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Journal of Biomedicine and Biotechnology
Volume 2012 (2012), Article ID 325426, 7 pages
http://dx.doi.org/10.1155/2012/325426
Research Article

Changes in the Material Characteristics of Maize Straw during the Pretreatment Process of Methanation

1College of Agronomy, Northwest A&F University, P.O. Box 95, Yangling, Shaanxi 712100, China
2The Research Center of Recycle Agricultural Engineering and Technology of Shaanxi Province, Yangling, Shaanxi 712100, China
3College of Forestry, Northwest A&F University, Yangling, Shaanxi 712100, China
4Institute of Geography Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China

Received 26 March 2012; Revised 30 July 2012; Accepted 30 July 2012

Academic Editor: Anuj K. Chandel

Copyright © 2012 Yongzhong Feng et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

Pretreatment technology is important to the direct methanation of straw. This study used fresh water, four bacterium agents (stem rot agent, “result” microbe decomposition agent, straw pretreatment composite bacterium agent, and complex microorganism agent), biogas slurry, and two chemical reagents (sodium hydroxide and urea) as pretreatment promoters. Different treatments were performed, and the changes in the straw pH value, temperature, total solid (TS), volatile solid (VS), and carbon-nitrogen ratio (C/N ratio) under different pretreatment conditions were analyzed. The results showed that chemical promoters were more efficient than biological promoters in straw maturity. Pretreatment using sodium hydroxide induced the highest degree of straw maturity. However, its C/N ratio had to be reduced during fermentation. In contrast, the C/N ratio of the urea-pretreated straw was low and was easy to regulate when used as anaerobic digestion material. The biogas slurry pretreatment was followed by pretreatments using four different bacterium agents, among which the effect of the complex microorganism agent (BA4) was more efficient than the others. The current study is significant to the direct and efficient methanation of straw.

1. Introduction

The rural household biogas in China has rapidly developed in recent years. By 2010, the number of rural household biogas users had reached 41.8 million in China [1, 2]. However, the rural household biogas industry has been facing a fermented material shortage due to the changes in agricultural structure. Moreover, the use of anaerobic digesters has been discontinued due to material shortage [35]. In China, the straw yield is nearly 7 × 109 t every year [6, 7] (of which rice, corn, and wheat straw account for 79.5%) [8]. Aside from the small portions used as animal feeds or returned to the field, most straws are either used as fuels or burned directly in the fields, which cause a huge waste [911]. However, straw as fermented material possesses many problems, such as long run-up time, low gas output, low material utilization ratio, and material crusting [12, 13]. Crop straw has high contents of lignin, cellulose, and hemicellulose, and the degradation is difficult. These problems seriously affect the fermentation process and material processing of straw [14]. Therefore, straw pretreatment is essential for an efficient direct methanation.

Maize straw is a lignocellulosic biomass which contains components such as cellulose (34.0%), hemicellulose (37.5%), and lignin (22%). The carbon-nitrogen ratio (C/N ratio) for maize straw is about 66.31%, while the proper C/N ratio for anaerobic digester should be within the range of 25–35 [15]. At present, straw pretreatment studies focus on adjusting the nutritional value of straw and improving its characteristics [16, 17]. Adjusting the nutritional value is usually achieved by regulating the C/N ratio by mixing straw with fermented materials having different carbon and nitrogen contents. Therefore, exogenous nitrogen needs to be supplemented to increase the nitrogen fraction for more efficient anaerobic digestion of maize straw. Nitrogen can be added in the form of inorganic form (e.g., ammonium bicarbonate) or organic form (e.g., urea or animal manure). Animal manure and other organic wastes are additional nutrient sources, provided they are readily available for anaerobic digestion. Nitrogen fertilizer (e.g., ammonia or urea) is another nitrogen source that can be easily added to the maize straw if nitrogenous wastes are not available [18]. On the other hand, straw characteristics are improved by using physical, chemical, or biological pretreatment, which improve the straw’s utilization rate [16]. Lignocellulose is difficult to degrade biologically. Pretreatment of straw by mechanical size reduction, heat treatment, and/or chemical treatment usually improves its digestibility. Chemical pretreatment methods that have been explored in previous research include bicarbonate treatment [19], radiation [20], alkaline peroxide treatment [21], and ammonia treatment [22]. Among them, ammonia treatment has several advantages over the other ones, since ammonia itself is a nitrogen source for biodegradation.

Based on the theory and practice of straw anaerobic digestion and rural methane fermentation, this study investigated pH, temperature, total solid (TS), volatile solid (VS), and carbon-nitrogen ratio (C/N ratio) of maize straw during biological and chemical pretreatment processes. Moreover, the changes in the material characteristics during the process were compared, and efficient straw pretreatment agents were chosen according to the degree of straw maturity. The current study also provides theoretical reference for practical methanation.

2. Materials and Methods

2.1. Raw Material

Air-dried maize straw used in this study was collected from the experimental field of Northwest Agriculture and Forestry University in Yangling, China. Before the pretreatment, the maize straw was chopped into 2-3 cm pieces [23]. The raw material contained 7 9 . 5 0 ± 0 . 4 2 % of TS, and there were about 89.20% VS in the dry matter. The C/N ratio of the raw material was 66.31.

2.2. Biological Pretreatment

The biological pretreatment promoters were mixed microorganism, which were bacterium agent 1(BA1) [24] (stem rot agent, main composition: Bacillus polymyxa, Bacillus subtilis, Bacillus brevis, Bacillus licheniformis, Brevibacterium sulphureum, and so on.), bacterium agent 2(BA2) [25] (“result" microbe decomposition agent, main composition: Saccharomyces cerevisiae, Coccidioides, H. anomala, S. cerevisiae, Bacillus licheniformis, Pseudomonas, Leucothrix, Lactobacillus delhi and so on.), bacterium agent 3(BA3) [26] (straw pretreatment composite bacterium agent, main composition: Bacillus subtilis, Streptomyces microflavus, Trichoderma koningii, Chaetomium globosum, and so on.), and bacterium agent 4(BA4) [27] (complex microorganism agent, main composition: Bacillus subtilis, Bacillus natto, Streptoverticillium baldaccii, Thermoactinomyces vulgaris, Saccharomyces cerevisiae, Candida utilis, Candida tropicalis, Aspergillus niger, Aspergillus oryzae, Rhizopus nigricans, and so on.).

These four kinds of microorganism were weighed 0.04, 8.00, 8.00, and 8.00 g, respectively, according to their different number of viable bacteria. Then these pretreatment promoters were put into four different 2000 mL beakers, which contain 2000 g fresh water. After that, the mixer was put into a constant temperature incubator for a 24 h cultivation in 37°C [28]. The activated promoters were then added into the pretreatment reactor, which contained 800 g maize straw. The pretreatment process was 10 days.

Biogas slurry was obtained from an anaerobic digester that produced gas normally in Yangling, China. 2000 g biogas slurry was added in the pretreatment reactor with 800 g maize straw, and the pretreatment process was 10 days.

2.3. Chemical Pretreatment

Sodium hydroxide and urea were used in this study. The amount of chemicals added was referred to in the previous researches [29, 30]. This study added 800 g maize straw, 2000 g fresh water, and then 160 g sodium hydroxide and 160 g urea, respectively. The pretreatment process lasted for 10 days.

In this study, fresh water was used as the control group, and 2000 g was added into 800 g maize straw for a ten-day pretreatment. All operations were of unified management, and the experiment was repeated three times.

2.4. Tested Indexes and Methods

The pH value was measured by intelligent pH meter (pHs-3CT, China) every day. Temperatures at the center of each pile as well as environmental temperature were recorded manually by a thermometer every day. The untreated and treated maize straw samples were analyzed for TS and VS, according to the APHA standard methods [31]. The total organic carbon (TOC) was determined using the K2Cr2O7 volumetric and outside heating methods [32]. The total organic nitrogen (TON) was analyzed by Kjeldahl method (Model KDN-08C, Shanghai, China) as recommended by Cottenie et al. [33], while the carbon-nitrogen (C/N) ratio was calculated using values of the TOC and TON.

3. Results

3.1. Changes in the Physical and Chemical Characteristics of Maize Straw before and after Pretreatment

The characteristics of maize straw between before pretreatment and after ten-day pretreatment were compared in Table 1. After pretreatment, TS of maize straw was dramatically decreased, which was between 1 1 . 0 7 ± 1 . 3 3 % and 2 0 . 0 0 ± 0 . 3 0 %. Significant differences were observed between control group ( 1 1 . 5 3 ± 0 . 5 5 %) and experimental groups, except those treated with BA1 ( 1 1 . 0 7 ± 1 . 3 3 %) and BA2 ( 1 1 . 8 3 ± 0 . 2 1 %). An extremely significant difference was also observed between the control group and the specimens pretreated with BA4 ( 1 4 . 3 1 ± 0 . 3 7 %), urea ( 1 4 . 6 4 ± 0 . 6 0 %), and sodium hydroxide ( 2 0 . 0 0 ± 0 . 3 0 %). The VS content of the sodium hydroxide-treated specimen ( 4 4 . 6 3 ± 0 . 4 5 %) was significantly different from that of the raw material ( 8 9 . 2 0 % ± 0 . 3 1 ), while VS of the other treatments fluctuated between 8 6 . 1 1 ± 0 . 3 9 % and 9 3 . 1 9 ± 0 . 3 8 % without substantial change. Compared with raw material, TOC of all experimental groups decreased. TOC of the sodium hydroxide-treated specimen was only 1 5 . 0 3 ± 0 . 2 4 %, indicating that majority of water-insoluble carbon was decomposed and transformed during the pretreatment process. TON of the groups treated with BA1 (0.54%) and sodium hydroxide ( 0 . 2 5 ± 0 . 0 2 %) both decreased, while others increased. The C/N ratios of the pretreated straws were lower than that of the raw material, implying that pretreatment reduces the C/N ratio of fermented materials, which is significant to the life activities of methanogenic bacteria.

tab1
Table 1: Basic characteristics of maize straw before and after ten-day pretreatment.
3.2. Changes in pH

pH plays a crucial role in the growth metabolism of microbes. Microorganism used in this study was a mixture which contained bacterium, fungus, saccharomycetes, and actinomycetes, with its suitable pH varying from 4.5 to 6.5. pH of BA1 treated decreased to the range of 4.1 to 4.8 from the 5th day, which is unfavorable for bacterium growth. pH of BA2 treated fell to 4.4 on the 4th day. However, it gradually increased later, and hence, the bacterium activity significantly decreased. pH of BA3 treated was stable between 4.7 and 6.2 before the 8th day. However, pH was then decreased to 4.3 at the 9th day and kept at the same level at the 10th day. pH of BA4 treated remained between 4.7 and 5.9. Thus, the bacterium grew well under the moderate conditions. Compared with that of control group, pH of biogas slurry-treated group was higher at the first two days. Then, it started to decline three days later and stabilized between 6.15 and 7.75, maintaining a neutral condition, which fell in the scope of the suitable pH.

pH of two chemically treated specimens was both higher than the others, particularly between 8.9 and 9.2 and between 11.3 and 11.8 for the urea and sodium hydroxide-treated groups, respectively. pH of control group was kept falling down and then fluctuated near 4.4 since the 4th day (Figure 1).

325426.fig.001
Figure 1: Changes in pH level during the pretreatment process.
3.3. Changes in Temperature

Temperatures of the environment and every treated group were shown in Figure 2. The temperature of the environment significantly changed during the 6th and 8th days, whereas those of the treated groups did not. The temperature of the group treated with BA1 was slightly lower than that of environment during the 3rd and 5th days, whereas the other bacterium agents groups had higher temperatures than that of environment. This result can be attributed to the restrained growth of BA1 due to the interaction of the pH and temperature during the process, which thus causes the decline of the decomposition characteristics of the material. The temperatures of the groups treated with BA3 and BA4 were high and thus beneficial to the straw decomposition. Moreover, the temperatures of the two chemically treated groups slightly fluctuated along the temperature of environment. During the 1st day, the temperature of the urea-treated group was quite low (only 11.5°C) and that of the sodium hydroxide-treated group was higher (19.0°C). Both seemed to stabilize after that and, hence, were beneficial for the organic decomposition in straw. The temperatures of the biogas-slurry-treated and control groups were subject to the environment.

325426.fig.002
Figure 2: Changes in the temperature during the pretreatment process.
3.4. Changes in TS and VS

TS and VS are two indexes of the degree of decomposition maturity and are important parameters of the fermented substrate concentration. Figure 3 showed that the TS contents of all experimental groups were higher than that of the control group since the 4th day, indicating the effect of the promoters on straw decomposition. However, these TS contents all decreased as time elapsed. During the 1st day, the TS content of the urea-treated group was the highest, followed by that of the sodium hydroxide-treated group. However, the former declined by 9.79%, whereas the latter decreased by only 2.1%. Among the biological promoters, TS of the group treated with BA4 was higher than those of the others, whereas those of the groups treated with BA1 and biogas slurry stayed at low levels without significant changes. In summary, during the pretreatment process, the two chemical promoters induced the highest degrees of straw decomposition maturity, whereas BA4 and BA1 and biogas slurry had lesser effects.

325426.fig.003
Figure 3: Changes in the TS content during the pretreatment process.

Figure 4 showed the changes in VS. VS of all groups stabilized between 88.31% and 93.61% without significant fluctuations and differences, except those of the groups treated with sodium hydroxide and biogas slurry. VS of the sodium hydroxide-treated group was the lowest (43.35% to 51.18%), followed by that of the group with biogas slurry (84.95% to 87.80%), with slight fluctuations.

325426.fig.004
Figure 4: Changes in the VS content during the pretreatment process.
3.5. Changes in C/N Ratio

C/N ratio (Figure 5(a)) of pretreated straw increased firstly and decreased subsequently, and had the same trend as TOC (Figure 5(b)). However, TON (Figure 5(c)) varied slightly except urea-treated group. Urea as a rich nitrogen promoter added exogenous nitrate in material. So C/N ratio of urea-treated group was the lowest from beginning to end. Its C/N ratio was only 3.80 on the 1st day. However, it gradually increased with time and remained between 3.80 and 22.36. C/N ratios of BA1-treated, sodium hydroxide-treated, and control groups were very high during and after pretreatment, which were 51.65, 61.64, and 57.76 in average, respectively. In biological pretreatment, BA2, BA3, and BA4 treated had the same value in TOC and TON, and the C/N ratio was very close to 46.58, 45.86, and 43.59 in average, respectively. For its lower TOC and higher TON, C/N ratio of biogas slurry-treated group was kept at a lower level (33.12 in average). And the same results were achieved by Zhong et al. [34].

fig5
Figure 5: Changes in C/N ratio, TOC, and TON during the pretreatment process: (a) changes in C/N ratio, (b) changes in TOC, (c) changes in TON.

4. Discussions

Straw maturity is a key factor of the pretreatment. Several authors have concluded that using a single parameter as a maturity index is insufficient and that amalgamation of several parameters is usually needed. Various physical, biological, and chemical parameters have been used to monitor the quality and maturity of compost [3537]. The effects of different promoters on the changes of the indexes during the pretreatment process varied, as well as the requirements of the different promoters on the pretreatment external conditions. Only in suitable temperatures, pH levels, and other environment conditions can bacterium agents obtain good effects. Too high or low temperatures and unsuitable pH levels can impede the normal life metabolism of microorganisms and thus influence the degree of straw decomposition maturity during the pretreatment process [38]. For the group treated with the stem rot agent (BA1), pH level of the material was lower during the early stages and was even as low as 4.1 during the 5th day. The temperatures on the 3rd and 5th days were lower than the environmental temperature, thus restraining the growth of microorganism and negatively affecting the straw organic degradation. Complex microorganism agent- (BA4-) treated group could maintain a better living condition for microbe, and its treatment effect was superior to other bacterium agent treatments. Urea and sodium hydroxide are both alkaline and, hence, beneficial to the degradation of lignocellulose and hemicellulose. Studies results showed that sodium hydroxide treatment can improve the conversion rate of lignocelluloses [3947]. Moreover, the results of the studies by Chandra and Jackson [29] and Chesson [48] suggested that the degradation of lignocellulose was optimal upon the addition of 10% of sodium hydroxide. During the pretreatment process, the TS contents of the urea and sodium hydroxide-treated groups were both high. These results indicate that, under alkaline conditions, the lignocellulose degradation rate is improved, macromolecular substances are decomposed, the water-holding capacity of straw is decreased, and the water content of straw is lower than those of other samples of equivalent weight. The sodium hydroxide-treated group had an obviously lower VS content than those of the other groups. However, its C/N ratio was higher. Thus, some restrictions were encountered when the group was used as fermented materials, and better effects could have been achieved by adding nitrogen to regulate the C/N ratio to a suitable value. The biogas-slurry-treated group was more suitable for use in microorganism anaerobic fermentation, with only modest changes in the material’s characteristics and a suitable C/N ratio of 33.23. The control group had a lower pH level, temperature, and TS content. Its C/N ratio was higher, and the straw degradation was bad. Hence, its treatment effect was worse than those of the promoters.

5. Conclusions

Synthesizing each index of pretreatment material, it can be summarized that the effect of sodium hydroxide-pretreated group was better than any others, followed by urea-treated group. In biological pretreatment, biogas slurry was the best promoter, for its good corrosion effect, and more economic. BA4 also had a good effect on straw maturity, and the next is BA3 treated. BA1 treated was the worst group, because its microorganisms’ survival conditions were limited by unsuited pH and temperature.

As compared with biological pretreatment, chemical treatment is easier to operate and has good effect. However, it will be a difficult and expensive task to recycle the chemicals used for the hydrolysis to avoid the environmental pollution. On the other hand, although the biological pretreatment was less effective than the sodium hydroxide and urea treatment, there exists a big room for improvement of the microbial degradation of cellulosic biomass by optimization of the fungal growth conditions and manipulation of the process parameters such as pH and temperature. However, in order to approach the biomass-to-fuels issue in a more environmentally friendly way, we will continue to improve the efficiency of biological treatment of maize straw to optimize the biogas production.

Acknowledgments

This study was financially supported by China’s Technology Support Project for the Eleventh Five-Year-Plan: Research and Demonstration of the Key Technology on the Sustainable Development of Resettlement Area in Sanjiangyuan (Grant no. 2009BAC61B04) and the Twelfth Five-Year-Plan: High-yielded Biogas Technology Integrated Demonstration on Mixing Materials (Grant no. 2011BAD15B03) and the Special Energy Project by China’s Ministry of Agriculture in 2012.

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