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Study 3
A range finding study with alternative substrates

Glutathione S-Transferase as a Biological Marker of Aquatic Contamination
Research Thesis in Applied Toxicology
Tomas James Rees, Portsmouth University, UK
In Collaboration with the Water Research Centre, Henley
© August 1993

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Introduction
Materials and Methods
Results
Discussion

Introduction

GST exists as a family of isoenzymes. Six have been identified in the rat, and three in humans (Habig, W.H., Jakoby, W.B., 1981). Although the isoenzymic makeup of the mollusc Anodonta is unknown, at least two (and possibly three) isoenzymes have been identified in Sphaerium (Johnson, I., Fleming, R., Garrood, A. C., Beverley, M., 1992). A generalised pattern is hard to establish, however it is readily apparent that the isoenzymes of GST have differing activities towards a range of substrates. These can provide the basis of a mechanism to differentiate between them (Habig, W.H., Jakoby, W.B., 1981).

George et al. (1989) found that activities towards other substrates in a range of fish were very low (typically less than 10% of the CDNB conjugating activity) (George, S., Buchanan, G., Nimmo, I., Hayes, J., 1989). However Jewell et al. (1989) also found that, in the red swamp crayfish, GST activity towards CDNB is associated with two isoenzymes which can be physically separated from GST activity towards p-nitrophenylacetate and p-nitrophenyltrimethylacetate (Jewell, C.S., Lee, R.F., Winston, G.W., 1989). Since there is good evidence that isoenzymes may be differentially regulated (see earlier literature review), an assay specific toward a different GST isoenzyme may provide a test which overcomes some of the problems encountered with a CDNB based assay. Specifically, interference encountered at 340 nm, lack of inducibility, and fluctuations in control levels.

To this end, a range finding study of 6 potential GST substrates was undertaken, with a view to eliminating those with no discernable activity, and identifying optimum assay conditions for those with demonstrable activity.

Materials and methods

The assay was a modification of that given in the introduction. The cytosolic extracts used were those of swan mussels which had been exposed to 3200 ng/l lindane for 7 days and then frozen (Polak, M., 1992). 2 samples of gill tissue, and 2 samples of digestive gland tissue, were chosen at random from those available (G 19, G6, DG 134, DG 114).

The test substances used were;

1-chloro-2,4-dinitrobenzene (CDNB),
p-nitrobenzyl chloride (PNBC),
p-nitrophenyl acetate (PNPA),
ethacrynic acid (EA),
nitropyridine oxide (NPD),
1,2-epoxy-3-(p-nitrophenoxy)propane (ENP).

These substrates were chosen on the basis of their identification in previous work (Johnson et al., 1992) as substrates of GST, and on their availability from commercial suppliers. The concentrations used were based on those used in the previous in work or derived from the literature (Habig et al., 1974). The pH of the buffer and the wavelength at which absorbance was initially measured were also derived from Johnson, et al. 1992 and Habig & Jakoby (1974). Where sources were in disagreement both permutations were assessed. The basic conditions are outlined below:

Substrate Stock concentration pH Wavelength
CDNB 50 mM 6.5 340 nm
PNBC 20 mM 6.5 310 nm
PNPA 20 mM 6.5, 7.0 400 nm
EA 4 mM 6.5 270 nm
NPD 4 mM 7.0 295 nm, 360 nm
ENP 100 mM 6.5 360 nm

Intially, an absorption spectrum (blanked against water) was obtained for the test substance in an assay mixture of 1.6 ml buffer, 0.2 ml GSH, 0.1 ml test substance (total volume 1.9 ml). A 0.1 ml aliqout of cytosolic extract (DG 134) was added and the absorbance change (dABS) over 3 minutes at a single wavelength was measured. This mixture was then allowed to stand. If no significant change in absorbance at the selected wavelength was detected, the test was repeated with extract G 19.

An absorbance spectrum was then obtained of the assay mixture which had been allowed to stand. This gave the absorbance of the reaction after around 10 minutes, and was analysed to identify any potentially more suitable wavelengths for further study. If no activity could be found, the remaining 2 extracts were studied with 0.1 ml of the buffer replaced by an additional 0.1 ml of extract. If activity was detected, further permutations were investigated in order to find the optimum assay conditions.

Results

Absorbances of the assays sans extract are given in Figures 3.1-3.6. For three of the test substrates (PNBC, NPD, ENP), no activity at any wavelength was discernable over the time course of the experiment (PNBC, NPD, ENP). The absorbance spectra of the other three substrates (CDNB, PNPA, EA) after around 10 minutes reaction are given in Figures 3.7-3.9. The optimum assay absorbance for PNPA was identified as 330 nm, rather than the 400 nm previously suggested (Johnson et al., 1991). Typical changes in absorbance at the test wavelength over 3 minutes are given in Figures 3.10-3.12.

Discussion

Three compounds have been identified for further investigation. The active compounds are essentially those previously found to be active in Sphaerium corneum (Johnson et al., 1991), with the addition of PNPA. This may be because the wavelength measured by Johnson et al. in the investigation of PNPA activity in Sphaerium (400 nm) is slower to develop than the absorbance at 330 nm. It is probably analogous to the secondary absorbance (at 390 nm) observed in Study 1 with CDNB. The activity of EA was found to be very low. However the solution was assesed at a concentration of 1.2 mg/ml, whereas the nominal solubility in ethanol is 50 mg/ml (Sigma Chemical Co. LTD., personal communication). Future tests should therefore use a more concentrated solution.