轴向中空壁管抗冲击性能试验研究与数值分析∗

轴向中空壁管作为一种新型结构壁管,几何构型简单、空间利用率高、且能量耗散性好,近年来在市政工程中得到广泛应用。为研究轴向中空壁管在低速冲击作用下的力学响应和耗能特性,设计了 20 个试验工况,以落锤冲击试验模拟施工过程中受到的落石冲击和机械撞击作用,基于量纲分析法提出冲击力峰值的计算方法,通过有限元软件 ABAQUS 对试验结果进行验证,并根据有限元计算结果分析管道在低速冲击作用下的变形特性和损伤机理。研究表明：数值分析结果与试验结果吻合较好,冲击力时程曲线趋势基本一致,冲击力峰值误差在 5% 以内。 轴向中空壁管具有良好的抗冲击性能,其双壁中空结构具有较好的能量耗散性,落锤与管道接触瞬间会产生较大的冲击力,12.9 kg 的落锤从 2 m 处自由下落冲击管道可产生 15.28 kN 的冲击力。对比 20 个试验工况的冲击力峰值试验值与计算值,误差均较小,最大误差为 5.8%,即冲击力峰值计算方法准确性较高。随着落锤高度和质量的增加,冲击力峰值增大,损伤区域和凹痕深度也随之增大,最大塑性应变由外壁内侧转移到外壁与加劲肋的连接处, 呈现出外壁损伤和加劲肋损伤两种损伤模式。提出的冲击力峰值计算方法和管道塑性损伤规律可以为施工过程中轴向中空壁管在落石冲击和机械撞击作用下的安全评价提供理论依据。     

新型阻燃剂TCPP对斑马鱼的毒性研究

为了明确新型阻燃剂磷酸三(2-氯丙基)酯(TCPP)的生态风险,本研究采用斑马鱼为模式生物,评价了TCPP对成鱼和胚胎的毒性效应。急性毒性研究结果表明,TCPP对斑马鱼成鱼的96 h致死中浓度(LC50)为47.06 mg·L~(-1),而对胚胎96 h-LC50为26.01 mg·L~(-1),且会影响胚胎的正常发育,导致孵化出的仔鱼产生畸形。成鱼14 d延长毒性试验结果表明,TCPP对斑马鱼成鱼的无可观察效应浓度(NOEC)为1.00 mg·L~(-1),染毒暴露后肝脏和性腺指数随TCPP浓度增加轻微下降,但肝脏中卵黄蛋白原(VTG)的含量和性腺中芳香化酶的活性随TCPP浓度增加普遍升高。此外,TCPP的暴露还会导致斑马鱼脑垂体中合成促性腺激素的相关基因表达量增加。因此,TCPP对斑马鱼成鱼和胚胎的急性毒性均为低毒级,但长期暴露会干扰内分泌系统的调控功能,影响斑马鱼的正常发育。     

反硝化生物膜对PBS表面形态及化学组分的影响

PBS是一种新型的可生物降解聚合物(BDPs),可以用做反硝化碳源和生物膜载体,去除饮用水源水中的硝酸盐.利用红外光谱和扫描电子显微镜对反硝化生物膜生长前后PBS颗粒表面形态、化学组成的变化进行了分析.结果表明,PBS仅在微生物作用下降解并为反硝化菌提供碳源.PBS颗粒可以在12 h内使进水中53 mg·L^-1的硝态氮降低到10 mg·L^-1以下(我国饮用水水质标准为:NO₃^--N<15 mg·L^-1).红外光谱表明,反硝化微生物附着生长后其PBS在2 925 cm^-1和2 850 cm^-1附近的吸收带以及3 200 cm^-1～3 410 cm^-1处峰值减弱,说明PBS材料中甲基、羟基官能团比例下降,而其它官能团没有发生明显的变化,PBS的主要单体组分淀粉和乙烯都可以被反硝化微生物用作碳源.扫描电子显微镜观察结果表明,反硝化生物膜附着生长后,PBS颗粒表面会出现空洞,扩大了生物膜生物附着生长的表面积,有利于形成致密的反硝化生物膜,对反硝化菌形成保护作用.     

对化学品登记要求的数据解释——急性毒性和急性刺激

本文对化学品登记时所要求的部分健康效应数据一急性毒性和急性刺激做了解释.涉及到的测试参数包括:急性经口毒性、急性经皮毒性、急性吸入毒性、急性皮肤刺激/腐蚀和急性眼睛刺激/腐蚀.     

Sorption of tetracycline to sediments and soils: assessing the roles of pH,the presence of cadmium and properties of sediments and soils

Batch sorption experiments were conducted to evaluate the sorption behavior of tetracycline (TC, H₃L) on sediments and soils in the presence and absence of cadmium (Cd), as affected by pH and properties of sediments and soils. The results indicated stronger nonlinearity and higher capacity of TC sorption on sediments than on soils. Sorption of TC also strongly depended on environmental factors and sediment/soil properties. Lower pH facilitated TC sorption through a cation exchange mechanism, which also took place at pH values above 5.5, where TC existed as a zwitterion (H₂L⁰) or anions (HL^- and L^2-). When pH was above 7, however, ligand-promoted dissolution of TC might occur due to TC weakening the Al-O bond of aluminum oxide and the Fe-O bond of iron oxide. Natural organic matter (NOM) plays a more important role in TC sorption than cation exchange capacity (CEC) and clay contents. The presence of Cd (II) increased TC sorption on both sediments and soils, which resulted from the decrease of equilibrium solution pH caused by Cd²⁺ exchange with H⁺ ions of sediment/soil surfaces. The increase of TC sorption was also related to the formation of TC-Cd complexes, where Cd²⁺ acted as a bridge between the sediment/soil and TC.     

1982-2006年中国半干旱、干旱区气候与植被覆盖的时空变化

利用1982 - 2006年英国CRU(Climatic Research Unit)全球气温降水数据和NOAA/NASA归一化植被指数(the Normalized Difference Vegetation Index,NDVI)数据,分析了中国内陆半干旱和干旱区的气候、植被覆盖的时空变化.结果表明,虽然中国内陆半干旱和干旱区的部分区域降水减少,但整体上向暖湿化发展.在暖湿化背景下,中国内陆半干旱和干旱区的植被总体以改善为主(＞1％·(10a)-1),特别是新疆西北部和青海东南部;但局部有微弱的减少趋势[(0～1)％·(10a)-1],如新疆南部和东部、甘肃西北部.最后,以乌鲁木齐为例,分析发现气温增加导致植被生长季延长和降水的增加,使得过去25年乌鲁木齐的植被覆盖有明显的改善.     

Reduction of hexavalent chromium with scrap iron in a fixed bed reactor

The reduction of hexavalent chromium by scrap iron was investigated in continuous long-term fixed bed system. The effects of pH, empty bed contact time (EBCT), and initial Cr(VI) concentration on Cr(VI) reduction were studied. The results showed that the pH, EBCT, and initial Cr(VI) concentration significantly affected the reduction capacity of scrap iron. The reduction capacity of scrap iron were 4.56, 1.51, and 0.57 mg Cr(VI)·g^-1 Fe⁰ at pH 3, 5, and 7 (initial Cr(VI) concentration 4 mg·L^-1, EBCT 2 min, and temperature 25°C), 0.51, 1.51, and 2.85 mg Cr(VI)·g^-1 Fe⁰ at EBCTs of 0.5, 2.0, and 6.0 min (initial Cr(VI) concentration 4 mg·L^-1, pH 5, and temperature 25°C), and 2.99, 1.51, and 1.01 mg Cr(VI)·g^-1 Fe⁰ at influent concentrations of 1, 4, and 8 mg·L^-1 (EBCT 2 min, pH 5, and temperature 25°C), respectively. Fe(total) concentration in the column effluent continuously decreased in time, due to a decrease in time of the iron corrosion rate. The fixed bed reactor can be readily used for the treatment of drinking water containing low amounts of Cr(VI) ions, although the hardness and humic acid in water may shorten the lifetime of the reactor, the reduction capacity of scrap iron still achieved 1.98 mg Cr⁶⁺·g^-1 Fe. Scanning electron microscope equipped with energy dispersion spectrometer and X-ray diffraction were conducted to examine the surface species of the scrap iron before and after its use. In addition to iron oxides and hydroxide species, iron-chromium complex was also observed on the reacted scrap iron.     

Gridded usage inventories of chlordane in China

Chlordane (1,2,4,5,6,7,8,8-octachloro-3a,4,7, 7a-tetra-hydro-4,7-methanoindane) is one of organochlorine pesticides (OCPs) which has been listed as one of the persistent organic pollutants (POPs) to be reduced and finally eliminated in the Stockholm Convention on Persistent Organic Pollutants, because of its great persistence, toxicity, bio-accumulation and long-range transport potential. It is critical to create a national chlordane usage inventories for China to compile chlordane emission inventories, which is helpful for carrying out risk assessments and other researches related to chlordane in China. The annual data of chlordane usage was calculated and modified in accordance with the reported annual production of chlordane which was caculated on the basis of the termite distribution, the data of chlordane usage rate and the annual new construction area (NCA).With the help of Geographic Information System, the usage data of this NCA were allocated to a grid system then, with a 1/4° longitude by 1/6° latitude resolution and a size for each grid cell of approximately 25 km by 25 km. Between 1988 and 2008, the total usage of chlordane in China was 2745 t, accounting for approximately 80% of the production in the same period. Zhejiang Province was the largest consumer of chlordane in China, whose usage adds up to 980 t, greatly exceeding other provinces/regions, followed by Jiangsu Province (534 t) and Sichuan Province (428 t). The region with the least usage of chlordane was Beijing. Provinces of Guizhou, Henan and Hebei did not use any chlordane, even though termites had occurred in these provinces. Gridded usage inventories showed that the intensive use of chlordane was concentrated in the southeast part of China, Yangtze River Delta and Pearl River Delta in particular. The satisfaction of the inventories was supported by the consistence between the estimated data of annual usage and the reported annual production of chlordane, and by the consistence between distribution pattern of chlordane’s usage and ambient air concentration.