Arbuscular mycorrhizal fungi (AMF), which are present in most natural environments, have demonstrated capacity to promote biodegradation of organic pollutants in the greenhouse. However, it is not certain whether AMF can spontaneously establish in phytoremediation systems constructed to decontaminate groundwater, because of the unusual conditions during the construction and operation of such systems. To assess this possibility, root samples from a wetland constructed for the phytoremediation of groundwater contaminated with benzene, methyl tert-butyl ether and ammonia were analysed. Substantial AMF colonization was observed in plant roots sampled close to the inlet of a basin filled with fine gravel and planted with Phragmites australis. In addition, analysis of a fragment of the nuclear large ribosomal subunit, amplified by nested PCR, revealed the presence of AMF molecular operational taxonomic units closely related to Funneliformis mosseae and Rhizophagus irregularis in the samples. These findings demonstrate the capacity of generalist AMF strains to establish spontaneously, rapidly and extensively in groundwater bioremediation technical installations.
If you can't find a tool you're looking for, please click the link at the top of the page to "Go to old article view". Alternatively, view our Knowledge Base articles for additional help. Your feedback is important to us, so please let us know if you have comments or ideas for improvement.
An arbuscular mycorrhiza is a type of close, mutualistic association that forms in root systems between diverse plant species and members of a small group of soil fungi (arbuscular mycorrhizal fungi, AMF; Smith and Read, 2008). The association allows the exchange of nutrients (carbohydrates provided by the plant, mineral nutrients provided by the fungi), and markedly increases the host plant's tolerance of various biotic and abiotic stress factors. Arbuscular mycorrhizal fungi also influence the transport and distribution of organic pollutants in plants (Debiane et al., 2009; Langer et al., 2010), reportedly reducing their concentrations in shoots of colonized plants, while increasing their concentrations in roots, particularly in the rhizodermis (Huang et al., 2007; Wu et al., 2009). These effects may help to protect plants from damage by organic pollutants. Beneficial effects of the presence of AMF on soil bacteria (Toljander et al., 2007), notably bacteria capable of degrading organic compounds (Corgié et al., 2006; Alarcon et al., 2008), have also been reported. By both protecting plants from adverse effects of organic pollutants and promoting associated bacteria, AMF can accelerate the biodegradation of organic pollutants. Several studies have recently demonstrated beneficial effects of AMF on the biodegradation of organic pollutants, including: the dissipation of polycyclic aromatic hydrocarbons (PAHs) by Lolium multiflorum (Yu et al., 2011), dissipation of PAHs by Medicago sativa under low water and phosphate availability (Zhou et al., 2009), and phytoremediation of aged petroleum contamination by Triticum aestivum (Malachowska-Jutsz and Kalka, 2010). Arbuscular mycorrhizal fungi can therefore be considered ideal inhabitants of technical installations for the plant-based bioremediation of groundwater contaminated by organic pollutants. However, such installations are often constructed without including a significant source of AMF propagules. Furthermore, the stressful conditions in such installations – such as poor substrates, and potentially toxic concentrations of organic pollutants for the fungi (Verdin et al., 2006; Debiane et al., 2011) – may hinder the successful establishment of AMF.
To investigate the ability of AMF to establish under such conditions, we analysed AMF colonization levels in plant roots sampled from a wetland constructed to decontaminate groundwater polluted with benzene, methyl tert-butyl ether (MTBE) and ammonia. The wetland was continuously streamed (inflow rate 6 l h−1) by water containing 20, 3.7 and 45 mg l−1 of these compounds respectively. Arbuscular mycorrhizal fungi present in roots from Phragmites australis growing in this wetland were phylogenetically analysed by cloning and sequencing a 400 bp fragment of the nuclear large ribosomal subunit, amplified by nested PCR.
Results and discussion
Spontaneous colonization of constructed wetlands
The constructed wetland investigated in this study was established in March 2007. It consists of a basin that receives a stream of contaminated groundwater. Phragmites australis plantlets were planted at the inlet end, which is filled with light gravel. Close to its outlet area there is a compartment lacking the gravel substrate where P. australis is growing in water, forming a dense root mat (Fig. 1). Root samples taken from the part of the constructed wetland with the gravel substrate in 2011 were substantially associated with AMF (colonized proportions by length, 40%, 25%, 25%, 60% and 80%; see Fig. 1 legend for details), clearly showing that these fungi successfully colonized this unusual environment within 4 years. Thus, establishment of AMF does not appear to have been profoundly hindered in the inlet part of the wetland, although it was exposed to the highest concentrations of organic pollutants. In contrast, no colonization of roots by AMF was observed in the part of the basin where the plants were growing in free water with no gravel substrate, suggesting that a solid substrate was required for AMF colonization. The likeliest sources of the colonizing fungi were airborne propagules or mycelia already present in the P. australis plantlets when they were transferred to the constructed wetland.
Generalist AMF strains as early and rapid colonizers of the constructed wetland
Considerable frequencies of very similar patterns were detected in restriction fingerprinting of PCR products cloned from a fragment of the large ribosomal subunit, indicating that the AMF community within the constructed wetland had low diversity at the sampling time. Fifty-one clones with identical patterns were removed from the analysis, leaving 34 unique clones for sequence analysis, and only two AMF taxa were detected: Rhizophagus irregularis and Funneliformis mosseae. The restriction endonuclease Taq I was used for restriction fingerprinting, partly because it has been recommended for T-RFLP analysis of the PCR fragment analysed in this study (Mummey and Rillig, 2007), and partly because almost all AMF species in the phylogenetic tree shown in Fig. 2 could be differentiated using this enzyme in a virtual digest. In particular, it was possible to differentiate all other species from R. irregularis and F. mosseae, the two AMF found in the wetland samples, excluding the possibility that AMF species were missed because of the use of Taq I for restriction fingerprinting prior to sequence analysis. As the primer pairs used in our analysis are not capable of amplifying sequences of members from the genus Diversispora or the families Archaeosporaceae and Paraglomaceae (Gamper et al., 2009), however, the possible presence of additional AMF from these groups cannot be excluded. Phylogenetic analysis using the set of consensus sequences for AMF (see fig. 1 in Krüger et al., 2011) clearly showed that all sequences analysed in our study clustered with the AMF genera Rhizophagus or Funneliformis (data not shown). Only four sequences clustered with different fungal groups, one of which proved to be a chimeric sequence in later analysis, while the other three were very similar to sequences of the basidiomycotan genus Cryptococcus. We have previously observed unspecific amplification of nuclear rRNA from this genus using the primers FLR3 and FLR4 on a number of occasions. Cryptococcus is a large fungal genus with some species that are pathogenic for humans. Although substrate (light gravel) and inflowing water (contaminated groundwater) can be expected to be relatively poor inocula in general, introduction of members from Cryptococcus by these sources cannot be excluded. Alternatively, airborne spores have been described for the pathogenic species (Hajjeh et al., 1995; Kidd et al., 2007) and appear also possible as sources of inoculation in the case presented here.
To examine the sequences clustering with Rhizophagus or Funneliformis in more detail, all reference sequences not belonging to either of these genera or the out-group genus Glomus were removed, while more sequences from Rhizophagus and Funneliformis – summarized by Krüger and colleagues (2011) – were included in the analysis. After sequence alignment and construction of a maximum likelihood tree (using the general time reversible evolutionary model), the sequence groups clustering with Funneliformis showed a close relationship with F. mosseae, while those clustering with Rhizophagus clustered exclusively with sequences from R. irregularis (Fig. 2). The phylogenetic tree produced from the applied sequences (Fig. 2) was therefore restricted to those branches in R. irregularis and F. mosseae that can be differentiated by virtual digestion using Taq I. As already mentioned, the possible presence of additional AMF from the Diversispora, Archaeosporaceae or Paraglomaceae cannot be excluded, because of limitations of the primers used in our analysis. Nevertheless, the observation only of sequences connected to R. irregularis and F. mosseae, after screening 85 and sequencing 34 sequences, corroborates the preliminary indications that the constructed wetland contained an AMF community with very low diversity.
Rhizophagus irregularis refers to a large part of the taxonomic group that was previously known as Glomus intraradices, while F. mosseae was previously named Glomus mosseae (Schüßler and Walker, 2010). Both of these species are known to be typical generalist AMF (Öpik et al., 2006; Rosendahl et al., 2009; Oehl et al., 2010) that have been found in diverse habitats around the world. Although they have not been mentioned specifically in analyses of AMF succession (Piotrowski and Rillig, 2008), they seem to be pioneer AMF strains in the constructed wetland we studied.
Elke Häusler provided excellent technical assistance. The constructed wetland examined was established and funded by the Helmholtz Centre for Environmental Research – UFZ within the scope of the SAFIRA II Research Programme (Revitalization of Contaminated Land and Groundwater at Megasites, subproject ‘Compartment Transfer – CoTra’). The manuscript has been reviewed by SEES Editing (Weston-Super-Mare, North Somerset, UK).