Team:Imperial College/Growth Assays
From 2013.igem.org
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| [[File:CLE.png|thumbnail|right|450px|<b>CLE growth assay</b> E. coli (MG1655) transformed with CLE (BBa_K1149009) were grown with either 0% or 2% Xylose to induce CLE and sfGFP expression. Growth was at 37oC with shaking. Error bars are SEM, n=4. ]] | | [[File:CLE.png|thumbnail|right|450px|<b>CLE growth assay</b> E. coli (MG1655) transformed with CLE (BBa_K1149009) were grown with either 0% or 2% Xylose to induce CLE and sfGFP expression. Growth was at 37oC with shaking. Error bars are SEM, n=4. ]] | ||
- | | [[File:CLE_fluor.png|thumbnail|right|450px|<b>CLE induction assay</b> E. coli (MG1655) transformed with CLE (BBa_K1149009) were grown with either 0% or 2% Xylose to induce CLE and sfGFP expression. Growth was at | + | | [[File:CLE_fluor.png|thumbnail|right|450px|<b>CLE induction assay</b> E. coli (MG1655) transformed with CLE (BBa_K1149009) were grown with either 0% or 2% Xylose to induce CLE and sfGFP expression. Growth was at 37°C with shaking. Error bars are SEM, n=4. ]] |
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| [[File:ESTCS2.png|thumbnail|right|450px|<b>ETSCS2 growth assay</b> E. coli (MG1655) transformed with ESTCS2 (BBa_K1149002) were grown with either 0uM or 6uM Arabinose to induce ESTC2 and sfGFP expression. Growth was at 37oC with shaking. Error bars are SEM, n=4.]] | | [[File:ESTCS2.png|thumbnail|right|450px|<b>ETSCS2 growth assay</b> E. coli (MG1655) transformed with ESTCS2 (BBa_K1149002) were grown with either 0uM or 6uM Arabinose to induce ESTC2 and sfGFP expression. Growth was at 37oC with shaking. Error bars are SEM, n=4.]] | ||
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| [[File:F_arabinose_induction.png|thumbnail|right|450px|Fluorescence of the cells under IPTG induction over a 6h period.]] | | [[File:F_arabinose_induction.png|thumbnail|right|450px|Fluorescence of the cells under IPTG induction over a 6h period.]] | ||
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+ | The null hypothesis, arabinose concentration does not influence growth of MG1655 in M9 minimal (M9M) media and M9 minimal waste conditioned media (M9MWCM) was tested using a two-tailed t-test. This must be rejected because p < 0.0001, thus arabinose concentration has an influence on growth in M9M and M9MWCM. | ||
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| [[File:F_glucose_inhibition.png|thumbnail|right|450px|Fluorescence of the cells under IPTG induction over a 6h period.]] | | [[File:F_glucose_inhibition.png|thumbnail|right|450px|Fluorescence of the cells under IPTG induction over a 6h period.]] | ||
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+ | The null hypothesis, glucose concentration does not influence growth of MG1655 in M9 minimal (M9M) media and M9 minimal waste conditioned media (M9MWCM) was tested using a two-tailed t-test. This must be rejected because p < 0.0217, thus glucose concentration has an influence on growth in M9M and M9MWCM. | ||
Revision as of 23:33, 30 September 2013
Contents |
Growth and Toxicity Assays
This page includes all of our experimental growth, toxicity and sole carbon source assay data.
Growth assays with different experimental media
In additional to standard LB and minimal media, several novel experimental media were developed in order to characterise Biobricks within a mixed waste/landfill setting. These media were characterised through an examination of pH and through an array of growth assays with the project chassis, E.coli (MG1655).
Conclusion: MG1655 E. coli are viable and grow in all of our experimental medias. We have established a novel media that is optimised for characterisation of biobricks within a mixed waste/landfill context.
Long term waste growth assays
These assays were designed to test whether our chassis, E. coli (MG1655) could grow directly with waste over a long period of time.
Waste media
Conclusion: MG1655 E. coli are viable and grow on mixed waste alone. Therefore we have established that our chassis could survive in a mixed waste bio-reactor context, which is validation of our concept to industrially implement our system.
Waste conditioned media
These assays were designed to test whether our chassis, E. coli (MG1655) could grow with waste conditioned media (WCM) over a period of 24-48 hours. Waste conditioned media is a filter sterilised version of the waste media and was designed for several reasons; Firstly we were unsure whether mixed waste would be toxic to Ecoli and hence a less concentrated version may be more suitable and secondly large chunks of waste would prevent accurate OD600 measurements and therefore we decided to filter out the largest chunks.
Conclusion: MG1655 transformed with either empty vector (EV) control or mCherry stress biosensor (BBa_K639003) vector are viable and can grow in waste conditioned media. Therefore waste conditioned media is an appropriate and novel experimental media with which to characterise biobricks within a mixed waste/landfill context. These data are also characterisation of an existing biobrick (BBa_K639003)
Growth and induction assays of our Biobricks
Growth and induction assays of our project biobricks. Several of our constructs contain sfGFP within an operon and therefore fluorescence can be utilised to determine if expression is being induced by either addition of Arabinose or Xylose as appropriate to the construct.
Empty Vector Control
Growth assay characterisation of existing biobricks
Stress biosensor characterisation (BBa_K639003)
Originally we intended on using [http://parts.igem.org/Part:BBa_K639003 BBa_K639003] to detect whether our cells were stressed when grown with an array of potentially toxic plastics and degradation products. However, as the data below shows, the promoter is leaky and expresses mCherry in a non stressed state. As an alternative we utilised the stress sensor as a marker for our chassis E. coli (MG1655) for an array of qualitative and quantitative waste growth and toxicity assays.
Note: The stress sensor induces mCherry production through a mechanism involving the ppGpp stress response. Induction with IPTG bypassess this mechanism through an inhibition of LacI, resulting in mCherry expression.
phaCAB biobrick characterisation
LB
M9 Minimal
M9 Supplemented
pBAD characterisation
The null hypothesis, arabinose concentration does not influence growth of MG1655 in M9 minimal (M9M) media and M9 minimal waste conditioned media (M9MWCM) was tested using a two-tailed t-test. This must be rejected because p < 0.0001, thus arabinose concentration has an influence on growth in M9M and M9MWCM.
The null hypothesis, glucose concentration does not influence growth of MG1655 in M9 minimal (M9M) media and M9 minimal waste conditioned media (M9MWCM) was tested using a two-tailed t-test. This must be rejected because p < 0.0217, thus glucose concentration has an influence on growth in M9M and M9MWCM.
Glucose
ANOVA analysis shows that the null hypothesis that there is no significant difference between M9M and LB in empty vector and phaCAB is true (F 3,24 = 0.8451, p < 0.4827). In addition to this the null hypothesis that there is no significant difference between M9S and LB similarly must be rejected as p > 0.05 (F 3,24 = 0.9802, p < 0.06009)
Plastic Toxicity Assays
L-lactic Acid
Ethylene glycol
Reduced growth at 30oC likely due to decreased efficiency of MG1655 ethylene glycol break down enzymes. These enzymes (see UC Davis 2012) are endogenously expressed and detoxify Ethylene Glycol.
3-hydroxybutyrate (3HB)
Acetoacetate
Poly(3-hydroxybutyrate) P(3HB)
Poly(lactic acid) (PLA)
Sole carbon source
3HB
Acetoacetate
Compiled sole carbon growth
phaCAB on M9 minimal and supplemented media
phaCAB with novel promoter