醌基功能型高分子生物载体(PET-AQS)制备及催化生物反硝化特性研究

通过化学合成,将蒽醌磺酸钠(AQS)固定在聚对苯二甲酸乙二醇酯(PET)上形成醌基功能型高分子生物载体并研究其在生物反硝化上的应用.通过红外光谱衰减全反射法(ATR-IR)和能谱(EDS)分析,醌基基团成功固定在高分子表面,且醌基质量摩尔浓度为0.140 6 mmol·g-1.醌基功能型高分子生物载体(PET-AQS)能加速生物反硝化,且速率常数Kx与载体投加浓度呈零级反应动力学.在投加PET-AQS 0.056 2 mmol的反硝化体系中,循环使用10次,反硝化速率均是空白体系的1.2倍以上,表明PET-AQS具有良好的重复利用稳定性,有利于实际应用.     

热带海洋大气环境下制动盘防护工艺耐腐蚀性能分析

目的研究汽车制动盘的三种防护工艺在热带海洋大气环境下的耐腐蚀性能。方法针对三种防护工艺的制动盘,在万宁试验站采用户外暴露试验方法开展对比试验。结果某无铬锌铝涂层1防护工艺的制动盘严重生锈,腐蚀程度最严重。某无铬锌铝涂层2和石墨烯防护工艺的制动盘在热带海洋大气环境中发生轻微生锈。结论在热带海洋大气环境下,某无铬锌铝涂层1防护工艺的耐蚀性能最差,某无铬锌铝涂层2和石墨烯防护工艺耐蚀性能良好,具有更好的环境适应性。     

基于长基线测量的水下电场特性分析研究

目的研究海洋环境电场的空间分布。方法借助长基线测量系统提供的一定空间增益,提高测量信号的强度,从而测量低频电场不同测量体在24 h内的幅度变化,以及0.1,0.2,0.5,1,10 Hz等5个不同典型频点的概率密度分布。结果水下电场的空间分布会由于电极间距的不同导致幅度有所差异,但整体的变化趋势基本一致。0.1,0.2,0.5,1 Hz频点随着频率的增加,幅度对整体的贡献越来越小,而10 Hz频点的幅度变化无明显规律。在24 h的连续观测中,DC-1 Hz极低频电场的幅度分布并不满足正态分布,而是随着时间变化具有一定的规律性。结论得到了不同频点的海洋水下环境电场的空间分布特性。     

Methane emissions from rice fields under continuous straw return in the middle-lower reaches of the Yangtze River

A three-year experiment was conducted in the middle-lower reaches of the Yangtze River in China to study the influence of continuous wheat straw return during the rice season and continuous rice straw return in wheat on methane (CH 4 ) emissions from rice fields in which, the rice-wheat rotation system is the most dominant planting pattern. The field experiment was initiated in October 2009 and has continued since the wheat-growing season of that year. The analyses for the present study were conducted in the second (2011) and third (2012) rice growing seasons. Four treatments, namely, the continuous return of wheat straw and rice straw in every season (WR), of rice straw but no wheat straw return (R), of wheat straw but no rice straw return (W) and a control with no straw return (CK), were laid out in a randomized split-plot design. The total seasonal CH 4 emissions ranged from 107.4 to 491.7 kg/ha (2011) and 160.3 to 909.6 kg/ha (2012). The increase in CH 4 emissions for treatments WR and W were 289% and 230% in the second year and 185% and 225% in the third year, respectively, in relation to CK. We observed less methane emissions in the treatment R than in CK by 14%-43%, but not statistically significant. Treatment R could increase rice productivity while no more CH 4 emission occurs. The difference in the total CH 4 emissions mainly related to a difference in the methane flux rate during the first 30-35 days after transplant in the rice growing season, which was caused by the amount of dissolved oxygen in paddy water and the amount of reducible soil materials.     

Transformation of N-, O-, and S- heterocycles (NOSHs) in estuarine sediments: Effects of redox potential and sediment particle size

The transformation of 19 N-, O-, and S- heterocycles (NOSHs) was examined in estuarine sediment-water microcosms. The effects of redox potential (Eh) and sediment particle size on compound transformation rates were evaluated, and stable products were identified. Results from stirred, controlled Eh/pH microcosms (CEPMs) showed that most of the NOSHs were significantly transformed under oxidized and reduced conditions over 15 week incubations, and the resulting product distributions were similar. In general, the rates and extent of transformation were greater in oxidized sediments of low surface area vs. those with high particle surface area and reduced redox conditions. Further experiments in sealed, unstirred microcosms also showed that NOSH transformation proceeded more slowly and on fewer compounds in fine vs. coarser grained sediments under oxidized conditions. Unlike the stirred systems, however, NOSH transformation rates were similar or greater under reduced vs. oxidized conditions. Thus, reduced, methanogenic clay of high surface area displayed some of the fastest rates of NOSH transformation. Data from liquid-liquid partitioning experiments suggested that this effect was related to the formation of NOSH complexes with iron and perhaps other redox-active metals in sediments.     

Acoustic Observations of Bottom Surge From Dredged Material Discharge in the Open Ocean

Bottom surges generated from dredged material discharges in the open ocean have been observed using high frequency acoustic concentration profilers in several field studies during the past five years. the locations, water depths, bottom slopes, oceanographic conditions, and dredged material composition differed from study to study. Observed surges at three dredged material disposal sites may develop more than one surge peak for a single discharge. for water depths of the order of 10 m, surge height of the leading peak was estimated to be about one quarter of the water depth. for water of greater depth, of the order of 100 m, surge height reached 70 m, about 70% of the water depth. Surge height is established instantaneously when dredged material hits the bottom, and remains relatively constant as the surge advances horizontally. Total surge length reached 150 m for water depths of 10 m when measured from the impact point to the leading edge. for water depths of more than 100 m, the surge length reached more than 100 m. Length of the leading surge peak was as large as 45 m at this water depth.

Dimensional analysis was applied to relate the surge height of the leading surge peak to discharge parameters and oceanographic conditions. Results showed that the ratio of surge height to water depth was proportional to 1/10 power of the ratio of discharge volume to the third power of water depth.     

Chemical Tracking and Marine Environmental Impact of Ocean Disposal of Calcium Carbonate Residue in the North Yellow Sea

The objective of this study is to determine the sedimentation rate and dispersion area of calcium carbonate residue dumped at sea and the impact to marine environment of dumping by a laboratory simulation experiment; chemical tracking in the field with the help of acoustic and optical tracking; and a comparative study of baseline conditions and marine environmental impact after dumping. Turbidity, pH and phosphate are selected as the chemical tracers to be monitored.

Results show that in the dumping area of 15 square miles with water depth of 50 m, if 217 t calcium carbonate residue is dumped (spot dumping) in the presence of a pycnocline with a current velocity of 60 cm/s (close to the maximum) the maximum dispersion distance of the calcium carbonate residue plume front is less than 2100 m; the dispersion area is less than 0.56 km²; and the maximum dispersion time is about 60 min when the turbidity and pH in the whole dispersion area return to background level. Therefore, the ocean disposal of calcium carbonate residue is feasible.     

Fe2+/Fe3+氧化还原系统预处理色酚废水的试验

介绍了采用Fe2+/Fe3+氧化还原系统对色酚废水进行预处理的工艺流程,确定了最佳工艺参数。研究结果表明,当还原反应的pH为9~11,反应时间20 min;氧化反应的pH为5.5~6,反应时间为30 min;FeSO4.7H2O加入量为5 kg/t废水时,CODCr去除率为75%~80%,并且处理后出水的色度、苯胺含量有明显改善,可生化性大大提高,十分有利于后续的生化处理。     

沈阳黄家傍河水源地河水入渗过程中氧化还原分带规律

在分析沈阳市黄家傍河水源地地质及水文地质条件的基础上,通过场地监测-室内实验相结合的方法,对黄家水源地河水入渗过程孔隙水氧化还原分带规律进行研究.结果表明：辽河河床沉积带在河水入渗途径上存在氧化还原分带,在水流垂向入渗的初始0~20cm、20~80cm、80~90cm及后续范围内依次存在O₂-NO₃^-混和还原带、锰氧化物还原带和铁氧化物还原带;反应中河水中溶解有机碳不能提供足够的电子还原氧化剂,溶解至入渗水流中的沉积物有机碳与河水溶解有机碳一起作为碳源参与了氧化还原反应.     

河水-地下水交互带内砷及金属的自然衰减过程

在简单介绍污染物自然衰减作用定义的基础上,重点分析了河水-地下水交互带内As和以矿山废水为来源的金属污染物的自然衰减行为:主要包括吸附作用,氧化还原作用,生物转化作用等。其中详细介绍了金属Fe、Al的氢氧化物/氧化物对As化合物和其他金属如Cd、Cu和Zn等的吸附作用;Ca2+、Fe2+、磷酸盐、重碳酸盐等阴阳离子和天然有机质对吸附作用的影响;金属微生物氧化还原作用以及微生物作用下As(V)与As(III)的相互转化过程。研究发现,阳离子可以增强金属的吸附作用,阴离子主要是参与竞争吸附;天然有机质对金属吸附过程的抑制作用阻碍金属的固定;交互带内氧化还原条件的变化可以引起一系列的氧化还原反应;微生物催化还原不利于As的自然衰减。最后指出目前河水-地下水交互带内金属污染物衰减过程研究存在的问题以及今后的发展方向。