The objective is to provide to our C. metallidurans strain, alcoholic fermentation genes (pyruvate decarboxylase and pyruvate deshydrogenase of Zymomonas mobilis) to permit it to produce ethanol from glucose.
To do this, we use the fusion protein of BBa_K1122673 part (
Edingurgh 2013 team) under Pan promoter control (ref parts : pan + composite), to obtain strong expression, in particular in presence of heavy metals.
We have made an expression plasmid construction by inserting in vector pBBR2MCS-1, for expression at C. Metallidurans, the Pan promoter and the fusion protein ORF of the part BBa_K1122673.
Then, C. Metallidurans is transformed with this construction by electroporation.
On construit un plasmide d'expression en insérant dans le vecteur d'expression pBBR2MCS-1 pour une expression chez métallidurans le promoteur pan et l'ORF de la protéine fusion XXX. On transforme ensuite CH34 par ce plamide par éléctroporation.
the pBBR1MCS-2is and the BBa_K1122673 part are digested by EcoR1 and Spa1 Fast digest restriction enzymes (Thermofisher Scientific). After purification by GeneJET Gel Extraction and DNA Cleanup Micro Kit (Thermo fisher) and checking the digestion success by electrophoresis, the BBa_K1122673 ORF insert is ligated into pBBR1MCS-2 and the resulting plasmid is transformed into Escherichia coli DH5alpha. The ligation success is verified by realizing a colony PCR. The Pan promoter is digested and inserted into pBBRMCS- BBa_K1122673 by following the same process than for BBa_K1122673, with HindIII and EcoR1 Fast digest restriction enzymes (Thermofisher Scientific).
C. Metallidurans CH34 is grown overnight in BM3, then diluted in a bigger volume of BM3 and re-incubated at 30°C for 2 days. Cells are then cooled in ice for 20minutes, centrifugated (15 minutes at 4000g) and resuspended into washing buffer (compsition - see table). the centrifugation and resuspension in washing buffer is repeated 3 times. The last re-suspension volume is calculated to obtain an optical density of 120 at 660nm. the bacteria are aliquoted and 4µL of the plasmid solution (100ng/4µL) are added to the samples to be measured. Samples are incubated 1 minute in ice before being transferred in cooled electroporator cuve and placed into the electroporator. After the electroporation, 1ml SOC medium is added immediately to the bacterias. Suspension is transferred in tubes and incubated at 30°C for 1h, then plated on selective medium ().
To get cellulose, cleaning paper is blended in water. First, a digestion test of the paper mixed by cellulases from Trichoderma reesei is performed by adding 125 U of cellulases to 300mg of paper and incubated for 24 hours at 37°C. The results are observed through the disappearance of paper aggregates.
Then, 1,2g of mixed paper is added to 250mL of 284 medium in presence of cellulase. The Other conditions are the direct presence of glucose in medium 284 (instead of gluconate), a rich medium (BM3), and autoclaved or non-supplemented sewage sludge.
pBBR1MCS-2-pan- BBa_K1122673 transformed C. metallidurans or CH34 are inoculated in the different conditions (using a BM3 preculture) in presence of cellulase or not, then the glucose and ethanol concentrations are measured from T=0h at T=26h by using DNS method for the glucose and densimeter method for the ethanol. Negatives control without bacteria is also carried out.
DNS assayclick to view experimental protocol
Prepare the following DNS solution:
- 3,5-DNS 1% : 10g/L
- NaOH 0.4M : 16g/L
- Double tartrate (Na;K).4H2O 30%: 300g/L
Heat the solution to dissolve it at 90°C in a bain-mari.
Adjust the volume after heating with water.
Realization of a calibration range:
Achieve a glucose concentration range of 0 to 10 mM (including the expected concentration range in the samples).
Add to 100µL of each glucose solution of known concentration, 200µL of DNS solution.
Heat to 95°C for exactly 5 minutes.
Allow to cool and then deposit 200µL of each sample on a 96-well plate.
Sample production:
For each sample, add 600µL of DNS solution to 300µL of sample and heat to 95°C for exactly 5 minutes.
Allow samples to return to room temperature.
Place 200µL of each sample in triplicate in the 96-well plate.
Determination of glucose concentration:
Read the absorbance at 530nm of the standard range and of each sample (in triplicates).
Make a calibration curve of the absorbance as a function of the known glucose concentrations.
Report the absorbance values at 530nm of the samples on the calibration curve and deduce their glucose concentration
Goal
The final tests confirmed the functionality of the project, that is to say, that Cupriavidus metalidurans has been modified by homologous recombination and is able to better or more specifically remove heavy metals from sludge, and that it is able to produce ethanol in sludge from glucose, obtained by digesting cellulose naturally present in sludge by cellulases.
Comparisons were made between C. metallidurans delaPbrR, CH34 and E. Coli S17-1 (negative control) strains for their heavy metal depollution capacity.
A comparison was also made between cultures grown in autoclaved or non-autoclaved sludge.
For these tests, several types of cultures are carried out.
The three strains are first put in the presence of Lead and Cadmium, in order to activate the resistance mechanisms to heavy metals.
These three strains are then cultivated in autoclaved or non-autoclaved sludge for 20 hours at 30°C.
An ICP analysis is performed, before and after culture, under the different culture conditions as well as on the bacteria alone (separated from the sludge).
Principle
Heavy metal depolluting test on the different strains cells : The three strains C. metalidurans CH34, C. metalidurans ΔPbrR and E. Coli S17-1 are initially seeded in BM3 and incubated at 30°C for 2 days to achieve preculture.
Each strain is then centrifuged and resuspended in medium 284 supplemented with lead (0.4mM) and cadmium (2mM) and incubated for 15 mins at 30°C.
This incubation allows the activation and implementation of the resistance mechanisms of C. metalidurans, so that they are already expressed during the culture in the sludge.
The concentrations of these metals have been chosen in such a way that they are just below the lethal concentrations.
After activation, the three strains are centrifuged and then resuspended under two culture conditions. The first is a culture in non-autoclaved sewage sludge, supplemented with BM3 (50/50, v/v). The second condition is a culture in autoclaved sewage sludge, supplemented with BM3 (50/50, v/v).
Growth monitoring was carried out in each culture condition, by measuring optical density at 600nm and spreading diluted samples by a factor of 102 and 106 on solid BM3 medium in order to count the bacteria.
After 20 hours of incubation, the different cultures were centrifuged, first at 300g for 5 minutes to recover the solid matter without bacteria contained in the sludge, then at 14000g for 5 minutes to recover the bacteria from each condition.
The solid matter, the bacterial pellet and the supernatant from the 14000g centrifugation were used to perform an analysis of the quantities of lead and cadmium by ICP.
The same manipulations were also carried out on mud samples supplemented with BM3, which were not sown with bacteria.
Material & methods
The three strains C. metalidurans CH34, C. metalidurans ΔPbrR and E. Coli S17-1 are initially seeded in BM3 and incubated at 30°C for 2 days to achieve preculture.
Each strain is then centrifuged and resuspended in medium 284 supplemented with lead (0.4mM) and cadmium (2mM) and incubated for 15 mins at 30°C.
This incubation allows the activation and implementation of the resistance mechanisms of C. metalidurans, so that they are already expressed during the culture in the sludge.
The concentrations of these metals have been chosen in such a way that they are just below the lethal concentrations.
After activation, the three strains are centrifuged and then resuspended under two culture conditions. The first is a culture in non-autoclaved sewage sludge, supplemented with BM3 (50/50, v/v). The second condition is a culture in autoclaved sewage sludge, supplemented with BM3 (50/50, v/v).
Growth monitoring was carried out in each culture condition, by measuring optical density at 600nm and spreading diluted samples by a factor of 102 and 106 on solid BM3 medium in order to count the bacteria.
After 20 hours of incubation, the different cultures were centrifuged, first at 300g for 5 minutes to recover the solid matter without bacteria contained in the sludge, then at 14000g for 5 minutes to recover the bacteria from each condition.
The solid matter, the bacterial pellet and the supernatant from the 14000g centrifugation were used to perform an analysis of the quantities of lead and cadmium by ICP.
The same manipulations were also carried out on mud samples supplemented with BM3, which were not sown with bacteria.
Primer table
Here are documented all the primer pairs we used in our experiments.
In the table, each pair is composed of two successive primers. the forward primer (first one in the table order) have is name ended by "_fwd" as the reverse primer has a name ended by "_rev".
The 8 first pairs correspond to the primer used for Cupriavidus metallidurans CH34 gene border amplification in perspective of homologous recombination. For all of these plasmids name is composed as follow :
"target gene name - side of the gene -(5 for upstream and 3 for downstream) _ orientation of the primer (forward or reverse)". The primer whom the name begins by Col is used in colony PCR, and the couple Cre157_fwd - Cre157_rev is designed to amplify Cre fragment from pCM157.
AAAAGATCTGGTGCTGATGACGGCCCTGG
AAACATATGCCTGCGCCCATAGAAACTCC
AAAGGGCCCCAGGAGGAAACTAAGGTGCG
AAAGTTAACAATCGTCTGCCCCCAACTCG
AAAAGATCTTAACGGCTAGCGTTCGCTGC
AAACATATGTCATGGCGTCGGATGGGAGA
AAAGGGCCCCCCATCCAAGCGACTAGGTG
AAAGTTAACCGACGTGGCCATCCTTGACG
AAAAGATCTATGAGCACATCCGTCAGGTC
AAACATATGGCATGGGAGGCCTTACC
AAAGGGCCCGGCCATCTACCCAGGTGTAA
AAAGTTAACGGATCTGGCATAACGTGGTG
AAAAGATCTGGCTTGGCGACCGGGTC
AAACATATGACATTGCTGTTTCCCCCGTA
AAAGGGCCCAAGGCCGCCAGCCTGC
AAAGTTAACGCCAAATGTCCGCTTCTTGT
TTTTCAATATTATTGAAGCATTTATCAGG
AAAAGATCTAATACGCAAACCGCCTCTC
AAAGTTAACCCTCTTCGCTATTACGCCAG
Mediums
Here are documented all the mediums we used in our experiments.
Lysogeny Broth
Description
Lysogeny broth, abreviated LB, is a common bacterial growth medium. It's particularly suited for Escherichia coli growth.
Nutrient broth
Description
Nutrient broth, abreviated NB, is another common bacterial growth medium. its composition is verry similar to the LB one. It's commonly used for Cupriavidus metallidurans CH34 growth.
284
Description
284 (Mergeay, 1995; Schlegel et al., 1961) is a tris buffered medium supplemented in heavy metal salts. It's used to study bacteria heavy metal resistance. the recipe presented below is from S. Monchy's thesis [284 composition source].
Recipe
284 medium
SL7 solution
Super Optimal Broth with Catabolite Expression
Description
Super Optimal Broth with Catabolite Expression, abreviated SOC, is a medium designed to optimize bacterial transformation efficiency. Here, it is used to resuspend bacteria after the electroporation.
References
[conjugaison] Wiesemann N, Mohr J, Grosse C, et al. Influence of copper resistance determinants on gold transformation by Cupriavidus metallidurans strain CH34. J Bacteriol. 2013;195(10):2298–2308. doi:10.1128/JB.01951-12
[pCM184] Broad-host-range cre-lox system for antibiotic marker recycling in gram-negative bacteria. Marx CJ, Lidstrom ME. Biotechniques. 2002 Nov;33(5):1062-7. 10.2144/02335rr01 PubMed 12449384
[pCM157] Broad-host-range cre-lox system for antibiotic marker recycling in gram-negative bacteria. Marx CJ, Lidstrom ME. Biotechniques. 2002 Nov;33(5):1062-7. 10.2144/02335rr01 PubMed 12449384
[electroporation] Taghavi S, van der Lelie D, Mergeay M. Electroporation of Alcaligenes eutrophus with (mega) plasmids and genomic DNA fragments. Appl Environ Microbiol. 1994;60(10):3585–3591.
[pBBR1MCS-2] Four new derivatives of the broad-host-range cloning vector pBBR1MCS, carrying different antibiotic-resistance cassettes. Kovach ME, Elzer PH, Hill DS, Robertson GT, Farris MA, Roop RM 2nd, Peterson KM. Gene. 1995 Dec 1;166(1):175-6. 0378111995005841 [pii] PubMed 8529885
[biobrick] http://parts.igem.org/wiki/index.php?title=Part:BBa_K1122674
[pan] Ribeiro-dos-Santos, G., Biondo, R., Quadros, O. de F., Vicente, E. J., & Schenberg, A. C. G. (2010). A metal-repressed promoter from gram-positive Bacillus subtilis is highly active and metal-induced in gram-negative Cupriavidus metallidurans. Biotechnology and Bioengineering, 107(3), 469–477. https://doi.org/10.1002/bit.22820
[composition du millieu 284] Sebastien MONCHY, "Organisation et expression des gènes de résistance aux métaux lourds chez Cupriavidus métallidurans CH34", These de doctorat en Sciences de la vie sous la dirrection de Max MERGEAY et Ariane TOUSSAINT, Bruxelles, Uinversité Libre de Bruxelles, 2007, 99p