Open Access

Improving the performance of enzymes in hydrolysis of high solids paper pulp derived from MSW

Biotechnology for Biofuels20136:107

DOI: 10.1186/1754-6834-6-107

Received: 10 May 2013

Accepted: 23 July 2013

Published: 25 July 2013



The research aimed to improve the overall conversion efficiency of the CTec® family of enzymes by identifying factors that lead to inhibition and seeking methods to overcome these through process modification and manipulation. The starting material was pulp derived from municipal solid waste and processed in an industrial-scale washing plant.


Analysis of the pulp by acid hydrolysis showed a ratio of 55 : 12 : 6 : 24 : 3 of glucan : xylan : araban/galactan/mannan : lignin : ash. At high total solids content (>18.5% TS) single-stage enzyme hydrolysis gave a maximum glucan conversion of 68%. It was found that two-stage hydrolysis could give higher conversion if sugar inhibition was removed by an intermediate fermentation step between hydrolysis stages. This, however, was not as effective as direct removal of the sugar products, including xylose, by washing of the residual pulp at pH 5. This improved the water availability and allowed reactivation of the pulp-bound enzymes. Inhibition of enzyme activity could further be alleviated by replenishment of β-glucosidase which was shown to be removed during the wash step.


The two-stage hydrolysis process developed could give an overall glucan conversion of 88%, with an average glucose concentration close to 8% in 4 days, thus providing an ideal starting point for ethanol fermentation with a likely yield of 4 wt%. This is a significant improvement over a single-step process. This hydrolysis configuration also provides the potential to recover the sugars associated with residual solids which are diluted when washing hydrolysed pulp.


Lignocellulose Cellulases Enzyme hydrolysis High solids hydrolysis Municipal solid waste (MSW) Bioethanol


Production of bioethanol as a transport fuel is predicted to reach 100 billion litres in 2015[1]. At present the demand is met using first generation bioethanol crops such as sugar cane and corn. In the near future, however, it is envisaged that second generation bioethanol made from lignocellulosic materials will begin to contribute. The conversion of these materials to fermentable sugars has been researched widely over the last few years. The final steps required to make the process economic at a commercial scale are linked to achieving glucose concentrations that match the downstream processing requirements for ethanol extraction. Larsson and Zacchi (1995) showed that costs for continuous distillation of ethanol do not rise significantly once an ethanol concentration above 40 g kg-1 (4% wt) has been achieved[2]. This requires an 8% wt sugar solution as a starting point for the fermentation, which for many feedstocks is equivalent to an initial lignocellulosic total solids (TS) content of ~20%[3]. Future large-scale production of ethanol from lignocellulosic biomass will therefore require enzyme hydrolysis at high solids contents, and demand not only high conversion yields but also high sugar concentrations in the hydrolysate.

Meeting these requirements presents some challenges, as hydrolysis at high total solids concentrations can lead to a decrease in substrate conversion, sometimes referred to as the ‘solids effect’[46]. Explanations for this include: insufficient mixing[7]; product inhibition as a result of increasing sugar concentration[8, 9]; decreased water availability[10, 11]; irreversible binding of adsorbed enzyme to the substrate, including non-productive binding to lignin[6, 12]; inhibition of enzyme adsorption[5]; and enzyme denaturation[6]. There may also be other, as yet unidentified, reasons for decreased conversion.

Limitations on mixing due to the high viscosity or nature of the substrate are an important aspect of the ‘solids effect’. One method to overcome these is the use of gravity or tumbling mixing, which has been shown to be a superior strategy compared to shaking at high solids concentrations[7]. An alternative strategy is fed-batch substrate addition which reduces the initial viscosity to allow improved mixing, and may therefore decrease the required processing times[13].

Product inhibition is one of the major limitations in realising the full potential of enzymic hydrolysis, as cellulase-containing enzyme preparations are inhibited by glucose and cellobiose[8, 14]. For this reason continuous removal of glucose through simultaneous saccharification and fermentation (SSF) was once thought to be the best way of obtaining reasonable titres of ethanol within relatively short process times. Many researchers today continue to believe that this is the best option[1517]. As the efficacy of commercial enzymes continues to improve, however, it must be questioned whether it is necessary to forgo optimal hydrolysis conditions, as is invariably the case when SSF is used[18]. Even though SSF can overcome the problem of glucose inhibition it has a further slight drawback, as ethanol can also inhibit the enzyme activity. This has been clearly shown for those cellulases taken from cultures of Trichoderma Resei used at 30°C[19, 20].

When dealing with concentrated sugar solutions, water availability must also be considered. As product sugars and other soluble compounds are released during hydrolysis they bind water, making it unavailable for the enzyme system. This effect has been demonstrated by replacing glucose with mannose, which does not directly inhibit the cellulase system, but its affinity for water makes this unavailable for the enzymes and hence reduces their performance[10]. It has also been shown that as the soluble content of the hydrolysate increases the effect is to pull water away from the surface of insoluble solids, limiting the activity of the enzymes on that surface with a consequent reduction in hydrolysis yield[11]. One method that has been shown to decrease product inhibition and/or increase water availability is the utilisation of membrane reactor systems which remove monomeric sugars after they are produced[21, 22]. Most of the published studies use a low concentration of total solids, however, which is unsuitable for industrial application.

Although enzymes are simply catalysts in the process, and can therefore theoretically be re-used, in practice this may be difficult due to denaturing, inhibition, or irreversible binding to the substrate or other non-targeted materials. The extent to which this occurs depends on the make-up of the enzyme mix. Most commercial enzyme preparations contain a mixture of enzymes and their associated binding domains, to ensure a strong affinity with the substrate and its sub-components[23, 24]. Cellulases tend to bind strongly to the substrate and after hydrolysis remain associated with the solid fraction. Weiss et al. (2013) showed that by recycling 85% of the insoluble residual solid with its bound enzymes, plus fresh substrate at 15% TS, the subsequent enzyme requirement could be reduced by 30%[25]. A commercial cellulase enzyme preparation will also contain β-glucosidase which cuts cellobiose and cellotriose into glucose monomers[26]. This enzyme is not bound to the substrate, and will partition into the sugar solution after hydrolysis. Cellulases have been used for up to four rounds of hydrolysis[27] whereas β-glucosidase is known to be less stable over prolonged or multistage reaction periods[28]. All enzymes in a commercial cellulase preparation may non-productively bind to lignin making them unavailable for hydrolysis[12] and they can also be inhibited by the presence of hemicellulosic components[8, 29]. Various strategies have been tested to overcome these inhibitive parameters including; pre-treatment to remove lignin and hemicellulose[3033], addition of compounds which reduce non-productive binding[34, 35] and the use of simultaneous saccharification and co-fermentation[36]. A detailed discussion of the enzyme system and its limitations can be found in a recent review by Van Dyk et al. (2012)[24].

If lignocellulosic material is to form the primary substrate for a sugar platform biorefinery then a number of factors need to be considered in relation to the product stream. Although the percentage conversion to sugar is a prime consideration, there is also a requirement to produce a high sugar concentration in the hydrolysate[2]. There must therefore be a trade-off between conversion efficiency, conversion rate, and product concentration. Yang et al. (2010 & 2011) showed that it is possible to obtain a very high substrate conversion (85%) in a period of 24 hours using a 3-stage hydrolysis system with intermediate washing steps[9, 37]. The sugar stream arising from each stage, however, contained a maximum sugar content of ~5.5% or 55.5 g L-1, which is below the ideal value for further fermentation. Once fermented, a hydrolysate of this strength would contain less than 4% wt ethanol, unless the sugar stream was first concentrated by methods such as multiple-effect evaporation or nanofiltration[38] that would reduce the net energy yield.

One reason for enhancing the performance of enzymes is the cost barrier they present to making cellulosic ethanol a commercial reality. It is estimated that the cost of commercially available enzymes still makes up at least 15% of the total cost of lignocellulosic ethanol production[39]. The current research thus aimed to examine a number of inter-dependent factors that control enzyme efficiency and can be manipulated to improve overall performance and product quality. The overall goal of the work was to maximise the efficiency of enzyme use to obtain a concentrated sugar solution from waste feedstock as a sugar platform for a waste biorefinery, without compromising yields or prolonging process times.

Results and discussion

Sugar potential of MSW pulp and control

On acid hydrolysis[40] the pulp derived from MSW yielded 55 : 12 : 6 : 24 : 3 of glucan : xylan : araban/galactan/mannan : lignin : ash respectively, while the control filter paper substrate yielded a 84 : 14 : 2 mix of glucan : xylan : araban/galactan/mannan. The MSW derived paper pulp showed a lignin concentration of 24% when compositional analysis was performed using the standard NREL method[40]. Analysis by the FibreCap method[41] showed, however, that only half of this is lignin of plant origin. The remaining portion is unclassified organic matter which was thought to be inert and did not interfere with enzyme hydrolysis.

Enzyme dosing and substrate feeding strategy

Preliminary experiments using different enzyme addition strategies were carried out to establish the best procedure for enzyme dosing when using the MSW pulp. In these the enzyme preparation was added either directly or mixed with dilution water at a 1:145 ratio of enzyme : pH 5 water. In both cases the hydrolysis was carried out at a TS concentration of 15% for a 48-hour period. The glucan conversion was equivalent in each case, at 67.3 ± 0.03 for direct addition and 66.8 ± 0.02 when diluted. This result confirms that mixing by tumbling allowed even distribution of the enzyme within the pulp.

A fed-batch experiment, in which the same total amount of solid was added but in equal aliquots at hourly intervals, was also trialled in this study but did not show any major advantage over batch addition as there was no increase in the final hydrolysis conversion, only a slightly faster initial liquefaction rate. There was also no increase in conversion when a split batch configuration was used, with half the substrate and enzymes added 6 hours after the first half. As no advantage could be seen at laboratory scale in using either a fed or split batch mode of operation, all further hydrolysis experiments were carried out in batch mode with mixing by tumbling.

Two-stage hydrolysis with intermediate fermentation

One aim of this experiment was to assess the effect of changing the length of the hydrolysis cycle and its effects on subsequent glucan conversion. Initial tests were run at 18.5 and 20% TS to determine the time required to achieve a glucose concentration of 8% wt in the hydrolysate. This was 48 hours with 18.5% TS, and 72 hours at 20% TS. The experiment was therefore run at 18.5% TS for 48 hours. The results are shown in Figure 1 and it can be seen that with an initial 48-hour hydrolysis stage the glucose concentration in the hydrolysate was 8.8 ± 0.2% wt. This was then fermented for 24 hours, yielding an ethanol concentration of 2.9 ± 0.6% wt. The yeast was not removed and reaction conditions were then optimised for a secondary hydrolysis (50°C, mixing by tumbling). After a total of 5 days an additional 1.8 ± 0.2% wt of glucose was found in the reaction mixture, giving the potential for a total ethanol yield over the two cycles of ~6 wt%.
Figure 1

Evaluation of the effect of an intermediate fermentation step using MSW pulp at 18.5% TS: a) percentage of glucose in hydrolysate, b) overall substrate conversion. No fermentation (−), fermentation following an initial 24 hour hydrolysis (− −), and fermentation following an initial 48 hour hydrolysis (−).

In a second experiment the initial hydrolysis cycle was reduced to 24 hours. This gave a lower glucose concentration of around 6.5% wt in the first hydrolysis, which was subsequently converted to 1.8 ± 0.3% wt of ethanol. This was followed by a second hydrolysis stage, which was much faster and yielded around 3% wt additional glucose within 48 hours, rising to ~4% wt over the 6-day hydrolysis period, giving a further 3.7 ± 0.3% wt of ethanol. The total ethanol concentration for the combined two-stage process was 4.2 ± 0.3% wt in a 4-day hydrolysis period and 5.5 ± 0.3% over the total 6-day hydrolysis period. In terms of percentage glucan conversion both two-stage systems gave a higher conversion than was achieved in the 18.5% TS control, as can be seen in Figure. Both the 24 and the 48-hour first stage hydrolysis procedure gave similar final yields, corresponding to total glucan conversions of 76.5 ± 0.5% and 73.1 ± 1.7% respectively (Figure 1b), compared to 68 ± 0.5% in the single-stage hydrolysis control over the same time period. There may be a slight advantage in using the 24-hour initial hydrolysis as early production of ethanol helps to maintain sterility within the system.

The rate of reaction in the second cycle following 24-hour hydrolysis was higher than after the 48-hour initial hydrolysis, and this tends to support the observation made by Pribowo et al. (2012), who suggested that if enzyme recycling is to be undertaken then it should be carried out within 24 hours[42]. The estimated ethanol yield in the second stage of the 48-hour hydrolysis experiment was based only on conversion of the glucose: in all the experiments the hydrolysate also contained up to 1.8% wt xylose, which could potentially be fermented to give additional ethanol if a C5/C6 fermenting strain were used.

The system above works to alleviate product inhibition, but of greater concern is the effect of non-metabolised sugars and other soluble compounds in the hydrolysate/fermentation broth on water availability, as this can also have a negative effect on hydrolysis.

Two stage hydrolysis with intermediate wash step

When working at high solids concentrations in the hydrolysis stage there is a significant retention of liquid within the residual solids[43]. In a 48-hour hydrolysis test using pulp at an initial 20% TS it was possible to centrifuge the residual solid to 40% TS: the same TS concentration was obtained by centrifugation between 2000–13,000 g. This meant that 65% of the hydrolysate liquid was extractable whilst 35% remained with the solid, representing a considerable amount of unrecovered sugar which may inhibit second stage hydrolysis. To overcome this, after removing the concentrated sugar solution by centrifugation, the residual sugars retained in the solids were removed by washing at pH 5 before being re-suspended in pH 5 phosphoric acid solution for second stage hydrolysis without further enzyme addition.

The results showed that when a pulp of 18.5% TS was hydrolysed for 48 hours with 55 mg CTec3 g-1 pulp and washed at pH 5, the sugar concentration in the residual solid was reduced from ~9.5% to ~1% (Figure 2a). On second stage hydrolysis of the re-suspended solids a further 14% of glucan could be converted, taking the total conversion efficiency from 67.2 ± 1.3% to 81.2 ± 0.7% (Figure 2b). This effect was thought to be due to an improvement in water availability by removal of the residual sugars, allowing enhanced enzyme activity in the second stage.
Figure 2

Effect of intermediate washing and β-glucosidase enzyme addition on MSW pulp (18.5% TS) hydrolysis: a) percentage of glucose in hydrolysate, b) overall substrate conversion. Unwashed control (−), washed without β-glucosidase addition (−); washed with β-glucosidase addition (− −).

Enzyme recovery through hydrolysate pulp washing

To see whether enzymes as well as sugars were recovered, the washwater was tested for enzyme activity using the filter paper and β-glucosidase activity tests. The tests were carried out with washwaters at pH 5 and 9. The results showed that the cellulase and β-glucosidase activities in the pH 9 washwater were 2.0-3.5 times higher in the washwater at pH 9 than at pH 5. These results are in accordance with those of other researchers who have shown higher enzyme recovery in alkaline conditions[44, 45]. It was noted, however, that recovery at the higher pH still only accounted for ≤ 10% of the original FPA enzyme activity. This suggests that most of the cellulase enzyme remains with the pulp and recovery is not feasible. Analysis of the hydrolysate from the secondary hydrolysis showed a slight increase in cellobiose concentration as compared to the initial hydrolysis, indicating a loss of β-glucosidase from the solid faction. This adds support to previous evidence that this enzyme does not bind to the substrate[28]. 15% of the original β-glucosidase activity from the CTec3 preparation was recovered in the pH 5 wash, whereas 30% was recovered in the pH 9 wash. These values do not include any recovered but denatured enzyme, however, which could account for a significant portion of the β-glucosidase initially added[28]. As the cellulase enzymes primarily remain with the pulp, these results indicated that it might be more beneficial to recycle the pulp with its bound enzymes rather than trying to recover enzymes in the washwaters only, as has been the focus in other research[46, 47].

Improving secondary hydrolysis by β-glucosidase addition

The two stage hydrolysis experiment with intermediate wash step indicated that a proportion of the β- glucosidase was removed in the washing process. This enzyme is important as it is required to convert cellobiose to glucose and it was thought that the action may release cellobiose from the active sites of cellobiohydrolases, and thus facilitate the processive action of the enzymes[48]. Thus it is an essential component in reactivation of the enzyme systems, and if the depletion observed as a result of washing could be replenished an even higher glucan conversion might be achieved. In this experiment β- glucosidase was therefore added as a single enzyme component to the make-up water after the pH 5 wash, at two different concentrations.

When β- glucosidase was added at 12.5 mg g-1 of original pulp no significant effect was seen, but at 25 mg g-1 of original pulp there was a marked increase in glucose concentration giving a hydrolysate with > 5% wt glucose, as shown in Figure 2a. The final glucan conversion following this addition was 88% (Figure 2b). This conversion yield was verified by measuring the weight loss of the substrate which was found to be 87.8%, thus confirming the result.

The final glucose concentration from the two-stage hydrolysis would be ~7.5%, obtained by mixing the concentrated sugar stream (~10%) from the first hydrolysis prior to the washing step with the sugar stream from the second stage hydrolysis (~5%). This is just below the preferred starting point for fermentation, but there is clearly considerable potential for optimisation of the system. Furthermore, this result can be achieved in a 4-day period compared to the 7 days required to obtain a similar yield using the two-stage hydrolysis with fermentation approach.

The experiment was repeated with a second batch of pulp at a slightly higher initial TS concentration of 20 % and a lower initial enzyme dose of 50 mg CTec3 g-1 pulp. The same response to β-glucosidase addition was noted; however the final glucose concentration was lower, possibly due to increased solids effects coupled with the slightly reduced enzyme dose. The final sugar concentration of 6% from mixing the primary and secondary hydrolysates was also lower than ideal. This variability clearly shows both the need for optimisation and for careful control of process conditions.

In addition to showing the positive effect of β-glucosidase on glucan conversion, the results also suggest that the enzyme solution may contain some xylanase. As seen in Figure 3, when β-glucosidase was not added or when it was added at a low concentration of 12.5 mg g-1 original pulp, the xylose in solution did not increase; whereas when β-glucosidase was added at 25 mg g-1 original pulp there was an increase in xylose within the solution which coincided with the increased glucan conversion. Varnai et al. (2010) showed that even a very small amount of xylan, 0.34% on a TS basis, can limit the hydrolysability of a lignocellulosic substrate: adding xylanases to their system gave a 12% increase in cellulose hydrolysis[49]. Other researchers have also shown the detrimental effect of xyloligomers on cellulose hydrolysis and have demonstrated the synergistic effect that can occur when xylanases are added to a cellulase enzyme mix to help increase cellulose conversion[29, 33, 50]: these studies indicate the importance of the xylan distribution and its role in limiting enzyme hydrolysis.
Figure 3

Effect of different β-glucosidase additions on hydrolysate xylose concentration. No enzyme post wash [PW] (−), 12.5 mg β-glucosidase g-1 original pulp (−), 25 mg β-glucosidase g-1 original pulp (− −).

Reuse of washwater as a means of reclaiming its sugars and enzyme activity

Hydrolysate pulp washing was necessary as the residual sugars are known to be inhibitory to cellulases; they do however represent a valuable product. It was therefore important to determine the sugar concentration within the pulp at which inhibition occurred. This was tested for Cellic CTec3 using pulp at 6.5% TS spiked with glucose concentrations from 3.3-6% wt. The test was carried out against controls without glucose addition using both pulp and filter paper. The results are shown in Figure 4 and indicate that an initial glucose loading of 3.3% wt did not cause major inhibition over a 48-hour hydrolysis period, regardless of the enzyme dosing used. At 6% wt initial glucose loading, however, significant inhibition was seen. This information was used to establish the minimum amount of water for post hydrolysis washing that would allow re-use of the washwater for dilution of a new batch hydrolysis.
Figure 4

Effect of initial glucose concentration on final glucan conversion over 48 hours.

To test this, pH 5 washwater after hydrolysis of pulp at 20% TS was used as part of the dilution medium in preparing a new batch of pulp for hydrolysis, giving an initial glucose concentration of 1.05% wt. It was found that the conversion efficiency over a 48-hour period was the same as with no initial sugar, but the final sugar yield was higher due to the initial glucose content (Figure 5). This approach also ensures that the low but still present enzyme activity in the washwater is utilised.
Figure 5

Effect of the re-use of washwater as dilution water for a new batch of hydrolysis. Control with dilution by pH 5 water (−), dilution with pH 5 washwater containing residual 1.05% wt glucose (−).

Overall discussion

Table 1 compares the 4-day single stage results in terms of glucan conversion with those obtained from both intermediate fermentation and intermediate wash strategies. Two-stage hydrolysis with intermediate fermentation improved glucan yield but this was more successful with a 24-hour than 48-hour initial hydrolysis, indicating that product inhibition was less likely to occur when glucan conversion was more evenly distributed between the two stages. The use of an intermediate wash step that removed residual sugars from the substrate produced an even higher glucan conversion, confirming that water availability may have been a key factor in reducing the activity of enzymes retained on the solid fraction.
Table 1

Comparison of all two stage hydrolysis systems after 96 hours of hydrolysis

Experimental condition

% Conversion in primary hydrolysis

% Total conversion after secondary hydrolysis

% Conversion improvement compared to control

A. Single stage hydrolysis (96 hours)

68.0 ± 5



B. Two-stage hydrolysis with intermediate fermentation (24-hour initial hydrolysis)

46.5 ± 0.36

76.5 ± 0.5

8.5 ± 0.5

C. Two-stage hydrolysis with intermediate fermentation (48-hour initial hydrolysis)

65.8 ± 0.3

73.1 ± 1.7

5 ± 1.7

D. Two stage hydrolysis with intermediate wash step

67. 2 ± 1.3

81.2 ± 0.7

13.2 ± 0.7

E. Two stage hydrolysis with intermediate wash step and β-glucosidase addition

67.2 ± 0.8

87.6 ± 0.4

19.6 ± 0.4

The most significant result was obtained when β-glucosidase was replenished after the first stage hydrolysis as this apparently helped to reactivate cellulases that were bound to the substrate. Using this strategy gave a higher glucan conversion at a lower enzyme dose than in many other high solids hydrolysis studies[5153]. The importance of obtaining a concentrated sugar solution from this high conversion yield should also be noted. The liquid hydrolysate stream from an intermediate wash strategy may not require a concentration step prior to fermentation, saving on energy costs and allowing higher net ethanol yields per tonne of substrate. Moving away from SSF to a separate hydrolysis process also opens up opportunities for use of the concentrated sugar stream for other biorefinery applications beside ethanol production[54].


Sugar product inhibition could be alleviated using two-stage hydrolysis with an intermediate fermentation step where both hydrolysis and fermentation were performed under their optimum process conditions. Carrying out a 24-hour fermentation step after an initial 48-hour hydrolysis and then readjusting the system for a further hydrolysis step gave a 9% increase in glucan conversion, as compared to a control that did not undergo fermentation.

Washing the residual solids at pH 5 to remove sugars allowed the solid-bound enzymes to show further activity, giving a potential 14% increase in conversion compared to a control without washing. This was attributed to increasing the water availability in the system, by removing xylose and other soluble compounds.

Replenishment of β-glucosidase lost in the washing process further boosted conversion, resulting in a glucan yield of ~88%. Mixing the hydrolysates from the primary and secondary hydrolysis (before and after the wash) gave a glucose solution of just less than 8% wt, the minimum starting point for fermentation, after only 4 days. Furthermore this strategy also allowed the washwater to be re-used for dilution of a new batch of material for hydrolysis. It was found that a glucose concentration of < 3% wt did not cause significant product inhibition of Cellic CTec3. Thus returning glucose at a concentration of 1-2% into a new batch hydrolysis augmented the glucose concentration without affecting the rate of reaction.



Municipal solid waste pulp

This was provided by Fiberight Ltd from its pilot plant in Lawrenceville, Virginia, USA. The municipal solid waste (MSW) had been first autoclaved and then washed to remove plastic, metals and mineral contaminants, and was supplied at a total solids (TS) content of 30.0 - 37.5% after mechanical dewatering.

Control substrate

Fisher Brand filter paper (Cat no. FB59035, Fisher scientific, Loughborough, UK), was used as a defined source of paper cellulose without lignin and ash.

Enzymic hydrolysis

Enzyme, reaction mixture and conditions

The commercial cellulase mixture Cellic CTec3 (Novozymes, Copenhagen, Denmark) was used for hydrolysis. The reaction medium was water adjusted to pH 5 with phosphoric acid. Hydrolysis was carried out in Nalgene™ PPCO centrifuge bottles to which the substrate was added at a concentration of 18.5 or 20% TS before being autoclaved at 121°C for 15 minutes. Once cooled the substrate was charged with Cellic CTec3 enzyme at a concentration of 50–55 mg per g of substrate, equivalent to 6 – 6.5 FPU g-1 dry substrate. The mix was then incubated at 50°C in a tumbler mixer at 33 rpm. Hydrolysis was allowed to proceed for periods of up to 8 days, with 0.2 ml samples being taken at regular intervals after centrifugation at 5000 g for 5 minutes. The sugar content of the samples was determined by high performance anion exchange chromatography with pulsed amperometric detection (HPAEC-PAD).

Enzyme assays

Filter paper activity (FPA), and β-glucosidase activity were measured using methods adapted from that of Ghose (1987)[55].

Filter paper activity was used to determine cellulase activity of recovered enzymes from hydrolysate after separation by ultrafiltration. Whatman No. 1 filter paper was cut into strips weighing 50 mg. A strip was placed into a test tube with 1 ml of water adjusted to pH 5 with phosphoric acid and equilibrated to 50°C. 0.5 ml of the ultrafiltered test solution was then added, and the mixture was incubated at the same temperature for 1 hour. Further reaction was stopped by placing the tubes in boiling water for 5 minutes, and the glucose concentration was measured by HPAEC. All assays were carried out in triplicate..

β-glucosidase activity was measured by adding 1 ml of a 19.6 mmol L-1 cellobiose solution at to 1 ml of ultrafiltered enzyme solution, both at 50°C. The mixture was incubated in test tubes at 50°C for 1 hour. The reaction was quenched by placing the tubes in boiling water for 5 minutes. The glucose released was measured by HPAEC. All assays were performed in triplicate.

The tests were standardised by comparison to the FPA and β-glucosidase activity of CTec3 at a dilution of 1 g enzyme preparation per 80 g of pH 5 water, as this was the enzyme concentration used in this study. Cellic Ctec3 had an FPU of 120 ml-1. As the protein concentration could not be determined in the ultrafiltered solution the β-glucosidase activity of the recovered enzyme was compared to that of the fresh enzyme which could produce 8.4 mg glucose per minute per g of enzyme preparation.

Sugar analysis

Sugar potential and MSW compositional analysis

The sugar composition of the MSW pulp was determined using the NREL method for ‘Compositional analysis of structural carbohydrates’[40]. 0.3 g of pulp was hydrolysed for 1 hour at 30°C with 4.92 g of 72% sulphuric acid. After this the sulphuric acid was diluted to 4% with deionised water, and the mixture placed in an autoclave for 1 hour at 121°C. The residual solids were filtered from the solution, which was analysed for sugar content using HPAEC. The residual solid was dried overnight at 105°C and the dry weight was taken as the lignin and ash content. The solid was then placed in a furnace at 550°C for 2 hours to determine the ash content, and the lignin component was taken to be the total solid minus the ash.

HPAEC - PAD. Samples for sugars determination were placed on ice as soon as they were taken, and if not analysed immediately were frozen. Before analysis both fresh and defrosted samples were centrifuged at 13,000 g for 7 minutes in a Galaxy 16DH centrifuge (VWR, UK). The supernatant was diluted and placed in a 5 ml sample vial with a 0.45 μm nylon filter cap. Sugar analysis was carried out on a Dionex DX-500 system using a method adapted from that of Davis (2008)[56]. In this glucose, xylose, galactose, arabinose, mannose and cellobiose were separated at 30°C on a CarboPac PA1 column (250 × 4 mm) in combination with a CarboPac guard column (25 × 4 mm) (Dionex, Sunnyvale, CA, USA). The mobile phase components were 200 mmol L-1 sodium hydroxide (A), distilled water (B) and 170 mmol L-1 sodium acetate in 200 mmol L-1 sodium hydroxide (C). The system set up used a 2.5 μL sample loop and 300 mmol L-1 sodium hydroxide post-column eluent at a pressure of 2.76 bar to aid sugar detection.

Separation of enzyme from sugar solution


this was carried out using an AKTA crossflow automated filtration system (GE Heathcare Life Sciences, Uppsala, Sweden). Samples were first filtered through a mesh with a pore diameter of 0.5 mm. The filtered liquid was then run through a 500 kD hollow fibre with a 1 mm lumen i.d. The flow was shear controlled at 8000 s-1 with a trans membrane pressure (TMP) of 0.5 bar. The permeate product was collected and used as the feed for a Kvickstart cassette with a 10 kD cut off and flux controlled at a TMP of 1 bar to separate the enzymes from the sugars.


All ethanol fermentations used Youngs’ super wine yeast compound (Youngs, Bilston, UK). 1 g of yeast was cultured for 24–72 hours in 200 ml of pH 5 basal medium containing 30 g L-1 glucose and 10 g L-1 yeast extract. The yeast was harvested by centrifuging a portion of the fermentation broth. Once centrifuged the supernatant was removed, leaving a wet yeast pellet of 1.7 g which was re-suspended in 2 ml of pH 5 solution. This suspension was then added to centrifuge bottles containing hydrolysate, following a nitrogen purge. Fermentation was carried out over 24 hours at 30°C with orbital shaking.

Experimental design to test performance improvements resulting from interventions or changes in conditions

Two-stage hydrolysis with intermediate fermentation

Pulp was hydrolysed for 24 or 48 hours followed by a 24-hour fermentation that was sufficient to consume most of the sugar produced. After fermentation, the reaction medium was readjusted to pH 5 to give optimum conditions for hydrolysis, and incubated with tumbling at 50°C for a further period of between 2 and 5 days. During all stages samples were taken for quantification of the type and yield of individual sugars, from which ethanol yield could be calculated. The experiment was carried out at pulp concentrations of 18.5 and 20% TS.

Two stage hydrolysis with intermediate wash step

After primary hydrolysis of MSW pulp for 48 hours the hydrolysate was centrifuged and the supernatant, consisting of the concentrated sugar solution, was separated from the residual solid. The residual centrifuged pulp was then washed once for 1 hour with 100 ml of water at either pH 5 or pH 9. The enzyme activity of the supernatants was determined by first separating the enzymes from the sugars by ultrafiltration and then by assaying the filter paper and β-glucosidase activity.

The washed residue was re-suspended in a pH 5 solution (volume equivalent to the removed sugar solution) and, without the addition of further enzyme, was then incubated at 50°C and tumbled to promote second stage hydrolysis. Samples were removed from the hydrolysis reaction mixture at regular intervals and assayed for their sugar concentration using HPAEC.

Reuse of washwater as a means of reclaiming its sugars and enzyme activity

The washwater from the enzyme recovery experiment above was used as dilution water for a fresh batch of hydrolysis in which the pulp was autoclaved for 15 minutes at 121°C at a TS concentration of 30–37.5% and then diluted to 20% TS using the washwater.

β-glucosidase addition

After centrifugation, washing and re-suspension of hydro-lysed pulp in pH 5 solution, β-glucosidase was added at concentrations of 25 and 12.5 mg enzyme per g pulp (original weight) and hydrolysis conditions were restored. Samples were then taken for sugar analysis over the second hydrolysis period of up to 4 days.

All experiments were carried out in duplicate and repeated twice.



Filter paper activity


High performance anion exchange chromatography with pulsed amperometric detection


Municipal solid waste


Post wash


Simultaneous saccharification and fermentation


Trans-membrane pressure


Total solids



The work was funded in part by Fiberight Ltd and in part by a scholarship from the University of Southampton. The authors are grateful to Nick Thompson and Peter Speller of Fiberight for their practical advice and assistance.

Authors’ Affiliations

Faculty of Engineering and the Environment, University of Southampton


  1. Licht FO: World Ethanol Markets: The outlook to 2015. UK: Tunbridge Wells; 2006.Google Scholar
  2. Larsson M, Zacchi G: Production of ethanol from dilute glucose solutions A technical-economic evaluation of various refining alternatives. Bioprocess Biosyst Eng 1996, 15: 125-132. 10.1007/BF00369615View ArticleGoogle Scholar
  3. Larsen J, Østergaard Petersen M, Thirup L, Wen Li H, Krogh Iversen F: The IBUS Process – Lignocellulosic Bioethanol Close to a Commercial Reality. Chem Eng Technol 2008, 31: 765-772. 10.1002/ceat.200800048View ArticleGoogle Scholar
  4. Wang W, Kang L, Wei H, Arora R, Lee Y: Study on the decreased sugar yield in enzymatic hydrolysis of cellulosic substrate at high solid loading. Appl Biochem Biotechnol 2011, 164: 1139-1149. 10.1007/s12010-011-9200-8View ArticleGoogle Scholar
  5. Kristensen JB, Felby C, Jorgensen H: Yield-determining factors in high-solids enzymatic hydrolysis of lignocellulose. Biotechnology for Biofuels 2009, 2: 10. 10.1186/1754-6834-2-10View ArticleGoogle Scholar
  6. Yu ZY, Jameel H, Chang HM, Philips R, Park S: Evaluation of the factors affecting avicel reactivity using multi-stage enzymatic hydrolysis. Biotechnol Bioeng 2012, 109: 1131-1139. 10.1002/bit.24386View ArticleGoogle Scholar
  7. Roche C, Dibble C, Stickel J: Laboratory-scale method for enzymatic saccharification of lignocellulosic biomass at high-solids loadings. Biotechnology for Biofuels 2009, 2: 28. 10.1186/1754-6834-2-28View ArticleGoogle Scholar
  8. Xiao ZZ, Zhang X, Gregg DJ, Saddler JN: Effects of sugar inhibition on cellulases and beta-glucosidase during enzymatic hydrolysis of softwood substrates. Appl Biochem Biotechnol 2004, 113: 1115-1126.View ArticleGoogle Scholar
  9. Yang J, Zhang X, Yong Q, Yu S: Three-stage hydrolysis to enhance enzymatic saccharification of steam-exploded corn stover. Bioresour Technol 2010, 101: 4930-4935. 10.1016/j.biortech.2009.09.079View ArticleGoogle Scholar
  10. Roberts KM, Lavenson DM, Tozzi EJ, McCarthy MJ, Jeoh T: The effects of water interactions in cellulose suspensions on mass transfer and saccharification efficiency at high solids loadings. Cellulose 2011, 18: 759-773. 10.1007/s10570-011-9509-zView ArticleGoogle Scholar
  11. Selig MJ, Hsieh C-WC, Thygesen LG, Himmel ME, Felby C, Decker SR: Considering water availability and the effect of solute concentration on high solids saccharification of lignocellulosic biomass. Biotechnol Prog 2012, 28: 1478-1490. 10.1002/btpr.1617View ArticleGoogle Scholar
  12. Rahikainen J, Mikander S, Marjamaa K, Tamminen T, Lappas A, Viikari L, Kruus K: Inhibition of enzymatic hydrolysis by residual lignins from softwood-study of enzyme binding and inactivation on lignin-rich surface. Biotechnol Bioeng 2011, 108: 2823-2834. 10.1002/bit.23242View ArticleGoogle Scholar
  13. Yang MH, Li WL, Liu BB, Li Q, Xing JM: High-concentration sugars production from corn stover based on combined pretreatments and fed-batch process. Bioresour Technol 2010, 101: 4884-4888. 10.1016/j.biortech.2009.12.013View ArticleGoogle Scholar
  14. Andric P, Meyer AS, Jensen PA, Dam-Johansen K: Reactor design for minimizing product inhibition during enzymatic lignocellulose hydrolysis: I. Significance and mechanism of cellobiose and glucose inhibition on cellulolytic enzymes. Biotechnol Adv 2010, 28: 308-324. 10.1016/j.biotechadv.2010.01.003View ArticleGoogle Scholar
  15. Olofsson K, Bertilsson M, Liden G: A short review on SSF - an interesting process option for ethanol production from lignocellulosic feedstocks. Biotechnology for Biofuels 2008,1(1):1-14. 10.1186/1754-6834-1-1View ArticleGoogle Scholar
  16. Kemppainen K, Ranta L, Sipilä E, Östman A, Vehmaanperä J, Puranen T, Langfelder K, Hannula J, Kallioinen A, Siika-aho M, et al.: Ethanol and biogas production from waste fibre and fibre sludge – the FibreEtOH concept. Biomass and Bioenergy 2012, 46: 60-69.View ArticleGoogle Scholar
  17. Watanabe I, Miyata N, Ando A, Shiroma R, Tokuyasu K, Nakamura T: Ethanol production by repeated-batch simultaneous saccharification and fermentation (SSF) of alkali-treated rice straw using immobilized Saccharomyces cerevisiae cells. Bioresour Technol 2012, 123: 695-698.View ArticleGoogle Scholar
  18. Viikari L, Vehmaanperä J, Koivula A: Lignocellulosic ethanol: from science to industry. Biomass and Bioenergy 2012, 46: 13-24.View ArticleGoogle Scholar
  19. Holtzapple M, Cognata M, Shu Y, Hendrickson C: Inhibition of Trichoderma reesei cellulase by sugars and solvents. Biotechnol Bioeng 1990, 36: 275-287. 10.1002/bit.260360310View ArticleGoogle Scholar
  20. Wu Z, Lee YY: Inhibition of the enzymatic hydrolysis of cellulose by ethanol. Biotechnol Lett 1997, 19: 977-979. 10.1023/A:1018487015129View ArticleGoogle Scholar
  21. Mores W, Knutsen J, Davis R: Cellulase recovery via membrane filtration. Appl Biochem Biotechnol 2001, 91–93: 297-309.View ArticleGoogle Scholar
  22. Zhang MJ, Su RX, Li QA, Qi W, He ZM: Enzymatic saccharification of pretreated corn stover in a fed-batch membrane bioreactor. Bioenergy Research 2011, 4: 134-140. 10.1007/s12155-010-9107-1View ArticleGoogle Scholar
  23. Ramos LP, Breuil C, Saddler JN: The use of enzyme recycling and the influence of sugar accumulation on cellulose hydrolysis by Trichoderma-Cellulases. Enzyme Microb Technol 1993, 15: 19-25. 10.1016/0141-0229(93)90111-EView ArticleGoogle Scholar
  24. Van Dyk JS, Pletschke BI: A review of lignocellulose bioconversion using enzymatic hydrolysis and synergistic cooperation between enzymes-Factors affecting enzymes, conversion and synergy. Biotechnol Adv 2012, 30: 1458-1480. 10.1016/j.biotechadv.2012.03.002View ArticleGoogle Scholar
  25. Weiss N, Borjesson J, Pedersen LS, Meyer AS: Enzymatic lignocellulose hydrolysis: Improved cellulase productivity by insoluble solids recycling. Biotechnology for Biofuels 2013, 6: 5. 10.1186/1754-6834-6-5View ArticleGoogle Scholar
  26. Chirico WJ, Brown RD: β-Glucosidase from Trichoderma reesei. Eur J Biochem 1987, 165: 343-351. 10.1111/j.1432-1033.1987.tb11447.xView ArticleGoogle Scholar
  27. Tu MB, Chandra RP, Saddler JN: Recycling cellulases during the hydrolysis of steam exploded and ethanol pretreated lodgepole pine. Biotechnol Prog 2007, 23: 1130-1137.View ArticleGoogle Scholar
  28. Varnai A, Viikari L, Marjamaa K, Siika-aho M: Adsorption of monocomponent enzymes in enzyme mixture analyzed quantitatively during hydrolysis of lignocellulose substrates. Bioresour Technol 2011, 102: 1220-1227. 10.1016/j.biortech.2010.07.120View ArticleGoogle Scholar
  29. Qing Q, Yang B, Wyman CE: Xylooligomers are strong inhibitors of cellulose hydrolysis by enzymes. Bioresour Technol 2010, 101: 9624-9630. 10.1016/j.biortech.2010.06.137View ArticleGoogle Scholar
  30. Pan XJ, Xie D, Gilkes N, Gregg DJ, Saddler JN: Strategies to enhance the enzymatic hydrolysis of pretreated softwood with high residual lignin content. Appl Biochem Biotechnol 2005, 121: 1069-1079.View ArticleGoogle Scholar
  31. Taherzadeh MJ, Karimi K: Pretreatment of lignocellulosic wastes to improve ethanol and biogas production: A review. Int J Mol Sci 2008, 9: 1621-1651. 10.3390/ijms9091621View ArticleGoogle Scholar
  32. Qi BK, Chen XR, Su Y, Wan YH: Enzyme adsorption and recycling during hydrolysis of wheat straw lignocellulose. Bioresour Technol 2011, 102: 2881-2889. 10.1016/j.biortech.2010.10.092View ArticleGoogle Scholar
  33. Zhang JH, Tang M, Viikari L: Xylans inhibit enzymatic hydrolysis of lignocellulosic materials by cellulases. Bioresour Technol 2012, 121: 8-12.View ArticleGoogle Scholar
  34. Sewalt VJH, Glasser WG, Beauchemin KA: Lignin Impact on Fiber Degradation. 3. Reversal of Inhibition of Enzymatic Hydrolysis by Chemical Modification of Lignin and by Additives. J Agric Food Chem 1997, 45: 1823-1828. 10.1021/jf9608074View ArticleGoogle Scholar
  35. Yang B, Wyman CE: BSA treatment to enhance enzymatic hydrolysis of cellulose in lignin containing substrates. Biotechnol Bioeng 2006, 94: 611-617. 10.1002/bit.20750View ArticleGoogle Scholar
  36. Zhang J, Lynd LR: Ethanol production from paper sludge by simultaneous saccharification and co-fermentation using recombinant xylose-fermenting microorganisms. Biotechnol Bioeng 2010, 107: 235-244. 10.1002/bit.22811View ArticleGoogle Scholar
  37. Yang J, Zhang X, Yong Q, Yu S: Three-stage enzymatic hydrolysis of steam-exploded corn stover at high substrate concentration. Bioresour Technol 2011, 102: 4905-4908. 10.1016/j.biortech.2010.12.047View ArticleGoogle Scholar
  38. Qi BK, Luo JQ, Chen GQ, Chen XR, Wan YH: Application of ultrafiltration and nanofiltration for recycling cellulase and concentrating glucose from enzymatic hydrolyzate of steam exploded wheat straw. Bioresour Technol 2012, 104: 466-472.View ArticleGoogle Scholar
  39. Humbird D, Davis R, Tao L, Kinchin C, Hsu D, Aden A, Schoen P, Lukas J, Olthof B, Worley M: Process design and economics for biochemical conversion of lignocellulosic biomass to ethanol. NREL Technical report. In NREL/TP-5100-47764. NREL, Golden: CO, USA; 2011. Scholar
  40. Sluiter A, Hames B, Ruiz R, Scarlata C, Sluiter J, Templeton D, Crocker D: Determination of Structural Carbohydrates and Lignin in Biomass. CO, USA: NREL, Golden; 2011. Scholar
  41. Kitcherside MA, Glen EF, Webster AJF: FibreCap: an improved method for the rapid analysis of fibre in feeding stuffs. Anim Feed Sci Technol 2000, 86: 125-132. 10.1016/S0377-8401(00)00153-XView ArticleGoogle Scholar
  42. Pribowo A, Arantes V, Saddler JN: The adsorption and enzyme activity profiles of specific Trichoderma reesei cellulase/xylanase components when hydrolyzing steam pretreated corn stover. Enzyme Microb Technol 2012, 50: 195-203. 10.1016/j.enzmictec.2011.12.004View ArticleGoogle Scholar
  43. Ioelovich M, Morag E: Study of Enzymatic Hydrolysis of Pretreated Biomass at Increased Solids Loading. Bioresources 2012, 7: 4672-4682.View ArticleGoogle Scholar
  44. Rodrigues AC, Leitão AF, Moreira S, Felby C, Gama M: Recycling of cellulases in lignocellulosic hydrolysates using alkaline elution. Bioresour Technol 2012, 110: 526-533.View ArticleGoogle Scholar
  45. Wang QQ, Zhu JY, Hunt CG, Zhan HY: Kinetics of adsorption, desorption, and re-adsorption of a commercial endoglucanase in lignocellulosic suspensions. Biotechnol Bioeng 2012, 109: 1965-1975. 10.1002/bit.24483View ArticleGoogle Scholar
  46. Xue Y, Jameel H, Park S: Strategies to Recycle Enzymes and Their Impact on Enzymatic Hydrolysis for Bioethanol Production. Bioresources 2012, 7: 602-615.View ArticleGoogle Scholar
  47. Tu MB, Chandra RP, Saddler JN: Evaluating the distribution of cellulases and the recycling of free cellulases during the hydrolysis of lignocellulosic substrates. Biotechnol Prog 2007, 23: 398-406. 10.1021/bp060354fView ArticleGoogle Scholar
  48. Bu LT, Nimlos MR, Shirts MR, Stahlberg J, Himmel ME, Crowley MF, Beckham GT: Product Binding Varies Dramatically between Processive and Nonprocessive Cellulase Enzymes. J Biol Chem 2012, 287: 24807-24813. 10.1074/jbc.M112.365510View ArticleGoogle Scholar
  49. Várnai A, Siika-aho M, Viikari L: Restriction of the enzymatic hydrolysis of steam-pretreated spruce by lignin and hemicellulose. Enzyme Microb Technol 2010, 46: 185-193. 10.1016/j.enzmictec.2009.12.013View ArticleGoogle Scholar
  50. Hu JG, Arantes V, Saddler JN: The enhancement of enzymatic hydrolysis of lignocellulosic substrates by the addition of accessory enzymes such as xylanase: is it an additive or synergistic effect? Biotechnology for Biofuels 2011, 4: 36. 10.1186/1754-6834-4-36View ArticleGoogle Scholar
  51. Zhang X, Qin W, Paice MG, Saddler JN: High consistency enzymatic hydrolysis of hardwood substrates. Bioresour Technol 2009, 100: 5890-5897. 10.1016/j.biortech.2009.06.082View ArticleGoogle Scholar
  52. Zhang Y, Liu YY, Xu JL, Yuan ZH, Qi W, Zhuang XS, He MC: High Solid and Low Enzyme Loading Based Saccharification of Agricultural Biomass. Bioresources 2012, 7: 345-353.Google Scholar
  53. Xue Y, Jameel H, Phillips R, Chang HM: Split addition cif enzymes in enzymatic hydrolysis at high solids concentration to increase sugar concentration for bioethanol production. J Ind Eng Chem 2012, 18: 707-714. 10.1016/j.jiec.2011.11.132View ArticleGoogle Scholar
  54. Connor MR, Liao JC: Microbial production of advanced transportation fuels in non-natural hosts. Curr Opin Biotechnol 2009, 20: 307-315. 10.1016/j.copbio.2009.04.002View ArticleGoogle Scholar
  55. Ghose TK: Measurement of Cellulase Activities. Pure Appl Chem 1987, 59: 257-268. 10.1351/pac198759020257Google Scholar
  56. Davis MW: A rapid modified method for compositional carbohydrate analysis of lignocellulosics by high pH anion-exchange chromatography with pulsed amperometric detection (HPAEC/PAD). J Wood Chem Technol 1998, 18: 235-252. 10.1080/02773819809349579View ArticleGoogle Scholar


© Puri et al.; licensee BioMed Central Ltd. 2013

This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.