EFFECT OF LIGHT INTENSITY ON PHOTOSYNTHESIS BY THERMAL ALGAE ADAPTED TO NATURAL AND REDUCED SUNLIGHT1 Thomas D. Brock and M. Louise Brock Department of Microbiology, Indiana University, Bloomington 47401 ABSTHACT Thermal algae in alkaline hot springs of Yellowstone National Park (Wyoming) grow as compact mats in which self-shading is extensive, as shown by measurement by autoradiography of photosynthetic activity of cells at different levels in the mat. The effect of light intensity on photosynthesis of the algal mats was studied using neutral density filters during incubation with l”CO Despite the intense sunlight at the altitude of Yellowstone, light inhibition by full sur$ght was observed only occasionally; the rate of photosynthesis fell progressively with decreasing light, although the most efficient use was at 7-14s of full sunlight. Later, the light intensity over portions of the algal mats was reduced to 18% of full sunlight by installing neutral density glass plates, and changes of chlorophyll content, cell number, and response of photosynthesis to light intensity were determined over the next year. Although the chlorophyll content of the algae at the surface of the mat rose quickly, the chlorophyll content of the mat as a whole rose slowly or not at all; the photosynthetic response of the algal mats to full and reduced sunlight also changed slowly or not at all. Although individual algal cells can adapt rapidly to changes in light, the entire population, because of its existence in compact mats, adapts slowly. At the latitude of Yellowstone there is sufficient light throughout the year to enable algal growth to occur even at temperatures near the upper limit at which blue-green algae can grow; in Iceland, hot spring algae cannot grow during several winter months. Natural ultraviolet radiation neither inhibited nor stimulated photosynthesis. shaped forms usually classified in the ( Copeland 1936). The relationship of photosynthesis to genus Synechococcus We have described elsewhere (Brock and light intensity in natural algal populations Brock 1967) methodology for measuring is of considerable theoretical interest. Earphotosynthesis of hot spring algae by the lier work has made USC either of natural 14C method. Since the water column over populations for which the previous light the algal mats is shallow (14 cm) and regime had not been controlled (Goldman, Mason, and Wood 1963; Stepanek 1965; because of the altitude and climatic conditions at Yellowstone, the algae are often Rodhe 1965) or laboratory cultures (Jorgenexposed to high light intensities, noontime sen and Steemann Nielsen 1965; Yentsch and Lee 1966; Brown and Richardson 1968) values of over 1.3 g cal cm-2 min-l being for which light intensities as high as those rather frequent. By use of neutral density filters it is possible to reduce the light frequently found in nature are difficult intensity during 14C incubation experimento obtain. tally and hence to define the response This paper describes a series of experiments on the effect of light intensity on of the algae to different intensities. It is also possible to study the rate of adaptanatural algal populations in a thermal tion of the algae to an experimentally respring in Yellowstone National Park (Wyo,duced light regime under conditions where ming), In the temperature range used, light is essentially the only variable. the only algae present are unicellular rodThe current study extended over three 1 For the purposes of this paper, “light” is consummers and two winters and was supstrued to include all wavelengths of electromagported by National Science Foundation netic radiation to which the Kipp and Zonen Grants GB-5258 and GB-7815 and in the solarimeter is sensitive. No psychophysical conlater stages by U.S. Atomic Energy Comnotation is implied. 334 INTRODUCTION l?IIOTOSYNTHESIS BY mission Contract COO-1804-7. T. D. Brock was a Research Career Development Awardee of the U.S. Public Health Service. Some of the winter observations were carried out while T. D. Brock was a member of Yellowstone Field Research Expeditions directed by Dr. V. Schaeffer and supported by the National Science Foundation. The cooperation of Mr. J. Good and Dr. J. Douglass of the National Park Service is gratefully acknowledged. This work benefited from the able technical assistance of S. and J. Murphy, P. Hollernan, and T. Daley. METIIODS All experiments were done with algal mats growing in the effluent channel of Mushroom Spring, a large alkaline spring in the Lower Geyser Basin of Yellowstone National Park. Thermal and chemical characteristics of this spring have been described ( Brock 1967a, b) . Methodology for quantification o,f chlorophyll and photosynthesis has been described (Brock and Brock 1967). In the current work, the 0.28cm2 cores used for isotope studies were placed in s-ml screwcapped vials. NaH14C03 with a specific radioactivity of 10 @i/l00 pg was used at a final concentration in the vials of 0.1 pCX/ml, except in the autoradiography experiments where 1 &i/ml was used. Temperature was measured with thermistors, which were checked occasionally against mercury thermometers. Incident radiation was measured with a Kipp and Zonen solarimeter (Delft, Holland) connected either to a Keithley electrometer or to1 a Cole-Parmer Mark VII recorder. According to the manufacturer, the solarimeter produced 8.8 mv when receiving 1 g cal cm-2 min-l radiation. For winter studies, light was measured with a hand-held Gossen Super Pilot light meter using an incident light attachment and the readings converted to light intensity using a calibration curve given by the manufacturer. The light meter previously had been checked against the solarimeter and was reasonably accurate. The light intensities listed for the experiments represent THERMAL 335 ALGAE integrated values for the periods of incubation with radioisotope. To reduce light intensities during imubation with isotope, nylon mesh fabrics were used. The light reduction by various fabrics was measure,d using a Westotn foot-candle meter. The per cent transmission of the fabrics was the same on a bright clear day (8,000 ft-c) as on a cloudy day (3,090 ft-c). The absorption spectra of the nylon fabrics were completely flat over the range from 760 to 320 nm. After calibration, the fabric was sewn into small bags that accepted snugly the s-ml vials. Bags providing 70% transmission were made using two layers of white nylon chiffon ( Sears, Roebuck and Co.). Black nylon chiffon ( Sears, Rolebuck and Co.) was used for the other bags as follows: 44% transmission, 1 layer; 14% transmission, 2 layers; 7% transmission, 3 layers. The bags were color coded during, manufacture. To achieve complete darkness, vials were wrapped in aluminum foil. Methodology for cell counting and autoradiography has been described (Brock and Brock 1968a, b ) . RESULTS Effect of natural ultraviolet radiation on photosynthesis It is well known that natural ultraviolet radiation is more intense at higher altitudes (Gates 1962). The study area in Yellowstone where our experiments were done is at an altitude of 2,231 m, the water level over the algal mats is only 1-2 cm thick, and the water itself shows no absorption in the ultraviolet down to 300 nm. Since the glass vials used in the photosynthesis experiments show strong end absorption below 350 nm, it was important to know whether the experiments on the effect of light intensity were biased owing to the screening of natural ultraviolet radiation by the glass vials. Inhibition of photosynthesis by natural ultraviolet radiation has been reported by Findenegg (1966) and Rodhe, Hobbie, and Wright ( 1966). Photosynthesis of algal cores was measured by the 14C method using quartz 336 THOMAS D. BROCK TABLE 1. Radioactivity oj Synechococcus at different levels through an algal core” determined by autoradiography Layer Surface Next to surface Next to bottom Bottom AND cetls as Labe$d) cells 0 No. silver grains per labeled cell 95 57 20 35 4.8 3.5 1.8 1.3 * Thickness of core, about 5 mm; each layer analyzed, about 1.2-1.3 mm. Core 0.75-cm diameter. Source of core, station VI, 57C. Incubation 4 hr at temperature of origin in 1 &i/ml NaIIrdCO, in 5-ml volume. Slides for autoradiography washed five times in deionized water, dipped in Kodak NTB-2 liquid emulsion diluted l/2.5, exposed four days and processed in Kodak DlB developer. cuvettes. To ensure the same geo,metry throughout, controls, cons,isted of quartz cuvettes in which all radiation below 350 nm was excluded by the use of four layers of Saran Wrap (Dow Chemical Co.), a material showing strong end absorption below this wavelength, The average rates of photosynthesis from two separate experiments were as follows: uncovered quartz cuvettes, 1,309 cpm hr-1 rug chlorophyll-l; Saran-covered quartz cuvettes, 1,262 cpm hr-l lug chlorophyll-l. Since these results are not significantly different we conclude that natural ultraviolet radiation neither inhibits nor stimulates photosynthesis, and that the use of glass vials which do not pass ultraviolet radiation is therefore justified for light intensity experiments. Vertical xonation of photosynthetic ability in algal cores The microbial mats in these alkaline hot spring channels consist of a compact thin layer of algae enmeshed in a matrix of filamentous bacteria on top of a thicker layer of bacteria alone. The thickness of the upper layer containing algae is usually about 0.5 cm and the thickness of the whole core varies from 1 to 2 cm. Since the algae require light for growth, it seemed likely that the thickness of the algal layer is determined by self-shading. To verify this, the photosynthetic ability of algae at different levels through the 0.5cm algal layer was determined by quantitative autoradiography. Cores were incubated in M. LOUISE B-ROCK high concentrations of NaII14COs (1 &i/ ml) for 4 hr to ensure heavy labeling, and layers about 1.5 mm thick were removed and macerated; the resulting suspensions were used to prepare slides for autoradiography ( Brock and Brock I968u). After exposure and processing, the radioactivity of the cells was determined by counting the number of silver grains per SynechoCOCCUS cell (Table 1). Photosynthesis is maximal in the surface layer and falls off progressively in the deeper portions of the core, but some photosynthesis still occurs in the lower portions of the core. These results, which confirm the hypo,thesis of self-shading, are of considerable significance in interpreting the results of the later experiments on the effect of light intensity on photosynthesis. The autoradiographic studies reported in Table 1 were done with algae from a temperature of 57C, where algal standing crop is the highest (Brock and Brock 1966; Brock 1967a). At higher temperatures, the thin cores made it impossible to perform similar studies. It seems unlikely, however, that self-shading occurs, in the thin mats at these higher temperatures. Effect of light intensity on photosynthesis by normul algal populations Experiments have been done to measure the rate of photosynthesis of the algal populations at different light intensities. Light intensity was reduced using neutral density filters. Most of the experiments were done on clear, cloudless days when insolation was maximal, in the summers of 1966, 1967, and 1968, and in February 1968, at various stations along the thermal gradient from a temperature of 7OC down to 55C. Representative results are given in Tables 2 and 3. In general there is little evidence of light inhibition at full sunlight, and the rate of photosynthesis falls as light decreases. From these data the rate of photosynthesis per unit of sunlight was calculated, so that the efficiency of light utilization could be determined (Tables 2 and 3). The efficiency of utilization of sunlight is usually greatest at intensities PIIOTOSYNTIIESIS TABLE 2. Filter % transmission 100 70 44 14 7 0 Effect BY of light intensity W 0.55 0.39 0.24 0.08 0.04 0 * Light intensity t Photosynthesis 1,700 1,300 870 170 26 26 P/L1 100 70 4 14 7 0 at station I, 71C Expt 3 (13 July 1967) 3,200 3,500 3,600 2,200 680 - P P/L1 LI 1.3 0.92 0.56 0.18 0.09 0 1,100 1,500 1,100 390 300 26 870 1,600 1,900 2,200 3,300 - 1.2 0.86 0.54 0.18 0.09 0 P P/L1 1,800 2,100 1,500 420 46 74 1,500 2,400 2,700 2,400 520 - expressed as g cal cm-2 min-? expressed as cpm hr-1 ,ug chlorophyll-‘. Adaptation to reduced light The fact that there was little or no inhibition of photosynthesis by high light intensities suggested that perhaps the algae were completely adapted to high light conditions, Therefore, we experimentally reduced the light over portions of the algal mats and determined the response to light intensity after various times 0.f adaptation. A gray glass was used to reduce the light intensity (“Gray Lite” #52, Pittsburgh Plate Glass Co. ) . The absorption spectrum of this glass is not precisely neutral, as it shows minor absorption peaks at 650, 590, and 540 nm as well as troughs at 560 and 400 nm; we assumed that these minor diversions were not significant for this work. When two layers of this glass each 1/ inch ( 0.64 cm) thick were placed together, the light intensity was reduced 82%, and this combination was used in the following work. The plates of glass ( 46 x 61 cm) Filter 5%transmission on photosynthesis LI 7-14% of full sunlight, although photosynthesis is actually less than at high light intensities. TABLE 3. 337 ALGAE Expt 2 (10 July 1967) Expt 1 (6 July 1967) LI* TIIERMAL Effect of light intensity on photosynthesis at various (For units, see Table 2) Station II (68C) LI 1.3 0.89 0.56 0.18 0.09 0 P 1,200 1,400 1,200 850 340 50 were suspcndcd by a wooden framework just above the water surface (see Fig. 3, Brock and Brock 1968Ir). Glass was installed on 2 August 1967 over areas of algal mat immediately below stations I, II, III!& and VI. Station 111% had to be abandoned later when the channel in this region was altered by a hailstorm, but the glass at the other stations has been maintained in place for over a year. Within two days after the glass plates were installed, the algal mats under them became noticeably darker green than the control areas, and they became progressively darker over the next two weeks. Table 4 shows that the visual observations of rapid increase in chlorophyll content were not confirmed by the quantitative assays. The most reasonable explanation is that the changes seen occurred only in the algal populations at the immediate surface of the mat, whereas the quantitative measurements reflect the chlorophyll content of the whole core. In Table 5, comparisons are made between equivalent stations, one in full sun- hot spring stations, Station 111% (65C) P/L1 940 1,600 2,200 4,800 3,800 - 13 July 1967. Station VI (58C) LI P P/L1 LI P P/L1 1.2 0.84 0.53 0.17 0.08 0 1,200 800 850 400 250 82 1,000 950 1,600 2,400 2,900 - 1.2 0.82 0.51 0.17 0.08 0 880 840 820 510 300 63 760 1,000 1,600 3,100 3,600 - 338 THOMAS TABLE 4. Changes after installation 0* 3 in chlorophyll and cell count neutral density glass at station II 7.4 7.3 8.7 8.9 9.3 8.0 6.3 21 12 z 13 50 186 (winter) 299 333 * 2 August AND of Chl a (fig/core) Day D. BROCK No. cells/ core Chl (bg/ 10’ cells) Tcmp (“C) 10 x 10’ 8.6 x 10’ 15 x 10’ 3.5 x 10’ 12 x 10’ - 0.74 0.85 0.56 1.8 1.9 - 68.5 66.4 70.0 69.5 71.5 69.5 66.5 66.5 66.5 1967. light and another which had been under glass for 299 days. In all cases the cell counts of the stations in reduced light are lower than those in full sunlight. To adjust for these differences, chlorophyll values are also reported as the amount of chlorophyll per cell. At stations I and II the populations under reduced light have more chlorophyll per cell than those in full light, whereas at station VI the two populations have essentially the same values. Presumably at station VI the algal mat is sufficiently thick so that self-shading is complete in full sunlight, whereas at stations I and II the thinner algal mats result in incomplete self-shading, permitting the entire algal mat to adapt to reduced light. Since even at station VI the mat under the glass was noticeably greener than that of the control station, we assume that adaptation to reduced light by the surface algal material has occurred here, although we h ave no way of detecting it by our measurements. In Table 5 one set of meaTABLE 5. Comparison of chlorophyll M. BROCK surements is given for station II in winter, when more frequent cloudy days and shorter day length results in reduced light intensity and less total light. There is an increase in chlorophyll content per cell in the control winter samples compared to summer samples, except at station VI. All of the algal mats of the alkaline hot springs are markedly darker green in winter than in summer, although these differences also are not revealed dramatically by quantitative determinations except at temperatures near the upper limit for algal growth, where because of the very thin mats, selfshading is minimal. Effect of light intensity on photosynthesis by populations adapted to reduced light Tables 6 and 7 present data on the effects of light intensity on photosynthesis of algal populations at stations II and VI adapted for varying periods of time to reduced light. Although the general picture is similar to that of Tables 2 and 3, two differences should be noted. The expected inhibition of photosynthesis by full sunlight is noted occasionally in the populations adapted to reduced light. For station II (Table 6) the efficiency of photosynthesis at the low light intensity, 7% of full sunlight, is less than that of the unadapted populaton ( Table 3)) which is surprising, as it might have been anticipated that the populations adapted to low light would be able to use it more efficiently. The increased chlorophyll content of the surface layers might result in increased shading of the lower layers, thereby diminishing the ability of the core as a whole to use low light intensities. and cell count of stations reduced sunlight (R) Chl a (fig/core) Days Station LOUISE in full sunlight (F) and those in Chl/ 10’ cells No. cells/core F R F R F R 8.6 13 57 17 21 27 11 x 10’ 13 x lo7 29 x loq 7.0 x lo7 12, x lo7 14 x lo7 0.81 0.99 1.9 2.4 1.8 1.9 9.9 x 10’ 3.5 x lo7 1.3 1.8 299 I II VI 186 II (winter) 13, 6.3 PHOTOSYNTHESIS TABLE BY THERMAL 339 ALGAE of algal populations at station II adapted for dif6. Effect of light intensity on photosynthesis ferent periods of tim.e to reduced light. (1870 of full sunlight; for units, see Table 2; day 0, 2 August 1967) Filter % transmission 100 70 44 14 7 0 333 days 186 days 13 days LI P P/L1 LI P P/L1 LI P P/L1 1.4 0.99 0.63 0.20 0.10 0 360 550 650 620 31 6 260 560 1,000 3,100 310 - 1.1 0.79 0.50 0.16 0.08 0 500 410 390 320 13 12 450 520 780 2,000 160 - 1.2 0.86 0.54 0.17 0.09 0 530 940 830 620 55 40 440 1,100 1,500 3,600 610 - This reduced efficiency in the use of low is not noted for the light intensities adapted population at station VI. DISCUSSION The response to light of a compact algal mat such as is found in thermal springs is much more complex than that of algal suspensions, either in nature or in laboratory cultures. Perhaps the most surprising aspect of our results is how slowly and imperfectly the hot spring algal populations adapt to a changing light regime. The reasons for this seem obvious, howresults ever, from the autoradiographic which show that even within an algal mat 0.5 cm thick the rate of photosynthesis was markedly reduced in the lower portions of the core, probably due to self-shading. Although visual observations show that the thin surface layer of the algal mat rapidly adapts to reduced light, the mat as a whole adapts slowly. Unfortunately, it has not been possible to devise simple methods for analyzing responses to light of the algae at different levels within the mat because of the difficulty of separating various strata of cells accurately. The absence of a striking inhibition of photosynthesis by full sunlight in the natural mats is noteworthy. Light inhibition has been frequently reported in aquatic algal populations (reviewed by Goldman et al. 1963) and the concept of sun and shade phytoplankton was discussed by Yentsch and Lee ( 1966). Recently Brown and Richardson (1968) have described the responses of a variety of algal cultures to varying light intensities and have shown that the blue-green algae in general are sensitive to high light intensities. The light intensities which the hot spring algae arc exposed to in Yellowstone are considerably higher than those experienced by most other algae. At the altitude of Yellowstone, 2,133-2,148 m, light intensities are considerably higher than at sea level, and clear skies often prevail for many days or weeks. Further, the water over the algal mats is usually shallow, so that little of the available light is absorbed by the water. Thus it might have been anticipated that full sunlight would inhibit photosynthesis. That it does not is probably a reflection of the compact nature of the algal mat which ensures extensive self-shading. Only after reduced light intensities had been maintained over the algal mats for many weeks did light inhibition by full sunlight become evident. The absence of an effect of natural ultraviolet radiation on algal photosynthesis is probably also due to self-shading. TABLE 7. Effect of light intensity on photosynthesis of algal populations at station VI adapted for different periods of time to reduced light. (180/o of full sunlight; for units, set Table 2; day 0, 2 August 1967) Filter 70 transmission LI P P/L1 LI 100 70 44 14 7 0 1.4 1.0 0.64 0.20 0.10 0 1,400 1,200 1,100 870 560 47- 1,000 1,200 1,700 4,400 5,600 1.3 0.93 0.59 0.19 0.09 0 13 days 333 days P P/L1 710 550 1,200 1,300 1,000 1,700 740 3,900 220 2,400 58 - 340 THOMAS D. BROCK AND Electron microscopic evidence of adaptation of the algae to reduced light has been obtained by the authors in collaboration with Dr. M. Edwards. Algal cells were removed with a micropipette from the surface layers of mats that had developed under both full and reduced sunlight. Observations of ultrathin sections revealed that cells taken from habitats in full sunlight had few thylakoids (photosynthetic membranes), whereas cells from habitats where light had been experimentally reduced for a year had extensive photosynthe tic membrane systems. The upper temperature limit for photosynthetic organisms is about 73C (Brock 1967c). It was of interest to know if the algae found near this upper limit could maintain populations throughout the year, despite the considerable variation in total amount of light available. Observations of hot spring algae in Yellowstone have shown that the upper temperature limit is the same in winter as in summer. Our expcrimental studies using neutral density glass to reduce available light to 18% of full sunlight have also shown that the algal populations maintain themselves in a nearly steady state throughout the year. Because insolation does not significantly affect the temperature of a hot spring habitat, the ability of the algal population to maintain itself at low light intensities is more critical than it would be in other aquatic environments, since in the hot springs respiratory activity is presumably undiminished in the winter. The situation in Yellowstone can be compared with that of Iceland, which because of its higher latitude has a greatly reduced day length in winter. Tuxen (1944) has calculated that in Iceland a hot spring alga will receive 50 times more light in June than in December and has estimated that for at least two months around the winter solstice there will not be sufficient light for photosynthesis to exceed day and night respiration. According to the direct observations of Schwabe ( 1936), life in Icclandic hot springs comes to an apparent stop from November to January. Our own M. LOUISE BROCK observations are in agreement since an Icelandic spring which had high standing crops when we first sampled it in late July (Brock and Brock 1966) had low standing crops in early May of the following year, and the upper temperature limit was about 15 degrees lower, presumably because the algal mat had not recovered completely from the previous winter. We have been able to duplicate Icelandic conditions in Yellowstone even in summer by the use of opaque filters ( Brock and Brock 1968b) ; the rate of algal disappearance in complete darkness is rapid, usually being complete within a month. REFERENCES BROCK, M. L., AND T. D. BROCK. 1968~. The application of micro-autoradiographic techniques to ecological studies. Mitt. Intern. Ver. Limnol. No. 15. 29 p. 1967a. Relationship between BRWK, T. D. standing crop and primary productivity along a hot spring thermal gradient. Ecology, 48: 566-571. -. 1967b. Microorganisms adapted to high Nature, 214: 882-885. temperatures. Life at high temperatures. -* 1967c. Science, 158 : 1012-1019. 1966. Temperature -, AND M. I,. BROCK. optima for algal development in Yellowstone Nature, 209: 733and Iceland hot springs. 734. -, AND --. 1967. The measurement of chlorophyll, primary productivity, photophosphorylation, and macromolecules in benthic algal mats. Limnol. Oceanog., 12: 600605. 196%. The measurement -, AND -. of steady-state growth rates of a thermophilic J. Bacterial., 95: alga directly in nature. 811-815. BROWN, T. E., AND I?. L. RICHARDSON. 1968. The effect of growth environment on the physiology of algae: light intensity. J. Phycol., 4: 38-54. COPELAND, J. J. 1936. Yellowstone thermal Ann. N.Y. Acad. Sci., 36: Myxophyceae. l-229. kurzwelFINDENEGG, I. 1966. Die Bedeutung liger Strahlung fiir die planktische PrimZrproduktion in den Seen. Verhandl. Intern. Ver. Limnol., 16: 314-320. 1962. Energy exchange in the GATES, D. M. biosphere. Harper and Row, N.Y. 151 P. GOLDMAN, C. R., D. T. MASON, AND B. J. B. injury and inhibition WOOD. 1963. Light in Antarctic freshwater phytoplankton. Limnol. Oceanog., 8: 313-322. l?IIOTOSYNTIIESIS TORGENSEN, E. G., AND E. ST-ANN NIEUEN. 1965. ’ Adaptation in plankton algae, p. 3,746. In C. R. Goldman [ed.], Primary proUniv. ductivity in aquatic environments. Calif. Press, Berkeley. RODIIE, W. Standard correlations be1965. tween pelagic photosynthesis and light, p. 365-382. In C. R. Goldman [ea.], Primary productivity in aquatic environments. Univ. Calif. Press, Berkeley. -, J. E. HOBBIE, AND R. T. WRIGEIT. 1966. Phototrophy and heterotrophy in high mountain lakes. Verhandl. Intern. Ver. Limnol., 16: 302-313. SCHWABE, G. II. 1936. Beitrage zur Kenntnis BY TIIERMAL ALGAE 341 Arch. IIydroislandisches Thermalbiotone. biol., 6 ( suppl. ) : 161-352. 1965. Numerical aspects of nanSTEPANEK, M. noplankton production in rcscrvoirs, p. 29,3307. In C. R. Goldman [ea.], Primary productivity in aquatic environments. Univ. Calif. Press, Berkeley. TUXEN, S. L. 1944. The hot springs of Iceland, their animal communities and their zoogcographical significance. In The zoology of Iceland, v. 1, part 11. Munksgaard Publ., Copenhagen. YENTSCII, C. S., AND R. W. LEE. 1966. A study of photosynthetic light reactions, and a new interpretation of sun and shade phytoplankton, J. Marine Res., 24: 319-337.
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