Acanthamoeba castellanii alone is not a growth promoter for Hordeum vulgare.

Protists are important key players in the microbial loop and influence their environment by grazing, which leads to the return of nutrients into the soil and reduces pathogen pressure on plants. Specifically, protists on and around plant roots are important for plants' development and growth. For this study, the fourth most important crop in the world, Hordeum vulgare, was selected. Seeds of H. vulgare were inoculated with Acanthamoeba castellanii alone or with additional soil bacteria at the beginning and during the experiment. The germination of the seeds and the growth of the plants in pouches were monitored over 3 weeks. No differences were found in leaf growth, root growth, root and leaf nitrogen content or ammonia content of the liquid from the pouches. In contrast, the relative increase in root and leaf dry weight showed a small difference compared to the controls. The results of this experiment demonstrated that seed inoculation with A. castellanii alone or with additional unidentified soil bacteria did not have a major effect on the growth and development of barley. Nevertheless, small changes in plant development were detected, indicating that A. castellanii should be considered for further investigation of co-inoculations with plant growth-promoting bacteria and additional nutrients.

Elevated atmospheric CO2 concentrations caused a shift of the metabolically active microbiome in vineyard soil.

BACKGROUND: Elevated carbon dioxide concentrations (eCO2), one of the main causes of climate change, have several consequences for both vine and cover crops in vineyards and potentially also for the soil microbiome. Hence soil samples were taken from a vineyard free-air CO2 enrichment (VineyardFACE) study in Geisenheim and examined for possible changes in the soil active bacterial composition (cDNA of 16S rRNA) using a metabarcoding approach. Soil samples were taken from the areas between the rows of vines with and without cover cropping from plots exposed to either eCO2 or ambient CO2 (aCO2). RESULTS: Diversity indices and redundancy analysis (RDA) demonstrated that eCO2 changed the active soil bacterial diversity in grapevine soil with cover crops (p-value 0.007). In contrast, the bacterial composition in bare soil was unaffected. In addition, the microbial soil respiration (p-values 0.04-0.003) and the ammonium concentration (p-value 0.003) were significantly different in the samples where cover crops were present and exposed to eCO2. Moreover, under eCO2 conditions, qPCR results showed a significant decrease in 16S rRNA copy numbers and transcripts for enzymes involved in N2 fixation and NO2- reduction were observed using qPCR. Co-occurrence analysis revealed a shift in the number, strength, and patterns of microbial interactions under eCO2 conditions, mainly represented by a reduction in the number of interacting ASVs and the number of interactions. CONCLUSIONS: The results of this study demonstrate that eCO2 concentrations changed the active soil bacterial composition, which could have future influence on both soil properties and wine quality.

Macroecology of methane-oxidizing bacteria: the ß-diversity of pmoA genotypes in tropical and subtropical rice paddies.

Studies addressing microbial biogeography haveincreased during the past decade, but research onmicrobial distribution patterns is still in its infancies,and many aspects are only poorly understood. Here,we compared the methanotroph community in paddysoils sampled in Indonesia, Vietnam, China and Italy,focusing on the distance­decay relationship.We usedthe pmoA gene as marker for methanotroph diversityin terminal restriction fragment length polymorphism,microarray and pyrosequencing approaches. Wecould observe a significant increase of ß-diversity with geographical distance across continents (12 000 km).Measured environmental parameters explained only asmall amount of data variation, and we found no evidencefor dispersal limitation. Thus, we propose historicalcontingencies being responsible for theobserved patterns. Furthermore, we performed anin-depth analysis of type II methanotroph pmoA distributionat the sequence level. We used ordinationanalysis to project sequence dissimilarities into athree-dimensional space (multidimensional scaling).The ordination suggests that type II methanotrophs inpaddy fields can be divided into five major groups.However, these groups were found to be distributed inall soils independent of the geographic origin. Byincluding tropical field sites (Indonesia and Vietnam)into the analysis, we further observed the firstpaddy fields harbouring a methanotroph communitydepleted in type II methanotrophs.

Termites facilitate methane oxidation and shape the methanotrophic community.

Termite-derived methane contributes 3 to 4% to the total methane budget globally. Termites are not known to harbor methane-oxidizing microorganisms (methanotrophs). However, a considerable fraction of the methane produced can be consumed by methanotrophs that inhabit the mound material, yet the methanotroph ecology in these environments is virtually unknown. The potential for methane oxidation was determined using slurry incubations under conditions with high (12%) and in situ (∼0.004%) methane concentrations through a vertical profile of a termite (Macrotermes falciger) mound and a reference soil. Interestingly, the mound material showed higher methanotrophic activity. The methanotroph community structure was determined by means of a pmoA-based diagnostic microarray. Although the methanotrophs in the mound were derived from populations in the reference soil, it appears that termite activity selected for a distinct community. Applying an indicator species analysis revealed that putative atmospheric methane oxidizers (high-indicator-value probes specific for the JR3 cluster) were indicative of the active nest area, whereas methanotrophs belonging to both type I and type II were indicative of the reference soil. We conclude that termites modify their environment, resulting in higher methane oxidation and selecting and/or enriching for a distinct methanotroph population.

Revisiting methanotrophic communities in sewage treatment plants.

The methanotrophic potential in sewage treatment sludge was investigated. We detected a diverse aerobic methanotrophic community that potentially plays a significant role in mitigating methane emission in this environment. The results suggest that community structure was determined by conditions specific to the processes in a sewage treatment plant.