Center for Fundamental and Applied Microbiomics, Biodesign Institute, Arizona State University, Tempe, Arizona, USA.
School of Life Sciences, Arizona State University, Tempe, Arizona, USA.
Appl Environ Microbiol. 2019 Jul 18;85(15). doi: 10.1128/AEM.00735-19. Print 2019 Aug 1.
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. 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.
生物土壤结皮(biocrusts)是由蓝细菌或其他微生物初级生产者形成的表土群落,是干旱和半干旱环境的典型特征。生物土壤结皮促进了一系列生态系统服务,如抗侵蚀和土壤肥力,但它们经常受到人为干扰而退化,导致这些服务的丧失。这促使人们有兴趣开发恢复技术。一种方法是从感兴趣的区域获取生物土壤结皮的残余物,在微生物“苗圃”中进行大规模培养,该苗圃生产大量高质量的接种物,用于野外部署。然而,生长动态和为持续生产而重复使用所产生接种物的能力尚未得到评估。为了优化生产,我们跟踪了来自寒冷(大盆地)和炎热(奇瓦瓦)沙漠的生物土壤结皮苗圃的生长动态。在寒冷沙漠生物土壤结皮中,光合生物量在 3 至 7 周内达到峰值,而在炎热沙漠生物土壤结皮中则在 12 周内达到峰值。我们还重复使用了由此产生的生物土壤结皮接种物来接种连续的孵育,使用 16S rRNA 基因扩增子测序跟踪光养生物量和蓝细菌群落结构。重新接种时,炎热沙漠的生物土壤结皮几乎没有活力,而寒冷沙漠的生物土壤结皮继续生长,但代价是物种组成的逐渐变化。这导致我们不鼓励重复使用苗圃种植的接种物。令人惊讶的是,复制之间的生长差异很大,整体产量很低,我们认为这归因于具有毒性且随机分布但迄今未知的蓝细菌病原体的存在。我们提供了避免在该过程中发生病原体感染的建议。生物土壤结皮群落为干旱土地土壤提供了重要的生态系统服务,例如促进抗侵蚀的土壤表面稳定和有助于整体土壤肥力。生物土壤结皮群落受到人为退化(通过牲畜放牧、农业、城市扩张和践踏)的影响很常见,而且影响很大,导致这些生态系统服务的丧失。由于尘土飞扬,这不仅影响了本地生态系统的健康,也影响了当地居民的公共健康。正因为如此,全世界都在开发生物土壤结皮恢复方法。在这里,我们提出了优化基于苗圃的方法,以扩大生物土壤结皮接种物的生产,用于田间恢复,重点是时间动态和生物材料的重复使用。出乎意料的是,我们还报告了复杂的种群动态、显著的空间变异性和低于预期的产量,我们将其归因于蓝细菌病原体的存在,这些病原体的传播可能会因一些苗圃生产标准实践而加剧。