水生生物质的甲烷发酵

D.L. Wise, D.C. Augenstein, J.H. Ryther
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引用次数: 33

摘要

对4种水生生物质进行厌氧发酵生成甲烷,作为潜在能源资源评价的一部分。对两种淡水杂草(浮萍和水螅)和两种海洋藻类(江蓠和Ulva lacuca)进行了评价。挥发性固体,灰分含量,热值和元素分析报告这些生物质。这四种菌种均在中温(37°C)条件下在501个CSTR装置中发酵,使用的是由重量相等的污水污泥和水生生物质组成的营养丰富的饲料,固体浓度约为5%,保留时间为26天。此外,在嗜热(60°C)条件下,以相似的方式对两种淡水杂草进行了评估。生物转化效率是基于测量的能量输出(如甲烷)和测量的能量输入(如生物质的热值)。结果发现,在中温条件下,淡水杂草中25 - 34%的能量值被回收,这一低值可能是由于发酵罐未达到稳态条件所致。在相同的条件下,海洋物种恢复了27 ~ 45%的能量值。然而,在嗜热条件下,淡水杂草的转化率从32%提高到46%。研究发现,通过假设海藻中所有挥发性固体的氧化态与纤维素相当,可以获得与直接测量相同的生物转化效率,这似乎表明生物可降解多糖的比例很高。然而,淡水杂草显示出基于热量值的转化比假设所有挥发性物质本质上都是纤维素的转化率低得多。这可能表明发生了纤维素组分的生物转化,但在这些条件下,生物质中剩余的高能量成分(如木质素)是不可生物降解的。碱性预处理(饱和石灰)浮萍的生物转化率与未处理浮萍的生物转化率基本相等。对这两种海洋物种进行了抑制研究,以解释其多糖磺化程度高,生物转化率低于预期。这一假设被证明是无效的,接种微生物的缓慢适应被认为是观察结果的可能解释。此外,在中温条件下使用最小的接种量进行原位或批量发酵。淡水水生生物量均为21个单位,水螅类生物量为51个单位。结果发现,80%的甲烷是在运行的头两个月里产生的。此外,这些简单的中温原位单元的生物转化率与CSTR单元在亲热条件下的生物转化率相当,均为34-46%。在简单的原位单元中获得基线生物质转化结果似乎是最实际的。预处理替代方案和改进传统CSTR技术的新型处理技术似乎是提高生物转化能源效率的必要条件。
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Methane fermentation of aquatic biomass

Four aquatic biomass species were anaerobically fermented to methane as part of an evaluation of these biomass as potential energy resources. Two freshwater weeds (Duckweed (Lemna sp.) and Hydrilla verticillata) and two marine algae (Gracilaria ceae and Ulva lactuca) were evaluated. Volatile solids, ash content, calorific values, and elemental analyses are reported for these biomass. All four were fermented at mesophilic (37°C) conditions in 50 1 CSTR units using a rich nutrient feed of essentially equal parts by weight sewage sludge and aquatic biomass in an approximately 5% solids concentration slurry and with a 26-day retention time. In addition, the two freshwater weeds were evaluated in a similar manner at thermophilic (60°C) conditions. Bioconversion efficiency was based on measured energy out, as methane, and measured energy in, as calorific values of the biomass. It was found that 25 to 34% of the energy value in the freshwater weeds was recovered at mesophilic conditions, a low value perhaps due to the fact that steady-state conditions were not reached in the fermenters. For the marine species, 27 to 45% of the energy value was recovered under the same conditions. Conversion of the freshwater weeds at thermophilic conditions, however, was from 32 to 46%. It was found that by assuming all total volatile solids in the seaweed had an oxidation state equivalent to cellulose the same bioconversion efficiency was obtained as measured directly, appearing to indicate a high fraction of biodegradable polysaccharides. Freshwater weeds, however, demonstrated a much lower conversion based on calorimetric values than with the assumption that all volatile material was cellulosic in nature. This may indicate that bioconversion of a cellulosic fraction occurred, but that residual higher energy components in the biomass such as lignin were nonbiodegradable under these conditions. Results of the bioconversion of alkaline pretreated (saturated lime) Duckweed were approximately equal to those with the untreated biomass. An inhibition investigation to explain lower than anticipated bioconversion was conducted on the two marine species based on their high degree of sulfonation of polysaccharides. This hypothesis proved to be invalid, and slow acclimatization of innoculating microorganisms was given as a possible explanation of observed results. Further, in situ or batch fermentation were carried out at mesophilic conditions using minimal inoculum. Both freshwater aquatic biomass were evaluated in 2 1 units, while Hydrilla was also evaluated in a 50 1 unit. It was found that 80% of the methane was evolved in the first two months of operation. Moreover, bioconversion performance in these simple mesophilic in situ units were equal to that in the CSTR units at thermophilic conditions, namely 34–46% conversion. Obtaining baseline biomass conversion results in simple in situ units appears most practical. Pretreatment alternatives and novel processing techniques which improve on conventional CSTR technology appear to be required to improve bioconversion energy efficiencies.

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