黄河三角洲河口地区经济发展思路探讨

随着国家对黄河三角洲高效生态经济区发展规划的批复,如何加强黄河入海流路管理及其范围内土地开发,既要符合国家对河口治理的综合规划和土地规划,又能促进黄河三角洲高效生态经济快速发展,已成为突出问题。文章对黄河入海河口基本情况及如何管理和对其范围内土地进行合理利用开发提出了建议和意见。     

长江口及其邻近海域粘性泥沙的数量与输移

长江口的粘性泥沙有89.6%以上来源于长江补给区,一部分来源于废黄河与黄海补给区。长江补给区的粘性泥沙的汇入百分数及其输沙量两者均为已知,据此计算出长江口粘性泥沙沉积量为4.554×10~7t/a,从长江口输向杭州湾与东海补给区的粘性泥沙输沙量为2.247×10~7t/a,废黄河与黄海补给区输向长江口的输沙量为2.730×10~7t/a。长江口粘性泥沙的数量同1915年与1963年实测地形图比较量算的数量为4.469X10~7t/a基本相符。     

氟离子对在河口区存在形态的理论研究

利用Davies离子强度校正方程,把在标准条件下获取的氟离子对的化学稳定数校正到35%的海水条件下,并应用逐步凑分法计算出F-离子对的几种存在形式:游离态F-占49.9%,MgF+占46.8%,其余为CaF+和NaF0.     

江苏省风能资源重新估算与分布研究

利用1971—2000年江苏省67个台站的多气象要素资料,挑选风能资源评估的代表年,重新计算江苏省风能资源状况,发现与上世纪80年代全国风能评估结果以及90年代的评估结果有很大差异,全省风能总储量估算为3.03×1010W,实际可开发量约为0.24×1010W。风能资源在江苏沿海和海岛比较丰富,是未来开发的重点区域,而在绝大部分内陆地区风能贫乏,贫乏区占据全省的92.2%。     

基于Surpac软件的矿床模型构建及矿体资源量估算-以陕西山阳夏家店金钒矿床为例

文章介绍了陕西省山阳县夏家店金钒矿床矿体地质特征,矿体赋存于与寒武系有关的地层及断裂构造中。根据矿床以往地质勘查工程资料,应用Surpac软件建立了矿床数据库,建立了矿区地表模型、矿体模型和品位块体模型,模型形象直观的展现了矿区地形地貌、矿体展布位置及形态。应用普通克立格法建立的矿体品位块体模型,简洁清晰的表达了矿体品位分布位置及高低,并对部分矿体采用不同的基本块体单元估算了资源量,分析认为采用的基本块体单元越小,估算的矿体资源量越精确。将其与勘查报告中采用传统地质块段法估算的资源量进行了对比,表明采用该软件估算的矿体资源量可靠准确,计算过程高效、便捷。     

2001年世界黄金供需形势

2001年受美国经济放缓,尤其是"9·11"事件的影响,世界黄金需求下降2 6%,金价低迷,以271 04美元 盎司的年均金价再次刷新了1978年以来的最低价位。持续恶劣的价格环境,促进了黄金矿业公司间的相互兼并,以此降低经营成本,提高国际竞争能力。受金价下跌的影响,金矿勘查费用再次下降。尽管如此,2001年黄金仍是全球固体矿产勘查投资最多的矿种,是全球勘查开发热点,黄金储量和储量基础仍保持增长态势,金资源保证程度增加。金产量并未因金价下跌而减少。     

神经网络油气检测技术

多参数神经网络油气检测技术首先提取四大类２６ 个地震波特征参数,并定量描述这些参数,然后用神经网络技术对这些参数进行分析,预测油气分布,使油气识别工作定量化、计算机化。本次研究开发了一套神经网络油气识别软件,并利用其对东濮凹陷胡１９ 块进行油藏精细描述,预测沙三下砂组含油面积０－７ ｋｍ２ ,石油地质储量７０ ×１０４ 吨。     

Transport simulation of sorptive contaminants considering sediment-associated processes

Sediment-associated processes, such as sediment erosion, deposition, and pore water diffusion/advection affect sorptive contaminant transport. By considering these processes, we developed an equation to simulate contaminant transport. Erosion and deposition processes are considered as erosion and deposition fluxes of sediment, and adsorption-desorption processes of contaminants by sediment are simulated using the Langmuir Equation. Pore water diffusion is calculated based on the contaminant concentration gradient across the sediment-water interface. Pore water advection is estimated using pore water contained in the sediments of erosion flux. The equation is validated to simulate total phosphorus concentrations in Guanhe estuary in the northern Jiangsu, China. The simulated total phosphorus concentrations show better agreement with field observations compared to estimations that do consider sediment-associated processes.     

Geochemical characteristics of phosphorus near the Huanghe River estuary

INTRODUCTIONPhosphorus (P)isanimportantlimitingelementinglobaloceanicproductivity (Holland ,1 978) ,soknowledgeofPisakeytobetterunderstandingofthecyclingofcarbon ,nitrogen,sulfur,andothernu trientelements.Inasimplemassbalancemodel,thelevelofdissolvedPintheoceanisafunctionoftherateofinputviarivers,andtherateofoutputviadepositioninsediments.Inthepresentstudy,thefocusisontheriverinePinputbytheHuangheRiver (YellowRiver)totheBohaiSea,andespeciallyontheamountofPsolubilizedfromsolidphasesupo…     

Impact factors on distribution and characteristics of natural plant community in reclamation zones of Changjiang River estuary

To identify impact factors on the distribution and characters of natural plants community in reclamation area, with survey data from 67 plant quadrats in July 2009, soil properties data from 216 sampling points in April 2009, and TM (30 m) data in 2006, the composition and characteristics of natural plants community in different time of the Fengxian area in the Changjiang (Yangtze) River estuary were analyzed with two-way indicator species analysis (TWINSPAN), multivariate analysis of variance (MANOVA), detrended canonical correspondence analysis (DCCA) and canonical correspondence analysis (CCA). The results show that: 1) The plant communities in the reclaimed area are mainly mesophytes and helophytic-mesophytic transitional communities, showing a gradient distribution trend with the change in reclamation years. Species richness (MA), species diversity (H) and above-ground biomass also increase with the increase of reclamation years. Nevertheless, they appear to decline slightly in the middle and late reclamation period (> 30 years). 2) With the rise in land use levels, the changes in species richness and species diversity tend to increase at first and then decrease; species dominance (D), however, tends to decline; and above-ground biomass increases slightly. 3) The distribution of the plant community is mainly influenced by the following factors: land use levels (R = 0.55, p < 0.05), soil moisture (R = 0.53, p < 0.05), soil salinity (R = 0.43, p < 0.05) and reclamation time (R = 0.40, p < 0.05).