Review Paper15N2 as a tracer of biological N2 fixation: A 75-year retrospective
Introduction
15N2, or to be more precise 15N2 reduction, has played a key role in studies of biological N2 fixation over the past 75 years, since publication of the seminal paper of Burris and Miller (1941). Several general reviews have been written about the measurement of N2 fixation using 15N techniques, including 15N2 (Bergersen, 1980, Focht and Poth, 1987, Weaver and Danso, 1994, Zehr and Montoya, 2007). However, a contemporary overview of the subject is lacking, particularly the role of 15N2 as the only direct 15N method. The major drawback of using 15N2 is the high cost of the isotope which necessitates exposure of the plant to the substrate in a leak-free closed chamber, thus precluding the use of more realistic experimental set-ups such as open-top or flow-through chambers.
Millbank and Olsen (1981) and Warembourg (1993) provided descriptions of (i) systems to prepare, purify and store 15N2 (ii) the types of enclosures used for biological materials (iii) methods of environmental control of enclosures and (iv) operating procedures. Many other enclosure systems that were not reviewed by Millbank and Olsen (1981) or Warembourg (1993) have been described in the literature. Consequently we will provide an overview of the distinctive features of diverse systems used with vascular plants, including legumes and non-legumes.
In addition, we will explore the usage of 15N2 in fundamental studies of N2 fixation, including confirmation of putative N2 fixation in various biological systems, the calibration of assays to estimate the rate of biological N2 fixation, the identification of the biochemical products of N2 fixation and assimilation pathways within the plant, 15N2 stable isotope probing to identify uncultured diazotrophs in the biosphere and the role of 15N2 in quantifying N2 fixation and the dynamics of BFN within various components of terrestrial and fresh water ecosystems. We will discuss the practical problems encountered when employing 15N2 as a quantitative tracer, and highlight the problems associated with alternative indirect 15N methods. The focus of the review is terrestrial ecosystems, particularly agroecosystems, which also include flooded rice, but we do not cover the marine environment.
Section snippets
Cultures, excised nodules/nodulated roots, soil, and non-vascular plants
Burris and Miller (1941) were the first to report N2 fixation by a culture of Azotobacter vinelandii by exposure to 15N2, while Burris et al. (1943) exposed excised nodules and nodulated roots of pea to 15N2 to demonstrate legume-Rhizobium symbiotic N2 fixation. Subsequent studies with 15N2 confirmed biological N2 fixation with lichens and the liverwort Blasia (Bond and Scott, 1955), and free-living heterotrophs in soil (Delwiche and Wijler, 1956). Later work with 15N2 focused on N2 fixation in
Systems used to expose biological materials to 15N2
Various types of chambers have been constructed to enclose the roots or the roots + tops of the plant, with considerable variation in chamber volume (Table 1). Warembourg (1993) outlined the factors to be considered when deciding on chamber volume. Often relatively small volumes (<3 l) were used to reduce the cost of the isotope (e.g. Bond, 1955, De-Polli et al., 1977, Ruschel et al., 1979, Frey and Schüepp, 1992, Bremer et al., 1995), but some chambers were much larger varying from 60 l (
Identification of the biochemical products of biological N2 fixation and assimilation pathways
Various physiological studies since the mid 1940's have supplied 15N2 to free-living N2-fixing micro-organisms (Burris and Wilson, 1946, Zelitch et al., 1951), detached alder nodules (Alnus glutinosa; Leaf et al., 1958), detached bog-myrtle nodules (Myrica gale; Leaf et al., 1959), detached legume nodules (Aprison et al., 1954, Bergersen, 1965, Kennedy, 1966a, Kennedy, 1966b), isolated bacteroids (the N2-fixing forms of rhizobia present in nodule infected cells) from legume nodules (Bergersen
Calibration of assay procedures using 15N2
Numerous studies that were designed to calibrate the acetylene reduction assay were conducted with 15N2 using microbial cultures, excised nodules, excised nodulated roots, plant litter, stem segments, intact root systems and whole plants (Table 3). Calibration involved the simultaneous determination of the ratio of C2H2 reduced to N2 fixed. The ratios obtained were extremely variable being either higher or lower than the theoretical 3:1 (Table 3). Many factors were responsible for this
Stable isotope probing (SIP) with 15N2
Despite the vital importance of biological N2 fixation in maintaining terrestrial ecosystem sustainability, the taxonomic identity of the microorganisms involved has usually been confined to a small fraction of the microbiota that can be isolated and cultivated. The recent development in the coupling of molecular biological methods with SIP in biomarkers has provided a cultivation-independent means of linking the identity of bacteria with their function in the environment (Radajewski et al.,
Endophytic diazotrophs
15N2 has been used worldwide to identify endophytic biological N2 fixation in a range of cereals and tropical grasses. Chalk (2016) reviewed 22 published papers in which the 15N2 technique confirmed putative N2 fixation. Because a control or reference treatment is not required, N2 fixation can be measured either under natural (undisturbed) or imposed (e.g. inoculated) treatments. Exposure times were generally of short duration, usually a few days but seldom exceeding 1–2 weeks (Chalk, 2016).
Studies with rice
The distribution of 15N2 fixed between above- and below-ground components of paddy rice was determined by short- and long-term exposure to 15N2 at different growth stages (Table 5). The highest proportion of N2 fixed for short-term exposure was in the soil (>75%), with a greater proportion in tops than in roots, irrespective of growth stage, exposure time or whether roots or tops + roots were exposed to 15N2 (Table 5).
For a long-term exposure to 15N2 (10 weeks) a different distribution emerged
Patm estimated by indirect methods that use a reference plant
Indirect 15N-based methodologies using either E or NA approaches to estimate Patm by N2-fixing plant associations require a non-N2-fixing reference plant treatment to act as a surrogate to estimate the proportion of labelled to unlabelled soil N obtained by the N2 fixer (Unkovich et al., 2008, Chalk et al., 2016). The E method is based on the addition of a 15N-enriched material to the soil, but no addition is required with the NA method. The E method results in a marked temporal and spatial
Conclusions
15N2 has been used on many occasions since 1941 to examine the assimilatory pathways associated with biological N2 fixation, and to confirm putative N2 fixation by a range of biological materials. However, because of technical problems associated with the use of enclosures and the high cost of 15N2, the direct method has seldom been used to obtain quantitative estimates of N2 fixed over a plant's life cycle. The relatively small chamber volume has generally restricted the scale of experiments
Acknowledgements
The senior author thanks the Chinese Academy of Sciences (CAS) for a Visiting Fellowship under the CAS President's International Fellowship Initiative for 2016, Grant No. 2016VMB029.
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