Как выбрать гостиницу для кошек
14 декабря, 2021
Tracy P. Houghton,1 David N. Thompson,*1
J. Richard Hess,1 Jeffrey A. Lacey,1
Michael P. Wolcott,2 Anke Schirp,2 Karl Englund,2
David Dostal,2 and Frank Loge2
11dahn Natinnal Engineecing and Envicnnmental Labncatncy,
Idahn Falls, ID 83415-2203,
E-mail: thnmdn@inel. gnv; and
2Washingtnn State Univecsity,
Pullman, WA 99164-1806
Combining biologic pretreatment with storage is an innovative approach for improving feedstock characteristics and cost, but the magnitude of responses of such systems to upsets is unknown. Unsterile wheat straw stems were upgraded for 12 wk with Pleurotus ostreatus at constant temperature to estimate the variation in final compositions with variations in initial moisture and inoculum. Degradation rates and conversions increased with both moisture and inoculum. A regression analysis indicated that system performance was quite stable with respect to inoculum and moisture content after 6 wk of treatment. Scale-up by 150x indicated that system stability and final straw composition are sensitive to inoculum source, history, and inoculation method. Comparative testing of straw-thermoplastic composites produced from upgraded stems is under way.
Index Entries: Fungal upgrading; engineered storage; biological preprocessing; Pleurotus ostreatus; straw composite.
Agricultural crop residues are a valuable renewable biomass resource. In 1999, American farmers harvested 53,909,000 acres of wheat (1). The straw from this acreage of wheat represents >50 million t annually. Currently, some of the straw is harvested (baled) for use as livestock bedding or low-grade animal feed. However, these low-value uses provide only a
*Author to whom all correspondence and reprint requests should be addressed. Applied Binchemistcy and Bintechnnlngy 71 Vnl. 113-116, 2004
minimal return. Nationally, only about 3.2% of the economic return on wheat is from straw (1). Producers have long recognized the potential economic and environmental benefits of producing forage, bioenergy, and bioproducts from excess wheat straw residue. However, because of the low bulk density of straw and the loss of fermentable sugars to microbial activity during storage, there are harvest, transportation, storage, and preprocessing methods and logistics issues that must be worked out before the excess straw can be economically utilized on a national scale.
The U. S. Department of Energy and U. S. Department of Agriculture recently began a concentrated national effort under the Biomass Research and Development Act of 2000 to develop and demonstrate working biorefineries in the near term. The "vision" and "roadmap" documents for near-term utilization of agricultural residues to produce fuels, chemicals, and bioproducts have recently been completed and focus primarily on corn stover and cereal straws as the feedstocks (2,3). Objectives and research pathways identified in the roadmap document for stover and straw preprocessing and storage issues include the following (3):
1. Cost-Effective Pre-Delivery Treatment Processes—The development and testing of cost-effective pre-conversion treatment processes to increase energy — and chemical-density of raw materials at the point of harvest.
2. Best Practices for Harvesting and Storage—The biomass/agricul — tural communities must identify, develop, test, and implement best practices for cost-effective and environmentally sound pre-treatment, collection, storage, and transport of plant and animal residue-based feedstocks. This should lead to improved plant and animal residue recovery, more effective separation, improved handling and storage technologies/procedures, and reduced environmental impacts.
Thus, several issues related to preprocessing and storage have been identified as important research and development priorities for the near term. An innovative and potentially useful approach to addressing these issues would be to combine preprocessing and storage into a single system. In this way, energy use and infrastructure could be reduced by modifying the feedstock while it is waiting to be utilized. These modifications could be biological or chemical in nature. In the case of biological treatments, for such a system to be workable, it would be necessary for microbes carrying out the desired modifications to outcompete indigenous microorganisms vying for the same resources.
Straw utilization for composites is limited by poor resin and polymer penetration, and excessive resin consumption owing to the straw cuticle, fines, and the lignin-hemicellulose matrix (4). Some white-rot fungi, including Pleurotus ostreatus, degrade the cuticle and selectively degrade lignin and hemicellulose, leaving behind relatively more cellulose (4). Thus, treatments by these fungi could potentially be used to improve resin penetration and resin binding without the use of physical or chemical pretreatments. Although long treatment times and large footprints limit the use of fungal treatments on a large scale, distributed fungal pretreatments could alleviate land requirements.
In a previous study (4), we presented the results of a preliminary investigation to determine whether P. ostreatus could be competitive with indigenous organisms in unsterilized wheat straw stems. A detailed description of the potential benefits of preparing straw-thermoplastic composites from wheat straw stems upgraded by selective degradation by a white-rot fungus was provided in that study (4). In general, the potential benefits focus primarily on the reduction of fines (reduced external surface area) via a selective harvest method (5), and removal of amorphous matrix components by P. ostreatus to increase internal surface area and allow better penetration of composite formulation components into the lignocellulose matrix (4). Our previous study was conducted with the aim of moving toward the development of a passive, potentially distributed fungal upgrading system to improve feedstock characteristics for production of straw-thermoplastic composites (4). As envisioned, the system would be constructed and operated similarly to passive composting systems and could be operated for 12 wk or longer in a distributed or centralized manner, depending on land use requirements. Such a system fits within the frameworks of both engineered storage systems and pre-conversion processing.
In the preliminary study it was found that above about 11 mg of P. ostreatus/g of stems and 0.77 g of H2O/g of stems, the inoculated P. ostreatus was generally competitive with indigenous microbes (4), which is consistent with a previous report showing good competitiveness of Pleurotus sp. with soil microorganisms (6). In the present article, we describe completed laboratory studies conducted at the Idaho National Engineering and Environmental Laboratory (INEEL) that were tasked with determining acceptable moisture and inoculum ranges for pilot-scale fungal upgrading tests. Inoculated P. ostreatus was found to more completely dominate degradation of the straw stems as inoculum size and moisture content increased, but to be less selective with respect to polysaccharide degradation. Inoculum and moisture levels of 40 mg of P. ostreatus /g of stems and
1.6 g of H2O/g of stems, respectively, allowed successful competition of the inoculum with indigenous organisms and gave acceptable amounts of degradation of xylan and glucan (on a total degradation basis). Statistical analysis of the data was conducted to predict the variability of final compositions in response to ±30% variations in initial moisture and inoculum levels. Minimal variations in final composition would be desirable to ensure consistent product composition in outdoor systems having few environmental controls. In addition, we present the experimental design for the composite formulation/extrusion testing, as well as initial results from several extrusion tests conducted at the Wood Materials & Engineering Laboratory at Washington State University (WSU). In the near term, these data will be used to devise and test a pilot-scale fungal upgrading windrow system at WSU for demonstration of larger-scale operation and extrusion.
Composition of Westbred 936 Straw Stem Fraction Used in Fungal Treatment Studies"
a Uncertainties given are the SDs for four independent replicate measurements. b Based on 100% dry wt of material. c Remaining fraction attributed to unknown uronic acids, proteins, and so on, and to recovery errors in analysis techniques. |