Lichen species dominance and the resulting photosynthetic behavior of Sonoran Desert soil crust types (Baja California, Mexico)
© Büdel et al.; licensee Springer. 2013
Received: 29 January 2013
Accepted: 21 March 2013
Published: 26 March 2013
Lichen dominated biological soil crusts (BSCs) occur over large areas in the Sonoran Desert of the southwestern USA and northwest Mexico. In Baja California BSCs show a distinct patchiness and several types can be distinguished. Two chlorolichen- and two cyanolichen-dominated BSCs were selected. We hypothesize that patchiness and the resulting domination of certain functional lichen groups will result in patchiness of photosynthetic CO2-uptake related to environmental factors as well.
Four different soil crust samples were placed in cuvettes and their CO2 exchange was recorded in an open system with an infrared gas analyzer. Air blown over the BSCs had a controlled CO2 content of 350 ppm. Four cuvettes were operated in parallel. Photosynthetic CO2 exchange was continually recorded throughout the experiment.
Besides the dominating chlorolichens Psora decipiens and Placidium squamulosum and the cyanolichens Peltula patellata and P. richardsii, several other lichen species and 12 cyanobacterial species were found in the biological soil crusts sampled. The chlorolichen BSCs already gained positive net photosynthesis with high air humidity alone, while the cyanolichen types did not, but showed smaller CO2-uptake depression after water suprasaturation. Such specific net photosynthesis responses to mode of hydration and to crust water content seem to correlate with precipitation characteristics of their habitat.
Species specific photosynthetic performance related to activation of respiration and net photosynthesis as well as to crust water content help to explain niche occupation and species composition of BSCs. Different functional types have to be considered when they have a patchy distribution.
KeywordsBiological soil crust Lichens Cyanobacteria Photosynthesis Reactivation Sonoran desert
More than 35% of the Earth’s landmass is arid to semiarid and soils of these regions are frequently covered by biological soil crusts, BSCs (Pointing and Belnap 2012). They are intimate associations between soil particles, cyanobacteria, algae, microfungi, lichens and bryophytes (Belnap et al. 2003). In such regions BSCs can have a strong influence on ecosystem functioning. In particular they can improve the stability of soils and the resistance to soil erosion by wind and water increases with BSC development independent of the substrate. BSCs also improve soil fertility and influence hydrological cycles. The effects of various types of BSC have been well studied in arid and semi-arid environments and it is in such nutrient and/or water poor environments that they make their greatest impact (Belnap and Lange 2003). By fixing atmospheric carbon, the photoautotrophic components of the BSC can underpin the trophic hierarchy by leaching some fixed carbon into the soils (Dudley and Lechowicz 1987, Dümig et al. 2013) and by themselves being a food resource for heterotrophs. In addition BSC components like free living cyanobacteria and cyanolichens can also fix atmospheric nitrogen and supply this to the communities. These ecosystem services are of special importance in areas where no higher primary producer influences the simple and nutrient poor soils.
Being composed of different organisms does not necessarily mean that they all contribute equally to biomass. Depending on environmental conditions, certain groups of organisms dominate over others, resulting in crusts where most of the biomass is typically either formed by cyanobacteria, by cyano- and/or chlorolichens lichens, or by liverworts or mosses. Although patchiness and pattern formation in time and space of BSCs is a known phenomenon (Belnap et al. 2006), little is known about the factors driving small scale patterns of abundance and distribution (Martinez et al. 2006; Richter et al. 2012). Few studies have dealt with small scale pattern formation of crusts. However, one study revealed a scale-dependent positive correlation between abiotic stress such as water and nutrient availability and co-occurrence of BSC-lichens (Maestre et al. 2009).
Sampling and collecting sites
List of lichens and cyanobacteria determined in the Baja California-Sonoran desert BSC type
A) 30 km South of Bahia de Los Angeles
B) N ear Todos Santos
C) S of Ciudad Insurgentes
D) NW of San Ignacio, Desierto de Vizcaino
Borzia trilocularis Cohn ex Gomont
Gloeocapsa atrata Kützing
Gloeocapsa kützingiana Nägeli
Gloeocapsa punctata Nägeli
Microcoleus subtorulosus Gomont ex Gomont
Nostoc microscopicum Carm. ex Bor. et Flah.
Phormidium californicum Drouet
Phormidium inundatum Kützing ex Gomont
Schizothrix fragilis Kützing ex Gomont
Scytonema ocellatum (Dill.) Lyng. ex Born. et Flah.
Stigonema hormoides Bornet et Flahault
Collema cf. crispum
Heppia adglutinata (Kremp.) A. Massal.
Heppia despreauxii (Mont.) Tuck.
Peltula patellata (Bagl.) Swinscow & Krog
Peltula richardsii (Herre) Wetmore
Pseudopeltula heppioides Henssen
Placidium squamulosum (Ach.) Breuss
Psora decipiens (Hedw.) Hoffm.
Toninia sedifolia (Scop.) Timdal
Toninia lutosa (Ach.) Timdal
Patchiness of BSCs in Baja California was noticed during 3 field trips in the framework of the lichen flora of the Sonoran Desert project (see Nash et al. 2002, 2004, 2007, Volumes 1–3), covering all regions of Baja California. Patchiness of BSCs in terms of varying lichen species composition was found a regular feature and patches dominated by one species ranged between few square centimeters to a square meter (own unpublished observation).
A soil crust piece of 19.4 cm2 dominated by approximately 570 thalli of Psora decipiens (Hedw.) Hoffm. (chl) from calcareous soil, Mexico, Baja California, along route 1, 30 km south of turnoff to Bahia de Los Angeles, ca. 100 m a.s.l., 28°45 N, 114°07′W, leg B. Büdel, no. 20207a. Average precipitation is ~250 mm/year commencing from October to April with a peak in January to March. The chlorophyll a of the sample refers to 287.21 mg/m2.
23.1 cm2 BSC dominated by approximately 580 thalli of Placidium squamulosum (Ach.) Breuss (chl), Mexico, Baja California Sur, turnoff to Presa de Santa Cruz at 42 km, post along Hwy 19 to Todos Santos, 180 m a.s.l., 23°33′N, 110°13′W, leg. B. Büdel, no. 20152b. Average precipitation is ~195 mm/year commencing from July to December with a peak from August to October. Chlorophyll a = 175.59 mg/m2.
11.5 cm2 BSC dominated by approximately 63 thalli of Peltula richardsii (Herre) Wetmore (cyl) from floodplains on loamy soils with Pachycereus-cacti and Acacia, Mexico, Baja California Sur, 8 km W of Ciudad Constitucion, S of Ciudad Insurgentes, 20 m a.s.l., and 25° 00′N, 111°43′W, leg. B. Büdel, no. 20194a. Average precipitation is ~120 mm/year commencing from July to January with two peaks, one from July to September, the second in December and January. Chlorophyll a = 27.1 mg/m2.
23.1 cm2 BSC dominated by approximately 785 thalli of Peltula patellata (Bagl.) Swinscow & Krog (cyl) from soil patches between large boulders, Mexico, Baja California Sur, 3,5 km from highway 1 along road to Punta Abreojos, NW of San Ignacio, Desierto de Vizcaino, 300 m a.s.l., 27°15 N, 113°11′W, leg. B. Büdel, no. 20201a. Average precipitation is ~110 mm/year commencing equally from June to March. Chlorophyll a = 113.5 mg/m2.
Samples of the soil crust were fixed in their natural position in a stainless steel wire basket and positioned in small acryl-glass cuvettes, which were submerged in a water bath for temperature control (15.0 ± 0.1°C in darkness). The CO2 uptake and release of the sample was recorded in an open system with an infrared gas analyzer (BINOS, Rosemount, Hanau, Germany) in the differential mode. For this, air was blown over the BSCs through the cuvettes, the CO2 concentration of which was controlled at 350 ppm by a gas-mixing device that added pure CO2 to CO2-free air by means of mass-flow controllers. Before entering the cuvette, the air was led through a Peltier-operated water-vapor trap that precisely regulates the water vapor concentration. The air dew point was recorded by dew point mirrors before and after the cuvettes. In one cuvette, air humidity was additionally recorded with a humidity sensor (Rotronic Company, Zurich, Switzerland). Four cuvettes were operated in parallel to each other (the measuring system was built by Walz Meß- und Regeltechnik, Effeltrich, Germany). Photosynthetic CO2 uptake and respiratory CO2 release were continually recorded throughout the experiment with an accuracy of ± 0.15 ppm. Soil crust CO2 exchange was related to surface area. Lichen chlorophyll was determined according to Ronen and Galun (1984).
All of the measurements were standardized as follows (Lange and Kilian 1985): the soil crust material was held for 3 days in a growth chamber at 21°C with a regime of 12 h light:12 h dark and was sprayed with deionized water once a day. This treatment served to reactivate the biological soil crusts to a standard level of photosynthetic activity (for more details of methodssee Lange et al. 1993).
Two types of experiments have been conducted. For the resurrection experiment with high air humidity, the BSCs were dried to a low water content of about 1 to 4% of their dry weight by placing them in a desiccator over silica gel for 3,5 days. The dry thalli were then transferred to the gas exchange cuvettes where they were treated from the beginning with air of 96% relative humidity (at 15°C). Great care was taken that water did not condense on the thallus of the lichens at any time during this procedure. The samples in the cuvettes were kept dark with light (200 μmol photons/m2 ∙ s PAR) switched on for 15 minutes in intervals of 1 – 4 hours for detection of possible CO2-fixation.
After 72 hours of humidity treatment, the enclosed soil crusts reached equilibrium with respect to the water potential of the surrounding air, i.e. their weight (water content) no longer increased. Subsequently (after 72 hours of treatment in the routine experiments), they were sprayed with water. During the following period of alternating light and dark phases and treatment with air of 80% relative humidity, the gas exchange of the initially saturated soil crusts was monitored while they dried out.
In order to determine the specific water content related photosynthesis of the four different BSC-types, all samples were moistened by spraying them with water until maximal hydration. The four stainless steel wire baskets with the BSC-types were then placed in the measuring chambers and exposed to 200 μmol photons/sec · m2 photosynthetic active radiation at 15°C; incoming air humidity was set to 96% at the beginning of the experiment and later on reduced to 80%. Every few hours (3–15 hours intervals) the samples were measured for their net photosynthesis and dark respiration. Immediately after each measurement, samples were removed from the cuvettes and their weight was determined in order to calculate the decrease of the BSC water content. This process was continued for 97 hours with each BSC-sample until cease of any CO2 exchange due to total drying.
In addition to the dominating lichen species Psora decipiens, Placidium squamulosum, Peltula patellata and P. richardsii, several other lichen species and 12 free living cyanobacterial species were found at the four BSC collection sites in Baja California. For a complete cyanobacterial and lichen species inventory see Table 1. The experimental material (Figure 1) contained one lichen species only, but was accompanied by free living cyanobacteria (Table 1) on top of the soil between lichen thalli. Their coverage of the total sample area was always less than 2%. While the two chlorolichen-dominated BSCs came from sites with an annual precipitation of 190 and 250 mm, precipitation of the two cyanolichen dominated BSCs sampling sites is roughly half as much, 110 and 120 mm.
The initially dry Placidium squamulosum (chl) dominated crust (Figure 1b) showed first reactions of R 4 hours 30 minutes after exposure to high air humidity alone. Net photosynthesis started 24 hours after exposure and reached 14.7% of its maximal CO2-uptake after subsequent moistening with liquid water (Figure 2). In the second experiments, the drying down curves after maximal water saturation of the crust, maximum rates (90-100%) of NP were determined at crust water content between 0.40 to 0.77 mm precipitation equivalents. At higher degrees of hydration, a moderate suprasaturation depression of CO2 uptake appeared, that reduced NP to 59.5% of its maximum rates in the same experiment (Figure 3).
The initially dry Peltula richardsii (cyl) dominated crust (Figure 1c) did not show any reaction of R and NP to 72 hours exposure with high air humidity alone (Figure 2). Respiration and NP were only activated by spraying with water after 72 hours exposure to high air humidty (Figure 2). Testing the relation of CO2 uptake depending on crust water content in the second experimental setup, these crust type reached maximal CO2 uptake (90-100%) in a range of 0.72 to 1.17 mm precipitation equivalent. Higher degrees of hydration resulted in a moderate suprasaturation depression of CO2 uptake, reducing NP to 40.3% of its maximal rates (Figure 3).
For the initially dry P. patellata (cyl) dominated crust (Figure 1d), neither reactivation of R, nor activation of NP was observed after exposure to high air humidity alone for 72 hours. Respiration and NP were only reactivated after spraying with liquid water (Figure 2). The second experimental setup revealed with 0.48 to 1.05 mm precipitation equivalent the widest range of crust water content, at which maximal (90-100%) CO2 uptake was gained. Higher crust water content resulted in a strong suprasaturation depression of CO2 uptake, which reduced NP to 23.4% of its maximal rates (Figure 3).
The BSCs investigated here all belong to the late successional phase, referring to BSC type 4 (cyanobacterial crust with cyano- and chlorolichens) described by (Büdel et al. 2009) from southwest Africa. The species list given in Table 1 is not representative for the Baja Californian BSCs, as it only lists species found in the samples that were used for the experiments presented here. From own observations and literature we know, that much more lichen-, liverwort-, moss-, cyanobacterial-, and algal-species occur (Flechtner et al. 1998; Rosentreter and Belnap 2003; McCune and Rosentreter 2007). In the present work we focused on the patchiness of photosynthetic performance related to patchiness of dominating lichens species in BSCs at different sites. While R and NP of the two BSC types dominated by cyanolichens could not be activated by high air humidity alone, the two chlorolichen dominated crust types both recovered R and NP at different rates. With high relative air humidity (96%), the Psora decipiens crust reached almost 38% and the Placidium squamulosum crust roughly 15% of their referring maximum rates attained after hydration with liquid water. This is well in accordance with the findings of (Lange and Kilian 1985) and (Lange et al. 1993), who first showed that, in contrast to chlorolichens, cyanolichens of different taxonomical groups cannot be activated with high air humidity alone. The large difference between maximum rates reached and the time for reactivation of NP between the two species (Figure 2, upper graphs) suggest an advantage for Psora decipiens in habitats that regularly experience high air humidity as for example near the coastline.
Compilation of maximal net CO 2 -fixation rates of BSC-lichens and lichen dominated BSCs of different geographical origin (PAR 200–500 μmol/m 2 ∙ s; temperature 15 - 22°C)
Origin of sample
Maximal net CO2-fixation
μmol CO2/m2 ∙ s
[nmol CO2/mg (Chla) ∙ s]
Namib Desert, Namibia
BSC, Peltula patellata
Baja California, Mexico
BSC, Peltula richardsii
Baja California, Mexico
BSC, Psora decipiens
Baja California, Mexico
BSC, Placidium squamulosum
Baja California, Mexico
Namib Desert, Namibia
southern Utah, USA
southern Utah, USA
Namib Desert, Namibia
southern Utah, USA
southern Utah, USA
Studies on the photosynthetic performance of lichens as components of BSCs from temperate regions (Germany) included the species Peltigera rufescens (Weiss) Humb. (cyl), Fulgensia fulgens (Swarz) Elenk. (chl), Diploschistes muscorum (Scop.) R. Sant. (chl), Collema tenax, C. cristatum (L.) Weber (cyl), Cladonia convoluta (Lamb) P. Cout. (chl), C. rangiformis Hoffm. ( (Hahn et al. chl), and Squamarina lentigera 1989; Lange 2000a; Lange and Green 2003, 2004). In all of these studies diurnal courses of photosynthesis under natural conditions, photosynthetic performance at different light intensities, and water content of individual species (separated from other BSC organisms) were investigated (Table 2). It was shown that all chlorolichens investigated like for example Cladonia convoluta could be activated by early morning dewfall. However, for the cyanolichen Collema cristatum in the same habitat at the same time, this event was just enough to reactivate respiration (Lange 2000b). The Psora decipiens and Placidium squamulosum crusts reached maximum NP rates at lower water content (0.3 and 0.44 mm precipitation equivalent) than the Peltula richardsii crust (0.72 mm), while P. patellata (0.48 mm) was more or less similar with the Placidium squamulosum crust.
The relation of high thallus water content and photosynthesis was investigated in the BSC lichens Cladonia convoluta, C. pocillum (Ach.) O.J. Richter (chl), Diploschistes muscorum, Squamarina lentigera, Collema tenax, Toninia sedifolia (Scop.) Timdal ( from steppe vegetation in Germany (Lange et al. chl), and Fulgensia fulgens 1995). In this study four different response types to water suprasaturation were found: type A lichens (Cladonia convoluta, Diploschistes muscorum) with no or almost no CO2-uptake depression, type B lichens (Squamarina lentigera) with only a little depression, type C lichens (Collema tenax, Toninia sedifolia) with a large and increasing depression as the water content increases, and finally the type D lichens (Cladonia pocillum, Fulgensia fulgens) with a strong depression but an inflection so that NP is low but constant. According to this classification, the Psora decipiens and probably the Placidium squamulosum dominated BSCs from our study behave like type D lichens (Figure 3), while the Peltula richardsii and P. patellata dominated BSC types refer to type C.
Using the BSC green algal lichens Diploschistes muscorum and Fulgensia fulgens (Schreber) Norm. (chl), (Lange et al. from a temperate steppe formation, together with the lithophilic D. scruposus 1999) investigated the response of photosynthesis to external CO2 concentration in interaction with the thallus water content. They showed that indeed a water suprasaturation-induced increase in thallus conductance is responsible for CO2-uptake depression. When exposed to stepwise elevated external CO2 concentrations, the effect of CO2-uptake depression was alleviated, and it eventually disappeared totally (with Fulgensia fulgens at 4500 ppm CO2, Diploschistes muscorum 1000 ppm, D. scruposus 1500 ppm). This clearly shows that species composition of BSC lichens and therefore their productivity might not only be influenced by temperature as a consequence of global warming, but also and probably to an even larger degree, by increasing ambient air CO2 concentrations.
Our results show that patchiness of BSC composition (i.e. dominance of single species) is reflected also in patchiness of photosynthetic performance, a phenomenon which seems to be especially important if different functional types of BSC components are involved. This fact might help to interpret soil-crust performance. Thus, as an example, functional patchiness might be part of an explanation for observed differences of soil nutrient availability (soil organic carbon and total nitrogen), that was observed to be significantly different among three desertified grasslands along a degradation gradient, or for the spatial heterogeneity of soil nutrients and respiration of BSC cover in Inner Mongolia (Yu-Chun et al. 2010).
Eldridge and Ferris (1999) reported that the phylogenetic and morphologically closely to Psora decipiens related lichen Psora crenata (Taylor) Reinke (chl), a common BSC component in the Americas and Australia, needs years if not tens of years after disturbance to recover in Australia. Given the important ecological role of BSCs in dry lands of the Earth, also with regard to CO2-fixation (Elbert et al. 2012), detailed knowledge about the mechanisms determining species composition and BSC development in a spatiotemporal scale, is inevitable.
While the Psora decipiens dominated BSC might have an advantage in habitats with frequent high air humidity (e.g. along the coastline), the cyanolichen dominated BSC-types (Peltula patellata, P. richardsii) might have advantage in dryer sites that are subject to floodings. Placidium squamulosum dominated BSCs are somehow in-between, as they can reactivate NP at least to a small proportion, but, to a lesser degree, also can stand water suprasaturation. However, these theoretical conclusions have to remain speculative and are meant as working hypotheses for continuation of research. As a consequence of our studies, it becomes obvious that investigating photosynthetic carbon gain of BSCs cannot just be performed on small soil crust samples of few square centimeters, but need to cover the full spectrum of BSC patches dominated by different species and species composition.
Biological soil crust
Photosynthetic active radiation (400 – 700 nm)
We express our sincere thanks to Ellen Kilian (†) and Hans Reichenberger for technical support. Thomas H. Nash III is thanked for excellent logistics and support during the field trip to Baja California.
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