首页> 外文会议>36th Heat Transfer and Fluid Mechanics Institute, Jun 3-4, 1999, Sacramento >EMISSION AND ABSORPTION MEASUREMENTS OF ENERGETIC MATERIAL COMBUSTION IN MOLTEN SALT
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EMISSION AND ABSORPTION MEASUREMENTS OF ENERGETIC MATERIAL COMBUSTION IN MOLTEN SALT

机译:盐溶液中能量物质燃烧的排放和吸收测量

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The potential to use molten salts as high-temperature reaction media has been recognized for many years. In particular, the molten salt destruction (MSD) process has been developed as an attractive means of destroying waste energetic materials (Upadhye et al, 1994). This process involves injecting a slurry composed of air, water, and waste energetic materials into a molten salt bath, where the energetic materials react to produce mostly CO_2, N_2, and H_2O (Watkins et al, 1994). While MSD has been demonstrated to be a cost-effective and environmentally-benign technique for destroying energetic materials, there are fundamental questions that need to be addressed. For example, data are lacking on the extent to which molten salts are chemically altered by the injection of energetic materials, and a better understanding of the intermediate chemical species present during energetic waste decomposition is needed. In addition, little is known about general combustion behaviors such as bubble formation characteristics, gas evolution, and overall lifetimes of energetic samples immersed in molten salts. This study examines the characteristics of energetic materials injected into molten salt baths. Behaviors of the high explosives LX-17 (92.5 wt% l,3,5-triamino-2,4,6-trinitrobenzene (TATB), 7.5 wt% Kel-F 800 plastic binder), LX-04 (85 wt% octahydro-l,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX), 15 wt% Viton A plastic binder), and 2,6-dinitrotoluene (DNT) were studied when these materials were immersed into LiCl-KCl-NaCl eutectic at 700 ℃. This temperature is representative of conditions encountered in MSD reactors (Upadhye et al, 1994 and Watkins et al, 1994). The LX-17, LX-04 and DNT samples were initially 0.33 g. In addition to measuring absorption and emission spectra, high-speed photographs were taken during sample decomposition.
机译:多年来人们已经认识到使用熔融盐作为高温反应介质的潜力。尤其是,熔融盐破坏(MSD)工艺已被开发为破坏废物含能材料的一种有吸引力的手段(Upadhye et al,1994)。该过程涉及将由空气,水和废高能材料组成的浆液注入熔融盐浴中,在高能盐材料中,高能材料反应生成大部分CO_2,N_2和H_2O(Watkins等,1994)。尽管已证明MSD是销毁高能材料的一种经济高效且对环境有益的技术,但仍需要解决一些基本问题。例如,缺乏有关通过注入高能材料而化学改变熔融盐的程度的数据,并且需要对高能废物分解过程中存在的中间化学物质有更好的了解。此外,对于一般的燃烧行为,如气泡形成特性,气体逸出以及浸入熔融盐中的高能样品的总寿命,知之甚少。这项研究检查了注入熔盐浴中的高能材料的特性。高炸药LX-17(92.5 wt%l,3,5-三氨基-2,4,6-三硝基苯(TATB),7.5 wt%Kel-F 800塑料粘合剂),LX-04(85 wt%八氢将-1,3,5,7-四硝基-1,3,5,7-四唑啉(HMX),15 wt%的Viton A塑料粘合剂和2,6-二硝基甲苯(DNT)浸泡在其中LiCl-KCl-NaCl在700℃下共晶。该温度代表MSD反应器中遇到的条件(Upadhye等,1994和Watkins等,1994)。 LX-17,LX-04和DNT样品最初为0.33 g。除了测量吸收光谱和发射光谱外,在样品分解过程中还拍摄了高速照片。

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