- Open Access
Light dazzles from the black box: whole-cell biosensors are ready to inform on fundamental soil biological processes
© Renella and Giagnoni. 2016
- Received: 13 October 2015
- Accepted: 14 March 2016
- Published: 31 March 2016
- Whole-cell biosensors
- Soil and environmental analysis
- Nutrient and contaminant bioavailability
- Ecological interactions in soil
- Future agriculture
Understanding of how microorganisms actually perceive the surrounding soil habitat and how they react to changes of environmental conditions is a great challenge to soil scientists and microbial ecologists, and is considered a need for the optimal management and conservation of soil microflora and microbially driven key soil functions. As a reactor, soil has been classically seen as a black box  capable of degrading and transforming all known chemical compounds, in accordance with the microbial metabolic infallibility dictum . This view was consolidated by the outcome of experiments based on the soil inoculation with organic substrates and inhibitors, or by exposing soils to varied moisture and temperature conditions followed by the analysis of the substrate use, products release or changes in the soil microbial communities. However, this approach does not provide information on the metabolic pathways active within microbial cells. The soil black box has been partially opened from the 1990s through the quantification of microbial C, N, P and S microbial pools from the 1970–1980s , and the characterization of the soil microbial communities by genomics , proteomics , transcriptomic , metabolomic  and lipidomic . However, there is a general consensus on the idea that the knowledge on microbial diversity and the rate of soil functions still do not allow to understand the factors leading to gene expression in the microbial communities, and that this gap prevents the development of an ecological theory of the soil environment. The scope of this review is to illustrate how the biosensors can reveal the mechanisms leading to gene expression in the complex soil matrix, hold potentials to optimize the crop nutrient use efficiency and provide new tools in the study of plant–microbe interactions. The final goal is to fuel the use of the whole-cell biosensors as a new paradigm in soil and agricultural sciences. Detailed description of the genetic construction whole-cell biosensor and signal detection systems are out of the scopes of the present review, and we refer to previous comprehensive reviews [8, 39, 42, 66, 71, 83, 84, 130, 131, 134].
Biosensors types and functioning
Whole-cell biosensors should be distinguished from the chemical sensors that, according to IUPAC, are devices in which the recognition system is a natural or engineered biological molecule reacting with a biochemical mechanism producing a detectable physical or chemical signal, linked to a device for signal transduction. The IUPAC further classifies the biosensors according to the biological specificity, mode of signal transduction and on the variation (consumption/production) of analyte concentration. This type of biosensors are not discussed in the present review, and readers interested in the potential of chemical biosensors are referred to the IUPAC Gold Book , and specifically for soil applications to the comprehensive review by . Chemical and cellular biosensors share the common recognition mechanisms, but for whole-cell biosensor recognition of a selected analyte occurs after its transport across the cell membrane and diffusion within the intracellular components, and hereafter will be termed biosensors.
Biosensors are either natural or engineered microorganisms, typically bacteria, producing a detectable signal encoded by a reporter gene, upon activation of a promoter gene induced by specific stimuli. Depending on the regulation of the promoter gene expression mechanism, biosensors can be classified as constitutive or inducible. The use of reporter genes for detecting the factors triggering genetic responses in living organisms dates back to the 1940s, when Monod  and Novick and Weiner  first described the functioning of the lac operon (the lacZ coding for the β-galactosidase enzyme) and its relation with microbial growth patterns. These seminal studies have been confirmed after the discovery of the biological role and structure of DNA, and other reporter genes such as, xylE (coding for the catechol-2,3-dioxygenase) and tfdA (coding for the 2,4-dichlorophenoxyacetate oxidase) have been widely used as biophysical model for understanding the microbial sensing of specific analyte in their environment . However, these early reporter genes are not useful for studying the metabolic activity of soil microorganisms because their products cannot be resolved against the strong background of these enzymes in soil. Differently, signals such as bioluminescence or fluorescent proteins can be easily and sensitively detected in soil.
Biosensors can be naturally or genetically modified microorganisms emitting luminescence or fluorescence constitutively or linked to the expression of specific functional genes. Because the signal intensity is related to the level of the cellular metabolism or the activation of specific promoters, luminescent and fluorescent microorganism have been increasingly used to gain indications of biological responses to changes in a complex and heterogeneous natural matrix as soil (Fig. 1).
Biosensors for environmental analysis
Strains and plasmids (in brackets) used for constructing whole-cell biosensors inserting lux, gfp and β-galactosidase reporter genes responding to different organic and inorganic compounds and elements
P. fluorescens HK44 (pUTK21)
P. putida RB1353/RB1351 (pUTK9)
P. putida RB1401 (pTOL)
P. putida TVA8 (pUTK214)
Stenotrophomonas sp ENV307 (pUTK60)
R. eutropha JMP134 (pUTK220)
Burkholderia sp (pUCD607)
Pseudomonas putida F1 (pUT mini-Tn5 luxCDABE)
N. europaea ATCC 19718(pHLUX20)
P. fluorescens A506 (pTS)
Heavy metals and metalloids
S. aureus RN4420 (pI258)
C. metallidurans CH34 (pMOL30)
Cd, Zn, Ni
R. leguminosarum bv trifolii F6 (pUCD607)
C. metallidurans AE1239 (pMOL30)
P. putida KT2440 (pUT-mer-lux)
Nutrients and physiologically active molecules
P. fluorescens 10586 (pP2)
P. fluorescens DF57 N3 (pP2)
P. fluorescens DF57 P9 (pP2)
P. putida KT2440 (pLYS24-davT-lux)
P. fluorescens WCS365 (pMP5291)
R. leguminosarum 4292 (pIJ1737) (pIJ1730)
R. leguminosarum 3841 (pOT1)
P. fluorescens F113 SF3 (pLS312), SF5 (pLS52)
Early environmental applications of biosensors employed naturally luminescent (490 nm) bacteria such as Vibrio fischeri (re-classified as Aliivibrio fischeri) for monitoring water quality , sediments and pore water toxicity [17, 31], waste toxicity  and efficiency of bioremedation . Several biosensor-based systems based on Vibrio fischeri as reporter strain have been commercialized such as Microtox® (Modern Water, UK), BioTox®, LUMIStox® (Hach Lange, Germany), TOXmini® (microLAN, The Netherlands) or ToxAlert® (Merck, Germany) and iTOX control® (microLAN, The Netherlands), BIOMET® and VITOTOX® (GENTAUR, Belgium) [18, 46, 52, 60, 69, 129]. These constitutive naturally luminescent biosensors provide information on the soil and environmental toxicity because the luciferase activity is related to cell integrity and full metabolic activity and is reduced upon cell damage or toxicity. A standard protocol for bioluminescence-based environmental toxicity assessment has been set up (ISO 11348 2007) and successfully used for the analysis of toxicity of polluted and remediated soils e.g. . Two naturally bioluminescent fungi, Armillaria mellea and Mycena citricolor have been also used to assess the toxicity to microeucaryotes . However, these biosensor types provide general information on the cell integrity but not on the response of specific genes to the presence of specific analyte.
Genetically modified biosensors
The soil-borne bacteria with the promoterless luxCDABE gene cassette inserted in transcriptional fusion with the promoter genes of operons inducible by naphthalene and its metabolite salicylate were Pseudomonas fluorescens HK44 and P. putida RB1353 [19, 55]. This pioneer work demonstrated that a regulatory genetic circuit could be artificially fused with an exogenous luciferase gene producing a bioluminescence signal upon exposure or uptake of specific analyte by the host cell, and opened the road to the construction of several and more analyte-specific whole-cell biosensors whose responses can be calibrated, and interpreted as microbial genetic responses to environmental stimuli. Further improvement of the original insertion scheme led to the set up of a large number of whole-cell biosensors in which the promoterless lux and gfp genes are fused under control of inducible promoters producing bioluminescence or fluorescence. A sample of whole-cell biosensors constructed on soil-borne bacteria is reported in Table 1.
Eukaryotic biosensors are based on lux-, luc- and gfp-inserted yeasts, microalgae and protozoa (for a review, see ). However, while microalgae and yeast-based biosensors have been mainly used for studying metal availability in water bodies and other environmental matrices, protozoa biosensors such as Tetrahymena thermophila inserted with the luc or gfp genes in transcriptional fusion with metallothionein genes inducible upon exposure to Cd and Pb showed promising applications [3, 4].
The most important feature of biosensors in soil and environmental studies is that they can indicate the bioavailability, which is the crossing of the cell membrane by selected analyte triggering a genetic of a genetic response. Currently, this information cannot be obtained by soil chemical analyses, and can only be indirectly inferred by studies on the genomic and proteomic responses of soil organisms ; in fact effects of nutrient or pollutant availability to soil microbial communities can be estimated from the induced permanent changes in the structure and diversity of the soil microbial communities.
Chemical characterization of bioavailability in soils is based on the assumption that it mainly depends on sorption/desorption processes that regulate the elemental concentrations in the soil solution from where plants and soil organisms perform the absorption process , and it has been demonstrated that the elemental absorption by plants is generally correlated to specific chemical pools , whereas the elemental availability to soil microorganisms is more difficult to be assessed by chemical methods . Differently, the measurement of biosensor responses to specific analyte in soil may allow an online monitoring of the elemental bioavailability by monitoring the induction of specific promoters, allowing a better assessment of bioaccumulation and biomagnification in food chains, and therefore improving the risk assessment for terrestrial ecosystems. Although the toxicity of a specific compound or element can vary for different organisms, it has been reported that the median effective concentrations (EC50) of more than 1200 chemical substances for prokaryotes, eukaryotes and humans can be compared to their effects on V. fischeri bioluminescence .
Biosensors for assessing nutrient availability
Plant uptake of nutrients occur in the rhizosphere which is the soil portion physically and chemically modified by the release of root exudates, and where potential competition for nutrients between plants and microorganisms takes place. Nutrient availability in rhizosphere and bulk soil be studied with the lux-inserted strains of P. fluorescens strains expressing bioluminescence under C, N and P and starvation conditions and proportionally reduce their bioluminescence upon the assimilation of the nutrients [67, 109]. These biosensors have been successfully used to estimate the nutrient availability in various soils and during the decomposition of the organic matter [34, 61], and to evaluate the nutrient flow in the rhizosphere . Protocols for simultaneous determinations of C, N and P availability using the P. fluorescens strains 10586 pUCD607, DF57 N3 and DF57 P9 have been set up by Standing et al. . Using the luminescent cellular biosensor P. fluorescens 10586 pUCD607  monitored the release of root exudates in response to NO3 −-N, and demonstrated that lowering of nitrate concentrations in the rhizosphere induced an increase of the rhizodepositions by Hordeum vulgare at the root apex. The nutrient assimilation in soil has been also studied with GFP-expressing biosensors under the control of the promoter of the operon narG in E. cloacae EcCT501R  and inaZ of P. syringae expressing the ice nucleation protein in response to increased intracellular concentrations of the NO3 −N. Using these biosensors DeAngelis et al.  demonstrated that the NO3 − availability increased in the rhizosphere of Avena fatua as compared to bulk soils and that nitrate fertilization could reduce the root/microbe competition for NO3 −N. It was also shown that N becomes limiting during the organic matter decomposition for soil microorganisms. Assimilation of orthophosphate by microorganisms has been monitored by the use of FRET biosensors on Synechococcus strains by engineering the genes encoding for the phosphate-binding protein . However, it should be underlined that N and P limitation in the rhizosphere could depend not only on their total concentrations but also on their chemical forms and speciation. For example, the lux-based Pseudomonas N-reporter strains reporting N limitation also reacts to the exposure to aminoacids such as glutamate or lysine, like in the case of the P. putida that responds to lysine in the rhizosphere or bulk soil of oat plants . Jaeger et al.  detected the presence of tryptophan and sucrose from the mature districts of lateral roots and sucrose to the root apex, respectively, using an Erwinia herbicola biosensor with the inaZ under control of a tryptophan-inducible gene. Using a P. fluorescens biosensor, in which the lux gene was under control of the promoter of rDNA synthesis, Marschner and Crowley  demonstrated that the release of root exudates sustained the higher cellular activity of P. fluorescens in the plant rhizosphere than in bulk soil. Ramos et al.  using a P. putida strain encoding an unstable GFP variant for gfp genes under control of rDNA promoters showed that active rhizobacteria were preferentially localized at the root apex as compared to the mature or senescent root districts.
Biosensors for assessing bioavailability of heavy metals and metalloids
Soils have high retention capacity to soil towards inorganic and organic pollutants due to their content of highly reactive inorganic and organic phases. Biosensors have been extensively used for studying the bioavailability of heavy metals and metalloids in polluted soils, mainly using lux and gfp reporter genes inserted under promoters responding to increased intracellular metal concentrations . Gram-positive and gram-negative bacteria resist to Hg through reduction of Hg2+ into its elemental form and volatilization through enzymes coded by the mer operon found on either chromosome, plasmids or transposons . The knowledge of the mer operon regulation has allowed the construction of lux-inserted biosensors by inserting the luxCDABE cassette in the Pmer promoter of the merTPC genes , through insertion of the regulatory merR gene with the reporter luc gene in the E. coli MC1061  or a luxCDABE construct of Pmer in P. putida KT2440 , with in vitro detection limits in the order of 0.1 fM. An E. coli-based biosensor was constructed by Ramanathan et al.  inserting the arsR regulatory gene upstream of a promoterless luxAB gene in a plasmidial ars operon, which can detect As without effects of other oxyanions such as phosphate, sulphate or nitrate. In C. metallidurans CH34 (formerly Ralstonia metallidurans), carrying genes encoding inducible multiple metal resistance on the plasmid pMOL28, allowed the construction of a Cr-responding biosensor  a chr-lux fusion (strain AE104 pEBZ141) that responded to both Cr(III) and Cr(VI), with Cr(VI) producing a 10-fold signal as compared to Cr(III). A biosensor responding to Cr based on O. tritici sensitive expressing the gfp gene under the control of the chr promoter and the chrB regulator . Biosensors for detecting Cd, Zn, Cu, Pb and other cationic trace elements have been created inserting reporter genes in genetic sequences encoding multiple resistance mechanisms of different microorganisms, such as P-type ATPase efflux pumps or multicomponent efflux mechanisms encoded by structural (e.g. cadA) and regulator (e.g. cadC) plasmidial genes or operons (Nies ). A Bacillus subtilis BR151 biosensor, carrying the pTOO24 plasmid inserted with the luc gene under transcriptional control of cadC of the cad operon was proposed by Tauriainen et al. . More metal-specific biosensors were constructed in E. coli inserting the luxAB in the promoters of genes conferring resistance through P-type ATPases  or using the regulatory mechanisms of the cop, pbr, czc operons induced by Cu, Pb or Cd, respectively, present on plasmids or megaplasmids of C. metallidurans and fused with the promoterless luxCDABE . A bioluminescent Cu-specific biosensor was constructed in P. fluorescens by Tom-Petersen et al. . Using a constitutive Cu-sensitive P. fluorescence strain Maderova et al.  showed that Cu bioavailability was different depending on the Cu source and that, although the responses were correlated to free Cu2+ concentrations it also indicated the bioavailability of other Cu forms, and the same was observed for Zn , confirming the previous finding by Brandt et al. , that dissolved organic matter can increase the metal bioavailability in soil.
Biosensors for assessing bioavailability of organic pollutants
Hydrophobic organic compounds once released into soil become less available due to sorption and exhibit declined toxicity with time. Typically, the sorbed compounds become less accessible upon time and are therefore considered unavailable . However, accumulation of organic pollutants in soils pose significant risks to human health and ecosystems , and there is still a large uncertainty on the best protocols for estimating their bioavailability in soil . A large number of biosensors is also available for detection of either natural organic substances or organic pollutants, potentially very useful for characterization of risks posed by contaminated soils. Alkanes and derivatives can be detected using biosensors developed by inserting the alk regulon of Pseudomonas oleovorans, with the luxAB genes from V. harveyi, and the constructed plasmid transformed in E. coli DH5R which becomes bioluminescent specifically when exposed to linear alkanes, whereas biosensors for linear alkylsulphonates based on Nitrosomonas europaea  or Stenotrophomonas and Ralstonia strains  have been constructed by luxAB gene fusion with catabolic genes. Biosensors responding to bioavailable benzene, toluene and xylene (BTEX) in soil have been constructed by inserting the luxCDBAE or luc genes (lucFF is the firefly Photinus pyralis luciferase gene) in different plasmidial genes involved in the catabolic pathways of such compounds, using P. putida strains [6, 20] or E. coli . Insertions of different reporter genes improve the sensitivity towards specific BTEX compounds because their degradation to pyruvate or acetaldehyde is controlled by several intermediate metabolites and enzymes. Sensitive gfp-based biosensors for the detection of toluene and benzene have been constructed by Stiner and Halvorsen  and Casavant et al. , inserting different plasmidial genes in P. fluorescent strains, and biosensor more specifically responding to benzene has been constructed by Di Gennaro et al. , and a comparative study on the lux- and gfp-based biosensors for the detection of toluene and related compounds in polluted soils was performed by Li et al. .
A particularly relevant class of organic pollutants in agriculture is antibiotics, which can accumulate in significant amounts , with detrimental effects on soil microbial diversity and functionality. An E. coli strain carrying a gene fusion between the plasmidial Ptet conferring resistance to tetracycline and gfp genes constructed by Hansen et al. , expressed the GFP when exposed to Streptomyces rimosus in soil microcosms. To our knowledge this was the only antibiotic biosensor used for detecting antibiotics in soil.
Detection of emerging pollutants
Soil is rich of natural nanomaterials but is also constantly subject to the accumulation of manufactured nanoparticles, increasingly used for commercial applications. Although there is a general consensus that beside their beneficial effects in crop protection, the manufactured nanoparticles may have also negative effects on soil microorganisms. Currently, there is no suitable protocol for the assessment of the bioavailability of the manufactured nanoparticles in soil, and specific whole-cell biosensors may be very useful for the related risk assessment. Bondarenko et al.  and Martineau et al.  used the lux-based metal-inducible P. putida KT2440 to assess the bioavailability of CuO and ZnO nanoparticles in the wheat rhizosphere, showing a dose-dependent inhibition of cell metabolism upon exposure to nanoparticles, caused by the quantitative release of Cu and Zn from the CuO and ZnO nanoparticles, which could be only partially quenched by the release of root exudates . These results, though need further confirmation in next soil studies, well illustrate how the use of whole-cell biosensors can help in addressing the effects of emerging pollutants on soil microorganisms; in fact, relying on these early studies the negative impact of nanoparticles on microorganisms seem more related to the massive release of heavy metals nearby the cell wall rather than to nanoparticle size and surface properties (e.g. roughness, zeta potential).
The Bacillus subtilis 1S34 strain, carrying luciferase gene fusion with various five promoters responding to inhibitors of fatty acid, DNA, cell wall and protein synthesis have been successfully tested with several antibiotics , may be tested for assessing the bioavailability of antibiotic residues in soil. These reporter strains seem promising because B. subtilis is a soil-borne microorganism, which should therefore be insensitive to soil factors.
Biosensors for detecting bioactive substances and cell stress
A bioactive compound is any substance triggering a response in living organisms, and there is an ever increasing interest in use them as biostimulants in agriculture, as they can regulate and enhance physiological processes and growth efficiency at crop level. There is increasing evidences that trace amounts of several plant, animal and microbial secondary metabolites , soil-borne humic substances , and volatile organic compounds  are bioactive towards soil microorganisms and plant roots, and can enhance plant vigour, yields and quality. However, it should be born in mind that plant responses can be either positive or negative depending on the substance bioactivity and dose, but in the polyphasic soil environment it ultimately depends on its bioavailability, and nowadays the mode of action of biostimulants is still poorly understood. Biosensor holds the potentials to report the presence and bioavailability of natural or synthetic bioactive molecules eliciting responses of fundamental importance for the ecological interactions in agro-ecosystems, such as competition, defence, attraction, signalling, antibiosis. A classical and agriculturally relevant plant/microbe interaction is the legume–Rhizobium where plant flavonoid compounds control early stages of the symbiosis by activating the rhizobial nod genes. A Rhizobium reporter based on a nodC-lacZ fusion was constructed by Bolanos Vasquez and Warner  to study activation by six different flavonoids from host bean plants. Identification of more specific molecular signals regulating bacterial growth and activity in the rhizosphere have been discovered with the reporter gene technique [2, 80, 105] and have allowed to identify specific rhizosphere-activated promoters in main rhizobacteria such as Rhizobium sp. and Pseudomonas sp. A gfp-inserted Rhizobium reporter strain was constructed by Allaway et al.  to identify the bacterial promoter genes activated in the rhizosphere, and several promoters controlling the syntheses of thiamine and cyclic glucan synthesis, controlling methionine synthesis or putrescine uptake were identified. An assessment of heavy metal impact on rhizobia as well as of the changes in the plant root exudation profile in metal-polluted soils were obtained using a Rhizobium leguminosarum lux-tagged reporter strain [96, 100]. Whole-cell biosensors also gave an important contribution to the understanding of the cell–cell communication and to the cell density-dependent gene regulation in the rhizosphere. It is well established that a large fraction of rhizobacteria produces different N-acyl-L-homoserine lactone (AHL) molecules, which mediate bacterial cell–cell communication , and Zhang and Pierson  demonstrated that AHL-regulated gene is also a key factor for root colonization by rhizobacteria. The knowledge of the genes responding to AHL and structurally similar compounds has allowed the construction of whole-cell bacterial biosensors expressing the GFP ([5, 119]; Burmølle et al. 2003). Seen the current interests around biostimulants enhancing plant growth and health, development of biosensors capable of signalling the bioavailability plant stimulants are of sure interest in modern agriculture.
Biosensors indicating cell stress have been constructed by inserting the lux gene under control of promoters responding to general stress conditions such as heat shocks (e.g. dnaK), of protein-damage sensitive genes (e.g. grpE), oxidative stress (e.g. katG), or promoters sensitive to membrane damages (e.g. fabA) in enteric bacteria such as E. coli and S. typhimurium [132, 136]. Lux- and gfp-constructs of genes involved in the DNA repair (SOS response) have been transformed in soil bacteria to detect the presence of genotoxic substances [92, 95, 102, 110].
Reconstitution media needed for reporter bacteria used in cellular biosensor tests
P. putida KT2440 (pLYS24-davT-lux)
M9 + benzoate + glucose with no NH4Cl
P. fluorescens DF5740E7, DF57-N3, DF57-11D1
Liquid Luria–Bertani medium + 0.9 % NaCl
P. fluorescens HK44 (pUTK21)
Yeast–peptone–glucose extract + 1 M KCl
V. fischeri (BioTox® test)
2.0 % NaCl
C. metallidurans (BIOMET®)
Tris salt medium (TSM) + Fe(NH4)3-citrate + gluconate
P. aureofaciens PGS12
Minimal Ayer culture medium + 25 mM HEPESa
R. leguminosarum 3841 (pOT1)
Acid minimal salt (AMS) + thiamine
P. fluorescens A506 (pTS)
M9 medium + thiamine + Casaminoacids + Noble agar
Towards portable biosensors
A great improvement of the applicability of biosensors to agricultural production and soil protection will come from the further advancements in miniaturization and portability of the signal detection systems for real-time detection and from the insertion of different reporter genes allowing the construction of microbial strains permitting simultaneous multi-analyte detection. The importance of onsite and online application of bioreporters was known since the early whole biosensor constructions. For example, Applegate et al.  used the P. fluorescens 5RL and P. putida TVA8 indicating naphthalene and toluene bioavailability, respectively, detecting the bioluminescence using a portable photomultiplier and compared the results with an off-site GC/MS analysis, showing consistent trends of environmental toxicity. A more recent example of portable biosensor is the ROTAS® (Rapid Onsite Toxicity Audit System), allowing for the field assessment of toxicity by measuring the decrease of the V. fischeri bioluminescence. While such portable systems have been used worldwide with good reproducibility levels, portable detection systems can be considered still in their infancy. A reporter strain expressing GFP and yellow and red fluorescent protein variants (YFP, RFP) has been constructed but the interpretation of multiple responses will also require sophisticate detection systems. A promising application of embedded V. fischeri for the in situ assay of naphthalene toxicity was presented by Jouanneau et al. , which may also be applied to the study of contaminated sites.
Biosensors assisting future agriculture
Biosensors are in perspective the best analytical tools for reporting the occurrence of chemical signals in the plant–microbe interactions because generally, the effector molecules are released in trace amounts and localized in hot spots, and this makes problematic their detection with chemical methods. In the future, more studies should be made to compare results using different scales of investigation; there are unique opportunities in comparing single-cell studies based on sensitive, fluorescent biosensors in combination with advanced confocal laser scanning microscopy with larger samples such as soil extracts or slurries, and with whole plant–soil detection studies based on direct bioluminescence recorded under a sensitive camera. Online monitoring using immobilized reporter cells on optic fibres  should be tested further; a recent application of optic fibres to monitor reporter bacteria in porous media was reported by Yolcubal et al. .
Application of biosensors to the soil–plant microbe interactions in the rhizosphere of agricultural soils may unlock the not fully unexploited soil biological potential in terms of plant growth and protection. For example, using the P. fluorescens F113 biosensor Smith et al.  reported that Pythium ultimum molecules which downregulated the rrn promoters controlled the ribosomal RNA synthesis, in the reporter strain and thus controlled the cellular growth rate. In another study, Lee and Cooksey  found that colonization of the root rotting Phytophthora parasitica by the fungal suppressive rhizobacteria Pseudomonas putida 06909 strain activated the bacterial promoters controlling ATP-binding cassettes (ABC transporters), which are transmembrane transporters translocating various substrates across cell membranes. These studies demonstrated that biosensors allow to study the gene-regulating signals in the rhizosphere and this information may be of interest for developing new biological plant-protecting strategies.
Biosensors may be used to assess the effects of genetically modified (GM) crops on soil properties, particularly their potential impact on nutrient cycling and plant/microbe interactions. Biosensors can be used to investigate the soil modification induced by GM plant roots in soil and gain an early understanding on soil functions, particularly in the rhizosphere. However, the main concern about GM crops is the release and persistence of transgenic DNA into soil, and to our knowledge there is still no whole-cell biosensors capable of signalling the presence of specific DNA sequences. In this field, chemical biosensors are much more developed than whole-cell biosensors. Also the detection of volatile organic compounds (VOCs) by whole-cell biosensors may be a valuable tool for a better understanding of the ecological implications and impact of the soil VOCs emissions, and on the transfer of pollutant VOCs to the atmosphere. Gil et al.  constructed a lux-inserted E. coli biosensor for VOCs detection, which was calibrated and tested with benzene. However, to our knowledge no applications to soil studies have been reported. In this sense, whole-cell biosensors may contribute to the frame of an ecological theory of soil microbial communities relying on the indication of plant/microbe and microbe/microbe interactions. An interesting microarrays for multiple bioreporter detection based on E. coli lux-based bioreporter array capable of detecting up to 689 transcriptional events presented by van Dyk et al.  also holds potential for soil applications.
To our knowledge there is currently no biosensors for reporting sulphur (S) bioavailability, mainly because the S bacterial metabolism is less known as compared to that of C, N and P, and also because S concentration in the environment has not been a limiting factor due to the large past emissions. However, S deficiency in agricultural soils is now emerging mainly due to the low use of fertilizer S, high S absorption by the crop genotypes and the constantly decreasing trend of S emissions, and actual sensing of S reporting bioavailability may contribute to improve the crop production, as S deficiency symptoms in crops are often confused with those of N, Mg, Mn or Zn deficiency. The main form of bioavailable S in soil is organic S, mineralized to SO4 2−‐S which is taken up by plants, and the chemical methods of soil analysis poorly define the bioavailable S pool in soil. Inserting of bacterial promoters such as atsA, tau, ytm would be suitable for constructing biosensors responding to bioavailability of inorganic, organic and volatile S have been identified, as demonstrated by fusion of the S responding promoters with the lacZ. Pioneer applications of whole-cell biosensors for the study of S bioavailability in the rhizosphere have been reviewed by Goron and Raizada .
Integrative sensing the agro-environment
Problems of future agriculture can be effectively addressed using biosensors to reduce risks, optimize the efficiency of plant mineral nutrition and control plant–microbe interactions. These main agricultural aspects can be monitored from future field trials specifically designed to collect, collate and analyse biosensor responses with formalized systems that make such responses easy-to-understand by farmers and advisors. New types of biosensors will be also needed to increase their sensitivity to environmental change. An improvement of the mechanisms of molecular recognition which will likely allow the construction of new and more stable and selective biosensors by means of the use of receptor proteins , also including the periplasmic proteins, which may also produce signals by the protein fusion with fluorophores . These ‘protein’ based biosensors may provide complementary information on to those of the ‘genetic’ biosensors and may also provide new information on the ability of microorganisms to act as ligands for elements, molecules and substances (e.g. humic substances) in soil, and therefore to not necessarily signal the absorption of analytes as a result of their assimilation. A technological development in this sense may follow that of Okumoto et al.  who studied the responsible excitation mechanisms during the neuronal transmission, where how the concentration of glutamic acid inside and to the surface of the cells was indicated by the fluorescent GLU/ASP binding protein ybeJ of E. coli fused with two variants of the GFP. These biosensors respond to the extracellular concentrations of glutamic acid and may be used in future for the in vivo monitoring of the N forms assimilated by soil microorganisms. A great advancement in our understanding of soil functioning may also come from more whole-cell biosensors with engineered promoters coding for the synthesis of periplasmic ABC proteins involved in the assimilation of large organic molecules from the external membrane towards the cytoplasm in soil microorganisms . More observations on the functioning of these mechanisms may revolutionize our knowledge on the dynamics of polysaccharides, peptides, of siderophores and other organic molecules such as those present in the humic substances  or those regulating the microbial activity in the rhizosphere.
Another unanswered question in soil biochemistry is the origin and location of enzyme activity in soil. It is generally accepted that the soil enzyme activity is predominantly extracellular, and therefore not directly related to the microbial metabolic activity; however, the induction and repression of the soil enzymatic activity upon the availability of organic substrates and end products, respectively has been often reported in the rhizosphere and bulk soil (e.g. [106, 107]). The increasing knowledge on the regulation of functional genes of soil-borne microorganisms may lead to construct whole-cell biosensors indicating the expression of gene coding for enzyme activities. For example, Schreiter et al.  inserted the lux gene under the control of promoter sequences of gene coding for the alkaline phosphatase into the two strains of the blue–green algae Synechococcus PCC 7942, expressing the enzyme under P-deficiency (M 1415) and under N-deficiency conditions (NblA-2000). Whole-cell biosensors may also provide new evidences on the topological localization of microorganisms in the soil habitat, in relation to the availability of specific compounds. This may be achieved following the approaches of Møller et al.  and Leveau and Lindow  for the study of bacterial biofilms and epiphytic bacteria, respectively, coupled with micropedology based on the use of soil thin sections coupled with the use of biosensors expressing fluorescent proteins.
Biosensor technology is constantly developing thanks to the increasing knowledge on the regulation of key functional genes in soil-borne microorganisms and precision of gene fusion technologies, and it is anticipated that next biosensors will be capable of signalling the bioavailability of specific analyte and the occurrence of ecological interactions with higher sensitivity and lower interference also in the soil environment. The broader use of biosensors may lead to a faster answering to basic and long-standing ecological questions in soil and environmental sciences. Because biosensors indicate analyte bioavailability and key biological interactions at sub-optimal and sub-toxic concentrations with far superior sensitivity than chemical methods, their responses should be included in both development of precision agriculture and in risk assessment for contaminated/remediated soils. However, the ever increasing construction of whole-cell biosensors is still not reflected in the real world where these tools are currently not routinely used when evaluating, for example, the crop nutrient efficiency or the environmental risk assessment, and most of the constructed biosensors are used for scientific research only and do not find practical application by both advisors and environmental agencies. Lack of knowledge and expertise with biosensors is also a main hindrance for including the whole-cell biosensors in the official methods for soil and environmental analysis. We are fully confident that existing and next generation of biosensors can be considered as tools for new paradigmatic strategies that improve agronomical practice and soil management and remediation, and should already integrate the soil chemical analysis of nutrient availability currently used by agricultural and environmental advisors.
The two authors equally contributed to the preparation of the present review article. Both authors read and approved the final manuscript.
The authors declare that they have no competing interests.
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