Abstract
Biological soil crusts (biocrusts) are topsoil communities formed by cyanobacteria or other microbial primary producers and are typical of arid and semiarid environments. Biocrusts promote a range of ecosystem services, such as erosion resistance and soil fertility, but their degradation by often anthropogenic disturbance brings about the loss of these services. This has prompted interest in developing restoration techniques. One approach is to source biocrust remnants from the area of interest for scale-up cultivation in a microbial "nursery" that produces large quantities of high-quality inoculum for field deployment. However, growth dynamics and the ability to reuse the produced inoculum for continued production have not been assessed. To optimize production, we followed nursery growth dynamics of biocrusts from cold (Great Basin) and hot (Chihuahuan) deserts. Peak phototrophic biomass was attained between 3 and 7 weeks in cold desert biocrusts and at 12 weeks in those from hot deserts. We also reused the resultant biocrust inoculum to seed successive incubations, tracking both phototroph biomass and cyanobacterial community structure using 16S rRNA gene amplicon sequencing. Hot desert biocrusts showed little to no viability upon reinoculation, while cold desert biocrusts continued to grow, but at the expense of progressive shifts in species composition. This leads us to discourage the reuse of nursery-grown inoculum. Surprisingly, growth was highly variable among replicates, and overall yields were low, a fact that we attribute to the demonstrable presence of virulent and stochastically distributed but hitherto unknown cyanobacterial pathogens. We provide recommendations to avoid pathogen incidence in the process.IMPORTANCE Biocrust communities provide important ecosystem services for arid land soils, such as soil surface stabilization promoting erosion resistance and contributing to overall soil fertility. Anthropogenic degradation to biocrust communities (through livestock grazing, agriculture, urban sprawl, and trampling) is common and significant, resulting in a loss of those ecosystem services. Losses impact both the health of the native ecosystem and the public health of local populations due to enhanced dust emissions. Because of this, approaches for biocrust restoration are being developed worldwide. Here, we present optimization of a nursery-based approach to scaling up the production of biocrust inoculum for field restoration with respect to temporal dynamics and reuse of biological materials. Unexpectedly, we also report on complex population dynamics, significant spatial variability, and lower than expected yields that we ascribe to the demonstrable presence of cyanobacterial pathogens, the spread of which may be enhanced by some of the nursery production standard practices.
Highlights
Biological soil crusts are topsoil communities formed by cyanobacteria or other microbial primary producers and are typical of arid and semiarid environments
With respect to our first goal, a strict reading of our results obtained here would be that growth dynamics are heterogenous but appear to be dependent on biocrust inoculum origin, including climatic aspects, whereby biocrusts from cold deserts took 3 to 7 weeks to reach maximum levels whereas biocrusts from hot desert took roughly twice as long (12 weeks)
Our data indicate that cold biocrusts will likely develop photosynthetic biomass at a higher rate than warm biocrusts, possibly due to longer active periods enabled by more frequent wetting: warm biocrusts were only watered every 3 days whereas cold desert biocrusts were watered every 2 days
Summary
Biological soil crusts (biocrusts) are topsoil communities formed by cyanobacteria or other microbial primary producers and are typical of arid and semiarid environments. Hot desert biocrusts showed little to no viability upon reinoculation, while cold desert biocrusts continued to grow, but at the expense of progressive shifts in species composition This leads us to discourage the reuse of nursery-grown inoculum. We present optimization of a nursery-based approach to scaling up the production of biocrust inoculum for field restoration with respect to temporal dynamics and reuse of biological materials. Compositionally simple cyanobacterial crusts can recover relatively quickly, in periods of months to several years [14, 19], if conditions are conducive to growth and propagules are present This scenario has spearheaded a recent surge in attempts to actively restore biocrusts. We wanted to test the possibility of reusing nursery-grown biocrusts for several growth rounds while maintaining high growth potential and a stable community composition, so as to further reduce the need for often meager field biocrust remnants
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