农业工程学报
農業工程學報
농업공정학보
2013年
10期
196-202
,共7页
张世红%李相鹏%何广昌%杨海平%王贤华%陈汉平
張世紅%李相鵬%何廣昌%楊海平%王賢華%陳漢平
장세홍%리상붕%하엄창%양해평%왕현화%진한평
废弃物%气化%温度分布%稻壳%花生壳%上吸式固定床%空气当量比%顶部点火
廢棄物%氣化%溫度分佈%稻殼%花生殼%上吸式固定床%空氣噹量比%頂部點火
폐기물%기화%온도분포%도각%화생각%상흡식고정상%공기당량비%정부점화
wastes%gasification%temperature distribution%peanut shell%rice husk%updraft fixed-bed gasifier%equivalence ratio%top-Lit
为了了解在固定床气化炉中生物质的气化特性和炉内温度演变规律,该研究采用顶部点火上吸式(top-lit up draft,简称TLUD)固定床气化炉研究了农业废弃物的气化行为,重点考察了不同空气流量下炉内温度分布、燃气成分和热值的变化规律,探讨了生物质气化过程机理.结果表明,气化过程明显分为2个阶段,即挥发份的析出和焦炭的缓慢气化.整个气化过程中燃气的热值可稳定维持在3 MJ/m3以上,温度场的演变过程与波传递具有相似性,花生壳和稻壳的最佳空气当量比分别为0.31和0.35,且其燃气中焦油含量很低,分别为0.25、0.49 g/m3.该研究为TLUD固定床气化炉的设计和运行提供了有益的参考.
為瞭瞭解在固定床氣化爐中生物質的氣化特性和爐內溫度縯變規律,該研究採用頂部點火上吸式(top-lit up draft,簡稱TLUD)固定床氣化爐研究瞭農業廢棄物的氣化行為,重點攷察瞭不同空氣流量下爐內溫度分佈、燃氣成分和熱值的變化規律,探討瞭生物質氣化過程機理.結果錶明,氣化過程明顯分為2箇階段,即揮髮份的析齣和焦炭的緩慢氣化.整箇氣化過程中燃氣的熱值可穩定維持在3 MJ/m3以上,溫度場的縯變過程與波傳遞具有相似性,花生殼和稻殼的最佳空氣噹量比分彆為0.31和0.35,且其燃氣中焦油含量很低,分彆為0.25、0.49 g/m3.該研究為TLUD固定床氣化爐的設計和運行提供瞭有益的參攷.
위료료해재고정상기화로중생물질적기화특성화로내온도연변규률,해연구채용정부점화상흡식(top-lit up draft,간칭TLUD)고정상기화로연구료농업폐기물적기화행위,중점고찰료불동공기류량하로내온도분포、연기성분화열치적변화규률,탐토료생물질기화과정궤리.결과표명,기화과정명현분위2개계단,즉휘발빈적석출화초탄적완만기화.정개기화과정중연기적열치가은정유지재3 MJ/m3이상,온도장적연변과정여파전체구유상사성,화생각화도각적최가공기당량비분별위0.31화0.35,차기연기중초유함량흔저,분별위0.25、0.49 g/m3.해연구위TLUD고정상기화로적설계화운행제공료유익적삼고.
The gasification behavior of agriculture waste was investigated using a Top-lit Up Draft (TLUD) fixed-bed gasifier system which consists of four subsystems (gasifier reaction system, temperature monitor system, tar sampling system, and gas measurement system), in an attempt to find out the influence of air flow on the gasifier’s temperature distribution, gas component, and heating value, and discuss the gasification mechanism of biomass. In the study, peanut shells and rice husks were chosen as experiment material. The reactor is made fromФ219 mm×6 mm stainless steel pipe with length of 800 mm. After the reactor filled up with sample materials (about 3.5 kg), a certain amount of air (range from 2.5 m3/h to 4.0 m3/h) was pumped in at the bottom, and the sample was lit at the top. The temperature was then tested by a temperature monitoring system, and the gas product was detected by a Gasboard-3100P-type multi-component portable infrared gas analyzer (Quartet Photoelectric Technology Co., Ltd. Wuhan, China), and the tar was collected by a tar sampling system. From the results of the investigation, the gasification process lasted about 100 min, and was divided into two stages. First, the main reaction was biomass drying, volatile releasing, and char gasification, and the main gas products were CO2, CO, H2, and CH4. About 50 min later, it went into the second stage, and the oxidization of solid char residue played a major role in the gasifier with a large amount of CO production. Throughout the whole reaction, the heating value of gas products was a minimum of 3 MJ/m3, and the evolution of the gasfier temperature profile was very similar with that of wave propagation. During the first stage of gasification, the maximum temperature of the gasifier was 730℃;when it switched into the second stage, the main reaction occurred at the bottom, and the max temperature would rise up to 1000℃. The airflow rate can be converted to the Air/Fuel equivalence ratio (ER), the most important aspect of gasifier operation. ER had great influence on biomass gasification property, and higher ER was favorable for the enhancing of gas yield, however, it had different effects on the releasing of flammable gas (CO and H2). The optimum gasfication condition was achieved when ER is 0.31 and 0.35 for peanut shell and rice husk, respectively, and the tar content of gas is very low (as low as 0.25g/m3 and 0.49g/m3, respectively). This study would be helpful to the design and operation of TLUD fixed-bed gasifiers.