课证融合模式下实训教学改革研究

课证融合模式就是将课程与职业资格证书相结合的教学模式,是对职业教学改革的探索。但当前存在的实训教学标准模糊、校企合作实训教学条件不足、教师队伍转型滞后、教材开发混乱等现象严重阻碍了课证融合模式的推行,职业院校应当从明确考核评价标准、改进培养方案、加大双师教师的引进和培养、科学开发实训教材等途径进行尝试,推进课证融合。     

物流量统计量纲研究

物流量量纲的统一标准化是物流量研究的基础,影响到物流规划实施的准确性.针对目前物流量统计量纲没有统一标准的问题,提出了物流标准当量这一物流量单位,统一了物流量统计口径,丰富了物流研究的相关于物流量的统计理论,使不同物流实现可加性,并可与市场容量挂钩,为更科学分析、研究和规划物流业打下基础.     

内蒙古河套灌区盐碱土壤N2O排放特征

选择内蒙古河套灌区强度盐碱土壤S₁[电导率（EC）2.60dS/m]和轻度盐碱土壤S₂[电导率（EC） 0.74dS/m]为研究对象,2014~2016年,利用静态箱法3年野外原位观测试验,研究盐碱土壤氧化亚氮（N₂O）排放通量.结果表明：2种不同盐碱程度土壤N₂O排放每年均存在显著差异,轻度盐碱土壤N₂O累积排放量低;随EC升高,土壤盐碱程度加重,土壤N₂O累积排放量升高.2014~2016年作物生长季（4~11月）轻度盐碱土壤N₂O累积排放量分别为180.6,167.6,118.2mg/m²;强度盐碱土壤N₂O累积排放量比轻度盐碱土壤分别增加19%、26%和45%,修复盐碱土壤成为减缓盐碱土壤N₂O累积排放的重要农艺措施.     

Disinfection byproducts in drinking water and regulatory compliance: A critical review

Disinfection by-products (DBPs) are regulated in drinking water in a number of countries. This critical review focuses on the issues associated with DBP regulatory compliance, including methods for DBP analysis, occurrence levels, the regulation comparison among various countries, DBP compliance strategies, and emerging DBPs. The regulation comparison between China and the United States (US) indicated that the DBP regulations in China are more stringent based on the number of regulated compounds and maximum levels. The comparison assessment using the Information Collection Rule (ICR) database indicated that the compliance rate of 500 large US water plants under the China regulations is much lower than that under the US regulations (e.g. 62.2% versus 89.6% for total trihalomethanes). Precursor removal and alternative disinfectants are common practices for DBP regulatory compliance. DBP removal after formation, including air stripping for trihalomethane removal and biodegradation for haloacetic acid removal, have gained more acceptance in DBP control. Formation of emerging DBPs, including iodinated DBPs and nitrogenous DBPs, is one of unintended consequences of precursor removal and alternative disinfection. At much lower levels than carbonaceous DBPs, however, emerging DBPs have posed higher health risks.     

Urban expansion and its contribution to the regional carbon emissions: Using the model based on the population density distribution

The method is used for calculating regional urban area dynamics and the resulting carbon emissions (from the land-conversion) for the period of 1980 till 2050 for the eight world regions. This approach is based on the fact that the spatial distribution of population density is close to the two-parametric Γ-distribution [Kendall, M.G., Stuart, A., 1958. The Advanced Theory of Statistics, vol. 1.2. Academic Press, New York; Vaughn, R., 1987. Urban Spatial Traffic Patterns, Pion, London]. The developed model provides us with the scenario of urbanisation, based on which the regional and world dynamics of carbon emissions and export from cities, and the annual total urban carbon balance are estimated. According to our estimations, world annual emissions of carbon as a result of urbanisation increase up to 1.25 GtC in 2005 and begin to decrease afterwards. If we compare the emission maximum with the annual emission caused by deforestation, 1.36 GtC per year, then we can say that the role of urbanised territories (UT) in the global carbon balance is of a comparable magnitude. Regarding the world annual export of carbon from UT, we observe its monotonous growth by three times, reaching 505 MtC. The latter, is comparable to the amount of carbon transported by rivers into the ocean (196–537 MtC). The current model shows that urbanisation is inhibited in the interval 2020–2030, and by 2050 the growth of urbanised areas would almost stop. Hence, the total balance, being almost constant until 2000, then starts to decrease at an almost constant rate. By the end of the XXI century, the total carbon balance will be equal to zero, with the exchange flows fully balanced, and may even be negative, with the system beginning to take up carbon from the atmosphere, i.e., becomes a “sink”. The regional dynamics is somewhat more complex, i.e., some regions, like China, Asia and Pacific are being active sources of Carbon through the studied period, while others are changing from source to sink or continue to be neutral in respect the GCC.     

大气污染总量控制规划专家系统中知识库子系统的研究

论述了大气污染总量控制规划专家系统（ＥＡＳＰＴＥＣＥＰ）中知识库的基本设计思想,知识库分为无级知识库和领域级知识库,元级知识库由类文件和元规则文件构成,领域级知识库则文件和参量文件构成,并在此基础上阐述了ＥＳＡＰＴＥＣＰ中知识库演绎推理系统,知识库解释系统,知识库管理系统等的设计与实现方法。     

地膜覆盖对菜地生态系统N2O排放的影响

为了探讨地膜覆盖对菜地N_2O的排放通量、土壤剖面N_2O浓度以及土壤温度和湿度的影响,选取西南地区常见菜地(辣椒-萝卜轮作)为研究对象,采用静态暗箱/气相色谱法,进行了为期1 a的野外观测实验.结果表明,在辣椒季,常规处理(不覆膜)N_2O的平均排放通量为1000.0μg·(m~2·h)~(-1),覆膜处理为400.6μg·(m~2·h)~(-1),覆膜显著低于常规处理(P0.05);而在萝卜季,N_2O的平均排放通量则表现为覆膜处理[128.1μg·(m~2·h)~(-1)]高于常规处理[107.8μg·(m~2·h)~(-1)],但两者差异未达到显著水平(P0.05).覆膜和常规菜地土壤中N_2O含量均基本随土层深度的增加而增加,表现为:30 cm20cm10 cm,相同处理各层次土壤N_2O含量间均呈显著相关,不同处理相同深度处的土壤N_2O含量间也存在显著的正相关关系.对不同土层中的N_2O含量与地表N_2O排放通量的相关性分析可得出,常规处理各土层处的N_2O含量与地表N_2O排放通量呈显著正相关关系.覆膜处理的N_2O排放通量仅与30 cm深土壤中的N_2O含量存在显著正相关关系.通过对土壤湿度和温度的观测可以得出,地膜覆盖对土壤的增温效应在夏季更加明显,对土壤的保水作用在秋冬季更加突出.相关性分析和主成分分析结果表明,土壤中氮素形态是决定农田N_2O排放最重要的因素,其中常规菜地N_2O排放主要受土壤中总氮含量的影响,而覆膜菜地N_2O的排放对土壤中无机态氮含量的变化更加敏感.     

中国西北寒旱区农牧民生活碳排放评估

围绕碳排放权开展的气候谈判愈来愈关注贫困人口与弱势群体的生存权与发展权,一方面由于受制于其薄弱的社会经济水平,贫困人口与弱势群体在气候变化实践中表现出更高的脆弱性,另一方面则因气候变化减缓与适应行动而造成的贫困人口生活成本的增加以及生活水平的下降。然而,对这些地区和人口的排放权判断主要基于国家层面和地区层面宏观数据的分析,其结果掩盖了国家和地区内部不同社会经济水平下的人口排放差异,不能准确揭示贫困人口和脆弱群体的低碳排放事实。本文基于国际碳排放评估对人口生活排放的需求,结合IPCC参考方法,利用投入产出分析模型构建了人口生活碳排放评价指标体系,并用于对甘肃、青海和宁夏干旱-高寒地区农牧民生活碳排放的样本调查和分析。评估表明,中国西北干旱—高寒区人口生活碳排放仅为1.85tCO2/人,其中用于满足基本生活需要的碳排放量达到87.25%。研究发现,生活在更冷(海拔更高)区域内的人口生活排放量更高;随着家庭收入的增长,人口生活排放量也随之上升;家庭成员数量越多,家庭的人均碳排放量就会越低。     

中国城市温室气体清单研究

介绍城市温室气体排放特征和国际城市温室气体清单研究进展,研究了全球城市化和城市CO2排放的强正相关性,以及中国城市清单方法研究起步较早但发展缓慢的特点。分析了城市温室气体清单相对国家清单的特征,即城市清单编制往往采用消费模式,区别于国家清单的生产模式;国际城市清单中往往包括了由于外调电和供暖产生的CO2排放,同时城市温室气体清单编制灵活性和针对性更强。针对我国城市温室气体清单研究的不足,提出了我国城市温室气体清单方法,强调中国城市采用尺度1+尺度2的范围,暂不考虑尺度3的范围,即生产+消费的混合模式,并且在城市市域温室气体排放研究的基础上,加强狭义城市温室气体排放水平的研究。选择北京市和纽约市,对比分析了两个城市CO2排放特征,结果显示,在确定的清单体系下,北京市和纽约市具有较好的可比性。纽约市的总排放量(尺度1+尺度2)略低于北京市排放量,人均排放量略高于北京市。     

饮用水水源地严格管理水质的对策分析——对实行严格水资源管理问题上的看法和建议

2012年1月国务院发布了《关于实行最严格水资源管理制度的意见》,这是众所关注的要事,实行了最严格水资源管理的原则精神以及确定县级以上政府负总责的规定.但对如何严格管理的技术路线和对策措施上,特针对现实中存在的主要问题提出以下3点看法和建议:①达到地面水环境质量Ⅱ类水质的饮用水水源地不一定未受污染;②保护区内企业车间排水口符合第一类污染物最高允许排放浓度规定是满足饮用水水源地要求的必要条件;③《地面水环境质量标准》(GB 3838-2002)对第一类污染物规定的Ⅱ类水质,是否体现了水环境背景值有较大存疑.