Comparisons of diazotrophic communities in native and agricultural desert ecosystems reveal plants as important drivers in diversity
FEMS Microbiology Ecology, 92, 2016, fiv166
doi: 10.1093/femsec/fiv166
Advance Access Publication Date: 24 December 2015
Research Article
RESEARCH ARTICLE
Martina Köberl1,∗,† , Armin Erlacher1 , Elshahat M. Ramadan2,3 ,
Tarek F. El-Arabi2,3 , Henry Müller1 , Anastasia Bragina1 and Gabriele Berg1
1
Institute of Environmental Biotechnology, Graz University of Technology, 8010 Graz, Austria, 2 Faculty of
Agriculture, Ain Shams University, 11566 Cairo, Egypt and 3 Biotechnology Laboratory, Heliopolis University,
11777 Cairo, Egypt
∗
Corresponding author: Petersgasse 12/I, 8010 Graz, Austria. Tel: +43 316 873-8423; Fax: +43 316 873-8819; E-mail:
Present address: Pacific Northwest National Laboratory, Biological Sciences Division, Richland, WA 99354, USA. Tel: +1 509 371-6925
One sentence summary: The diazotrophic microbiome of desert ecosystems is characterized by a high diversity and abundance and specific for each
plant rhizosphere.
Editor: Angela Sessitsch
†
ABSTRACT
Diazotrophs provide the only biological source of fixed atmospheric nitrogen in the biosphere. Although they are the key
player for plant-available nitrogen, less is known about their diversity and potential importance in arid ecosystems. We
investigated the nitrogenase gene diversity in native and agricultural desert soil as well as within root-associated
microbiota of medicinal plants grown in Egypt through the combination of nifH-specific qPCR, fingerprints, amplicon
pyrosequencing and fluorescence in situ hybridization–confocal laser scanning microscopy. Although the diazotrophic
microbiota were characterized by generally high abundances and diversity, statistically significant differences were found
between both soils, the different microhabitats, and between the investigated plants (Matricaria chamomilla L., Calendula
officinalis L. and Solanum distichum Schumach. and Thonn.). We observed a considerable community shift from desert to
agriculturally used soil that demonstrated a higher abundance and diversity in the agro-ecosystem. The endorhiza was
characterized by lower abundances and only a subset of species when compared to the rhizosphere. While the microbiomes
of the Asteraceae were similar and dominated by potential root-nodulating rhizobia acquired primarily from soil, the
perennial S. distichum generally formed associations with free-living nitrogen fixers. These results underline the importance
of diazotrophs in desert ecosystems and additionally identify plants as important drivers in functional gene pool diversity.
Keywords: desert farming; diazotrophs; medicinal plants; nitrogen-fixing communities; organic agriculture; Rhizobiales
INTRODUCTION
Nitrogen is one of the most yield-limiting factors in agricultural production systems throughout the world and an essential
macronutrient for plants. Nitrogen-fixing microorganisms provide the only natural source of fixed atmospheric nitrogen in the
biosphere (Gaby and Buckley 2012), and the capability for nitrogen fixation is widely dispersed among prokaryotic taxa including very divergent, distantly related bacteria and archaea (Zehr
and Turner 2001; Zehr et al. 2003). Biological nitrogen fixation by
diazotrophic bacteria together with the input of recycled organic
waste, such as manure or compost, is considered a sustainable
Received: 17 August 2015; Accepted: 17 December 2015
C FEMS 2015. This is an Open Access article distributed under the terms of the Creative Commons Attribution License
(http://creativecommons.org/licenses/by/4.0/), which permits unrestricted reuse, distribution, and reproduction in any medium,
provided the original work is properly cited.
1
Comparisons of diazotrophic communities in native
and agricultural desert ecosystems reveal plants as
important drivers in diversity
2
FEMS Microbiology Ecology, 2016, Vol. 92, No. 2
microscopy (FISH–CLSM) analyses targeting the most dominant
diazotrophic taxa were performed in order to reveal their habitat
preferences and colonization type.
MATERIALS AND METHODS
Experimental design and sampling
Nitrogen-fixing communities were studied at the organically
managed Sekem farm Adleya (www.sekem.com) located in the
north-eastern desert region of Egypt near Bilbeis (30◦ 13 44 N,
31◦ 23 39 E) at Sharqia governorate. Physicochemical data of the
soil is provided in Luske and van der Kamp (2009). The diazotrophic community of bulk agricultural soil was also investigated in comparison to the community of native desert soil
from the Sinai Peninsula, Egypt (30◦ 21 00 N, 32◦ 15 18 E). At each
site, four composite samples of soil in a horizon of 10–30 cm
depth were collected. Profiles of the nifH gene in communities
associated with the rhizosphere and endorhiza of three different
species of medicinal plants (M. chamomilla L., C. officinalis L., and
S. distichum Schumach. and Thonn.) cultivated on Adleya farm
were studied and compared. From each plant species, four independent composite samples consisting of 5–10 plant roots with
adhering soil were taken. The detailed sampling strategy is described by Köberl et al. (2011).
To isolate total community DNA from the soil and rhizosphere, 5 g of soil or roots with adhering soil were added to 45 mL
of sterile 0.85% NaCl and vortexed. For isolation from the endorhiza, 5 g of roots were surface-sterilized with 4% NaOCl for
5 min. The roots were washed three times with sterile distilled
water, then 10 mL sterile 0.85% NaCl were added and further homogenized using mortar and pestle. For isolation of total DNA
from the rhizosphere, endorhiza and soil, 4 mL of the suspensions were centrifuged (16,000 × g, 4◦ C) for 20 min and the resulting microbial pellets were stored at –70◦ C. In the desert soil,
a lower concentration of DNA was expected. Therefore, the pellets of 10 mL suspension were used for the isolation of total DNA.
Total community DNA was extracted using the FastDNA SPIN Kit
for Soil (MP Biomedicals, Solon, OH, USA).
Quantification of microbial nifH genes by qPCR
To determine nifH gene abundances, quantitative PCRs were performed according to Hai et al. (2009) with following modifications. Reactions were conducted in a total volume of 10 μL containing 1× KAPA SYBR FAST qPCR MasterMix Universal (PEQLAB,
Polling, Austria), 0.6 mg mL−1 BSA, 0.125 μM of primers nifH-F
and nifH-R (Rösch, Mergel and Bothe 2002), and 0.8 μL template
DNA dilutions with a concentration of ∼1 ng μL−1 (95◦ C, 10 min;
39 cycles of 95◦ C, 45 s; 55◦ C, 45 s; 72◦ C, 45 s; and melt from 72
to 95◦ C). Rotor-Gene 6000 real-time rotary analyzer (Corbett Research, Sydney, Australia) was used for fluorescence quantification. For absolute quantification, the PCR amplified nifH gene
fragment from Pectobacterium atrosepticum SCRI1043 was ligated
into the pGEM-T Easy Vector (Promega, Mannheim, Germany)
and transformed into Escherichia coli DH5α. Serial dilutions of PCR
fragments generated with the vector-specific primers USP and
RSP (Köberl et al. 2011) were u (...truncated)