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Journal of Applied Sciences and Environmental Management
World Bank assisted National Agricultural Research Project (NARP) - University of Port Harcourt
ISSN: 1119-8362
Vol. 10, Num. 3, 2006, pp. 93-96
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Journal of Applied Sciences & Environmental Management, Vol. 10, No. 3, September, 2006, pp. 93-96
The relative effects of some elements on the
DNS method in cellulase assay
*ALI
AKBAR SAFARI SINEGANI; GITI EMTIAZI
1Ali
Akbar Safari Sinegani, Assist. Prof., Faculty of Agriculture, Bu-AliSinaUniversity,
Hamadan, Iran.
2Giti
Emtiazi, Assoc. Prof., Faculty of Science, IsfahanUniversity,
Isfahan, Iran.
Code Number: ja06058
ABSTRACT: For
evaluating the relative effects of some polluting salts on the measurement of
cellulase activity assayed by 3,5-dinitrosalicylate (DNS) this study was done.
Glucose and cellulase solutions have been treated with salts. Exoglucanase and
endoglucanase were assayed by 3,5-dinitrosalicylate reagent. Measurement of
reducing sugar by DNS indicator in the presence of Ca+2, Ba+2,
Fe+3, Mn+2, Pb+2, Fe+2, Ag+1,
Zn+2, Co+2, and Al+3 salts overestimated and
in the presence of Mg+2, Cu+2, Cd+2, and Hg+2
salts underestimated the real contents. The intensity of DNS color and/or the
reducing power of glucose increased by decreasing radius of hydrated cation of
alkaline-earth elements (from Mg+2 to Ba+2) in glucose
solution. Exoglucanase and endoglucanase activities increased in the presence
of Na+, K+, Ca+2, Ba+2 and Mn+2
salts and decreased in the presence of NH4+ and Mg+2
salts. Among the trace elements studied, Fe+3, Pb+2, Fe+2,
Ag+1, Zn+2, Co+2, and Al+3 were the
most effective inhibitors of cellulase activity. These ions inhibited
exoglucanase more than endoglucanase. The effect of most ions on cellulase
activity may be related to negative or positive effect of them on the method of
cellulase assessment. So, for a better data interpretation in the study of ion
effects on the soil enzyme activity, both the effects of ions on the method of
enzyme assay, and the effects of ions on the enzyme activity should be studied.
@JASEM
Cellulase is an enzyme system that degrades
cellulose and releases reducing sugars as the end products. The system consists
of endo-l,4-B-glucanase (EC3.2.1.4), exo-I,4-B-glucanase (EC 3.2.1.91) and
B-D-glucosidase (EC 3.2.1.21). Endo-
α -1,4-glucanase (1,4-α-D-glucan-4-glucan-hydrolase)
has the role of randomly degrading α-1,4-glucosidic
bonds from the middle of the cellulose molecule. It does not attack cellobiose
but hydrolyzes cellodextrines and substituted celluloses, for instance carboxymethylcellulose.
Its specificity is moderate, different sub-types having various affinities for
different length oligosaccharides.
Exo-β-1,4-glucanase (1,4- β -D-glucan cellobiohydrolase) cuts step by
step cellobiose units from the non-reducing end of cellulosic chains. It
hydrolyses the cellodextrines but not the cellobiose. Its substrate specificity
is rather high enabling it to degrade more than 80% from the crystalline
cellulose while its degree of activity is different for different microorganisms.
α-Glucosidase (α-D-glucoside
glucohydrolase) hydrolyzes both cellobiose and cellooligosaccharides in
glucose. It is not able to degrade either cellobiose or cellodextrines with
high molecular weigh but favorites this process by removing cellobiose and this
way, diminishing the cellobiose accumulated in the medium. Such accumulation
could inhibit, by feed back, the activity of endo- and exoglucanase. The
capacity of degrading the natural cellulose involves the biosynthesis of the
whole enzyme system (Nevalainen and Penttil, 1995; Lee and Fan, 1980).
Soil enzymes were found to discriminate
between land management practices and to evaluate waste disposal on lands, and
therefore appear to be useful for monitoring changes in soil over time (Dick, R.P., 1997; Bandick and Dick, 1999; Badiane et
al, 2001). There is considerable documentation on the activities of many
enzymes inhibited by trace elements. The activities of the enzymes investigated
include α -glucosidase (Tyler, 1974), urease (Tyler, 1974; Tabatabai,
1977), phosphatase (Tyler, 1974; Juma and Tabatabai, 1977), arylsulfatase
(Al-Khafaji and Tabatabai, 1979), nitrate reductase (Fu and Tabatabai, 1989),
cellulase (Deng and Tabatabai, 1995), and cellulase
and α -glucosidase (Geiger et al, 1998).
In some studies salts and trace elements are added to soils, after time of
equilibration, enzyme activities are assayed. In some other studies enzyme
activity are assayed in salts or trace element affected soils. However there
are many factors in soils can change both the results of colorimetric
determination, and enzyme activity.
Dinitrosalicylic acid, potassium ferric
hexacyanid (Prussian blue) and
Somogyi-nelson (molybdenum blue) are three common methods generally used for
colorimetric determination of reducing sugars. The later two methods are more
sensitive than first one. However many of trace element e.g. Ag+1,
Ba+2, Cd+2, Cr+3, Cu+2, Fe+3,
Hg+2, Zn+2 and ... can effect on their results (Deng and
Tabatabai, 1994a,b). Dinitrosalicylic acid method is more suitable for
measuring high concentration of reducing sugars in solutions. It is not
sensitive as high as potassium ferric hexacyanid (Prussian blue) and
Somogyi-nelson (molybdenum blue) methods. This study was done to evaluate the
relative effects of some environmental polluting elements on the activities of
cellulase assayed by 3,5-dinitrosalicylate reagent (Mandel and Weber, 1969;
Miller, 1959). Our main objective, was to demonstrate the disruptive effects of common
and trace elements on both the colourimetric determination of reducing sugars,
and cellulase activity.
MATERIAL AND METHODS
For study the
effect of elements on the ability of glucose in reducing of DNS, a solution
with 1.5 gl-1 glucose in citrate buffer (pH=4.8) was prepared.
Except the blank solution, glucose solution was treated with common and trace
element salts. The final concentration of salts added to citrate buffer
solution of glucose was 0.04 N (~EC=4 dSm-1 that is near to ECe
of saline soils). This low pH inhibits salts to precipitate. Cations of Na+,
K+, NH4+, Ca+2, Mg+2, Ba+2
were added as the chloride, sulfate, bicarbonate, nitrate, phosphate, molibdate
or borate. The trace elements Fe+2, Mn+2, Hg+2,
Pb+2, Co+2, and Al+3 were added as the
chloride; Fe+2, Mn+2, Zn+2, Cu+2,
Al+3, Cd+2 and Ag+1 were added as the sulfate;
Pb+2, and Co+2 as the nitrate. After 30 min of
equilibration, the ability of glucose in reducing of DNS in the presence of
these elements was assayed by addition of 3,5-dinitrosalicylate reagent (Miller, 1959). The result of
glucose measurement in salt treated solutions was compared with the result of
glucose measurement in the blank solution untreated with salts.
Fluca prepared
cellulase (with 1.4 Uml-1 activity) was used in this study. The
concentration of cellulase was 0.2 gl-1 in citrate buffer solution
(pH=4.8) . Same as glucose solution, enzyme solution was treated with common
and trace elements. Final concentration of salts added to cellulase solution
was also 0.04 N. After 30 min of equilibration, cellulase activity was assayed.
The result of cellulase assessment in salt treated solutions was compared with
the result of cellulase assessment in the blank solution untreated with salts.
Endoglucanase
(CMCase, EC 3.2.1.4), and exoglucanase or cellobiohydrolase (FPase, EC
3.2.1.91) were assayed for the release of reducing sugar from carboxymethyl
cellulose (CMC) and filter paper (Whatman No.1), respectively. The reaction
mixture for reducing sugar assay contained (total volume 2ml) 0.5 ml enzyme
solution, 1.5 ml buffer 0.05 M citric acid (pH 4.8), and 0.05 g substrate.
After 1-hour incubation at 50 oC, the reaction was stopped by the
addition of 2 ml of 3,5-dinitrosalicylate reagent. The resulting mixture was
boiled for 15 minutes and reducing sugar content measured by absorbance at 575
nm. CMCase and FPase activities were expressed as micromoles of glucose
released per minute (international unit) per ml of culture extract (Mandel and
Weber, 1969; Miller, 1959).
The Results of
glucose measurement and cellulase assessment obtained from salt-treated
solutions were compared with that obtained from their respective blank
solutions (untreated with salts). The percentage of overestimate or
underestimate of glucose concentration and the percentage inhibition of
cellulase activity by each element was calculated from (S-B)/B*100, where S is
the glucose concentration or cellulase activity of salt-treated solution and B
is the glucose concentration or cellulase activity of the untreated solution.
Results reported here are averages of duplicate assays.
RESULTS
AND DISCUSSION
Results of the
effect of common salts on cellulase assays are shown in Table 1. Results
showed that, with few exceptions, most of the salts studied influenced the DNS
method in the assay of cellulase activity. The intensity of DNS color and/or
the reducing power of glucose in this method increased by addition of salts of
Na+, K+, and especially Ca+2 and Ba+2.
In contrast, the intensity of DNS color decreased by addition of NH4+
and surprisingly Mg+2 salts. The intensity of DNS color increases by
increasing the radius of alkaline-earth elements from magnesium to barium. So,
dependent on soil salinity and type of salts in soil, the measured soil
cellulase activity may be misrepresented. Measurements of reducing sugar in the
presence of Ca+2 and Ba+2 salts by DNS indicator with a
more intense color, overestimated and in the presence of Mg+2 salt
with a less intense color, underestimated the real contents.
Salts with same
cation and different anions had a different effect on the intensity of DNS
color changed by glucose. From table 1 it can be concluded that negative effect
of anions is in the order of MoO4=< SO4=<
Cl-< HCO3-< NO3-<
HPO4=< B4O7=.
Exoglucanase activity increased in the presence of Ca+2 and Ba+2
salts, but decreased in the presence of Na+, K+, NH4+
and Mg+2 salts. Deng and Tabatabai, (1995) by treating three
different soil with trace elements have shown that Ba+2, Co+2,
Mn+2, Ni+2, and W+4 against other trace
elements inhibited cellulase activity very low. However these results (as shown
before) may be related to the effect of these cations on the methods of
cellulase assessment. Unfortunately, these effects are not separated by
colorimetric methods.
Endoglucanase
activity has increased in the presence of Na+, K+, Ca+2,
and Ba+2 salts and decreased in the presence of NH4+
and Mg+2 salts. Generally, ions inhibited endoglucanase lower than
exoglucanase.
Table 1 Effect of different salts on determination of glucose
and cellulase activity *
Salts
|
Percentage of
inaccuracy in glucose determination
|
Percentage inhibition
of cellulase activity
|
Exoglucanase
|
Endoglucanase
|
NaCl
|
3.5
|
-20.1
|
11.9
|
KCl
|
0.0
|
-17.3
|
20.5
|
MgCl2
|
-27.7
|
-24.6
|
-21.3
|
CaCl2
|
30.7
|
14.6
|
29.8
|
BaCl2
|
43.4
|
41.9
|
28.3
|
NH4Cl
|
-13.8
|
-26.9
|
-15.3
|
Na2SO4
|
6.9
|
-22.5
|
0.0
|
K2SO4
|
0.0
|
-31.2
|
8.7
|
MgSO4
|
-20.8
|
-31.7
|
-25.7
|
CaSO4
|
27.7
|
-11.0
|
18.4
|
(NH4)2SO4
|
-6.9
|
-28.7
|
-21.3
|
NaNO3
|
-6.9
|
-16.9
|
13.2
|
KNO3
|
3.5
|
-20.2
|
12.6
|
Mg (NO3)2
|
-20.8
|
-34.8
|
-22.7
|
Ca (NO3)2
|
-17.3
|
-36.1
|
13.1
|
NH4 NO3
|
-24.2
|
-37.7
|
-14.9
|
Na2HPO4
|
-12.5
|
-17.6
|
-20.7
|
K2HPO4
|
-12.5
|
-16.9
|
-3.7
|
NaHCO3
|
-3.5
|
-28.2
|
-18.6
|
Na2MoO4
|
6.9
|
-23.2
|
-10.8
|
Na2B4O7
|
-59.9
|
-60.1
|
-34.4
|
*Each data
was calculated by (S-B)/B*100, in which: B is glucose concentration
or cellulase activity measured by DNS method in the blank solution
of glucose or cellulase (untreated with salts), and S is glucose
concentration or cellulase activity measured by DNS method in
the sample solution of glucose or cellulase (treated with a salt).
In saline soils
exoglucanase may be produce by microorganisms, but soil salinity may has a
higher effect on exoglucanase activity than endoglucanase activity. The
relative effectiveness of the trace elements in inhibition of cellulase
activity varied considerably, depending on the type of trace element applied.
Among the trace elements studied, Cu+2, Cd+2, and Hg+2
had negative effect on the intensity of DNS color and/or the reducing power of
glucose. Against them, Fe+3, Mn+2, Pb+2, Fe+2,
Ag+1, Zn+2, Co+2, and Al+3 had
positive effect on the intensity of DNS color and/or the reducing power of
glucose (table 2).
Exoglucanase and
endoglucanase activities only in the presence of Mn+2 salts
increased. In Deng and Tabatabai (1995) studies, Mn+2 was the least
inhibitor of cellulase activity assayed by the Prussian blue method. However a
part of inhibitory effect may be related to the specific effect of elements on
the method of enzyme assessment. Among the trace elements studied, Fe+3,
Pb+2, Fe+2, Ag+1, Zn+2, Co+2,
and Al+3 were the most effective inhibitors of cellulase activity.
Sensitivity of exoglucanase to trace elements was higher than that of
endoglucanase. Although, inhibition percentages of Hg+2, Cu+2,
and Cd+2 were relatively high but these may be related to negative
effect of them on the method of cellulase assessment.
Table 2- Effect of trace elements on determination of glucose
and cellulase activity *
Salts
|
Percentage of
inaccuracy in glucose determination
|
Percentage inhibition
of cellulase activity
|
Exoglucanase
|
Endoglucanase
|
FeCl3.6H2O
|
90.6
|
-53.6
|
-42.4
|
MnCl2.4H2O
|
46.0
|
42.7
|
16.8
|
HgCl2
|
-79.1
|
-88.0
|
-73.0
|
PbCl2
|
2.3
|
-27.2
|
-29.7
|
CoCl2.6H2O
|
16.0
|
-49.7
|
-6.4
|
AlCl3
|
3.9
|
-60.9
|
-43.8
|
FeSO4.7H2O
|
52.5
|
-17.9
|
-6.8
|
MnSO4.4H2O
|
69.5
|
63.1
|
37.8
|
ZnSO4.7H2O
|
16.9
|
-64.5
|
-20.2
|
CuSO4.5H2O
|
-24.0
|
-77.1
|
-39.9
|
Al2(SO4)3.18H2O
|
3.9
|
-65.7
|
-54.8
|
3CdSO4.8H2O
|
-17.5
|
-53.1
|
-46.1
|
Ag2SO4
|
27.4
|
-52.9
|
-43.4
|
Pb (NO3)2
|
59.8
|
-52.2
|
-45.4
|
Co (NO3)2.6H2O
|
16.0
|
-39.5
|
-7.7
|
*Each data was calculated by (S-B)/B*100, in which: B
is glucose concentration or cellulase activity measured by DNS
method in the blank solution of glucose or cellulase (untreated
with salts), and S is glucose concentration or cellulase activity
measured by DNS method in the sample solution of glucose or
cellulase (treated with a salt).
Deng and Tabatabai,
(1995) have reported that the degree of inhibition of soil cellulase activity
by most of the trace elements studied was much less than those reported for
inhibition of urease (Tabatabai, 1977). The lack of complete inhibition of cellulase activity in solution
by metal ions, especially Ag+1 and Hg+2, suggests that functional
groups other than sulfhydryl groups are involved in the active sits of enzymes
(exoglucanase and endoglucanase). It has been reported that at the active sites
of these enzymes there are hydrophobic amino acid (like tryptophan or tyrosine)
residues. They are not as readily complexed with trace metals as those
involving sulfhydryl groups.
Conclusion: Measurement of
reducing sugar in solution by DNS indicator in the presence of some ions overestimated
and in the presence of some other ions underestimated the real contents.
Results showed that the intensity of DNS color and/or the reducing power of
glucose increased by increasing radius of alkaline-earth cations. So, dependent
on soil salinity and type of cation or anion of a salt, assessment of cellulase
activity by colorimetric methods may be misrepresented. Exoglucanase and
endoglucanase activities in the presence of some ions (i.e. Na+, K+,
Ca+2, Ba+2, and Mn) increased and in the presence of many
other ions decreased. Fe+3, Pb+2, Fe+2, Ag+1,
Zn+2, Co+2, and Al+3 were the most effective
inhibitors of cellulase activity. Generally the effect of ions on exoglucanase
activity was more intensive than endoglucanase activity.
Generally, ions had
a noticeable effect on the intensity of DNS color and/or the reducing power of
glucose which can affect the cellulase activity determined. So, in the
colorimetric determination of cellulase activity in a salt treated solution the
percentage inhibition may be related to negative effect of ions on the method
of assessment. Unfortunately, the salt effects on cellulase activity and the
method of assessment can not be separated by colorimetric methods. If one ion
can change the properties of sugars, it will change the cellulase activity
determined by every colorimetric method. So, in the study of the effect one ion
on the enzyme activity, knowing the effect of ion on the method of enzyme assay
is very important for data interpretation.
REFERENCES
- Al-Khafaji, A.A., and Tabatabai, M.A. (1979) Effects of trace
elements on arylsulfatase activity in soils. Soil Sci., 127, 129-133.
- Badiane, N.N.Y., Chotte, J.L., Pate, E., Masse, D., Rouland, C.
(2001) Use of soil enzyme activities to monitor soil quality in natural and
improved fallows in semi-arid tropical regions. Appl. Soil Ecol. 18, 229238.
- Bandick, A.K. and Dick R.P. (1999) Field management effects on
soil enzyme activities. Soil Biol. Biochem., 31, 1471-1479.
- Deng, S.P., and Tabatabai, M.A. (1994a) Colorimetric determination
of reducing sugars in soils. Soil Biol. Biochem., 26, 473-477.
- Deng, S.P., and Tabatabai, M.A. (1994b) Cellulase activity of
soils. Soil Biol. Biochem., 26, 1347-1354.
- Deng, S.P., and Tabatabai, M.A. (1995) Cellulase activity of
soils: effect of trace elements. Soil Biol. Biochem., 27, 977-979.
- Dick, R.P. (1997) Soil enzyme activities as integrative indicators
of soil health, In: Pankhurst, C.E., Doube, B. M., and Gupta, V. V. S. R.,
(Ed.), Biological indicators of soil health. Cab International, pp. 121-150.
- Fu,
M.H., and Tabatabai, M.A. (1989) Nitrate reductase activity in soils: effects
of trace elements. Soil Biol. Biochem. 21, 943-946.
- Geiger, G., Brandl, H., Furrer, G., and Schulin, R. (1998) The
effect of copper on the activity of cellulase and -glucosidase in the
presence of montmorillonite or Al- montmorillonite. Soil Biol. Biochem., 30,
1537-1544.
- Juma, N.G., and Tabatabai, M.A. (1977) Effect of trace elements on
phosphatase activity in soils. Soil Sci. Soc. Am. J., 41, 343-346.
- Lee, Y.G., and Fan, L.T. (1980)
Properties and mode of action of cellulase. Adv. Biochem.Eng., 17, 101-129.
-
- Mandel
M. and J. Weber. (1969) Exoglucanase activity by microorganisms, Adv. Chem.
95:391-414.
- Miller,
G.L. (1959) Use of dinitrosalicylic acid reagent for determination of reducing
sugar. Analytical Chemistry. 31, 426-428.
- Nevalainen,
H., and Penttil, M. 1995) Molecular biology of cellulolytic
fungi, In: Kuck (Ed.), The mycota II. Genetics and biotechnology,
Springer-Verlag Berlin Heidelberg CO. pp. 303-319.
- Tabatabai,
M.A. (1977) Effects of trace elements on urease activity in soils. Soil Biol.
Biochem. 9, 9-13.
- Tyler, G. (1974) Heavy metal pollution and
soil enzymatic activity. Plant and Soil. 41, 303-311.
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