Team:Calgary/Project/FRED/Detecting

From 2012.igem.org

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<p align="justify">For a detailed protocol, please consult our methods section.</p>
<p align="justify">For a detailed protocol, please consult our methods section.</p>
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(1) Del Rio LF, Hadwin AK, Pinto LJ, MacKinnon MD, Moore MM. Degradation of naphthenic acids by sediment micro-organisms. J Appl Microbiol 2006 Nov;101(5):1049-1061. </p>
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(2) Herman DC, Fedorak PM, MacKinnon MD, Costerton JW. Biodegradation of naphthenic acids by microbial populations indigenous to oil sands tailings. Can J Microbiol 1994 Jun;40(6):467-477. </p>
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(3) Holowenko FM, Mackinnon MD, Fedorak PM. Naphthenic acids and surrogate naphthenic acids in methanogenic microcosms. Water Res 2001 Aug;35(11):2595-2606. </p>
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(4) Ramos-Padron E, Bordenave S, Lin S, Bhaskar IM, Dong X, Sensen CW, et al. Carbon and sulfur cycling by microbial communities in a gypsum-treated oil sands tailings pond. Environ Sci Technol 2011 Jan 15;45(2):439-446.
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(5) Reznikoff WS. Transposon Tn5. Annu Rev Genet 2008;42:269-286. </p>
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<p>
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(6) Sheridan DL, Hughes TE. A faster way to make GFP-based biosensors: two new transposons for creating multicolored libraries of fluorescent fusion proteins. BMC Biotechnol 2004 Aug 18;4:17. </p>
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(7) So J. Mini-transposon Tn5gfp constructs for differential tagging of microorganisms. Biotechnology and Bioprocess Engineering 1999;4(2):154-156. </p>
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(8) Timms-Wilson TM, Bailey MJ. Reliable use of green fluorescent protein in fluorescent pseudomonads. J Microbiol Methods 2001 Jul 30;46(1):77-80. </p>
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Revision as of 19:35, 25 September 2012

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A Transposon Screen for Detecting Naphthenic Acids

This year, our team wanted to identify a novel responsive element capable of detecting and quantifying naphthenic acids (NAs) in solution. While numerous studies have begun to identify species of bacteria capable of surviving and sensing NAs, the degradation pathways have not yet been fully characterized. Therefore, we needed to design and implement novel approaches to efficiently isolate the genetic elements that detect and potentially lead to the breakdown of naphthenic acids.


Transposons: What, How, Why?

The transposable element (TE), Tn5, is a conservative transposon that is able to insert a segment of genes bordered by specific 19bp insertion sequences (IS) from one part of the genome (e.g. plasmid vector) randomly to another location, such as the chromosome (Reznikoff, 2008). The transposition event is catalyzed by a transposase enzyme encoded by Tnp gene included in the TE.

By inserting a vector construct containing the TE with selectable markers (such as tetracyclin resistance and lacZ) into an organism with a desirable phenotype, we can find out what genetic elements (e.g. genes and promoters) are responsible for that particular function. This can happen via a random insertion of a TE containing a promoterless reporter gene downstream of promoter elements that creates a transcriptional fusion, providing activity in response to specific environmental stimuli. Another advantage of using a transposon approach is that it creates a saturating library of mutants where all possible genetic elements responding to a certain environmental stimuli can be identified. Therefore, saturated genome-wide mutant libraries generated by transposon-mediated mutagenesis are powerful tools that serve our purpose in identifying unknown non-essential genes (e.g. metabolism of alternative carbon sources) and characterizing the function of these unknown genes that are involved in NA detection and degradation. However, due to the random nature of TE insertions, two considerations need to be taken. First, to screen the entire genome of an organism, a large number of mutants needs to be generated, which is time-consuming. Second, the TE insertion is not permanent, and thus, the TE may move to another location after the first insertion. The first concern can ameliorated by using a bipartite-mating (conjugation) method to transfer the TE vector into the organism of choice, which is efficient at creating a massive library of mutants (see the method design section for details). The second concern is addressed by maintaining mutants under the appropriate selective pressure, ensuring the reporter gene is still fused to a promoter element upstream by screening for the reporter gene products (e.g. lacZ producing an insoluble blue pigment in the presence of X-Gal), and isolating the mutants' genomic DNA in a timely fashion.

Due to the complexity of biological systems, our team focused our efforts on identifying a system for identification of promoter elements that respond in the presence of environmental stimuli. Identifying such a system for naphthenic acids, if one exists, would allow for a specific response to be generated to many different kinds of naphthenic acids. Our hypothesis requires that the organisms we use respond specifically to naphthenic acids and result in specific upregulation of metabolic genes with little background effect in the cell. We recognize that any number of biological molecules within a NA-degrading organism may play role in the sensing and modification of NAs, such as enzymes, transcription factors, and even RNA elements (e.g. riboswitches). However, the identification of a promoter sequence takes us further in that we can better understand the mechanism of NA degradation by elucidating the genes involved. If this can be accomplished, then we can easily construct an organism capable of specifically and robustly detecting a variety of NAs, and modify them to reduce their toxicity. The transposon system not only allow the identification of such as sytstem, but also allow the resultant system to be broad enough to detect a variety of NAs, instead of simply model compounds.


Naphthenic Acid Degrading Organism Used

Pseudomonads are species of aerobic bacteria that have been isolated from oil sands tailings ponds and shown to biodegrade model and tailings-associated NAs (Ramos-Padrón et al. 2010; Herman et al., 1994; Del Rio et al., 2006; Gieg & Whitby, unpublished, 2012). Since they can degrade NAs, this suggests that there exist a system that actively recognizes and is up-regulated specifically in response to NAs. We wanted to use a commercially available strain of Pseudomonas fluorescens characterized for a response to model NAs (model single- and double-ringed compounds) and NAs isolated from tailings pond water (TPW). The P. fluorescens pf-5 strain is reported to survive in and degrade a commercial mixture of naphthenic acids (Acros) (Gieg & Whitby unpublished, 2012). Moreover, sequencing data is available for this strain with annotations (Pseudomonas Genome Database V2, http://pseudomonas.com/). This allows us to use sequencing data from the mutants and identify where in the genome the TE insertion occured, and what genes (if present) are located downstream of it.


Method Design

To construct the promoter library, a pOT182 vector construct (containing a IR-lacZ-Amp-pMB1ori-TetA-TetR-Tnp-IR transposable element) is introduced into commercially purchased E. coli SM10 donor strain. The plasmid is engineered in a vector containing a RP4 mob conjugation region, and a p15A origin of replication (ori). The IR-lacZ-Amp-pMB1ori-TetA-TetR-Tnp-IR construct is transferred from the E. coli donor strain to the recipient P. fluorescens pf-5 using bipartite mating via conjugation (enabled by the RP4 mob region). A random genomic library of transposon insertions is created in P. fluorescens, and selected by isolating the recipients on Pseudomonas Isolation Agar/PIA (the antibiotic Irgasan in this medium kills all other bateria, and only allows the survival of Pseudomonas spp.) and the recipient cells that have a genomic TE insertion using tetracyclin (conjugated plasmids cannot replicate in Pseudomonas, and thus the Pseudomonas that survived must have a TE insertion in the genomic DNA). If a promoter elements is fused upstream of the TE construct, then promoter activation will turn on the expression of lacZ, which be detected by the degradation of a colorless compound, X-Gal, to an insoluble blue pigment product (an indoxyl compound). If the fused promoter is activated in response to NAs, then lacZ will be produced in response to NAs. Desirable mutants are selected by plating the conjugated bacteria onto an agar plate containing PIA, tetracyclin (at a concentration that wildtype Pseudomonas fluorescens pf-5 is sensitive to), a NA mixture (Acros), and X-Gal. Mutants are sensitive to NAs will appear as blue colonies on the plate.

Promoters identified by the transposon mutagenesis strategy are characterized for their roles in the response to NA exposure with dose response curves, and compared to general stress-inducing agents (e.g. H2O2) and compounds such as fatty acids to ensure the specificity of the response. These measurements help to determine thresholds of detection, robustness of the signal, and specificity of response. The dose response curves will also assess the usefulness of correlating the concentration of NA to the level of response, and the possibility of measuring NA concentrations in a sample, rather than simply by presence/absence.

Last, self-cloning techniques are used to identify the upstream and downstream sequences from the TE insertion. IR-lacZ-Amp-pMB1ori-TetA-TetR-Tnp-IR is a self-cloning construct because it contains all the elements required for plasmid replication (i.e. origin of replication) and selection (Tet resistance). Genomic DNA from the desirable mutant is isolated, and restriction digested with either BglII or XbaI, which are restriction enzymes that do not cut within the transposon but numerous times with the genome. The resulting fragments may contain the TE construct with flanking sequences. The genomic fragments are circularized by self-ligation and transformed into E. coli Top10, and plated on LB agar with tetracyclin. The transformed cells now have plasmids containing the TE construct with the upstream and downstream flanking sequencing connected by the restriction site (of BglII or XbaI). Plasmids isolated from the transformed cells are used for sequencing. Sequencing primers are designed against the 19 bp recognition sequence in the TE to sequence outward from the transposon.

For a detailed protocol, please consult our methods section.

(1) Del Rio LF, Hadwin AK, Pinto LJ, MacKinnon MD, Moore MM. Degradation of naphthenic acids by sediment micro-organisms. J Appl Microbiol 2006 Nov;101(5):1049-1061.

(2) Herman DC, Fedorak PM, MacKinnon MD, Costerton JW. Biodegradation of naphthenic acids by microbial populations indigenous to oil sands tailings. Can J Microbiol 1994 Jun;40(6):467-477.

(3) Holowenko FM, Mackinnon MD, Fedorak PM. Naphthenic acids and surrogate naphthenic acids in methanogenic microcosms. Water Res 2001 Aug;35(11):2595-2606.

(4) Ramos-Padron E, Bordenave S, Lin S, Bhaskar IM, Dong X, Sensen CW, et al. Carbon and sulfur cycling by microbial communities in a gypsum-treated oil sands tailings pond. Environ Sci Technol 2011 Jan 15;45(2):439-446. (5) Reznikoff WS. Transposon Tn5. Annu Rev Genet 2008;42:269-286.

(6) Sheridan DL, Hughes TE. A faster way to make GFP-based biosensors: two new transposons for creating multicolored libraries of fluorescent fusion proteins. BMC Biotechnol 2004 Aug 18;4:17.

(7) So J. Mini-transposon Tn5gfp constructs for differential tagging of microorganisms. Biotechnology and Bioprocess Engineering 1999;4(2):154-156.

(8) Timms-Wilson TM, Bailey MJ. Reliable use of green fluorescent protein in fluorescent pseudomonads. J Microbiol Methods 2001 Jul 30;46(1):77-80.