PACT活性污泥中生物质量与粉末活性炭质量的计算和测定

本文根据活性污泥处理系统的物料平衡关系,提出PACT活性污泥中生物质量和粉末活性炭(PAC)质量的计算和测定方法.计算结果表明,曝气池混合液中PAC浓度随着PAC投加量和泥龄与水力停留时间的比值的提高而增加.通过实际测定活性污泥PAC在不同温度时的挥发量,得出三个联立方程式的基本系数,从而测得实际的PAC活性污泥试样中生物质量和PAC质量.     

污泥施肥时重金属镍对农作物的毒害研究

采用盆栽和小区试验,研究了在石灰性土壤中镍污染对小麦和水稻的影响;两种作物对土壤中镍的吸收、迁移和累积规律。建议农田污泥施肥时镍的控制标准为330PPm。     

铬在土壤-地下水系统中的污染研究

根据铬在土壤-地下水环境中的化学特性,通过实验,研究了两种价态的铬[Cr(Ⅲ),Cr(Ⅵ)]在水、土中的污染过程,并着重分析了Cr(Ⅵ)在水土体系中所产生的物理化学作用及其在土中的稳定性。结合铬污染实例,阐明了铬在水-土体系中污染的条件和迁移过程。     

化学法处理含酚废水的组合工艺系统和条件研究

采用化学法组合的三种工艺系统,对含酚废水进行了工艺条件的研究。结果表明,对于浓度<30mg/l含酚废水,采用氧化凝聚处理是有效的;而对于30～80mg/l含酚废水,选用氧化凝聚和吸附组合的工艺系统处理,能使排放水中酚和COD达标。     

新疆D矿田金矿资源定量评价

本文在建立D矿田找矿信息层次模型基础上,确定矿田统计单元划分和地质变量提取的赋值原则,将该矿田划分出466个统计单元,提取25个地质变量并进行二态赋值,而后应用数量化理论Ⅲ。特征分析法及勃尔法等方法,建立了矿田金矿资源定量评价模型,定位预测了45个勘探靶区。     

额尔齐斯—玛因鄂博断裂带——新疆一个重要的构造结合带

新疆阿勒泰区的额尔齐斯—玛因鄂博断裂带是划分阿尔泰褶皱区与北准噶尔褶皱区的一条重要构造结合带。南北两区,无论在地层、构造、喷发—侵入活动、矿化作用以及变质程度上均有明显不同,资料表明,它经历了长期的发育过程,最终发展成为两区的天然分界线。     

“华夏古陆”考异

自葛利普创名“华夏古陆”以来,经过半个多世纪的论辩与考订,对其地质构造属性,至今仍然否定与肯定交迭起伏,莫衷一是,本文从推覆构造,陆地漂移等实际资料着手,加以论证,认为它是经历深刻改造和发生巨大位移的变质岩断片体,地质构造属性已非“华夏古陆”原义。     

再论次生石英岩型非金属矿床

次生石英岩型非金属矿床明显受不同级别的火山构造控制,是中—酸性火山岩区一套很有特色的矿床组合;热源、水源、地层产状有机组合生成的环流热液是成矿的前提之一;成矿流体以重碳酸盐型、硫酸盐型为主,属中—低盐度热液;温度、pH值、fo_2等物理化学条件是矿床及矿种类刑的重要控制因素。本文在《次生石英岩容矿型非金属矿床系列的矿种、组合及其成矿作用特征》(1986)一文基础上,进一步总结这类矿床的成矿机理和地质地球化学模式。     

The responses of the hepatosomatic index (HSI), 7-ethoxyresorufin-O-deethylase (EROD) activity and glutathione-S-transferase (GST) activity in sea bass (Dicentrarchus labrax, Linnaeus 1758) caged at a polluted site: implications for their use in environmental risk assessment

The present study investigates the response of three hepatic biomarkers in adult sea bass (Dicentrarchus labrax, Linnaeus 1758) caged at a wastewater outlet of an oil refinery with fish caged at a pristine site used as controls. The biomarkers that were investigated were the hepatosomatic index (HSI), 7-ethoxyresorufin-O-deethylase (EROD) activity and glutathione-S-transferase (GST) activity. In addition, we have measured the levels of polycyclic aromatic hydrocarbons (PAHs) and selected heavy metals (lead, cadmium, mercury, copper and zinc) in sediment samples at the polluted site. Although the polluted site had high environmental levels of PAHs and heavy metals, there was no difference in hepatic EROD activity and HSI between fish caged at the polluted site and controls. On the other hand, GST activity was significantly lower in fish caged at the polluted site compared to controls. Our results point out that the studied biomarkers have limited use in environmental risk assessment studies, at least when caged adult sea bass is used as the sentinel species and complex toxicant mixtures are involved.     

Dissipation and residue behavior of mepiquat on wheat and potato field application

A modified LC-MS method for the analysis of mepiquat residue in wheat, potato, and soil was developed and validated. A hydrophilic interaction liquid chromatographic column has been successfully used to retain and separate the mepiquat. Mepiquat residue dynamics and final residues in supervised field trials at Good Agricultural Practice (GAP) conditions in wheat, potato, and soil were studied. The limits of quantification for mepiquat in all samples were all 0.007 mg kg^?1, which were lower than their maximum residue limits. At fortification levels of 0.04, 0.2, and 2 mg kg^?1 in all samples, recoveries ranged from 77.5 to 116.4 % with relative standard deviations of 0.4–7.9 % (n?=?5). The dissipation half-lives (T _1/2) of mepiquat in soil (wheat), wheat plants, soil (potato), and potato plants were 4.5–6.3, 3.0–5.6, 2.2–4.6, and 2.4–3.2 days, respectively. The final residues of mepiquat were below 0.153 mg kg^?1 in soil (wheat), 0.052–1.900 mg kg^?1 in wheat, below 0.072 mg kg^?1 in soil (potato), and below 1.173 mg kg^?1 in potato at harvest time. Moreover, pesticide risk assessment for all the detected residues was conducted. A maximum 0.0012 % of acceptable daily intake (150 mg kg^?1) for national estimated daily intake indicated low dietary risk of these products.