The present invention discloses a method to identify and quantify microorganisms useful in biomining processes that are present in a given sample. This method is presented as a useful tool in biomining, in every case where the present microbiological population needs to be evaluated, whether on the mineral, in solutions, in bioleaching heaps, in biomining laboratories or in any other circumstance that involves the use of such microorganisms.
Biomining is, in general terms, the use of microorganisms for metal recovery from mineral ores. Its most traditional expression is bioleaching, but not only this process is understood as biomining, but also the monitoring and intervention in such process, as these techniques are complex and are under constant development; and also laboratory research associated to process improvement or the development of new methodologies.
Until now, bioleaching continues to be the most important process in biomining field, and is defined as a method to solubilize metals from complex matrixes in an acid medium, using direct or indirect microorganism action. The microorganisms that are useful in these processes belong to Bacteria or Archaea kingdoms, and fulfill two basic conditions: they are acidophilic and chemolithotrophic.
Various microorganisms have been described to be useful in bioleaching processes, and ten taxons could be identified among them: 3 genera and 2 species from the Bacteria kingdom, namely Acidiphilium sp., Leptospirillum sp., Sulfobacillus sp. genera and Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans species, and five genera from the Archaea kingdom, namely Acidianus sp., Ferroplasma sp., Metallosphaera sp., Sulfolobus sp. and Thermoplasma sp. (Rawlings D E. Heavy metal mining using microbes. Annu Rev Microbiol. 2002; 56:65-91; Rawlings D E. Characteristics and adaptability of iron- and sulfur-oxidizing microorganisms used for the recovery of metals from minerals and their concentrates. Microb Cell Fact. May 6, 2005; 4(1):13).
Each of the above mentioned genera or species catalyzes different reactions and require in its turn different conditions to perform such reaction, which could be, for instance, aerobic or anaerobic, or could require some specific nutrient. Therefore, the environmental conditions in which a bioleaching process is performed will modify the bacterial composition of the community.
Additionally, the participation of microorganisms in a bioleaching process has been proposed to be direct and/or indirect (Rawlings D E. Characteristics and adaptability of iron- and sulfur-oxidizing microorganisms used for the recovery of metals from minerals and their concentrates. Microb Cell Fact. May 6, 2005; 4(1):13). When the action is direct, microorganisms directly oxidize the target metal or its counter-ion, in both cases liberating into the solution a target metal ion. On the other hand, when the action is indirect, the substrate of the microorganism is not the target metal neither its counter-ion, but instead chemical conditions are generated that allow the solubilization of said metal, either by acidification of the medium (e.g., by generating sulfuric acid) or by the generation of an oxidizing agent that ultimately interacts with the salt (metal and counter-ion) to be solubilized.
Regarding this aspect, it is possible that the bacterial community changes its species composition as a function of the bioleaching type being performed in different mineral samples and/or the environmental conditions in which this process is carried out.
For instance, Acidithiobacillus species are able to catalyze the oxidation of reduced sulfur compounds (e.g., sulfide, elemental sulfur, thionates, etc.) using oxygen as electronic acceptor and generating sulfuric acid as final product and reducing species like sulfite and thiosulfate as intermediate products, which allows the solubilization of metals associated to sulfides in the mineral. Acidithiobacillus ferrooxidans and Leptospirillum ferrooxidans are able to catalyze the oxidation of iron(II) to iron(III) using oxygen as electron acceptor, being the generated iron(III) a great oxidizing agent that can oxidize sulfides in the mineral or any other compound to be oxidized.
The usual mining practice in bioleaching processes is to leave a mineral heap in an acid medium, generally sulfuric acid, and constantly remove the acid medium to recover the metal by electrolysis. Usually heaps in which the recovery yield of the metal is efficient are obtained, and also “inefficient” heaps that have a low yield under the same operation conditions and characteristics of the substrate to be leached. The explanation to this unequal result requires the elucidation of differences in abundance and types of species in the microbiological community between both heaps. In this way, the low yield problem could be explained by the microbial community composition, and could be solved in its turn by inoculation of microorganisms that catalyze the reaction to be maintained during the bioleaching process. However, a method that enables to quantify the population of archaea and bacteria useful in biomining processes is not available up to this date. In this patent, a method is described that solves the technical problem previously described, by designing a method to identify and quantify the presence of known microorganisms that are most relevant in biomining processes, namely the bacteria: Acidiphilium sp., Leptospirillum sp., Sulfobacillus sp., Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans; and the archaea: Acidianus sp., Ferroplasma sp., Metallosphaera sp., Sulfolobus sp. and Thermoplasma sp.
Nested polymerase chain reaction (PCR) was the technique selected to develop this method. In this technique, a conserved genome region of the microorganisms is firstly amplified in a first PCR reaction, either on bacteria or archaea. We have selected gene 16SrDNA as the conserved region. Then, taxon-specific primers (targeting genera or species) are used to identify the presence of target microorganisms in a second PCR reaction. This second PCR reaction is performed using an equipment that allows measuring the increase of amplified product in each amplification cycle, and this information allows the quantification, by interpolation, of the original abundance of the target genome in the sample being analyzed. PCR reaction under these conditions is called quantitative PCR or qPCR.
A critical step in nested PCR technique is the design of primers for the second amplification reaction, which have to be specific for the taxon to be determined, and this aspect has a vital importance in this particular case, as the samples to which the process will be applied will usually be metagenomic samples. Therefore, it is necessary to reduce the possibility of primer unspecific hybridization to sequences present in the genome of microorganisms that have not yet been identified in the community. We have generated two fundamental tools for the design of these primers: firstly, a depurated 16SrDNA sequence database obtained from all disclosed 16SrDNA sequences; and a computational program for primer design that uses as input such database and allows designing thermodynamically stable taxon specific primers.
In the state of the art there are many examples of the application of nested PCR or qPCR, but none of them is focused to bacteria or archaea useful in biomining processes. For instance, J. L. M. Rodrigues et al (Journal of Microbiological Methods 51 (2002) 181-189) describe a qPCR to detect and quantify PCB-degrading Rhodococcus present in soil, where the 16SrDNA gene belonging to the strain with the target activity is sequenced, specific primers for said sequence are designed and qPCR reactions are carried out using said primers. In this document, a direct qPCR approach is used, instead of a nested qPCR, and it is directed to other type of microorganisms, whose handling has been widely studied and many techniques for DNA extraction are available. Another document that uses a similar approach is Patent Application EP 1 484 416, which discloses a method for the detection and quantification of pathogen bacteria and fungi present in an environment sample using qPCR. The method comprises the extraction of DNA from bacteria and fungi present in an environment sample, obtaining specific sense and antisense primers for each of the taxons to be detected and quantified; and performing qPCR reactions using a pair of primers for each of the target pathogens.
Although it is possible to enumerate documents in which microorganisms are identified and quantified using quantitative PCR techniques, as they are well known techniques in the art, the relevant point is the generation of a depurated database that allows to design specific primers and has not been implemented before for the identification of microorganisms useful in biomining processes, which is subject matter of this invention.
The present invention discloses a method to identify and quantify environmental microorganisms useful in biomining processes. These microorganisms are basically 10, belonging to Bacteria: Acidiphilium sp., Leptospirillum sp., Sulfobacillus sp., Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans; and Archaea: Acidianus sp., Ferroplasma sp., Metallosphaera sp., Sulfolobus sp. and Thermoplasma sp.
The method comprises performing a two-stage PCR known as nested PCR, where in the first stage, called primary PCR, 16S ribosomal DNA sequences (nucleotides 27 to 1492, with E. coli rDNA numbering) are amplified using universal primers for the Bacteria and Archaea kingdoms. In the second stage, these primary amplicons are used as template in qPCR reactions, called secondary PCR, in which internal universal primers for either Bacteria or Archaea kingdoms, as it corresponds, and specific primers designed in our laboratories for different taxons to be determined are used. The first PCR linearly multiplies 16S sequences from bacteria or archaea, thus increasing template abundance for the secondary PCR keeping the original microorganism proportion of the sample. This gives a higher sensitivity to the process when compared to the case of directly using taxon-specific primers on the sample. However, the method also works and is applicable without the primary PCR, and therefore this stage may be optional.
With qPCR results and other data obtained from the analyzed sample, the microorganism concentration of each analyzed taxon present in the sample is calculated using a mathematical formula.
FIGS. 1 to 7 show the results of Example 1, where the presence of Acidithiobacillus thiooxidans, Acidithiobacillus ferrooxidans, Leptospirillum sp., Acidiphilium sp. and total bacteria has been quantified in 7 different samples. In each Figure, results for each solid sample (MS), identified as MS-1, MS-2, MS-3, MS-4 and MS-5, and each liquid sample (ML), identified as ML-1 and ML-2, are plotted. Each plot shows quantified taxons in the abscissa and microorganism number per sample unit in logarithmic scale in the ordinate. Data giving origin to plots are shown in Tables 26 to 32.
From these results it is possible to observe which one is the predominant species in each of the mineral samples from bioleaching heaps (MS-1 to MS-5) and from liquid samples recovered from bioleaching effluents (ML-1 and ML-2). This value can also be correlated to total bacteria found in said samples. Thus, in 6 over 7 samples Leptospirillum sp. predominance is observed, and even more, only this microorganism genus is present in one of the liquid samples. Only one of the solid samples (MS-2) shows A. thiooxidans predominance, which leads to the conclusion that Leptospirillum sp. is the most abundant microorganism in this type of mineral samples.
As has been anticipated, the invention relates to a method that allows the identification and quantification of essential microorganisms in biomining processes. These essential microorganisms belong to 10 taxons, the genera Acidiphilium sp., Leptospirillum sp., Sulfobacillus sp. and the species Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans belonging to the Bacteria kingdom; and the genera Acidianus sp., Ferroplasma sp, Metallosphaera sp, Sulfolobus sp. and Thermoplasma sp. belonging to the Archaea kingdom.
As previously indicated, a method to identify and quantify biomining microorganisms would have applications in different industrial tasks and areas. For instance, a good tool for suitable control of bioleaching process could be the identification of microorganisms that are present in a bioleaching heap and how abundant they are, as it could be established whether is necessary to inoculate some particular microorganism or simply determine which nutrients should be added to the mixture, thus maximizing the quantity of mineral recovered in the process. The idea is to correlate the recovery efficiency of different metals present in the heap with the composition of the microbiological community in the heap, referred to the number and type of present individuals.
In general terms, samples to be analyzed in the method of the invention will be biomining samples, but this does not limit the scope of the invention, as the described method could be applied any time that one or more of the 10 taxons subject of this invention is to be identified and quantified.
In the description of the invention, all oligonucleotide sequences are written in direction 5′ to 3′. Described oligonucleotides correspond to primers for PCR reactions, which can be sense or antisense primers, which could be indicated specifically (e.g., as table titles) or alternatively by including letter “F” for sense or forward primers and “R” for antisense or reverse primers in the name of the primer.
The following is the description of each of the stages of the method in detail.
DNA Preparation.
In a first stage, it is necessary to extract DNA from the sample. Different methods to extract DNA from mineral or soil samples have been disclosed and any of them can be used, considering in each case the particular nature of the sample (Appl Environ Microbiol. July 2003; 69(7):4183-9; Biotechniques. April 2005; 38(4):579-86). In the case that total extracted DNA (from mineral samples, being e.g. grounded chalcopyrite type 1 or other) is turbid or has a yellow or orange color, it is recommended to repurify the sample using any existing purification technique; in our laboratories this step is performed using commercial DNA purification columns. The purified fraction is resuspended in sterile nuclease-free H2O.
Once total DNA samples have been purified, total DNA present in the sample should be quantified; again, this quantification could be performed using any existing method to quantify DNA; in our laboratories it is done by spectrophotometry.
After quantifying total DNA present in the sample, an aliquot is taken and diluted to a concentration suitable for the method, which finally ranges from 0.5 to 40 ng/μl, preferably from 1 to 30 ng/μl, and most preferably from 1 to 10 ng/μl. The dilution must be done using sterile nuclease-free water.
Primary PCR.
This stage is optional and could be skipped, however in our case it is advantageous to perform it as it restrict the analyzed subject universe and increases the sensitivity of the method. Using the DNA sample previously prepared at least one of the primary PCR is performed, one of them using primers to amplify 16S region from the Bacteria kingdom (“universal Bacteria primers”) and the other using primers to amplify 16S region from the Archaea kingdom (“universal Archaea primers”).
Primary PCRs are intended to amplify the region coding for 16S ribosomal RNA, for which any primer pair could be used in primary PCR that fulfill the described requirements; in our laboratories universal primers shown in the list included in Table 1 are preferentially selected.
1Bond P., 2000, Appl Environ Microbiol. 66(9):3842-9.
2Delong, E.F., 1992, Proc. Nac. Acad. Sci. USA 89: 5685-9.
It is important that primary PCR should be linear, i.e., amplification does not reach saturation, as the original proportion in the sample should be kept.
This PCR is also applied on a negative control, containing sterile water instead of DNA, and a five-point calibration curve, formed by a master mix and four serial dilutions thereof. The master mix is specific for each kingdom, Bacteria or Archaea, and is formed by a standard DNA mix belonging to each of the taxons to be determined. This means that in the PCR using universal Bacteria primers, the standard DNA mix used in the master mix will contain pure DNA extracted from all bacteria to be identified and quantified, as Acidiphilium sp., Leptospirillum sp., Sulfobacillus sp., Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans; whereas in the primary PCR using universal Archaea primers the master mix will contain DNA from all Archaea to be identified and quantified, as Acidianus sp., Ferroplasma sp, Metallosphaera sp, Sulfolobus sp. and Thermoplasma sp.
The master mix optimally contains from 1 to 100 ng of DNA from each of the strains, and preferably contains 100 ng of total DNA, although it is possible to work with higher or lower amounts. The calibration curve will be used in the quantification that will be performed with secondary PCR and corresponds to the master mix in concentrations 1×, 0.1×, 0.01×, 0.001× and 0.0001×. Each one of these dilutions is subjected to the primary PCR.
Preferably, each primary PCR is carried out using 1 μl of DNA, either for the sample or the calibration curve, or 1 μl of water for the negative control, plus 24 μl of the reaction mix whose composition is described in Table 2.
Primary PCR cycles are described in Table 3.
Wherein steps 2 to 4 are repeated from 15 to 20 times, avoiding saturation.
Once this primary PCR has been performed, the sequence of region 16S of all bacteria and archaea present in the original sample has been amplified.
Secondary PCR.
Then, a plurality of PCR is carried out, specific for each taxon to be identified, using specific primers that amplify inside the 16S rDNA region amplified in the primary PCR.
In this stage it is crucial to have specific and efficient primers to amplify the target fragment that have no cross-reaction with organisms from other taxons and are thermodynamically stable, i.e. do not form hairpins, homodimers or heterodimers. The primers used in this application have been designed using the method disclosed in Patent Application CL 2102-2005 filled by Biosigma; as said method guarantees the efficiency and specificity of the designed primers.
In each primary PCR a reaction has been carried out to amplify each of the samples, 5 point of the calibration curve and one negative control. Each secondary PCR will be performed on all the reaction products of each corresponding primary PCR reaction. Advantageously, all reactions are carried out in duplicate, and a negative control is added.
When we say that secondary PCR is performed on the corresponding primary PCR, we mean that if our target taxon to be amplified in the secondary PCR belongs to the Archaea kingdom, then we will use the primary PCR reaction products for archaea. Likewise, if the taxon to be quantified is a bacterium, we will use the primary PCR reaction products for bacteria in the secondary PCR.
It is important to point out that the method of the invention can be carried out to identify and quantify either all the described taxons or only one of them, and also all the possible intermediate combinations, and as a consequence every one of these options will remain being comprised inside the scope of the present invention.
The secondary PCR is a quantitative PCR (qPCR), therefore it should be performed in a suitable thermocycler and using fluorescent reagents for qPCR. There are different commercially available alternatives, either for equipment or reagents, and any of them can be selected to carry out the present method.
For each secondary PCR reaction the following mix is prepared:
To the mix described in Table 4, 1 μl of primary PCR reaction product or sterile water for the qPCR blank is added.
As previously indicated, the requirements to be fulfilled by each primer pair selected for the secondary PCR are: being specific for each taxon, having no cross-reactivity and being thermodynamically stable to assure primer availability in the PCR reaction. Our laboratory has developed a primer design program that gives a large amount of primers fulfilling these requirements. The method of the invention can be performed by combining any sense primer with any antisense primer designed by our program. In following tables, we give 20 sense primers and 20 antisense primers for each taxon, where any possible combination thereof could be selected for the qPCR. (Note: the sequences of the designed primers have been compared, by using Blast from NCBI, with previously existent sequence disclosures, thus guaranteeing its novelty as primers.)
Bacteria Kingdom:
Leptospirillum sp.
Sulfobacillus sp.
Acidithiobacillus ferrooxidans
Acidithiobacillus thiooxidans
Archaea Kingdom:
Ferroplasma sp.
Metallosphaera sp.
Sulfolobus sp.
Thermoplasma sp.
In secondary PCRs a reaction is also included to quantify total bacteria or archaea present in the sample; in this case known universal primers are used for both kingdoms which are selected among the primers included in Table 15.
1Bond P., 2000, Appl Environ Microbiol. 66(9):3842-9.
2Schauer M, 2003, Aquat Microb Ecol Vol. 31: 163-174.
3Nakagawa T, 2002, FEMS Microbiology Ecology 41:199-209.
4Schrenk MO, 1998, Science. 279:1519-22.
5Ellis R, 2003, Appl Environ Microbiol. 69(6):3223-30.
6Casamayor EO, 2002, Environ Microbiol. 4(6):338-48.
7Edwards K, 2003, Appl Environ Microbiol. 69(5):2906-13.
8Orphan VJ, 2001, Appl Environ Microbiol. 66(2):700-11.
Each secondary PCR has a specific cycle, wherein the alignment temperature changes, said temperature being specific for each used primer pair. Table 16 summarizes general conditions for all qPCR cycles.
(*) specific temperature for each used primer pair
Duration curve carried out at the end of cycle 40, gives the Tm of the amplification product, and is also used to establish whether more than one amplification product is present in the amplified sample, as each would generate its own curve.
The PCR thermocycler gives a result corresponding to DNA concentration present in each reaction, and this information is used to calculate the number of microorganisms present in the sample, which is called Q. This value is inferred by the computational program associated to the thermocycler based on: DNA concentration in calibration curve reactions and the cycle in which sample begins to amplify (or to exponentially increase its fluorescence value). The correlation between the logarithm of DNA concentration and the cycle in which amplification is observed generates a linear equation, from which DNA concentration in the analyzed samples is inferred.
Calculation of the Number of Microorganisms Present in the Sample
Taking into account the qPCR result and other data generated during the process, the inventors have developed a mathematical formula that allows calculating the exact number of microorganisms from a given taxon present in a given sample, specially a biomining sample. The formula is as follows:
where:
By applying the method of the invention, the number of microorganisms belonging to the taxons Acidiphilium sp., Leptospirillum sp., Sulfobacillus sp. Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans, Acidianus sp., Ferroplasma sp, Sulfolobus sp., Metallosphaera sp, and/or Thermoplasma sp. present in a sample can be determined.
Five solid samples obtained from mineral bioleaching heaps (MS-1 to MS-5) and 2 liquid samples recovered from bioleaching effluents (ML-1 and ML-2) were analyzed and total DNA was extracted from each one.
For all solid samples a further step was necessary, a re-purification of DNA, which consisted in a sample re-purification using any existing purification technique; in our laboratories this step is performed using commercial DNA purification columns to obtain a translucent appearance in the extraction solution.
Then, total DNA was quantified in each sample using a NanoDrop 1.0 spectrophotometer. Total extracted DNA nanograms (T) are shown in Table 17 together with the initial sample volumes (Cm). Registered results were:
Each of these samples was diluted with sterile nuclease-free water in order to obtain a concentration between 0.5 and 30 ng/μl. Table 18 shows the final volume to which the DNA solution was brought and its final concentration.
A calibration curve was simultaneously prepared to allow the calculation of DNA concentration in experimental samples. Four serial dilutions were prepared from a standard DNA mix containing 25 ng of DNA from each of the following microorganisms: Acidithiobacillus thiooxidans, Acidithiobacillus ferrooxidans, Leptospirillum sp. and Acidiphilium sp., in a final volume of 30 μl, to obtain 100 ng of total DNA in the standard sample, which in its turn is part of the calibration curve.
More specifically, DNA was used from the following strains:
The reaction mix for the primary PCR was prepared, wherein the amount of each constituent was multiplied by the total number of reactions to be carried out; a single reaction mix was prepared in order to homogenize reagent concentrations in the different PCR tubes. The reaction mix was aliquoted in 0.2 ml tubes, using a volume of 24 μl of reaction mix per tube.
In the present Example, the following reactions were performed in duplicate:
The prepared mix is shown in Table 19.
Used primers are described in Table 20.
This primary PCR reaction mix was homogenized and 25 aliquots were made with 24 μl each in 0.2 ml tubes appropriately labeled. To this mix 1 μl of sample DNA dilutions or 1 μl of calibration curve DNA was added as appropriate. To the primary PCR negative control 1 μl of sterile nuclease-free water was added instead of DNA.
Reactions were incubated in a MJ Research PTC-100 thermocycler, with the following cycle program:
Wherein steps 2 to 4 were repeated 18 times.
Subsequently 5 secondary PCR were performed, one for each taxon: Acidithiobacillus thiooxidans, Acidithiobacillus ferrooxidans, Leptospirillum sp., Acidiphilium sp. and one for total bacteria, using specific primers for each of them, which hybridize inside the region amplified in the primary PCR. Sense and antisense primers were selected for the different taxons from those included in the description of the tables corresponding to each taxon, Tables 5, 6, 8 and 9 in this case. On the other hand, for total bacteria primers described in the literature were used, which were included in Table 15.
Primers used for each taxon and their respective annealing temperatures are indicated in Table 22.
One qPCR was carried out on each primary PCR reaction product for each taxon to be determined, these reactions being performed in duplicate. The qPCR was carried out using Mix SYBR Green qPCR. For each secondary PCR one duplicate per each one of the 25 primary PCR reactions is considered plus one control, which gives a total of 51 reactions. For each PCR the reaction mix shown in Table 23 is prepared, where primers are those that are corresponding according to Table 22.
This reaction mix was homogenized and aliquoted in 51 0.2 ml tubes, which were duly labeled. To each of the tubes 1 μl of primary PCR or 1 μl of sterile nuclease-free water for the blank was added.
PCR tubes containing the reaction mix and sample were vortexed for 5 seconds and centrifuged for 1 minute at 2000 rpm, in order to homogenize and bring the reaction liquid to the bottom of the tube, respectively.
Then, the tubes with secondary PCR reactions were subjected to temperature cycles for amplification. According to the microorganism to be determined, different primer pairs were used and therefore different amplification programs were used. In the following Table, amplification programs used in the different secondary PCR reactions are shown.
(*) specific temperature for each used primer pair, as indicated in Table 22.
When the qPCR is finished, all data generated by the qPCR thermocycler are stored; this data corresponds to Q and is shown in Table 25, wherein DNA amounts in nanograms used for each reaction are included (U).
Taking into account the qPCR result and other data generated during the process, the following formula was applied, the meaning of which was defined above:
According to this, the following microbiological populations were determined in the analyzed samples:
A. ferrooxidans
A. thiooxidans
Leptospirillum sp.
Acidiphilium sp.
A. ferrooxidans
A. thiooxidans
Leptospirillum sp.
Acidiphilium sp.
A. ferrooxidans
A. thiooxidans
Leptospirillum sp.
Acidiphilium sp.
A. ferrooxidans
A. thiooxidans
Leptospirillum sp.
Acidiphilium sp.
A. ferrooxidans
A. thiooxidans
Leptospirillum sp.
Acidiphilium sp.
A. ferrooxidans
A. thiooxidans
Leptospirillum sp.
Acidiphilium sp.
FIGS. 1 to 7 are plots of the results described in Tables 26 to 32.
Two solid samples obtained from mineral bioleaching heaps (MS-6 and MS-7) were analyzed and total DNA was extracted from each one.
A further DNA re-purification step was required to obtain a translucent appearance in the extraction solution.
Then, total DNA was quantified in each sample using a NanoDrop 1.0 spectrophotometer. Total extracted DNA nanograms (T) are shown in Table 34 together with the initial sample volumes (Cm). Results are shown in Table 33.
Each of these samples was diluted with sterile nuclease-free water in order to obtain a concentration between 0.5 and 30 ng/μl. Table 34 shows the final volume to which the DNA solution was brought and its final concentration.
Two calibration curves were prepared simultaneously, one for the Bacteria kingdom and another for the Archaea kingdom, which allowed calculating DNA concentration in experimental samples. For the Bacteria kingdom 4 serial dilutions were carried out from a DNA standard, hereinafter called Bacteria standard, containing 100 ng of Sulfobacillus sp. DNA in a final volume of 30 μl, being the standard solution also part of the calibration curve.
More specifically, DNA was used from the strain:
For the Archaea kingdom, four serial dilutions were prepared from a standard DNA mix containing 50 ng of DNA from each of the following microorganisms: Sulfolobus sp. and Ferroplasma sp. in a final volume of 30 μl, obtaining 100 ng of total DNA in the standard mix, hereinafter called Archaea standard, which is also part of the calibration curve.
More specifically, DNA was used from the following strains:
Then, reaction mixes for the primary PCR were prepared, wherein the amount of each constituent was multiplied by the total number of reactions to be carried out; a single reaction mix was prepared in order to homogenize reagent concentrations in the different PCR tubes. The reaction mix was aliquoted in 0.2 ml tubes, using a volume of 24 μl of reaction mix per tube.
For the Bacteria kingdom and Sulfobacillus determination, the following reactions were set up in duplicate:
The prepared mix is shown in Table 35.
Primers were those described in Table 36:
This primary PCR reaction mix was homogenized and 15 aliquots were made with 24 μl each in 0.2 ml tubes appropriately labeled. To this mix 1 μl of sample DNA dilutions or 1 μl of calibration curve DNA was added as appropriate. To the negative control 1 μl of sterile nuclease-free water was added instead of DNA.
Reactions were incubated in a MJ Research PTC-100 thermocycler, with the following cycle program:
Wherein steps 2 to 4 were repeated 18 times.
For the Archaea kingdom and Sulfolobus sp. and Ferroplasma sp. determination, the following reactions were set up in duplicate:
The prepared mix is shown in Table 38.
Primers were those described in Table 39:
This primary PCR reaction mix was homogenized and 15 aliquots were made with 24 μl each in 0.2 ml tubes appropriately labeled. To this mix 1 μl l of sample DNA dilutions or 1 μl of calibration curve DNA was added as appropriate. To the negative control 1 μl of sterile nuclease-free water was added instead of DNA.
Reactions were incubated in a MJ Research PTC-100 thermocycler, with the following cycle program:
Wherein steps 2 to 4 were repeated 18 times.
Subsequently, 5 secondary PCR were performed, two on the primary PCR reaction product for the Bacteria kingdom, for Sulfobacillus sp. and for total bacteria; and three on the primary PCR reaction product for the Archaea kingdom, for Sulfolobus sp. and Ferroplasma sp. and for total archaea, using specific primers for each of them that hybridize inside the region amplified in the primary PCR. Sense and antisense primers were selected for the different genera from those included in the description of the tables corresponding to each taxon, Tables 7, 11 and 13 in this case. On the other hand, for total bacteria or archaea primers described in the literature were used, which were included in Table 15.
Primers used for each taxon and their respective annealing temperatures are indicated in Table 41.
One qPCR was carried out on each primary PCR reaction product for each taxon to be determined, these reactions being performed in duplicate. The qPCR was carried out using Mix SYBR Green qPCR. For each secondary PCR one duplicate per each one of the 15 primary PCR reactions is considered plus one control, which gave a total of 31 reactions. For each PCR the reaction mix shown in Table 42 was prepared, where primers are those that are corresponding according to Table 41.
This reaction mix was homogenized and aliquoted in 31 0.2 ml tubes, which were duly labeled. To each of the tubes 1 μl of primary PCR or 1 μl of sterile nuclease-free water for the blank was added.
PCR tubes containing the reaction mix and sample were vortexed for 5 seconds and centrifuged for 1 minute at 2000 rpm, in order to homogenize and bring the reaction liquid to the bottom of the tube, respectively.
Then, the tubes with secondary PCR reactions were subjected to temperature cycles for amplification. According to the microorganism to be determined, different primer pairs were used and therefore different amplification programs were used. In the following Table, amplification programs used in the different secondary PCR reactions are shown.
(*) specific temperature for each used primer pair, as indicated in Table 41.
When the qPCR is finished, all data generated by the qPCR thermocycler are stored; this data corresponds to Q and is shown in Table 44, wherein DNA amounts in nanograms used for each reaction are included (U).
Taking into account the qPCR result and other data generated during the process, the following formula was applied, the meaning of which was defined above:
According to this, the following microbiological populations were determined in the analyzed samples:
Sulfobacillus sp.
Sulfolobus sp.
Ferroplasma sp.
Number | Date | Country | Kind |
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2179-2005 | Aug 2005 | CL | national |