Uncertainty or trust? Political trust,perceived uncertainty and public acceptance of personal carbon trading policy

Environmental Geochemistry and Health - Achieving carbon neutrality has become a global consensus, and plenty of measures and policies have been proposed in various industries to obtain this...     

Steel slag quality control for road construction aggregates and its environmental impact: case study of Vietnamese steel industry—leaching of heavy metals from steel-making slag

Environmental Science and Pollution Research - Steel slag is an industrial by product of steel manufacturing processes and has been widely utilized within civil and construction materials for road...     

Curcumin antagonizes inflammation and autophagy induced by arsenic trioxide through immune protection in duck spleen

Environmental Science and Pollution Research - Arsenic is a toxic heavy metal widely found in the natural environment and has adverse effects on the health of waterfowl and human. Curcumin (CUR), a...     

西北煤炭开发生态风险管控区划分及管理策略

为维护我国西北地区生态安全,引导煤炭资源有序开发利用,以甘肃省、青海省、新疆维吾尔自治区为研究区域,结合西北地区典型内陆河流域地下水形成特征及区域生态环境特点,选取与区域煤炭综合开发活动具有重要关联的地下水资源、生态环境等指标,利用专家打分法确定评价指标权重,构建煤炭综合开发生态风险管控评价指标体系,通过对指标体系分级结果的空间转化,划分禁止开发区、限制开发区、适度开发区3个煤炭开发的生态风险管控区.结果表明:①禁止开发区面积约131.6×104 km2,占西北三省（自治区）总面积的46%,主要分布在柴达木、塔里木、准噶尔三大盆地的盆周及周边地区,总体上呈"三环"分布,禁止开发区应禁止一切煤炭开发活动.②限制开发区1区主要分布在新疆维吾尔自治区南部地区及天山北麓以及甘肃省河西走廊的人工绿洲,煤炭开发利用过程中要兼顾保护农田、地下水,维持防风固沙功能方可进行;限制开发区2区主要分布在甘肃省酒泉地区黑河流域,新疆维吾尔自治区阿克苏地区、喀什地区及和田地区的荒漠生态系统内以及环塔里木盆地外围地区,煤炭开发利用过程中需兼顾防风固沙功能及生态系统保护方可进行.③适度开发区分布较为分散,在保护特定生态系统功能的前提下可适度开发.研究显示,需针对上述不同类型的生态风险管控区提出差别化管理要求,重点对限制开发区、适度开发区的煤炭开发提出相应的生态保护要求,提出由限制为主转向优化发展为主的管理方略.      

促生剂投量对菌剂-促生剂协同修复沉积物的影响

采用5个110 L的模拟河道反应器,在投加菌剂的基础上(底泥稳定后向底泥和水中分别注射浓度为0.09%和0.03%的菌剂),生物促生剂投量分别设计为0(空白对照实验)、0.08、0.09、0.10和0.11 g·L~(-1),通过为期115 d的修复实验研究菌剂与促生剂协同作用时底泥微生物群落特征变化规律,进而分析其对底泥修复效果的影响.实验表明,投加促生剂后,115 d时Chloroflexi、Proteobacteria、Firmicutes、Betaproteobacteria及Bacteroidetes等主要功能菌群相对丰度增加,脲酶活性与蛋白酶活性后期时总体上低于单独投加菌剂组.促生剂投量为0.10 g·L~(-1)时,上覆水COD_(Cr)稳定浓度为16.82 mg·L~(-1),低于其余各组;底泥TOC含量由初始的0.808%下降至第115 d时的0.687%,去除率为14.9%,显著高于其余各组;促生剂投量为0.11 g·L~(-1)时,底泥全氮去除率最高为14.8%.生物促生剂促使微生物群落向更适宜降解去除氮素及有机质的方向演替,有效改善底泥环境.     

基于灰色聚类法的成都市大气污染评价

大气环境质量问题一直是关注的环境问题之一,而灰色聚类分析方法在很多领域已有应用。本文对成都市大气环境监测数据进行评价：采用灰色聚类分析方法,将污染因子（SO2、NO2、PM10）进行综合评价,标准化污染因子及评价指标。白化函数得到各个污染因子每年的5×4矩阵,按照聚类系数来判定综合指标类型,并进行评价。为成都市综合大气...     

复合式厌氧污泥床反应器处理城市生活污水的研究

复合式厌氧污泥床反应器是一种改进的厌氧处理工艺，可有效去除城市生活污水中的污染物，并提高了污水的可生化性，是一种较为理想的城市污水强化一级处理工艺。本文对该工艺，装置的特点和效果进行分析,并展望其应用前景。     

Environmental consequences of different beef production systems in the EU

The aim of this paper is to examine the environmental consequences of beef meat production in the EU, using a life cycle approach. Four beef production systems were studied – three from intensively reared dairy calves and one from suckler herds. According to the results of the analysis, the contributions from the production of 1 kg beef meat (slaughter weight) to global warming, acidification, eutrophication, land use and non-renewable energy use were lower for beef from dairy calves than from suckler herds (16.0–19.9 versus 27.3 kg CO₂e, 101–173 versus 210 g SO₂e, 622–1140 versus 1651 g NO₃e, 16.5–22.7 versus 42.9 m²year, and 41.3–48.2 versus 59.2 MJ, respectively). The breakdown analysis helped identify the key areas in the “cradle to farm gate” beef production system where sustainable management strategies are needed to improve environmental performance. The study also included a sensitivity analysis to preliminarily estimate GHG emissions from beef production systems if land opportunity cost and land use change related to grazing and feed crop production for beef were taken into account. If so, the contribution from the production of 1 kg beef to global warming would increase by a factor of 3.1–3.9, based on a depreciation period of 20 years. This highlights the importance of taking into account the impacts of land use in assessing the environmental impacts of livestock production.     

硅钼黄法测定海水中硅消除P干扰的研究

Si和P与钼酸铵反应均能生成钼黄,为了消除P对Si的干扰,国家标准采用加草酸溶液方法,研究发现该溶液不但破坏磷钼黄,也破坏硅钼黄,且反应速度很快,比色必须在2 min内完成,否则结果大大偏低。我们也用酒石酸溶液替代草酸溶液,虽然破坏硅钼黄速度减慢,但也不理想。本文通过实验推导和验证:如果已知P浓度,把测得的Si、P总浓度减去P的浓度乘0.389所得的值,就消除了P的干扰,方法简便准确。