门克庆井田水文地质条件对矿井开采顺序的影响

门克庆矿井水文地质类型为"复杂型",矿井达产时,设计布置3-1煤1个工作面和2-2中煤1个工作面,2层煤之间平均距离为34 m,2煤层回采过程中主要的充水含水层均为直罗组底部七里镇砂岩含水层。该含水层水压力大,达到4 MPa,疏放水钻孔单孔涌水量最大达到180 m3/h,富水性相对较强,且距离2-2中煤距离多小于5 m,导致2-2中煤巷道掘进过程中出现顶板淋水严重,锚索锚固困难等现象,无法保障2-2中煤的安全生产。笔者提出先开采下层3-1煤,待七里镇砂岩含水层水量、水压被疏降至可以保障2-2中煤顺利掘进和生产时,再开采上层2-2中煤的"反层序"采煤方法。生产实践证明,该方案是可行的。      

盐下转换波迭前深度偏移成像：墨西哥湾Mahogany地区

用迭前深度偏移方法处理了墨西哥湾Ｍａｈｏｇａｎｙ地区的四分量海义革震（４Ｃ－ＯＢＳ）测量数据中的水平分量,水平分量数据主要包含Ｐ－Ｓ转换波能量,这些转换波在从Ｐ波变为Ｓ波的传播路径中至少有一次波转换。利用本文介绍的技术,浅层低速沉积、盐体的顶和底以脑盐下沉积都得到了成像。     

Environmental impacts of dredging on seagrasses: a review

Main potential impacts on seagrasses from dredging and sand mining include physical removal and/or burial of vegetation and effects of increased turbidity and sedimentation. For seagrasses, the critical threshold for turbidity and sedimentation, as well as the duration that seagrasses can survive periods of high turbidity or excessive sedimentation vary greatly among species. Larger, slow-growing climax species with substantial carbohydrate reserves show greater resilience to such events than smaller opportunistic species, but the latter display much faster post-dredging recovery when water quality conditions return to their original state. A review of 45 case studies worldwide, accounting for a total loss of 21,023 ha of seagrass vegetation due to dredging, is indicative of the scale of the impact of dredging on seagrasses. In recent years, tighter control in the form of strict regulations, proper enforcement and monitoring, and mitigating measures together with proper impact assessment and development of new environmental dredging techniques help to prevent or minimize adverse impacts on seagrasses. Costs of such measures are difficult to estimate, but seem negligible in comparison with costs of seagrass restoration programmes, which are typically small-scale in approach and often have limited success. Copying of dredging criteria used in one geographic area to a dredging operation in another may in some cases lead to exaggerated limitations resulting in unnecessary costs and delays in dredging operations, or in other cases could prove damaging to seagrass ecosystems. Meaningful criteria to limit the extent and turbidity of dredging plumes and their effects will always require site-specific evaluations and should take into account the natural variability of local background turbidity.