FEMS Microbiology Ecology Published by Elsevier 365 45 (1987) 365-376 FEC 00141 Pigments, light penetration, and photosynthetic activity in the multi-layered microbial mats of Great Sippewissett Salt Marsh, Massachusetts Beverly Pierson a, Adair Oesterle u Biology Department, L. Murphy b University of Puget Sound, Tacoma, WA, and ’ Department of Microbiology and Immunology, Carolina, School of Medicine, Chapel Hill, NC, U.S.A. Received Accepted Key words: Bacteriochlorophyll; University of North 17 July 1987 22 July 1987 Anoxygenic photosynthesis; Green sulphur bacterium; Purple sulphur bacterium: Cyanobacterium chlorophyll 1. SUMMARY The multi-layered microbial mats in the sand flats of Great Sippewissett Salt Marsh were found to have five distinct layers of phototrophic organisms. The top 1-3 mm contained oxygenic phototrophs. The lower 3-4 mm contained anoxygenie phototrophic bacteria. The uppermost gold layer contained diatoms and cyanobacteria, and chlorophyll a was the major chlorophyll. The next layer down was green and was composed of primarily filamentous cyanobacteria containing chlorophyll a. This was followed by a bright pink layer of bacteriochlorophyll u-containing purple sulfur bacteria. The next layer was a peach-colored layer of bacteriochlorophyll b-containing purple sulfur bacteria. The lowest layer was a thin dull green layer of green sulfur bacteria containing bacteriochlorophyll c. The distribution of the chlorophylls with depth revealed that two-thirds of the total Correspondence to: B. Pierson, Biology Department, of Puget Sound, Tacoma, WA 98416, U.S.A. 0168-6496/87/$03.50 .a, George 0 1987 Federation University of European Microbiological in the mat was composed of bacteriochlorophylls present in the anoxygenic phototrophs. The cyanobacterial layers and both purple sulfur bacterial layers had photoautotrophic activity. Light was attenuated in the uppermost layers so that less than 5% of the total radiation at the surface penetrated to the layers of anoxygenic phototrophs. 2. INTRODUCTION Multi-layered (laminated) microbial mats composed primarily of phototrophic prokaryotes develop in a variety of environments exposed to light. The development of such mats occurs as long as some aspect of the environment suppresses the activity of invertebrate grazers that otherwise would consume the mat-forming organisms [l]. Some of the environmental parameters that can be sufficiently extreme to restrict the activity of grazers while permitting the growth of prokaryotes include temperature, pH, salinity and the concentration of sulfide. The laminated microbial mats Societies 366 that have been most extensively studied include those found in hot springs [2] and in hypersaline and intertidal environments [3,4]. Such mats are commonly composed of a surface layer of oxygenic cyanobacteria which may cover one or more layers of anoxygenic phototrophic bacteria, although exceptions to this mat structure do exist 151. In the intertidal environment, a green surface layer of filamentous and/or unicellular cyanobacteria is usually found covering a pink to red layer of purple sulfur bacteria [6]. If adequate organic matter is present in the substrate, biogenic sulfide produced by sulfate-reducing bacteria diffuses up through the lower layers and may be used to support anoxygenic photosynthesis [6]. Phototrophic bacteria may be found at considerable depths in these mats and several different types may be present. The presence of light and its quality and intensity are likely to be very significant in determining the activity of these bacteria. Recently published data by Jorgensen and Des Marais [7] on the penetration of light in mats and its relationship to the activity of purple sulfur bacteria support this idea. In Great Sippewissett Salt Marsh on the southern part of Cape Cod, MA, U.S.A., we found an intertidal zone in which some sand flats were covered by mats of considerable thickness and complexity. These mats consisted of a surface layer of cyanobacteria that frequently occurred in two recognizable layers, an upper golden layer of cyanobacteria mixed with diatoms and a lower dark green layer of primarily cyanobacteria. Under the layer(s) of cyanobacteria there were three distinct layers of anoxygenic phototrophic bacteria: a pink colored layer of purple sulfur bacteria which covered an orange or peach-colored layer of purple sulfur bacteria which in turn covered a dull green layer of green sulfur bacteria. The individual layers ranged in thickness from 1 to 2 mm and the mat as a whole varied from 4 to 9 mm in thickness. We were not aware of any other intertidal mats having so many different layers of phototrophs. Most mats that have been studied contain only two phototrophic layers and the photosynthetic activity is confined to only the top one or two millimeters. Many phototrophic bacteria are also capable of chemotrophic growth and the mere presence of phototrophic organisms does not mean that they are necessarily photosynthesizing [8]. Because of the unusually large number of layers in this mat, its overall thickness, and its complexity we wanted to determine how much light penetrated into the mat, what pigment complexes were present in the mat layers that could absorb this light and if the organisms in the mat layers were photosynthetically active. This paper describes the results of our observations. An accompanying paper [9] describes the results of an ultrastructural examination of the mat community to determine the types and relative numbers of the different phototrophs present. 3. MATERIALS AND METHODS 3.1. Light penetration in the mats The penetration of total photosynthetically significant radiation (visible and near infrared) through the mat layers was measured with an LI-COR LI-185B radiometer equipped with an LI-200SB pyranometer sensor. This sensor has maximum sensitivity at 950 nm and ranges from 20% maximum at 450 nm to 40% maximum at 1050 nm. Cores 1.7 cm in diameter were taken with a brass cork borer and placed over the sensor. A tight-fitting plunger could be used to adjust the position of the core within the borer. Total radiation penetrating to the bottom of the core was measured. Slices 1 mm in thickness were then cut sequentially from the bottom of the core, and the total radiation penetrating through the remaining core was measured. Since the core was in a brass sleeve, only the radiation impinging directly upon the surface of the core contributed to the radiation measured within the core. Alternatively, penetration of radiation in the mat was measured by taking a large core with a glass petri dish cover. The core was then sandwiched between the petri dish cover and the inverted bottom of the dish. The sensor was placed in the hole in the mat left by the core. The large core sandwiched in glass was then re-inserted in the mat on top of the sensor. Mat layers were then sequentially removed by scraping from the bottom of the core to the 361 top, and total penetration of radiation was measured after the removal of each layer. In this way, radiation coming to each mat layer from a much larger angle was measured. No attempt was made to measure radiation reflected back from lower layers. 3.2. Pigmentation in the mat layers The pigments in the colored layers were determined by slicing l-mm thick disks from the 1.7-cm diameter cores described in Section 3.1 and extracting the pigments from each disc with absolute methanol. Alternatively, the pigment-protein complexes were prepared in cell-free extracts. All absorbance spectra were recorded with a Cary 14 spectrophotometer. 3.2.1. Methanol extracts. Discs (1 mm in thickness) cut from cores (1.7 cm in diameter) contained 227 mm3 sand mat and were extracted in 3-5 ml of absolute methanol for 5 min in the dark. Alternatively, specific colored layers of mat were selected (approx. 200 mm3 sample volumes) for extraction. Nearly all pigments were removed by a one-step extraction with methanol. Subsequent extractions with fresh methanol were done as needed until the remaining sand-mat debris was colorless. Extracts were clarified by pressure filtration through 2.4 cm Whatman glass fiber (GF/C) filters. The specific absorption coefficient of 75.0 lg-i. cm-’ in methanol at 665 nm [lo] was used to determine the concentration of chorophyll a. The molar extinction coefficient of 60 mM-’ . cm-’ at 773 nm in methanol was used to determine the concentration of bacteriochlorophyll a [ll]. The specific absorption coefficient of 86 lgg’ . cm-’ in methanol at 670 nm was used to determine the concentration of bacteriochlorophyll c [12]. The molar extinction coefficient of bacteriochlorophyll b in methanol at 790 nm was estimated to be 66 mM_’ . cm-’ (10% greater than that of bacteriochlorophyll a) since the coefficient in ether is thought to be approximately 10% greater than that of bacteriochlorophyll a in ether [ll]. No other values of molar extinction coefficients or specific absorption coefficients for bacteriochlorophyll b were available. 3.2.2. Pigment/protein complexes in cell-free extracts. The in vivo absorption spectra were de- termined on cell-free extracts of microorganisms from the slices of cores or selected colored layers obtained as in Section 3.2.1. In this case the sand mat was mixed with Tris-sodium-magnesium (TSM) buffer [13] instead of methanol and agitated to dislodge all organisms from the sand. Cell suspensions in buffer were then decanted from the colorless sand grains. The cells were disrupted ultrasonically for 2 min in 15-30 s intervals with an Ultrasonic Processor (Heat Systems-Ultrasonics Inc. Model W220) using a standard tip. Debris was removed by low-speed centrifugation and the absorption spectra were recorded using the clarified extracts. 3.3. Photosynthetic activity Photosynthetic activity was determined by measuring the uptake of [‘4C]bicarbonate. Mat layers were carefully divided on the basis of color. Cells were removed from sand grains by gentle agitation with filtered seawater. No attempt was made to maintain anoxic conditions during these manipulations. Appropriate volumes were dispensed into 2-ml glass vials. All cells were incubated in a total volume of 1.0 ml seawater. Cells from the cyanobacterial layer were incubated with 0.1 pCi/ml NaH14C0, (New England Nuclear, specific activity 8.4 mCi/mmol). Cells from the purple sulfur bacterial layers were incubated in 0.5 pCi/ml NaHi4C0,, 0.1 mM Na, S. 9H,O, and 5. lop6 M 3-(3,4-dichlorophenyl)-l,l-dimethylurea (DCMU). The DCMU was added to these samples to inhibit oxygenic photosynthetic activity by cyanobacteria present in these layers. All incubations reported here were done under 150 W incandescent reflector flood lamps. Light intensity was regulated by distance from the lamp or by using layers of cheesecloth as a neutral density filter. All incubations were at ambient temperatures (20-25” C) and for 30 min except for the time course experiments in the dark. At the end of incubations, activity was stopped with the addition of 0.1 ml of 37% formaldehyde. Samples were stored in the dark at 4°C until processing. Samples were filtered through membrane filters with 0.45 pm pore size (Gelman). The cells on the filter were washed with 3.0 ml 1 M NaHCO, followed 368 by 1.0 ml 2% HCl and 1.0 ml distilled water. Filters were suspended in 10 ml Aquasol- (New England Nuclear) and counted in a Beckman liquid scintillation counter (LS 7800). 4. RESULTS 4.1. Description of the mat layers The different colors of the mat layers were due to the different pigments present in the microorganisms making up the layers. A detailed description of the cellular composition of the layers is given in Nicholson et al. [9]. Five different colored layers were numbered sequentially beginning with the surface layer for purposes of discussion. The surface layer (layer 1) was a golden color and consisted microscopically of diatoms and filamentous cyanobacteria. It was a fairly loosely packed layer and was not always present. The next layer down (layer 2) was green and consisted of densely packed filamentous cyanobacteria (species of Oscillatoria) and some unicellular organisms. It was very cohesive. Layer 3 was pink and consisted primarily of unicellular purple sulfur bacteria (Thiocapsa roseopersicina and species of Thiocystis and Chromatium) in clusters with some filamentous cyanobacteria. Layer 4 was a peach color and consisted primarily of unicellular purple sulfur bacteria (Thiocapsa pfennigii), most of which were in clusters. Layers 3 and 4 were dense and cohesive. The deepest layer in the mat (layer 5) was a dull green color and consisted of primarily unicellular green sulfur bacteria (Prosthecochloris aestuarii). It was a less cohesive layer. The boundaries between the layers were very distinct. Many different cores were taken from this mat system for the analyses reported below. Figs. 2, 4 and 5 illustrate the correlation between the l-mm segments of each core and the actual positions of the colored layers within that core. In all figures in which data are presented from l-mm segments of such cores, the depth profile for each core under analysis is presented on the left side of the figure using the same symbols as in Fig. 2 to show the position of the colored layers in that particular core. Each of the colored layers, except for layer 5, ranged from 1 to 2 mm in thickness in all of the cores. Layer 5 was usually less than 1 mm thick. 4.2. Analysis of chlorophyll pigments in the mat layers The colored layers were carefully separated from each other and the pigments were extracted in methanol. The absorption spectra of all five layers had intense and overlapping broad maxima in the region from 400 to 500 nm (data not shown). However, the spectra were distinctly different in the red and near infrared part of the spectrum (Fig. 1). The absorption spectra for layers 1 and 2 were qualitatively identical in this region with only two absorption maxima at 665 and 614 nm due to chlorophyll a. The spectrum from layer 3 had the same two maxima as well as a much larger peak at 773 nm due to bacteriochlorophyll a. The spectrum from layer 4 had two prominent maxima, one at 790 nm due to bacteriochlorophyll Absorption Spectra af 0.5. 0.5 04. A 0.4 R 0.3 03. 614 0.z mat Lagers Layers 1 + 2 665 Layer 3 614 0.1 !u!!A SOD 700 800 600 700 800 Lc!!L! nm 0.4 773 665 0.2 0.1. 0.5 (methand) nm Layer 4 I Layer 5 0.5 669 I OR3 669 790 Oq3 0.2 0.2 0.1 0.1 790 600 7,0,0 800 0.4 lil, 600 700 nm 800 Fig. 1. The red and near infrared absorption spectra of methanolic extracts of the different colored layers. Layers 1 and 2 had identical spectra and only one is shown. The layers had been carefully separated from each other to avoid crosscontamination. Peaks at 614 and 665 nm are due to chlorophyll 0. The peak at 773 nm is due to bacteriochlorophyll a. The peak at 790 nm is due to bacteriochlorophyll b. The peak at 669 nm is due to bacteriochlorophyll c. 369 b and one at 669 nm due to bacteriochlorophyll c. The spectrum from layer 5 had a small peak at 790 nm and a prominent peak at 669 nm due to bacteriochlorophyll c. When the mat was sectioned in 1 mm increments from top to bottom and the distribution of the chlorophylls was determined quantitatively throughout the mat (Fig. 2 and Table l), the maximum concentration of chlorophyll u (0.159 pg. mmm3 sediment) was found at a depth of 2-3 mm in the green cyanobacterial layer, although significant amounts of chlorophyll a were also found in the next mm section in the pink layer. Bacteriochlorophyll a was found to have a more narrow distribution and the maximum concentration (0.242 I-18* mm-j sediment) occurred at a depth of 3-4 mm in the middle of the pink layer. Significant amounts of bacteriochlorophyll b were found in the lower green layer but the maximum concentration (0.052 pg . mmm3 sediment) occurred at a depth of 4-6 mm at the bottom of the pink and in the peach-colored layer. Significant amounts of bacteriochlorophyll c occurred in the peach layer, but the maximum concentration (0.117 pg. mme3 sediment) was found at a depth of 6-7 mm in the lower green layer (layer 5). The only pigments detected in the gray sand below 7 mm were traces of bacteriochlorophyll b and c. Neither of these pigments was detected at depths of less than 4 mm. Neither chlorophyll a nor bacteriochlorophyll a were detected below 5 mm in the mat, and although both were found in the top mm of the mat, only very low levels of the bacteriochlorophyll a were detected in the top 2 mm. To determine the absorption characteristics of each of the colored layers in vivo, cell-free extracts were prepared for each layer. The absorption properties in the region of 400-500 nm were intense and showed extensive overlap in all the layers (data not shown). The distinctive absorption characteristics of each layer were in the red and near infrared parts of the spectrum. Fig. 3 includes the absorption spectra of cell-free extracts of all the layers. Layers 1 and 2 were identical with a single large maximum at 676 nm due to chlorophyll a and a smaller peak at 620 nm due to phycocyanin. Layer 3 had two prominent Pigment Distribution with Depth Extracts in Illethanol core ’ i A Chl a (665 nm) 0 BChl a (773 nm) 0 BChl b (790 nm) 0:04 0:08 0:12 0:16 0:20 0124 I 28 Pigment Concentration (ug mrnm3sediment) Fig. 2. Pigment distribution with depth (extracts in methanol). A 1.7 cm diameter core was sectioned in l-mm increments. The sections were extracted in methanol and the concentrations of the various chlorophylls (in pg.rnrn-’ sediment) were determined for each section. The concentrations of the pigments were plotted as a function of depth in the mat. The five distinct and differently colored mat layers are designated by different symbols in the core diagram on the left side of the figure. The horizontal dashes from 0 to 1.5 mm represent layer 1; the solid lines from 1.5 to 3 mm represent layer 2: the widely spaced dots from 3 to 4.5 mm represent layer 3; the closely spaced dots from 4.5 to 6 mm represent layer 4; the diagonal dashes from 6 to 7 mm represent layer 5. The same symbols used in this diagram to represent the different colored layers are used in all other core diagrams. The diagonal pattern from 7 to 8 mm represents a zone of gray sediments, and the diagonal pattern from 8 to 9 mm represents the zone of black sediments. Chl. chlorophyll; Bchl, bacteriochlorophyll. maxima at 844 and 794 nm due to bacteriochlorophyll a. Layer 4 had a prominent maximum at 1015 nm due to bacteriochlorophyll b and a significant peak at 748 nm due to bacteriochlorophyll c. The absorption at 844 nm is due mostly to bacteriochlorophyll u and some bacteriochlorophyll b (which also absorbs near 840 nm). The bacteriochlorophyll a also caused 370 I Table Chlorophyll distribution Chl, chlorophyll; with depth Bchl, bacteriochlorophyll. Concentration of each chlorophyll (pg.mmm3 (fraction of total)) Depth (mm) Chl (I Total chlorophylls Bchl a Bchl b Bchl c (pg.mmm3) 0.005 0.009 0.087 0.242 0.059 0 (0) 0 (0) 0 (0) 0 (0) 0 (0) 0 (0) 0 (0) 0 (0) 0.074 0.090 0.246 0.399 0.234 0.166 0.157 0.032 O-l 1-2 2-3 3-4 4-5 0.069 0.081 0.159 0.157 0.066 5-6 6-7 7-8 0 (0) 0 (0) 0 (0) 0 (0) 0 (0) 0 (0) 0.052 0.052 0.040 0.008 Total pigment (pg) (in column 1 X 1 X 8 mm deep) 0.532 0.402 0.152 (0.93) (0.90) (0.65) (0.39) (0.28) the band at 794 nm. Layer 5 had only one absorption maximum (748 nm) due to bacteriochlorophyll c. A core of the mat was sectioned in 1 mm intervals and the depth distribution of the in vivo 04 I i! i! i ! -. n 1 -, 600 700 800 Wavelength 900 (nm) 1000 (0.07) (0.10) (0.35) (0.61) (0.26) (0.22) (0.31) (0.26) (0.26) 0.057 0.114 0.117 0.024 0.312 (0.24) (0.69) (0.74) (0.74) 1.398 absorption maxima was determined (Fig. 4). A pattern similar to that found in the methanol extracts was observed. The maximum ACT6(chlorophyll a) was found at a depth of l-2 mm in the green layer (layer 2). Significant amounts of chlorophyll a were also found throughout the mat to a depth of 5 mm. The maximum A,, (bacteriochlorophyll a) was found at a depth of 3-4 mm in layer 3 (the pink layer). Significant amounts were also found in the green cyanobacterial layer although very little was found in the top 2 mm of the mat. The maximum A,,,, (bacteriochlorophyll b) was found at a depth of 4-5 mm in layer 4 (the peach layer). None was found in the top 3 mm. c) was The maximum A,,, (bacteriochlorophyll found at a depth of 4-6 mm, in layers 4 and 5. Traces were found in the 3rd mm of the mat, and none was found above this. _ .. . II00 Fig. 3. Red and near infrared absorption spectra of cell-free extracts in buffer. Absorption spectra of the cell-free extracts in buffer were prepared for each of the colored layers. The layers had been carefully separated from each other to avoid cross-contamination. The spectra for layers 1 and 2 were identical. The peak at 676 nm is due to chlorophyll a. The peaks at 844 nm and 794 nm are due to bacteriochlorophyll n. The peak at 748 nm is due to bacteriochlorophyll c. The peak at 1015 nm is due to bacteriochlorophyll b. Bacteriochlorophyll b also contributes to absorption at 844 nm but probably not at 794 nm. 4.3. Light penetration in the mat The penetration of visible and near infrared radiation through the various mat layers was measured on clear days during periods of high incident solar radiation. All measurements were made using natural sunlight. The total incident radiation reaching the surface of each colored layer was measured by burying the sensor in the mat so that it was covered only by the appropriate layer(s). With a total incident radiation (TIR) of 970 Wmd2, 66% of this (640 WmP2) penetrated the 371 Pigment _ Distribution In Vivo with Depth Light Penetration and Relative Rbsorbance of Illat Layers core core Penetration 0 1 -1 A 0 0 8 Chl a BChl a BChl b BChl c (676nm) (844 nm) (1015 nm) (748 nm) II Cl 0.2 0.4 0.6 0.8 Rbsorbance 1.0 1.2 Fig. 4. Pigment distribution with depth (in viva). A 1.7 cm diameter core was sectioned in l-mm increments. The microbial cells were dislodged from the sand grains and were disrupted ultrasonically in buffer. The absorption spectra were recorded for each of the cleared extracts. The relative absorbances for each pigment at its far-red absorption maximum (see Fig. 3) were plotted as a function of depth in the mat. top gold layer of the mat reaching the surface of the green layer. The surface of the pink layer, however, received only 10.4 WmP2 (1.1% TIR). The surface of the peach layer received 0.18 Wmm2 (0.02% TIR). The surface of the lower green layer received 0.10 Wm-* (0.01% TIR). The total radiation penetrating through all of the colored layers of the mat was 0.04 Wme2 (0.004% TIR). The penetration of radiation through a core of the mat was measured in l-mm increments (Fig. 5). The incident radiation at each depth in Wmm2 is listed in the figure and the log of the incident radiation is plotted with depth. Again it can be seen that while only about 20% of the TIR was attenuated in the top mm (the gold layer), 97% of 3 s I Legend (log I) 2 Surface lmm 2mm 3mm 4mm 5mm 6mm 7mm 8mm 9mm Rbsorbance = 1000 W/m* = 850 = 28.0 = 23.0 = 2.8 = 2.4 q 1.4 q 1.0 = 0.65 q 0.45 log (IO / I) Fig. 5. Penetration of total radiation through the mat and relative absorbance of the mat in l-mm increments. Total radiation (visible and near infrared) was measured with a LI-COR pyranometer (Wmm2) through a 1.7 cm diameter core held within a brass sleeve. 1 mm sections were sequentially cut from the bottom of the core and total radiation penetrating the remaining core was measured after each cut. The total incident radiation at the surface of the mat was 1000 Wmm2.The log of incident radiation (log I) at each depth is plotted and the bars indicate the absorbance of each millimeter segment calculated from the log of the ratio of the total incident radiation at the surface of each segment to the total radiation transmitted through each segment, log ( I,/1 ). the TIR at the surface was attenuated at a depth of 2 mm. These particular core measurements were made in the presence of a very high total surface radiation of 1000 Wme2. Under these conditions, 0.65 Wme2 (0.065% TIR) penetrated the entire mat. The absorbance (A) of each millimeter of mat in the core was calculated by determining the logarithm of the ratio of the incident radiation (I,) at that depth in the core to the total radiation 312 reaching the next mm in the core (Z). The relative of l-mm sections of the core in situ absorbances are presented in Fig. 5. In this particular core, layer 1 was exactly 1 mm thick and layers 2, 3 and 4, were all nearly 2 mm thick. Since the core was sectioned in l-mm increments, the sections fortuitously coincided nearly perfectly with the boundaries between the colored layers, and an interesting and predictable pattern of absorbance was revealed (Fig. 5). The first layer had a low absorbance factor, but in layers 2, 3 and 4, the top millimeter of each colored layer had a very high absorbance factor, while the 2nd mm of each colored layer had a much lower absorbance factor. The absorbance factors for the 1st millimeter segments of these three different colored layers decreased linearly, while the absorbance factors for the 2nd mm in each of these layers remained fairly constant. UPTAKE vs LIGHT INTENSITY LAYERS 1 + 2 ( Cyanobacteria and Diatoms - Chl a) 2500 -, OJ IdO I I I I 500 I I I I f 1000 Wm -2 4.4. Photosynthetic activity in the mat layers bicarbonate as a The uptake of 14C-labeled function of light intensity was determined in three of the colored layers: layers 1 and 2 combined, layer 3 and layer 4. Activity in layer 5 was not determined in this study. The chlorophyll a-containing cyanobacterial layers found in the top 2-3 mm of the mat, showed maximal uptake at 1000 Wm-‘, the highest light exposure measured at the surface under natural conditions and used in this study (Fig. 6). At lower intensities, a second peak of activity was observed in the range of 400-500 Wm-*. In cells from layer 3 found between 3 and 5 mm deep in the mat, maximum activity was found between 300 and 400 Wm-* (Fig. 7). A second although somewhat lower peak of activity was found at 800 WmP2. In cells from layer 4 found between 5 and 7 mm deep in the mat, maximum activity was found at 50 Wme2 (Fig. 8). A second although lower peak of activity was found at 200 Wrn-*. All of the layers showed substantial uptake of 14C-labeled bicarbonate in the dark. The activity in the dark was determined as a function of time of incubation from 0 to 60 min. The uptake in layers 1 and 2 was constant over this time interval. The uptake in layer 3 increased slightly with time to reach a maximum at 30 min and then remained Fig. 6. Uptake of [‘4C]bicarbonate as a function of total incident radiation (layers 1 and 2). A suspension of cells from the cyanobacterial layers was divided into equal aliquots. Each sample was incubated with [‘4C]bicarbonate at a final radioactive concentration of 0.1 pCi/ml for 30 min at eight different light intensities obtained from a 150 W reflector flood lamp. Samples contained no added sulfide or DCMU. The dashed line represents uptake in the dark. Chl, chlorophyll. constant. The uptake in layer 4 increased slowly with time for the entire 60 min. The dark uptake in layers 1 and 2 was 21% of the light uptake at 30 min under optimum conditions of 1000 WmP2. The dark uptake in layer 3 was 26% of the light uptake under optimum conditions of 300 Wme2 for 30 min. The dark uptake in layer 4 after 30 min was 30% of the light uptake under optimum conditions of 50 WmP2. 5. DISCUSSION The distribution pattern of the layers of phototrophic organisms in the Sippewissett Salt Marsh mat was similar to that reported for other mats in similar habitats [6,14] and to the plates of phototrophic microorganisms that form in aquatic habitats such as freshwater lakes and marine 373 UPTAKE vs LIGHT LAYER INTENSITY 3 ( Purple sulfur bacteria OJ I IdO I 500 I - Bchl a) I 1 1 1 10008 Wm -* Fig. 7. Uptake of [r4C]bicarbonate as a function of total incident radiation (layer 3). A suspension of cells from the purple sulfur bacterial layer (layer 3) was divided into equal aliquots which were incubated with [‘4C]bicarbonate at a final radioactive concentration of 0.5 pCi/ml for 30 mm at eight different light intensities obtained from a 150 W reflector flood lamp. Samples contained Na,S,9H,O (0.1 mM) and DCMU (5.10m3 mM). The dashed line represents uptake in the dark. Bchl, bacteriochlorophyll. UPTAKE vs LIGHT LAYER (Purple 6000 DPM INTENSITY 4 - Bchl b) sulfur bacteria 1 4000 - 160 260 360 Wm -* Fig. 8. Uptake of [t4C]bicarbonate as a function of total incident radiation (layer 4). A suspension of cells from the purple sulfur bacterial layer (layer 4) was divided into equal aliquots which were incubated with [t4C]bicarbonate at a final radioactive concentration of 0.5 pCi/ml for 30 min at nine different light intensities obtained from a 150 W reflector flood lamp. Samples contained Na,S.9H,O (0.1 mM) and DCMU (5.10m3 mM). The dashed line represents uptake in the dark. Bchl, bacteriochlorophyll. lagoons [15-171. The major difference between the Sippewissett mat and other previously described mat systems was the presence of the distinct layer of purple sulfur bacteria containing bacteriochlorophyll b in addition to the layer containing bacteriochlorophyll (I and a distinct layer of green sulfur bacteria containing bacteriochlorophyll c. Such layers of green sulfur bacteria occurring beneath layers of purple sulfur bacteria have been frequently described from planktonic systems [15-171, but we are unaware of any other mats or lacustrine systems that contain two distinct layers of purple sulfur bacteria, one with bacteriochlorophyll a and one with bacteriochlorophyll b, as well as a layer of green sulfur bacteria. The presence of Thiocapsa pfennigii in mats has been observed in electron micrographs of other ecosystems, but not as a distinct layer [18]. A similar peach colored layer beneath the bacteriochlorophyll u-containing layer has been observed in some of the gelatinous mats at Laguna Figueroa, Baja, Mexico (Pierson, B., and Stolz, J., unpublished observations). While the in vivo absorption spectra of the carefully isolated layers (Fig. 3) showed remarkable homogeneity of the chlorophyll pigments present, it is clear from the depth profiles (Fig. 2 and 4) that there was considerable overlap in the distribution of different chlorophylls across the boundaries of the layers. Since action spectra of photosynthetic activity have not yet been determined, we do not know which pigments are responsible for sustaining most of the photosynthetic activity in each layer. Quantitative analysis of the total chlorophylls present in each millimeter of mat (expressed in micrograms of chlorophyll per cubic mm of wet sediment) revealed some interesting characteristics of the distribution (Table 1). In the top 2 mm, 90-93s of the total chlorophyll was chlorophyll a, only 7-10s being bacteriochlorophyll a. The chlorophyll a decreased to 65% of the total in the 3rd mm and to 39% in the 4th mm. The 4th mm of the mat (found in the dense pink layer) was distinctive in having the highest total chlorophyll content of any depth (an impressive 0.399 pg. mmm3). The majority of the pigment at this depth (61%) was bacteriochlorophyll a. The 5th mm of the mat (also in the 314 dense pink layer) was of interest, since it contained nearly identical amounts of all four chlorophylls for a total chlorophyll content of 0.234 pg. mme3 of sediment. Below the 5th mm in the mat only bacteriochlorophylls b and c were present. Bacteriochlorophyll c was present in higher amounts (approximately 70% of the total chlorophyll) than bacteriochlorophyll b at all depths. When the total amount of each chlorophyll was determined for the entire core (Table l), chlorophyll a was the most abundant chlorophyll with 0.532 pg in the upper 5 mm of a one square millimeter column followed by bacteriochlorophyll a with 0.402 pg in the same 5 mm. Bacteriochlorophyll c was third with a total of 0.312 pg in the lower 4 mm of the same column, and bacteriochlorophyll b was present in the least amount with 0.152 pg in the lower 4 mm of the same column. For comparison with other ecosystems the total pigment content of the g-mm deep mat can be expressed in mg * m-2. The total pigment was 1398 mg . mm2 with 532 mg . m 2 due to chlorophyll a, 402 mg 1m-2 due to bacteriochlorophyll a, 152 mg . mP2 due to bacteriochlorophyll b and 312 mg . me2 due to bacteriochlorophyll c. This value (1398 mg * rne2) is within the range of total chlorophyll content of highly productive terrestrial systems and is much higher than that reported for most other aquatic and mat systems [3,14,19]. However, if one considers the chlorophyll a only (523 mg . mP2) then this mat is comparable in pigment content to other highly productive cyanobacterial mats [3,19]. It is the presence of the bacteriochlorophylls a, b, and c in the anoxygenic phototrophs comprising the lower layers of the mat that drives the total chlorophyll content to such high levels. These bacteriochlorophylls together account for almost 2/3 of the total chlorophyll in the mat. These chlorophylls and the potential contribution of the anoxygenic phototrophs to total productivity in mats have only occasionally been considered [3,7,14,19]. Although actual productivity was not measured in this study, it appears likely that the bacteriochlorophyll-containing anoxygenic phototrophs make a significant contribution to total mat productivity in this particular mat system. We are currently determining their role in primary productivity. The data on light penetration (Fig. 5) also support this hypothesis, since it was evident from these data that only certain wavelengths of light were attenuated by each colored layer. While examination of the in vivo absorption spectra (Fig. 3 make this statement seem obvious, it is not clear from the absorption spectra alone (Fig. 3) that all of the radiation at the wavelengths absorbed by a particular layer of phototrophs is actually completely attenuated by that layer. For example, one might imagine that the cyanobacteria in the top 3 mm of the mat might not absorb all of the radiation in the range absorbed by phycobilins and chlorophyll a, leaving significant amounts of radiation at these wavelengths available to be absorbed by cyanobacteria present as a minority population in the 4th mm of the mat. Recent data obtained by Jorgensen and Des Marais [7] on the penetration of radiation in hypersaline mats argue against this possibility. Examination of the total radiation absorbance factors (A) for each millimeter of mat plotted in Fig. 5 also argues against this possibility. While the concentration of chlorophyll a throughout the green layer is fairly constant (Fig. 2) the attenuation absorptivity of the layer is not (Fig. 5). It appears that most of the radiation that can be absorbed by the cyanobacterial pigments is absorbed in the 1st mm of the 2-mm thick layer, leaving very little for absorption in the 2nd mm of this layer. This suggests that cells in the lower part of any given layer receive far fewer quanta at the wavelengths they can absorb than cells in the upper portion of that layer. Since wavelengths not absorbed by the pigments in the green layer pass right through this layer, the cells in the pink layer below having pigments that can absorb these transmitted wavelengths contribute a high absorbance factor in the top millimeter of the pink layer. In any given layer, then, it is clear that the population of cells in the upper portion of that layer receive much more light than the cells in the lower portion. It is possible that this might explain the two different light intensity maxima observed in the light-dependent uptake of [‘4C]bicarbonate (Figs. 6-8). The cell preparations for each of the 375 uptake experiments included cells from both the upper and lower portions of each colored layer. The cells in the upper portion of each layer may be adapted to higher incident radiation than those in the lower part of each layer. It will be necessary to separate each colored layer into at least two sub-layers and to determine the light intensity optimum for each sub-layer to verify this suggestion. While a light-stimulated uptake of NAHCO, was observed in all layers studied, the dark uptake was also high, suggesting the presence of significant chemoautotrophic activity in these mat layers. Chemolithoautotrophic growth in isolates of Chromatium gracile and Thiocapsa roseopersicina can be sustained by hydrogen and reduced sulfur compounds [20]. Since no attempt was made to exclude oxygen during the preparation and incubation of cells in the uptake studies and since 0.1 mM sulfide was included in the incubations, conditions were satisfactory to sustain chemolithoautotrophic activity. We do not yet know how significant chemolithotrophy is to the overall activity of this mat. Comparison of the uptake in each layer as a function of light intensity (Figs. 6-8) revealed that the maximum uptake in the deeper layers in the mat (layers 3 and 4) occurred at lower light intensities than in the upper layers, suggesting that indeed populations of cells located deeper in the mat are adapted to lower levels of total incident radiation. White incandescent light was used for all the uptake experiments reported here. Since cells in all but the topmost layer are receiving light that is highly filtered by the colored layers above, it would be most desirable to determine the action spectra for photosynthetic activity in each of these layers. Indeed, preliminary experiments on light penetration using interference filters and spectroradiometry (Pierson, B., unpublished results) have shown that only near infra-red radiation reaches the deeper layers of the mat, and one would expect phototrophs here to be using exclusively these wavelengths to sustain photosynthesis. We are currently attempting to determine the spectral distribution as well as intensity of all radiation reaching lower layers and to determine which wavelengths are being used to sustain photo- synthesis in each layer. The Sippewissett Salt Marsh and sediments as a whole have been found to be highly productive ecosystems [21]. Our study has shown that the multi-layered phototrophic microbial sand mat communities within the salt marsh are extremely high in chlorophyll content, suggesting that they too are highly productive ecosystems. We are currently attempting to determine the productivity in situ of each of these mat layers. ACKNOWLEDGEMENTS We thank the Marine Biological Laboratory at Woods Hole, MA, for providing space and facilities to George Murphy and Adair Oesterle (students) and Beverly Pierson (instructor) at the MBL during the summer of 1984 when this research was conducted as part of the course, Microbiology: Molecular Aspects of Cellular Diversity. We also thank the Division of Biological Energy Research (DOE) and the Foundation for Microbiology for support of this work. REFERENCES [l] Awramik, S.M. (1984) Ancient stromatolites and microbial mats. In: Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. l-22, Alan R. Liss, New York [2] Castenholz, R.W. (1984) Composition of hot spring microbial mats: a summary, In: Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. 39-58, Alan R. Liss, New York. [3] Bauld, J. (1984) Microbial mats in marginal marine environments: Shark Bay, Western Australia and Spencer Gulf, South Australia. In: Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. 101-119, Alan R. Liss, New York. [4] Cohen, Y. (1984) The Solar Lake cyanobacterial mats: Strategies of photosynthetic life under sulfide, in Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. 133-148, Alan R. Liss, New York. [S] Pierson, B.K., Giovannoni, S.J. and Castenholz, R.W. (1984) Physiological ecology of a gliding bacterium containing bacteriochlorophyll a. Appl. Environ. Microbial. 47, 576-584. [6] Stal, L.J., Van Gemerden, H. and Krumbein, W.E. (1985) Structure and development of a benthic marine microbial 376 mat. FEMS Microbial. Ecol. 31, 111-125. [7] Jorgensen, B.B. and Des Marais, D. (1986) Competition for sulfide among colorless and purple sulfur bacteria in cyanobacterial mats. FEMS Microbial. Ecol. 38, 179-186. [8] Klmpf, C. and Pfennig, N. (1980) Capacity of Chromatiaceae for chemotrophic growth. Specific respiration rates of Thiocystis violacea and Chromatium uinosum. Arch. Microbial. 127, 125-135. [9] Nicholson, J.M., Stolz, J.F. and Pierson, B.K. (1987) Structure of a microbial mat at Great Sippewissett Marsh, Cape Cod, Massachusetts. FEMS Microbial. Ecol. 45, 343-364. [lo] Castenholz, R.W. (1977) The effect of sulfide on the blue-green algae of hot springs. Il. Yellowstone National Park, Microbial Ecol. 3, 79-105. [ll] Oelze, J. (1985) Analysis of bacteriochlorophylls. In: Methods in Microbiology, Vol. 18 (Gottschalk, G., Ed.), pp. 257-284, Academic Press, New York. [12] Stanier, R.Y. and Smith, J.H.C. (1960) The chlorophylls of green bacteria. Biochim. Biophys. Acta 41, 478-484. [13] Sistrom, W.R. and Clayton, R.K. (1964) Studies on a mutant of Rhodopseudomonas spheroides unable to grow photosynthetically. B&him. Biophys. Acta 88, 61-73. [14] Fenchel, T. and Straarup, B.J. (1971) Vertical distribution of photosynthetic pigments and the penetration of light in marine sediments. Oikos 22, 172-182. 1151 Kohler, H.-P., Ahring, B., Albella, C., lngvorsen, K., Keweloh, H., La&b, E., Stupperich, E. and Tomei, F. (1984) Bacteriological studies on the sulfur cycle in the anaerobic part of the hypolimnion and in the surface [16] [17] [18] [19] [20] [21] sediments of Rotsee in Switzerland. FEMS Microbial. Lett. 21, 279-286. Caldwell, D.E. and Tiedje, J.M. (1975) The structure of anaerobic bacterial communities in the hypolimnia of several Michigan lakes. Can. J. Microbial. 21, 377-385. Caumette, P. (1984) Distribution and characterization of phototrophic bacteria isolated from the water of Bietri Bay (Ebrie Lagoon, Ivory Coast). Can. J. Microbial. 30, 273-284. Stolz, J.F. (1984) Fine structure of the stratified microbial community at Laguna Figueroa, Baja California, Mexico. Il. Transmission electron microscopy as a diagnostic tool in studying microbial communities in situ, In: Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. 23-28, Alan R. Liss, New York. Javor, B.J. and Castenholz, R.W. (1984) Productivity studies of microbial mats, Laguna Guerrero Negro, Mexico. In: Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. 149-170, Alan R. Liss, New York. Kampf, C. and Pfenmg, N. (1986) Isolation and characterization of some chemoautotrophic Chromatiaceae. J. Basic Microbial. 26, 507-515. Howarth, R.W. and Marino, R. (1984) Sulfate reduction in salt marshes, with some comparisons to sulfate reduction in microbial mats. In: Microbial Mats: Stromatolites (Cohen, Y., Castenholz, R.W. and Halvorson, H.O., Eds.), pp. 245-263, Alan R. Liss, New York.
© Copyright 2026 Paperzz