by using gas chromatography with a flame ionization detector. Acetylene and ethylene were separated on a column (2 by 150 cm) of Porapak U at 700C. Photosynthetic activity was measured as described previously (1). Protein was determined by the method of Lowry et al. (9). The bacteria were grown in medium containing different ammonia concentrations in the form of NH4Cl under an atmosphere of nitrogen and a light intensity of 25 ,uEin m-2 Cl. Ammonia concentrations of up to 5 mg of nitrogen per liter did not inhibit and even stimulated nitrogen fixation to some extent compared with media lacking ammonia (Fig. 1). This stimulation in nitrogen fixation may be explained by stimulation of cell growth and multiplication in the presence of ammonia, resulting in an increase in the total amount of nitrogen fixation. Concentrations higher than 5 mg of nitrogen per liter inhibited nitrogen fixation. It would appear that ammonia concentrations found in the thermocline of Lake Kinneret (0.3 to 0.5 mg of N per liter) (5-7) do not inhibit nitrogen fixation of C. phaeobacteroides. Nitrogen fixation by C. phaeobacteroides de-

VOL. 41, 1981

NOTES

543

pended on light (Fig. 2). No nitrogen fixation depth (Fig. 3). The activity decreased with took place in the dark, and increased light inten- depth, reaching 0.65 ,g of ethylene produced per sity raised activity. ,ug of protein per h at the C. phaeobacteroides The effect of light was also studied by incu- bloom layer (20 m), where the low light intensity bating bottles containing a pure C. phaeobacte- (0.3 to 1.0 ,uEin m-2 8-1) was the limiting factor. roides culture at different depths in the lake for No acetylene reduction was obtained when cells 3 h. To minimize the effect of self-shading, the from the bloom layer were tested. The exposure cultures were incubated in the lake at the begin- to air during sampling probably inactivated the ning of the log phase (optical density at 715 nm, nitrogenase, resulting in no acetylene reduction. 0.4). A peak value of 5.5 ,ug of ethylene produced The photosynthetic activity pattern of a pure per Ag of protein per h was obtained at a 3-m culture of C. phaeobacteroides incubated at different depths in the lake resembled that of nitrogen fixation. Maximal photosynthetic activity was also observed at a depth of 3 m and decreased to almost zero at the thermocline (20 m) (Fig. 4). The coincidence of limited nitrogen

to

T

,pg ethyleneformed ,ug protein" h-'

p.. u

K

*2

.3

4

.5

6

_

2 4

I.4

6

E

10

12 5

eO

lS

0

25

FIG. 1. Effect of ammonia on nitrogen fixation by C. phaeobacteroides. Symbols: 0, no ammonia added; x, 0.2 mg of ammonia-nitrogen per liter; A, 1 mg of ammonia-nitrogen per liter; 0, 5 mg of ammonia-nitrogen per liter; 0, 10 mg of ammonia-nitrogen per liter.

w a

14

16h 20

FIG. 3. Nitrogen fixation by C. phaeobacteroides cultures at different depths in the lake. jug C uptake mg protein-1 h-1 .

7/

100

t~~~~~~

£

I

FIG. 2. Nitrogen fixation by C. phaeobacteroides at different light intensities. Symbols: x, 50 tLEin m 2 s-'; 0, 20 pEin m-2 s'1; *, 1 uEin m-2 s1; A, no light.

/

FIG. 4. Uptake of [14C]bicarbonate by pure C. phaeobacteroides cultures in light (x) and darkness (-) at different depths in the lake.

54A4

fixation and of photosynthetic activity under low light intensities has also been found with algal studies (12). Because of this light limitation in the thermocline, there is probably no contribution to the organic nitrogen load in Lake Kinneret by the C. phaeobacteroides bloom. on

APPL. ENVIRON. MICROBIOL.

NOTES

We thank D. Wynne for critically reading and commenting this manuscript and Y. Okon for helpful advice.

LIMRATURE CITED 1. Bergstein, T., Y. Henis, and B. Z. Cavari. 1979. Investigations on the photosynthetic sulfur bacterium Chlorobium phaeobacteroides causing seasonal blooms in Lake Kinneret. Can. J. Microbiol. 25:999-1007. 2. Dharmawardene, M. W., and W. D. P. Stewart. 1973.

Nitrogen fixation by photosynthetic microorganisms. Annu. Rev. Microbiol. 27:283-316. 3. Gogotov, I. N., T. V. Mitkina, and V. P. Glinsklii. 1974. Effect of ammonia on hydrogen evolution and nitrogen fixation in Rhodopseudomonaspalustris. Mikrobioligia 43:586-591. 4. Johansson, B., and H. Gest. 1976. Inorganic nitrogen assimilation by the photosynthetic bacterium Rhodopsendomonas capsulata. J. Bacteriol. 128:683-688. 5. Kinneret Limnological Laboratory. 1975. Lake Kinneret internal report. June 1976. Kinneret Limnological Laboratory, Tiberias, Israel. 6. Kinneret Limnological Laboratory. 1976. Lake Kinneret internal report. February 1977. Kinneret Limnological Laboratory, Tiberias, Israel. 7. Kinneret Limnological Laboratory. 1977. Lake Kinneret internal report. March 1978. Kinneret Limnological Laboratory, Tiberias, Israel. 8. Kobayashi, M., and M. J. Hague. 1971. Contribution to nitrogen fixation and soil fertility by photosynthetic bacteria. Plant Soil. Special vol., p. 443-456. 9. Lowry, 0. H., J. Rosebrough, A. L Farr, and R. J. Randall. 1951. Protein measurements with the Folin phenol reagent. J. Biol. Chem. 193:265-275. 10. Miymoto, K., F. C. Hallenbeck, and J. R. Benenann. 1979. Nitrogen fixation by thermophilic blue green algae (cyanobacteria): temperature characteristics and poten-

tial use in biophotolysis. Appl. Environ. Microbiol. 37: 454458. 11. Munson, T. D., and R. H. Burms. 1969. Nitrogen fixation by Rhodospirillum rubrum grown in nitrogen-limited continuous culture. J. Bacteriol. 97:1089-1093. 12. Peterson, R. B., E. E. Friberg, and R. H. Bums. 1977. Diurnal variation in N2 fixation and photosynthesis by aquatic blue-green algae. Plant. Physiol. 59:74-80. 13. Schick, H. J. 1971. Substrate and light dependent fixation of molecular nitrogen in Rhodospirillum rubrum. Arch. Mikrobiol. 75:89-101. 14. Sherman-Torrey, M., and G. F. Lee. 1976. Nitrogen fixation in Lake Mendota, Madison, Wisconsin. Limnol. Oceanogr. 21:365-378. 15. Siefert, E., and N. Pfennig. 1978. Hydrogen metabolism and nitrogen fixation in wild type and Nif- mutants of Rhodopseudomonas acidophila. Biochimie 60:261265. 16. Stewart, W. D. F., F. Fitzgerald, and R. H. Burris. 1967. In situ studies on N2 fixation using the acetylene reduction technique. Proc. Natl. Acad. Sci. U.S.A. 58: 2071-2078. 17. Stewart, W. D. F., T. Mague, G. P. Fitzgerald, and R. H. Burris. 1971. Nitrogenase activity in Wisconsin lakes of differing degrees of eutrophication. New Phytol. 70:497-509. 18. Takahashi, H. 1975. Nitrogen fixation and nitrogen cycle. Jpn. Int. Biol. Program. Synthesis. 12:69-77. 19. Vanerhoef, L. N., P. J. Leibson, R. J. Musil, C. Y. Huang, R. B. Fiehwag, J. W. Williams, D. L Wackwitz, and K. T. Mason. 1975. Variation in algal acetylene reduction (nitrogen fixation) in situ. Plant Physiol. 55:273-276. 20. Watanabe, I., and D. R. Cabrera. 1979. Nitrogen fixation associates with the rice plant growth in water culture. Appl. Environ. Microbiol. 73:373-378. 21. Winter, H. C., and D. I. Arnon. 1970. The nitrogen fixation system of photosynthetic bacteria. I. Preparation and properties of a cell free extract from chromatium. Biochim. Biophys. Acta 197:170-179. 22. Yoch, D. C., and D. I. Arnon. 1970. The nitrogen fixation system of photosynthetic bacteria. II. Chromatium nitrogenase activity linked to photochemically generated assimilatory power. Biochim. Biophys. Acta 197:180184.