挡烟垂壁作用下狭长通道内烟气输运特征研究

为揭示挡烟垂壁对狭长通道火灾烟气特征及温度分布的影响,运用火灾动力学软件FDS,研究了狭长通道内不同高度挡烟垂壁下火灾烟流运动行为,重点探讨了密度跳跃过程及近火源区烟气特征参数变化。结果表明:挡烟垂壁增加了密度跳跃中翻滚区的长度,缩小了卷吸空气范围,造成烟气质量流率相应减少;挡烟垂壁对烟气垂直速度分布的影响主要作用在挡烟区,且与垂壁高度有关;垂高大于0.3 m,受挡烟垂壁高度影响,在垂直高度1.5~2 m位置出现一定速度的烟气逆流,速度分布曲线呈现与无挡烟垂壁不同的凹陷区,非挡烟区烟气垂直速度服从高斯分布;与无挡烟垂壁相比,挡烟垂壁上游顶棚附近温度普遍增高,下游温度衰减速率随挡烟垂壁高度的增加而加快。     

ISM耦合ANP矿工安全注意力衰减影响因素模型

为了减少煤矿安全事故的发生,从“纵向过程观”角度,引入矿工安全注意力控制空间、安全信息分配空间和安全行为结果空间,建立矿工安全注意力衰减影响因素模型。首先,基于文献研究,建立矿工安全注意力衰减影响因素体系,一共包含12个指标;其次,利用解释结构模型（ISM）构建矿工安全注意力衰减的3级递阶有向图;最后,采用网络层次分析法（ANP）构建矿工安全注意力衰减影响因素的权重模型,并借助Super Decision（SD）软件求解。结果表明:安全自制力、行为习惯、工作负荷、风险应对力以及安全信息刺激频率为表层直接影响因素;安全认知、工作要求、作业环境特征、安全信息变化多样性和风险感知力为中层间接影响因素;管理方式和安全信息刺激强度为深层根本影响因素。主要影响因素有:安全认知、安全自制力、行为习惯、管理方式、安全信息刺激频率以及风险感知力。     

人因脆弱性对安全注意力衰减的SEM研究

为深入研究人因脆弱性影响因素对安全注意力衰减的深层次作用关系,基于复杂系统脆弱性（CSV）理论,采用因子分析法对人因脆弱性进行主成分分析,提取8个人因脆弱性因子;然后,引入安全注意力配置作为中介变量,借助结构方程模型技术建立人因脆弱性对安全注意力衰减的SEM。结果表明:安全注意力配置与安全素质、安全意识、受教育程度、工作年限、安全知识、工作倦怠、安全心理等因子显著相关;安全注意力衰减与安全意识、安全自制力、工作倦怠、安全心理等因子显著相关;安全注意力配置与安全自制力的关系不显著;安全注意力衰减与安全素质、受教育程度、工作年限、安全知识的关系不显著。     

青岛地铁超浅埋段爆破振动监测数据特征研究

为了更好地掌握超浅隧道爆破振动规律,以青岛地铁太延区间超浅埋隧道爆破振动为例进行了研究。在地表7层建筑物各层相同位置布置测振仪对爆破振速进行实时全面监测,通过对掏槽眼、辅助眼、周边眼爆破时单段最大起爆药量与实测振速关系的回归拟合,发现此隧道的爆破振动规律并不符合一般埋深隧道适用的萨道夫斯基公式,据此提出了临空自由面影响系数,得到了萨道夫斯基计算公式的修正拟合系数。修正后的萨道夫斯基公式可更好地反映3类炮眼爆破的实际振速衰减规律,该规律可为城市地铁类似隧道的爆破施工提供参考依据。     

Dendroremediation of trinitrotoluene (TNT) part 1: Literature overview and research concept

BACKGROUND, AIM AND SCOPE: For decades, very large areas of former military sites have been contaminated diffusely with the persistent nitroaromatic explosive 2,4,6-trinitrotoluene (TNT). The recalcitrance of the environmental hazard TNT is to a great extent due to its particulate soil existence, which leads to slow but continuous leaching processes. Although improper handling during the manufacture of TNT seems to be a problem of the past in developed countries, environmental deposition of TNT and other explosives is still going on unfortunately, resulting from thousands of unexploded ordnance or low order explosions at munitions test areas and at current battlefields. OBJECTIVE: Sustainable phytoremediation strategies for explosives in Germany, which intend to use trees to decontaminate soil and groundwater ('dendroremediation'), have to consider that most of the former German military sites are already covered with woodlands, mainly with conifer stands. Therefore, parallel investigation of the remediation potential is necessary for both of the selected hybrids of fast growing broadleaf trees, which are waiting for planting and forest conifers, which have already proven for decades that they are able to grow on explosive contaminated sites. MAIN FEATURES: A short literature review is given regarding phytoremediation of TNT with herbaceous plants and some general aspects of dendroremediation are discussed. Furthermore, an overview of our TNT-dendroremediation research network is introduced, which has the strategic goal to make dendroremediation more calculable for a series of potent trees for site-adapted in situ application and for the assessment of tree remediation potentials in natural attenuation processes. RESULTS AND DISCUSSION: Some of our methods, results and conclusions yet unpublished are presented. For a preliminary calculation of area-related annual TNT dendroremediation potential of five-year-old trees, the following values were assessed: Salix EW-13 6.0, Salix EW-20 8.5, Populus ZP-007 4.2, Betula pendula 5.2, Picea abies 1.9 and Pinus sylvestris 0.8 g m(-2) a(-1). For a 45-year-old spruce forest, an annual natural attenuation potential of 4.2 g TNT m(-2) a(-1) was found. CONCLUSION, RECOMMENDATIONS AND PERSPECTIVE: Our main results deliver quantitative proposals for dendroremediation strategies in situ and provide decision aids. Also aspects of growth of raw materials for energy production are considered. Our dendroremediation research concept for TNT and its congeners can be easily completed for other trees of interest and it can also be applied to herbaceous plants. Knowing the current bottlenecks of phytoremediation and considering the known environmental behaviour of other contaminants, elements of our methodological approach may be easily adapted to those pollutant groups, e.g. for pesticides, pharmaceuticals, PAHs, chlorinated recalcitrants and, with some restrictions, to inorganics and to multiple contaminations. Our dynamical dendrotolerance test systems will help to predict tree growth on polluted areas. To provide some light into the black box of TNT dendroremediation, experimental data regarding the uptake, distribution and degradation of [14C]-TNT in mature tree tissues will be reported in the second part of this publication.     

Geochemical techniques on contaminated sediments-river basin view

The big flood in the upper Elbe River catchment area has revealed a wide spectrum of problems with contaminated sediments. So far, an effective strategy for managing contaminated sediments on a river basin scale is still missing and it seems that not much has been learned from the lessons received during the last decade. In the following overview, special emphasis is given to the utilization of geochemically-based techniques for sediment remediation, which can be applied in different parts of a river basin. The examples presented here are mostly from the Elbe River catchment area. In general, new technical problem solutions need a set of practical process knowledge that uses a wide range of simulation techniques, as well as models in different spatial and temporal scales. The evaluation of recent flood events clearly demonstrates the importance of chemical expertise in the decision-making process for the sustainable development in river basins.     

Natural attenuation/phytoremediation in the vadose zone of a former industrial sludge basin

The natural attenuation of polyaromatic hydrocarbons (PAHs) in the vadose zone of a naturally revegetated former industrial sludge basin (0.45 ha) was examined. This was accomplished by comparing the concentration of 16 PAH contaminants present in sludge collected below the root zone of plants with contaminants present at 3 shallower depths within the root zone. Chemical analysis of 240 samples from 60 cores showed the average concentration of total and individual PAHs in the 0-30 cm, 30-60 cm, and bottom of the root zone strata were approximately 10, 20, and 50%, respectively, of the 16, 800 ppm average total PAH concentration in deep non-rooted sludge. Statistically significant differences in average PAH concentrations were observed between each strata studied and the non-rooted sludge except for the concentrations of acenaphthene and chrysene present at the bottom of the root zone in comparison to sludge values. The rooting depth of the vegetation growing in the basin was dependent on both vegetation type and plant age. Average rooting depths for trees, forbs (herbaceous non-grasses), and grasses were 90, 60, and 50 cm, respectively. The deepest root systems observed (100-120 cm) were associated with the oldest (12-14 year-old) mulberry trees. Examination of root systems and PAH concentrations at numerous locations and depths within the basin indicated that plant roots and their microbially active rhizospheres fostered PAH disappearance; including water insoluble, low volatility compounds, i.e. benzo(a)pyrene and benzo(ghi)perylene. The reduced concentration of PAHs in the upper strata of this revegetated former sludge basin indicated that natural attenuation had occurred. This observation supports the concept that through appropriate planting and management practices (phytoremediation) it will be possible to accelerate, maximize, and sustain natural processes, whereby even the most recalcitrant PAH contaminants (i.e. benzo(a)pyrene) can be remediated over time.     

Occurrence and attenuation of specific organic compounds in the groundwater plume at a former gasworks site

The changing contaminant pattern with travelled distance was investigated in the anaerobic groundwater plume downstream from an extended zone containing residual NAPL at a former gas manufacturing plant. With increasing distance, O- and N-heterocyclic aromatic compounds are enriched in the plume relative to the usually assessed coal tar constituents (poly- and monocyclic aromatic compounds). In a first approximation, the overall concentration decrease of the investigated compounds follows a first order overall decay. The half life distance in the plume downgradient from the source varied between 20 m for benzene and up to 167-303 m for alkyl-naphthalenes. Acenaphthene is degraded only within about 50 m downstream from the source area, then its concentration remains constant (ca. 180 microg/l) and far above the legal limit. Dimethyl-benzofurans were the most recalcitrant among all compounds which could be quantified with the analytical method available. The overall groundwater contamination in the plume is seriously underestimated if only BTEX and 16-EPA-PAHs are monitored.     

Changes in enantiomeric fraction as evidence of natural attenuation of mecoprop in a limestone aquifer

Natural attenuation of the chiral pesticide mecoprop [2-(2-methyl-4-chlorophenoxy)propionic acid] has been studied by determining changes in its enantiomeric fraction in different redox environments down gradient of a landfill in the Lincolnshire Limestone. Previous studies have shown that mecoprop degrades predominantly aerobically and that differences in the biological behaviour of the two enantiomers will change their relative proportions during biodegradation. Originally deposited as a racemic mixture, there has been no change in the enantiomeric fraction in the most polluted part of the landfill plume where conditions are sulphate reducing/methanogenic. In the nitrate-reducing zone, the proportion of (S)-mecoprop increases, suggesting preferential degradation of (R)-mecoprop; while in the aerobic zone, the proportion of (R)-mecoprop increases, suggesting faster degradation of (S)-mecoprop. Mecoprop persistence in the confined Lincolnshire Limestone further downdip is explained by inhibition of degradation in sulphate-reducing conditions, which develop naturally. Laboratory microcosm experiments using up to 10 mg l(-1) of mecoprop confirm these inferences and show that under aerobic conditions, (S)-mecoprop and (R)-mecoprop degrade with zero-order kinetics at rates of 1.90 and 1.32 mg l(-1) day(-1), respectively. Under nitrate-reducing conditions (S)-mecoprop does not degrade, but (R)-mecoprop degrades with zero-order kinetics at 0.65 mg l(-1) day(-1) to produce a stoichiometric equivalent amount of 4-chloro-2-methylphenol. This metabolite only degrades when the (R)-mecoprop has disappeared. The addition of nitrate to a dormant iron-reducing microcosm devoid of nitrate stimulated anaerobic degradation of (R)-mecoprop after a lag period of 21 days. There was no evidence for enantiomeric inversion. The study demonstrates the sensitivity of changes in enantiomeric fraction for detecting natural attenuation, and reveals subtle differences in mecoprop degradation in different redox environments within the Lincolnshire Limestone aquifer.     

基于城市火灾风险的消防站分级覆盖选址模型——以济南市区为例

为更科学规划消防站选址，实现有限资源下应急资源的合理配置，提高消防站联动效率，根据“不同火灾风险等级的需求点应得到主管消防站和不同数量增援消防站服务”的原则，提出1种消防站分级覆盖选址模型，同时使用覆盖衰减函数表示消防站对需求点的覆盖度；基于遗传算法设计消防站分级覆盖选址模型的求解流程；以济南市区为例，基于POI和火灾数据，使用核密度分析法进行城市火灾风险分级，进而对选址模型进行验证。结果表明:以覆盖火灾风险值为评价指标，分级覆盖选址模型的选址结果优于现状消防站、广义最大覆盖模型、P-中位模型和P-中心模型。