Difference between revisions of "Team:HebrewU/Results"

Chemically Induced Growth Rate Alteration: Though the chemicals used in our experiments were less toxic than TCDD, they are still recognized as harmful molecules. As such, it was reasoned that the presence of these molecules in the medium would inhibit or completely halt the growth of yeast. As some of the breakdown products of these compounds are also toxic (i.e. pyrocatechol), it was not clear if the enzymatic activity would reduce the inhibition or further decrease the growth rate.

To measure growth, measurements were taken with a spectrophotometer to track absorbance at 600nm. By reading the absorbance regularly (every 5-10 hours during lag phase and every 2-4 hours during log phase) we could accurately track the growth rates of each yeast line for comparison. Each experiment was conducted in triplicate and repeated twice.

To compare growth rates and discern if there were significant changes in growth, the following data analyses were conducted:

1. Isolation of exponential growth phase.
2. Rate of change (slope) calculated for each sample.
3. Comparison of these rates using Two-way T-test for Equal Means.

After testing yeast growth in the presence of these toxic compounds, the samples were analyzed to monitor changes in the chemical composition of the different treatments. To this end, cells were lysed, and total metabolites were extracted in methanol. Chemical and statistical analyses were conducted to survey the metabolic differences. Using chemical analysis, two parameters were tracked that would allow for quantifying the activity of the researched enzymes:

1. Concentration changes of the compound added to the medium.
2. Concentration changes of the expected metabolites in the sample.

At first, High-Pressure Liquid Chromatography (HP-LC) was employed, but the molecules in question were not easily tracked by this method. This resulted in a switch to High-Resolution Liquid chromatography-mass spectrometry (HR-LC-MS), specifically using atmospheric pressure chemical ionization (APCI). APCI is a method of ionization which ionizes the sample through the addition of atoms, or small molecules, creating a charge that is read by the machine. The results produced are chemical compounds found in the sample, represented by molecular mass. The masses produced are accurate to 5 digits after the decimal- which increases accuracy in identifying chemical equations from the mass values.

The LC-MS analysis was untargeted. This means the equipment was not directed to look for a specific molecule or mass; rather it processed all the available data from each sample. As it was not certain that the starting compound could be easily tracked, this method allowed unpredicted products of the compounds’ breakdown to be assessed.

To sift through the thousands of compound masses delivered by these assays, Sieve and Compound Discoverer software was used to align the sample peaks and to produce the primary statistical analysis of the differences between treatments. Even after this help from software, there were thousands of outputted compounds. To narrow the field of compounds, the following criteria were outlined:

1. Compounds with at least a 60% increase in samples containing both the compound and the enzymes, compared to the control groups. This would suggest that the compound is the result of the presence of both the enzymes and substrate.
2. Statistical significance was determined using an alpha value of ≥ 0.05 for T-test.
3. Compounds with a molecular weight in the range of expected metabolites.
4. Chemical equations corresponding to anticipated metabolites with minor variations as a result of the ionization process.

To examine whether 1,2,4,5-Tetracholobenzen (TCB) affected the growth rate of the yeast, we treated six subculture replicates (OD₆₀₀~0.025): three with 0.45uM of TCB and three methanol controls. Monitoring the growth from the lag- through the linear-phase, we could not detect any differences between the growth rate of chemical treatment and the control medium (Figure 1) regardless of the presence of the enzyme. Statistical analysis of the differences between the slopes is presented in Table 2.

As there was no observed growth-inhibition, it was concluded that the IC50 for TCB is higher than its solubility in water and that its metabolic products are not toxic; or that there was no substantial enzymatic activity. Since TCB and its potential degradation products could not be monitored by this bioassay, we tested the chemical composition of the cells.

The expected chemical reactions were the removal of chlorine molecules. As the benzene ring is a very stable structure, and the Dehalogenase does not act to dismantle it, the expected metabolites would be a 6-carbon ring with hydrogen molecules or OH groups replacing the Cl molecules. The chemical analysis showed both the increase and decrease of numerous compounds in the media (Figure 2) Following the parameters outlined in the chemical analysis section, ion masses possibly representing metabolites of TCB were found (Table 1).

Table 3: LCMS results for TCB samples in range of relevant molecular weight.

Not all of the masses with relevant chemical equations could be accounted for due to a large number of enzymatic processes in yeast. Based on the range in which they fell, however, it is likely they are products of the dehalogenation of TCB.

Additionally, some of the masses represent anticipated molecules produced by the metabolic pathway. For example, a molecular weight of 165.0763 represents the molecular equation: C₆H₁₂O₅. One of the spatial structures this equation can take is Cyclohexanepentol (Figure 3a). This molecule could likely represent our original 6-carbon ring, with all 4 of its chlorine molecules replaced by hydroxy groups, and an additional hydroxy group added during ionization or protonation of an oxygen molecule already present.

Moreover, the molecular weight 153.04249 is of interest, representing the molecular equation C₇H₇O₃N. This is possibly our original benzene ring with hydroxy groups. Though a specific reaction which would introduce an N molecule was not anticipated, nitrogen is abundant in yeast cells (Figure 3b). Both of these molecules represent promising results. They point to the complete dechlorination of the Tetrachlorobenzene and suggest the possibility that this enzyme could help transform 2,3,7,8 TCDD into the non-chlorinated Dibenzo-p-dioxin.

To examine Dibenzofuran’s (DBF) effect on yeast growth rate, we treated 12 subculture replicates (OD₆₀₀~0.025), at 4 varying concentrations: Methanol Control (mock), 0.5, 1, and 1.5 mM. As shown in Figure 4, the effect was significant and dose-dependent.

Using the Control group as the “maximum potential” for growth under the given conditions, we measured inhibition as affected by DBF (Figure 5B). This graph is based on measurements after 48 hours of growth.

With the above data, it was decided to run experiments with the enzymes at a concentration of 0.5 mM. This appears to be enough to inhibit growth, but not high enough to inhibit yeast growth even with 50% of the compound broken-down; such as could be the case at a higher dosage i.e. 1.5 mM.

When tested the growth rate of a yeast strain with degrading enzymes (DE) compared with to empty vector (EV) stains. We expected to see a change in growth rate as both substrate and degradation products may be toxic. As shown in Figure 6, the DE’s growth was further inhibited by the enzymes in the presence of DBF, meaning that the toxicity of the product exceed that of the substrate.

Table 4: Two-way T-test analysis for equal means to measure the change in growth rates.

It was discernible from the bio-assay that there was metabolic activity based on changes in growth rate. We then progressed to chemical analysis to better understand these processes. As with the TCB, we saw a number of changes in the medium (Figure 6). Employing a process similar to that described in the TCB section, we identified the compounds enriched in the treated sample (Table 5).

As these molecules consisted of more carbon atoms, anticipating the given structures for each mass became substantially harder, and our predictions less accurate. However, the masses 206.16661 and 137.03550 correlate closely with molecules in the designed pathway. 2,2',3-trihydroxybiphenyl and salicylic acid (a breakdown product of Dibenzofuran but not TCDD) weigh 202.2 and 138.1 Da, respectively. The replacement of a carbon molecule with oxygen or changes in the hydrogen content during ionization could account for these changes in mass.

The results here are preliminary but substantial. To further understand the chemical makeup of the breakdown products, continued Mass-Spec analysis is required. To do this we can employ a number of methods:

1. Obtain pure chemical standards corresponding to the molecules we suspect as breakdown products. We can run these standards against our sample and see if similar profiles appear.
2. LC-MS/MS: we can break down specific molecules we suspect as metabolites and run them in Mass-Spec. These broken-down products have a very specific time signature. If we put together the molecules from this small window of time and are able to rebuild the molecule in question, it would strongly imply that we have identified the correct molecule.
3. Use heavier molecules such as radioactive isotopes or Hydrogen-deuterium exchange, to see if there are shifts in the masses of the observed compounds.

These methods would further strengthen our ability to correctly identify the breakdown molecules we are working with. Additionally, growth-curve experiments with more toxic chemicals, even using 2,3,7,8-TCDD itself could potentially show clearer results in the biological assay. We have completed the first stages of research, and have already transformed plants with the Haloacid Dehalogenase. Further examination is required as we continue to develop a genetically engineered solution to TCDD, chlorinated pollutants, and dioxins.