Cellulase I (17 U/mg (CMCase),crude enzyme used in feed additive) and cellulose II (200 U/mg (CMCase), Trichoderma reesei, purified enzyme used in laboratory) were purchased from Huamei Biochemical Company, Zhengzhou, China. Both materials were dipped in an enzyme buffer solution (0.2 mol/L Na-acetate buffer (pH 4.8)). The enzyme concentration in the reactive system was 0.1U CMCase. Carboxymethyl cellulose (CMC, medium viscosity) was purchased from Kermel Chemical Reagent Co. Ltd., Tianjin, China. Buffer salts and other reagents were bought from commercial sources.

Various concentrations of salts in the reaction systems were prepared as follows: NaCl and KCl (1, 10 and 100 mmol/L), or AlCl₃, MgCl₂, CaCl₂ and CoCl₂ (0.05, 0.1, 1, 5, and 10 mmol/L), CoCl₂ (100 mmol/L) and Na₂SO₄, Na₂CO₃ and CH₃COONa (0.1, 0.5 and 1 mol/L), respectively. In the enzymatic reactions, 0.2 mol/L of sodium acetate buffer solution (pH 4.8) was used.

The cellulolytic activity of complete cellulase and activeity of endoglucanase were determined by measurement of reduced sugars in the process of enzyme reaction with filter paper (filter paper activity, FPA) or carboxymethyl cellulose (carboxymethyl cellulase activity, CMCase).

FPA was determined according to the methods of Ghose [12] and Miller [13]. Briefly, Whatmen No. 1 filter paper (50 mg, 1 cm × 6 cm) was dipped into 0.2 mol/L acetate buffer (pH 4.8) with various concentrations of metal ions and anions and reacted with cellulase at 50˚C for 1 h. The enzymes were incubated with 0.2 mol/L acetate buffer (pH 4.8) for 10 min at 50˚C prior to measurement of the residual activity under standard assay conditions. The reducing sugar was measured using 3, 5-dinitrosalicylic acid (DNS) reagent with glucose as a standard. One unit of activity was defined as the amount of enzyme which liberated 1 μmol of reducing sugars, expressed as glucose equivalents per minute. Activity of CMCase was measured with various concentrations of metal ions and anions in 6.25 g/L CMC, 0.2 mol/L acetate buffer, pH 4.8 at 50˚C for 30 min [14]. The enzymes were incubated with 0.2 mol/L acetate buffer (pH 4.8) for 10 min at 50˚C before measurement of the residual activity under standard assay conditions. The reducing sugar content was analyzed using the same method described above.

The relative activity was expressed as the ratio of the specific activity of the enzyme with and without metals or anions.

Extrapolation of the linear relationship to zero gave the initial rate to be used for determining kinetic constants for the enzyme. Maximum velocity (V_max) and Michaelis-Menten constant (K_m) of the cellulase in the presence of Al³⁺ (0, 2.5 or 5.0 mmol/L), Mg²⁺ (0, 5.0 or 10 mmol/L) were determined using CMC (from 6.25 g/L to 3.125 g/L (that is 1/[S] from 0.16 to 0.32)) as substrate in 0.2 mol/L acetate buffer (pH 4.8). About 0.05 ml cellulase II (0.1U CMCase) was added and incubated at 50˚C for 30 min. The reducing sugar produced was measured colorimetrically with DNS reagent [9]. The V_max and K_m were calculated from double-reciprocal plots according to the method of Lineweaver and Burk [15].

In Equation 1 above, V₀: enzyme reative velocity, K_m: Michaelis-Menten constant, V_max: Maximum velocity, [S]: Sunstrate concentration.

An analysis of variance was performed on the data using the computer program SPSS 9.0 for windows (SPSS Inc.), and Fisher’s Protected Least Significant Difference Test was used at the 0.05 level to determine differences between treatment means.

Na⁺ and K⁺ had a significant effect on the activity of crude cellulase at the tested concentrations although the change in relative enzyme activity was not large (from +10% to –10%, Figure 1(a)), which was in an agreement with that reported by Mawadza et al. [8]. As shown in Figure 1(b), cellulase activity decreased at all tested

concentrations of Mg²⁺. The inhibition pattern of cellulase by Mg²⁺ differed from that reported by Saha [16]. The inhibition was enhanced with the increase of Mg²⁺ concentration. Calcium ion positively influenced the activity of cellulase at concentrations less than 1 mmol/L and negatively at more than 1 mmol/L.

The cellulase activity was increased at the concentration of Al³⁺ below 1 mmol/L (Figure 1(c)) but enzyme activity decreased sharply when Al³⁺ concentration was varied from 1 mmol/L to 10 mmol/L. The relative enzyme activity was only 5.7% ± 0.33% at 10 mmol/L AlCl₃. This indicated that the threshold of Al³⁺ on cellulase was 1 mmol/L. Similarly, the influence of Co²⁺ on crude cellulase was increased at below 1 mmol/L. However, unlike Al³⁺, the inhibition of Co²⁺ on cellulase was increased slowly with increasing ionic concentrations (Figure 1(d)).

The culture supernatant (crude enzyme) was found to contain a complete cellulase (endoglucanase, cellobiohydrolase, and β-glucosidase) produced by fungus, hydrolysed cellulose to glucose, indicating that the cellulase system from the fungal strain contained all three enzymes needed for producing glucose from cellulose and had great potential to be used in enzyme saccharification of various cellulosic substrates [16]. As enzymes were purified, their specific activity increased and complete cellulase became the single enzyme composition. Cellulase enzyme systems were not merely an agglomeration of enzymes representing the three enzyme groups, but rather acted in a coordinated manner to efficiently hydrolyze cellulose [17]. The whole cellulase activity was commonly represented by FPA including synergistic actions of the three components (EG, CBH, cellobiase) [14]. Carboxymethylcellulose (CMC) has been widely used as a substrate for studies of endoglucanase production. The single endoglucanase activity was often represented by CMCase [14]. Considering the complex action of cellulase system, this study investigated the influence of ions on cellulase based on the specific activities of two different enzymes.

The CMCase activity of the purified cellulase (cellulaseⅡ) was not significantly affected (the relative enzyme activities ranged from 99.11 ± 0.7 ~ 101.1 ± 0.99%) by natrium at the determined concentrations. The effect of Na⁺ on cellulase was weak. The activity of cellulase were reduced only to 2% when the concentration of Na⁺ was varied from 1 mmol/L to 1 mol/L. Cobalt ions had significant positive effects on the CMCase for the purified cellulase (cellulaseⅡ). The effects were increased with concentration increased. The relative activity of cellulaseⅡ was 157.2% ± 6.55% at 10 mmol/L of cobalt ion (Figure 1(d)). Similar result was reported by Mawadza et al. [8], but in the reverse trend was observed by Murashimaa et al. [9]. The activity of crude cellulase was increased at lower ionic concentrations and decreased at higher ones. On the other hand, results for the purified cellulase revealed that the activity of enzyme remained consistent in the presence of Na⁺, whereas it increased in the presence of Co²⁺ with increase of ionic concentration. These results might be due to different isoforms of the enzyme. During the purification the complete enzyme became single enzyme composition and the system was demineralized. There were different reactions in crude cellulase because of its complex components. The main factors were the ionic concentration and valence. There were positive correlation between the degree of inhibition and valence of metal ions. Based on the result that different metals had different effect of inhibition at the same concentration and valence (Na⁺& K⁺, Ca²⁺ & Mg²⁺, Figures 1(a) and (b)), we concluded that the ionic strength had less effect than ion itself on the cellulase.

The activity of cellulose I decreased when anion concentration increases whereas the activity of cellulose II was little affected (Figure 2) at the similar conditions. The pH of the reaction system varied from 9.59 to 11.13, which is far from the optimum pH (4.75 - 6.12) of cellulase activity. Upon addition of CH₃COO^– and, the pH varied from 4.75 to 6.12 and from 4.71 to 4.89, respectively. Higher pH caused enzyme deactivation. Because addition of altered the pH considerably, the enzymatic activity could not be detected even if its concentration gradient was basically the same as that of CH₃COO^–. This suggested that NaCO₃ might not be good for pretreatment in biomass before or at one time using cellulase. Considering the fact that the optimum pH of cellulase is 4.0 - 6.0, the inhibition by anions might not be simply ascribed to the change in pH [16]. As shown in Figure 2, the inhibition of CH₃COO^– was evident while sulfate ions had negative effects on cellulase, even if at the narrow pH range (from 4.71 to 4.89) and the reaction system did not change significantly. Cl⁻ did not change pH of the solution but also decreased the activity of cellulase. The optimum pretreatment condition for bioconversion of lodgepole pine to ethanol was 4% SO₂ (w/w) [18]. When wheat straw or corn stem were treated by HCl or H₂SO₄ the output of carbohydrate was increased with the concentration of acids, but if following with cellulase that was not. The optimum pretreatment acid concentrations were about 1% [11,19]. Our experimental results might supply a reason that high concentration of anions ions inhibited cellulases activity.

The kinetic lines intersected at the same point on the

horizontal axis, –1/K_m. Maximum rate of reaction in the presence of Al³⁺ was significantly lower as compared to that without Al³⁺. The calculated K_m was 22.68 ± 0.28 g/L and V_max was 0.269 ± 0.066 mg/min at 5.0 mmol/L of Al³⁺; 0.376 ± 0.012 mg/min at 2.5 mmol/LAl³⁺; and 0.425 ± 0.013 mg/min at 0 mmol/LAl³⁺, respectively. These data indicated that Al³⁺ acted as a non-competitive inhibitor for cellulase (Figure 3(a)), which might be caused by conformational changes in the enzyme structure contributed by Al³⁺. The kinetic lines of Mg²⁺ (Figure 3(b)) intersected at the same point on the vertical axis. The value of K_m in the presence of Mg²⁺ was greater than those without Mg²⁺. The V_max value was approximately 0.434 ± 0.038 mg/min in the presence of Mg²⁺ (K_m = 22.74 ± 0.412 g/L at 0 mmol/L Mg²⁺, 33.0 ± 0.454 g/L at 5.0 mmol/L Mg²⁺, and 50.0 ± 0.280 g/L at 10 mmol/L Mg²⁺, respectively). These data indicated that the Mg²⁺ acted as a competitive inhibitor of cellulase. In the presence of Mg²⁺ the cellulase was an apparent lower affinity for the substrate than that without Mg²⁺. The slope of the linear regression increased as ionic concentration increased.

Based on these results, it was evident that univalent cations (Na⁺ and K⁺) were less influence but the divalent cations (Ca²⁺ and Mg²⁺) were varying levels of influence on cellulase, even as both of them are alkaline earth metals. From the data presented in Figure 3, the kinetic character of Mg²⁺ was a competitive inhibitor of cellulase. Endoglucanases had two conserved glutamate residues at the active site [8]. Metal ions might bind to these residual radicals to impact on cellulase activity. Mg²⁺ might combine with electronegative glutamate residues reversibly binding to the active site of enzyme, leading to changes in the enzymatic catalytic activity. On the other hand, cellulase was very active during reaction with acidic and hydroxylated amino acids, except for glutamate residues. Aspartate residues were common components of cellulase structure [11]. Unlike Mg²⁺, Al³⁺ caused non-competitive inhibition on cellulase. In presence of AlCl₃ the V_max value were lowered, and the K_m value not changed compared to the control (Figure 3). In noncompetitive inhibition, the inhibitor bound to enzyme at a site other than the active site [20]. Therefore, Al³⁺ might increase cellulase activity by changing enzyme dimensional structure at lower concentrations. When the changes reached a certain degree, the enzyme activity might decrease substantially and result in an Al³⁺ threshold effect.

In summary, the activity of cellulase was increased or slightly decreased by the tested ions at concentration below 1 mmol/L of metals, and inhibited strongly at concentration above 10 mmol/L of metals and 500 mmol/L anions. Enzyme kinetic analysis indicated that Mg²⁺ was a competitive inhibitor and Al³⁺ was a noncompetitive

inhibitor of cellulase, respectively. Their inhibition features were correlated with their concentrations. The inhibition produced by metal ions and anions exhibited less potent on pure enzyme than on crude one. The inhibition produced by metals with higher ionic valence was more potent on cellulase than the metals with lower ionic valence. It should be noted that the effect of metal ions and anions on activity of cellulase might vary by different detecting methods and purity of enzymes. The results indicated that FPA was a better method to estimate cellulase in enzymic saccharification of various lignocellulosic substrates. Crude cellulases should be more suitable for bioethanol industrial biodegradation of cellulosic fibers by virtue of their reaction to ions and complete enzyme.