中试规模动力波吹脱技术分离老龄化垃圾渗滤液中的高浓度氨氮

为解决老龄化垃圾渗滤液的脱氨难题,采用动力波吹脱技术对老龄化垃圾渗滤液进行氨氮吹脱分离,探究了吹脱时间、pH、气液比、温度和进水氨氮浓度对吹脱效能的影响。单因素实验结果表明：前3 h吹脱去除率增长最快,5 h后吹脱去除率变化较小;高pH下游离氨占比增大,对吹脱更为有利,pH为10.5左右时的工艺最为经济;动力波吹脱适用温度范围广,在10 ℃和25 ℃时,去除率可达72.62%和90.68%;增加气液比可提高吹脱效率,但当气液比超过129后,吹脱效果增幅不明显;氨氮浓度对吹脱去除率的影响较小。正交实验结果显示：温度方差最大,pH、气液比方差次之,进水氨氮浓度方差最小,即表明温度对动力波吹脱脱氨影响最为显著;pH、气液比也是重要影响因素;初始氨氮浓度对吹脱效率影响不显著。在25 ℃、pH=10.5、气液比为129时,吹脱5 h的最优条件下,氨氮去除率约91.25%~94.15%。相比传统吹脱工艺,动力波吹脱技术能大幅提高氨氮分离效率。     

南京河西地区岩土体剪切波速与土层深度的关系

南京河西地区是南京市重点开发的新市区,该区域工程地质条件相似,主要为长江高河漫滩地质地貌单元。本文选取该地区47个典型钻孔的岩土体剪切波速资料,采用三种数学模型进行统计回归分析,运用相关系数R(或测定系数R2)检验Vs—H之间的线性相关关系,并根据计算的SD值选择较优的数学模型。统计结果表明,该地区各类岩土体的Vs—H线性相关关系显著,说明采用上述数学模型进行Vs—H回归是可行的。对两个工程场地进行剪切波速预测,并对场地类别作出划分,检验结果表明,该地区各类岩土体的Vs—H经验关系是可靠的,符合当地岩土特征,在样本深度范围内有足够的工程应用精度,可以应用。     

煤与瓦斯突出冲击波及瓦斯气流所致伤害研究

为揭示煤与瓦斯突出过程中冲击波及瓦斯气流传播特性,针对这种突出做功随瓦斯压力、煤的普氏系数和煤的放散初速度变化的特征,运用气体动力学理论,建立冲击波超压、冲击瓦斯流速度与传播距离以及煤层瓦斯压力等参数的关系,计算不同超压下瓦斯气流传播伤害的范围。理论计算与现场测试结果表明,突出冲击波属惰性弱冲击波;波阵面上的超压传播伤害距离与突出时瓦斯膨胀的强度、巷道断面及巷道壁面的摩擦力和局部阻力等因素有关;冲击产生的高压瓦斯气流是造成巷道内大量人员窒息伤亡的主要诱因;突出能量瞬间释放没有补给,冲击波及瓦斯气流会在巷道阻力等因素作用下迅速衰减。     

声波辅助清灰袋滤器的研究

通过改变声波的频率、声压等参数,观察了单独反吹清灰和声波辅助反吹清灰的试验结果。试验证明,声波能有效地降低滤袋的残余阻力和残留粉尘重量。     

Connecticut statewide sTEP wave evaluation

INTRODUCTION: Selective Traffic Enforcement Programs (sTEPs) are a proven method to change motorists' behavior. Since 1997, the Connecticut DOT's Division of Highway Safety has organized a statewide seat belt enforcement program, with sTEP waves every three or four months. To date, 28 waves have been implemented. METHOD: Pre-wave and post-wave seat belt observation surveys are conducted by both state and municipal police across the state. Survey results, as well as a summary of all enforcement activity during the wave, are submitted for evaluation. RESULTS: Connecticut seat belt use has continued to rise from one wave to the next in a predictable "saw blade" pattern. CONCLUSIONS: The data clearly demonstrate that agencies that have participated in a greater number of waves have experienced the greatest increase in belt use. Belt use has not yet plateaued and additional sTEP enforcement seems indicated. However, evidence from other states suggests that a plateau may occur somewhere in the mid 80% range. IMPACT ON INDUSTRY: Should this occur, Connecticut will work toward strengthening the round the clock model, emphasizing the importance of aggressive primary enforcement.     

爆炸冲击荷载对动物杀伤作用距离的试验研究

采用3 kg、5 kg和10 kg装药在自由场中爆炸,观察分析距炸点不同距离的家兔在爆炸冲击波下的伤亡情况.试验同时使用冲击波超压测量仪记录不同位置的冲击波超压.试验结果表明,在超压小于0.08×105 Pa时家兔基本安全,3 kg、5 kg、10 kg炸药爆炸时的安全距离分别为20 m、25 m、30 m.     

气体密度和初压对炸药爆炸压力衰减的影响

为研究气体密度和初压对爆炸压力的影响,以球形装药为例,在LS-DYNA中模拟不同气体密度、环境初压和真空度条件的TNT炸药爆炸,分析空气冲击波的形成过程和衰减规律。研究结果表明：在爆炸初期冲击波的波阵面位于爆炸产物边界,产物压力与冲击波压力存在强耦合作用;随着爆炸产物自身压力下降,其膨胀速度减慢,冲击波开始与爆炸产物分离,当产物中心压力下降为环境初压时,冲击波与爆炸产物彻底分离,其后以空气冲击波的形式独立传播。降低气体密度可以通过抑制冲击波形成,大幅降低爆炸压力;减小环境初压则通过加快冲击波的衰减速度,也可以在一定程度上降低爆炸压力。相较于单独改变密度和压力,提高真空度对冲击波压力的减小效果更好;近真空环境下无法形成空气冲击波,爆炸压力衰减速度快。     

高海拔排土场边坡安全稳定性SBAS-InSAR监测

为解决高海拔排土场边坡安全稳定性监测中常规监测仪器布置和人员值守的高投入、高风险问题,分析西藏山南桑日县某排土场边坡25景Sentinel-1A数据,利用短基线集合成孔径雷达干涉测量(SBAS-InSAR)技术监测终了排土场边坡从2018年11月4日-2020年12月23日期间的地表形变,采用基线估计状态空间模型、自适...     

爆炸冲击波作用下靶板的塑性大变形响应研究

对四边约束方形靶板 ,在爆炸冲击波作用下的塑性大变形响应情况 ,进行了理论分析与试验研究。运用能量守恒的方法 ,同时考虑试验过程中靶板的边界约束条件 ,得到了四边约束方形靶板在爆炸冲击波作用下发生塑性大变形时挠度的半经验公式。理论计算与试验结果吻合性较好 ,这种方法可应用于板结构在爆炸冲击波作用下的毁伤或防护方面的工程预测     

Differences and similarities of gas and dust explosions: A critical evaluation of the European ‘ATEX’ directives in relation to dusts

Explosive gas mixtures and explosive dust clouds, once existing, exhibit similar ignition and combustion features. However, there are two basic differences between dusts and gases which are of substantially greater significance in design of safety standards than these similarities. Firstly, the physics of generation and up-keeping of dust clouds and premixed gas/vapour clouds are substantially different. This means that in most situations where accidental explosive gas clouds may be produced quite readily, generation of explosive dust clouds would be highly unlikely. Secondly, contrary to premixed gas flame propagation, the propagation of flames in dust/air mixtures is not limited only to the flammable dust concentration range of dynamic clouds. The state of stagnant layers/deposits offers an additional discrete possibility of flame propagation.

The two European Directives 94/9/EC (1994) and 1999/92/EC (1999) primarily address gases/vapours, whereas the particular properties of dusts are not addressed adequately. Some recent IEC and European dust standards resulting from this deficiency are discussed, and the need for revising the two directives accordingly is emphasized.