济南市地下水资源现状分析及开发利用建议

本文采用较新的统计资料,对济南市地下水资源的开发利用现状及开采潜力,以行政区划为单元进行了分析论证.针对地下水资源开发利用中存在的环境水文地质问题,提出了开发利用规划和建议.     

Fatty Acid Composition Analyses of the DCMU Resistant Mutants of Nannochloropsis oculata (Eustigmatophyceae)

1　Introduction　Nannochloropsissp .areoneofpotentialsourcesofpolyunsaturatedfattyacids ,especiallytheeicosapen taentaenoicacid (EPA ,C2 0∶5 ) ,whichisimportantforbothanimalsandhumans .　Thefattyacidcompositionofthisalgaisaffectedbyvariousenvironmentalfactors ,suchaslightintensity(Sukeniketal.,1989;Sukeniketal.,1990 ) ,imply ingthatafactorinfluencingthephotosyntheticprocessmayaffectcellularfattyacidsynthesisandtheirmetabolism .AselectionprogramofincreasingcellularEPAcontenthasbeencarriedo…     

Deep Processes of Basin Evolution:A Case Study of the Southern Songliao Basin and Adjacent Area,NE China in Mesozoic-Cenozoic

1IntroductionOne of the key factors related to basin geody-namics is deep process controlling formation and evolution of sedimentary basin. Depth and tempera-ture of asthenosphere,existence of mantle plume,occurrence of mantle melting,and amounts of melts under depressurization during thinning of lithosphere are controlling factors influenced formation and characteristics of extensional basin directly (Li,1994). Rifting is probably governed by frictional forces exerted on the base of litho…     

华北地台东部石炭系—二叠系优质煤储层形成分布控制因素

优质煤储层在此指厚度大、分布广、储集物性好的煤层。沉积相对优质煤储层的形成和分布有重要控制作用。通过浅海和泻湖淤积填平发育起来的潮坪环境和三角洲环境是最有利的优质煤储层形成环境,煤储层厚度大、分布广。沉积环境对煤储层中的灰分含量和镜质组含量有重要影响,而灰分含量和镜质组含量又直接影响煤储层的储集物性。灰分充填了煤储层中的孔隙,其含量越高,储集物性越差;镜质组有利于割理的形成,其含量越高,储集物性越好。由于在灰分含量、煤岩显微组分等方面的差异,潮坪环境沉积的煤储层的储集物性优于三角洲的煤储层,下三角洲平原沉积的煤储层优于上三角洲平原沉积的煤储层。海平面变化对优质煤储层的形成和分布也有重要控制作用。高位体系煤储层富集,单层厚度大,横向分布相当稳定,尤其是高位体系域晚期,是形成优质煤储层最有利的层位。而水进体系域煤储层稀少,单层厚度小,横向分布不稳定,不利于优质煤储层形成。     

Correlations between heavy metals and organic carbon extracted by dry oxidation procedure in urban roadside soils

The organic fraction in soils has a significant influence on heavy metal transport. In this study, the organic carbon content was measured by dry oxidation procedure from 21 Xuzhou urban roadside soils to assess the relationships between the concentrations of heavy metals (Pb, Cu, Zn, and Cr) and the amount of organic carbon. The anthropogenic heavy metals (e.g. Pb, Cu, Zn) were strongly correlated with organic carbon (denoted by C_org−c) extracted by dry oxidation while natural heavy metal (e.g. Cr) showed no correlation to the C_org−c. The anthropogenic heavy metals were also strongly correlated with the amount of the total carbon. These results show that the anthropogenic heavy metals are mainly enriched in the organic matter in the Xuzhou urban roadside soils.     

Distribution of Cd,Pb, Zn and Cu and their chemical speciations in soils from a peri-smelter area in northeast China

An exploratory study on soil contamination of heavy metals was carried out surrounding Huludao zinc smelter in Liaoning province, China. The distribution of total heavy metals and their chemical speciations were investigated. The correlations between heavy metal speciations and soil pH values in corresponding sites were also analyzed. In general, Cd, Zn, Pb, Cu and As presented a significant contamination in the area near the smelter, comparied with Environmental Quality Standards for Soils in China. The geoaccumulation index showed the degree of contamination: Cd > Zn > Pb > Cu > As. There was no obvious pollution of Cr and Ni in the studied area. The speciation analysis showed that the dominant fraction of Cd and Zn was the acid soluble fraction, and the second was the residual fraction. Pb was mostly associated with the residual fraction, which constituted more than 50% of total concentration in all samples. Cu in residual fraction accounted for a high percentage (40–80%) of total concentration, and the proportion of Cu in the oxidizable fraction is higher than that of other metals. The distribution pattern of Pb and Zn was obviously affected by soil pH. It seemed that Pb and Zn content in acid solution fraction increased with increasing soil pH values, while Cd content in acid soluble fraction accounted for more proportion in neutral and alkaline groups than acidic one. The fraction distribution patterns of Cu in three pH groups were very similar and independent of soil pH values. And the residual fraction of Cu took a predominant part (50%) of the total content.     

青藏高原中、东部局地因素对地温的双重影响(Ⅰ): 植被和雪盖

青藏高原冻土区地温既受海拔、纬度和经度(干燥度)区域地带性规律控制, 同时它又受植被、雪盖、砂层、 水被和地质构造等局地因素的显著影响. 局地因素对地温的影响具有双重性: 在不同域值条件下, 它可增高或降低地温. 地温随植被覆盖度减小而逐渐增高, 但覆盖度减到0～20%时, 地温反而降低. 在青藏高原东部、南部和腹部的高山区, 冷季降雪多, 很多地段为稳定积雪区, 雪盖厚, 持续时间长, 对浅层地温起保温作用;而高原腹部的高平原、河谷和盆地冷季降雪较少, 雪盖薄, 持续时间较短, 一般保温作用微弱. 当雪盖厚度超过20 cm以后, 保温作用即开始增强;在暖季因积雪存在时间短, 雪盖薄, 短期内对浅层地温起冷却作用. 总之, 每种局地因素迫使地温向相反方向转化阶段是一个区间值, 为渐变过程. 随时空尺度变化, 局地因素的影响变化很大. 有些地段, 几种局地因素共同作用, 加上活动构造和地形、地貌等的影响, 使地温的时空分布和局地因素对其影响或控制变得错综复杂. 因此, 研究和预测地温特征和变化趋势, 需要在监测植被和积雪作用的基础上进行参数选择、 验证和优化.     

寒区线性工程沿线冻土区的植被恢复

寒区油气管道、公路、铁路等线性工程占地、建设和开挖对沿线寒区生态环境是一个切割、破碎的过程, 对自然植被和下伏冻土造成了很大的扰动. 管道泄露引发的油污还可引起植被的退化和死亡. 植被覆盖层破坏后改变了原有的地气界面之间的水、热交换条件和力学性质, 反过来又可加速引发下伏冻土和线性工程地基的退化. 基于保护线性工程地基及下伏冻土的目的, 同时顺应环境保护的要求, 目前就寒区线性工程的植被恢复问题已经有许多探索和实践. 当前, 寒区植被恢复注重最低限度的人为介入干预下的自然恢复, 根据线性工程沿线土壤、湿度、营养条件、物种分布和丰度, 视具体情况选择物种, 确定建植方法. 阿拉斯加管道和青藏铁路植被恢复上的经验和方法, 可为拟建的冻土区中俄输油管道项目沿线的植被恢复问题提供科学的参考和借鉴.     

祁连山不同植被类型对积雪消融的影响

为研究祁连山植被对积雪消融的影响, 利用人工调查积雪深度逐日变化量和积雪盖度变化, 并结合空气雪面感热通量(SH)观测, 对祁连山水源林生态站排露沟流域海拔2 600～2 700 m青海云杉林、灌丛林、林缘、阳坡草地在2003-2007年的积雪消融进行了研究, 每年的观测从10月降雪开始到翌年5月积雪消融完结束, 共获取数据134 400个. 结果表明: 当SH<0时, 积雪消融停止;当SH>0时, 积雪消融开始;植被可以减缓积雪消融速率, 有植被的地方消融速率减慢, 反之则加快;不同植被消融速率大小顺序为草地>林缘>灌木林>乔木林;同一植被、不同坡向消融速率不同, 半阳坡云杉林＞半阴坡云杉林＞阴坡云杉林. 积雪含水率随气温升高而增大, 1月融化积雪占整个积雪的5%, 2月增大到28%, 大量积雪在3月消融, 占55%. 从坡位看, 下坡消融速率最大;在一个垂直带上, 低海拔消融速率大于高海拔. 温度是影响积雪消融的主要因子, 积雪消融速率随温度升高而增大, 反之则减小.     

东北多年冻土区埋地输油管道周围温度场特征非线性分析

为解决冻土区输油管道周围土壤的温度计算问题,根据考虑相变瞬态温度场的控制微分方程,应用Galerkin法推导出了二维温度场的有限元计算公式.以东北多年冻土区中俄原油管道工程为背景,根据该工程区的冻土条件和气候条件,应用该方法对温热型输油管道土壤温度场进行了计算预报与对比分析.结果表明:对于输送油温为15 ℃、直径为0.914 m以及管顶埋深为2.0 m的管道,在没有铺设保温材料情况下,管顶之上的土壤在管道运行的第1年就达到热平衡状态,同时土壤融化速率在第1年达到最大,随后4a时间里迅速减小,第5年后融化速率变化趋于稳定;管道运行一段时间后,管道周围的融化圈随冷暖季节的变化呈交替式的扩展;在管道运行30 a后,融深＞10 m,即管底下的融化层厚＞7 m,而在铺设5～8 cm的聚氨酯保温材料后,融深控制在3.08～3.88 m,即管底下融化层厚为0.2～1.0 m.因此,合理使用保温方法能有效防止冻土区管道冻害的发生,同时达到保护冻土环境的目的.