海水入侵指标对比分析与评价—以珠江口地下水含水层为例

合理评价海水入侵对于地下水含水层管理和居民生活健康有着重要的意义。当前海水入侵评价应用较广泛的为包含单一因子和基于统计分析的多种水化学方法。本文综合阐述了海水入侵评价中所用的水化学指标、原理与方法,包括在国内评价体系中少见的一些方法,并以珠江口地下水含水层为例,对比了各种指标的有效性,评价了各类方法的优缺点以及在实际应用中可能产生的问题。结果显示,以Cl-和TDS作为简单直接的单因子可以快速评价海水入侵,尤其对于大范围的海水入侵评价十分有效。而和Ca2+,HCO₃-,SO₄2-等变化有关的指标具有地域性,在研究区对海水入侵的指示并不是十分敏感。在复杂评价因子中,与离子交换有关SAR,BEX以及GQI_SWI与Cl-相关性较高,可以较好的指示海水入侵及水岩相互作用。经过分析,受到地下含水层和地表水道双重介质入侵的影响,研究区海水入侵范围在过去几个年代有向北推进的趋势。本研究对于高速经济发展下的沿海地下水含水层管理和评价有重要的指导意义。     

全球海洋初级生产力与海洋环境要素时空关联模式挖掘分析

全球海洋初级生产力在海洋环境要素的驱动下呈现不同的时空分布特征,但在不同的海域两者之间的关联模式并不清晰。本文从地理时空规则挖掘的角度,利用1998年1月—2016年12月之间的序列多源遥感产品数据,探讨了全球海洋初级生产力和海洋表面温度、海面高度异常、海面降雨、混合层深度和ENSO（El Ni?o-Southern Oscillation）事件的时空关联模式。研究结果表明:1）在西赤道太平洋,海面高度异常降低、海面降雨异常降低和混合层深度异常升高会提升真光层营养盐供应,致使海洋初级生产力的异常升高。2）在中赤道太平洋,海面高度异常升高、海面降雨异常升高和混合层深度异常降低会抑制真光层营养盐供应,致使海洋初级生产力的异常降低。3）在东赤道太平洋,海面高度异常升高和海面降雨异常升高会抑制真光层营养盐供应、混合层深度异常升高降低了铁元素含量,从而导致海洋初级生产力的异常降低。4）在南太平洋,浮游植物丰度与营养盐呈负相关,海洋表面温度异常升高/异常降低会提升/抑制微生物光合作用效率、海面高度的异常升高/异常降低会抑制/提升真光层营养盐供应,致使海洋初级生产力的异常升高/异常降低。5）厄尔尼诺事件相较于拉尼娜事件更容易引起海洋初级生产力的异常变化。     

Optimal range of plug-in electric vehicles in Beijing and Shanghai

Both China’s national subsidy policies for plug-in electric vehicles (PEVs) purchasers and passenger cars corporate average fuel consumption and new vehicle credit regulation (dual-credit policy) favor long-range 300+ km battery electric vehicles (BEVs) and 80+ km plug-in hybrid electric vehicles (PHEVs). However, these electric vehicles tend to have lower energy efficiency and higher purchase and operation costs. Vehicle with larger batteries can also be less equitable because the subsidies are often provided to more expensive vehicles and wealthier owners. This study takes advantage of a novel dataset of daily driving data from 39,854 conventional gasoline vehicles in Beijing and 4999 PHEVs in Shanghai to determine the optimal range of BEVs and PHEVs within their respective cities. We simulate a model to explore ranges with which PEVs emit less GHGs than that of a baseline hybrid and conventional gasoline vehicle while ensuring that all daily travel demands are met. Our findings indicate that in both cities, the optimal ranges to balance cost and travel demand for BEVs are 350 km or less and for PHEVs are 60 km or less in Beijing and 80 km or less in Shanghai. We also find that to minimize carbon dioxide (CO₂) emissions, the ranges are even lower 10 km in Beijing and 30 km in Shanghai. Our study suggests that instead of encouraging long-range PEVs, governments should subsidize PEV models with shorter ranges. Parallel efforts should also be made to both increase renewable energy over fossil fuels and expand charging facilities. Although individual mobility demand varies, the government could reduce occasional long-distance driving by subsidizing alternative transportation choices. Providing week-long driving trials to consumers before their purchases may help decrease the demand of very long range PEVs by alleviating the range anxiety through a learning process.

     

水解酸化-MBR组合工艺处理雏鸡孵化场废水

文章介绍了采用水解酸化-MBR组合工艺处理雏鸡孵化场废水的应用实例。结果表明,当进水COD、BOD5、NH3-N和SS浓度分别为1 230、268、22和456 mg/L时,污染物去除率依次分别为96.7%、97.5%、82.7%和98.6%。经该工艺处理后的出水水质稳定,并达到了《城镇污水处理厂污染物排放标准(GB 18918—2002)》一级A标准。     

东海表层沉积物中多环芳烃的分布特征及来源解析

本研究对东海沉积物中多环芳烃(PAHs)组成及含量进行了分析,发现多环芳烃总浓度为8.2~180.2 ng/g,和国内外其它区域相比,整体处于一个低至中等程度的污染水平。东海沉积物中PAHs的分布整体表现为中间低、两端高的格局。内陆架是长江入海物质的主要沉积区,也是PAHs的主要汇集区;陆架北部区域的物质来源复杂,但总体受长江入海泥沙的控制,自西向东PAHs含量梯度递减;研究区域的东北部,较高的PAHs可能源于济州岛的输入;冲绳海槽也含有较高PAHs;而残留沉积区中PAHs含量极低。通过多环芳烃组成特征判断,东海表层沉积物中PAHs主要来自煤、木材、油类的燃烧,还有部分来自油类的泄漏。同时不同区域Ba P/Be P、Ba A/Chry比值的差别表明内陆架及冲绳海槽的PAHs主要来自河流输送,残留沉积区的PAHs可能主要来自大气沉降。     

轻烃回收装置工艺过程危险分析及控制探讨

采取系统的分析方法 HAZOP技术对LNG接收站轻烃回收装置整个工艺流程和控制的危险与可操作性问题进行全面分析,并在HAZOP分析的基础上对LNG升压泵电力引线保压风险,低温蒸气中断风险、闪蒸罐和脱甲烷塔压力控制的风险、乙烷产品不外输工艺变更风等方面的风险进行了详细分析,并从安全设计、操作规程和安全管理等方面提出了相应的控制建议,以期为接收站轻烃装置的过程安全管理提供借鉴。     

Analysing the sensitivity behaviour of two hydrology models

Recently, the New Morris Method has been presented as an effective sensitivity analysis tool for mathematical models. The New Morris Method estimates the sensitivity of an output parameter to a given set of input parameters (first-order effects) and the extent these parameters interact with each other (second-order effects). This method requires the specification of two parameters (runs and resolution) that control the sampling of the output parameter to determine its sensitivity to various inputs. The criteria for these parameters have been set on the analysis of a well-behaved analytical function (see Cropp and Braddock, Reliab. Eng. Syst. Saf. 78:77–83, 2002), which may not be applicable to other physical models that describe complex processes. This paper will investigate the appropriateness of the criteria from (Cropp and Braddock, 2002) and hence the effectiveness of the New Morris Method to determine the sensitivity behaviour of two hydrologic models: the Soil Erosion and Deposition System and Griffith University Representation of Urban Hydrology. In the first case, this paper will separately analyse the sensitivity of an output parameter on a set of input parameters (first- and second-order effects) for each model and discuss the physical meaning of these sensitivities. This will be followed by an investigation into the sampling criteria by exploring the convergence of the sensitivity behaviour for each model as the sampling of the parameter space is increased. By comparing these trends to the convergence behaviour from Cropp and Braddock (2002), we will determine how well the New Morris Method estimates the sensitivity for each model and whether the sampling criteria are appropriate for these models. It will be shown that the New Morris Method can provide additional insight into the functioning of these models, and that, under a different metric, the sensitivity behaviour of these models does converge confirming the sampling criteria set by Cropp and Braddock.     

环境样品中 PCBs 的测定

通过碱解、酸洗、萃取、净化、浓缩、脱硫等步骤处理实际样品,利用毛细管柱GC/ECD进行PCBs的定性和定量.方法定性准确,定量良好,具有较高的回收率.各同系物的方法检出限,水样为0.01～0.08ng/L;土壤样为0.003～0.03μg/kg,可以应用于土壤、沉积物、水样、油样等环境样品中PCBs的测定     

The organic composition of diesel particulate matter, diesel fuel and engine oil of a non-road diesel generator

Diesel-powered equipment is known to emit significant quantities of fine particulate matter to the atmosphere. Numerous organic compounds can be adsorbed onto the surfaces of these inhalable particles, among which polycyclic aromatic hydrocarbons (PAHs) are considered potential occupational carcinogens. Guidelines have been established by various agencies regarding diesel emissions and various control technologies are under development. The purpose of this study is to identify, quantify and compare the organic compounds in diesel particulate matter (DPM) with the diesel fuel and engine oil used in a non-road diesel generator. Approximately 90 organic compounds were quantified (with molecular weight ranging from 120 to 350), which include alkanes, PAHs, alkylated PAHs, alkylbenzenes and alkanoic acids. The low sulfur diesel fuel contains 61% alkanes and 7.1% of PAHs. The identifiable portion of the engine oil contains mainly the alkanoic and benzoic acids. The composition of DPM suggests that they may be originated from unburned diesel fuel, engine oil evaporation and combustion generated products. Compared with diesel fuel, DPM contains fewer fractions of alkanes and more PAH compounds, with the shift toward higher molecular weight ones. The enrichment of compounds with higher molecular weight in DPM may be combustion related (pyrogenic).     

Environmental quality control and environmental games

Conclusion  In this paper we have considered a specific environmental game emphasizing both control-prevention efforts and the propensity to pollute by a firm which adopts a given pollution abatement technology. A random payoff game was constructed and solved under a risk neutral assumption and quadratic utilities for both the firm and the environmental controller. The game thus defined, provides a wide range of interpretations and potential approaches for selecting a control-inspection policies to prevent environmental risks. There are of course many facets to this problem, which could be considered and have not been considered in sufficient depth. For example, more complex control mechanisms and liabilities, the effects of insurance and risk sharing, the application of cooperative efforts and subvention of pollution abatement investments (through tax incentives and their like), etc. have not been considered [5,7]. These are topics for further research. The basic presumption of this paper is that it is very difficult to fully enforce pollution prevention by firms, as a result, some controls are needed to ensure that firms be controlled so that appropriate efforts are carried.