长链脂肪酸对厌氧颗粒污泥产甲烷活性的影响及其相互作用研究

采用间歇培养实验研究了辛酸、癸酸和月桂酸等三种长链脂肪酸对UASB反应器厌氧颗粒污泥产甲烷活性的毒性，以及癸酸对辛酸和月桂酸抑制作用的影响。结果表明，辛酸、癸酸和月桂酸对UASB反应器厌氧颗粒污泥的产甲烷活性有严重抑制，对厌氧颗粒污泥最大比产甲烷活性产生50%抑制的浓度(IC     

博落回急性及亚慢性毒性试验

博落回对小鼠经口急性毒性和对大鼠腹腔注射慢性毒性试验结果表明：博落回生物碱硫酸盐对昆明系小鼠的急性毒性为：水溶液ＬＤ５０＝９００ｍｇ·ｋｇ＾－１，水混悬液ＬＤ５０＝１０４３ｍｇ·ｋｇ＾－１，均属低毒级。博落回注射液对Ｗｉｓｔａｒ大鼠亚慢性毒作用的靶器官主要为肝，长时间或大剂量接毒引起肝细胞变性，增生，使雄性动物肝／体比明显增高，而血清谷－丙转氯酶下降。     

Effective alleviation of Cd stress to microbial communities in mining reclamation soils by thiourea-modified biochar amendment

Reclaimed soils in mining area usually display low fertility and present Cd stress. The amendment of modified biochar effectively fixes Cd in soils,enhances soil fertility, and reduces Cd stress in soil microorganisms. However, the effect of thiourea-modified biochar(TBC) on microbial adaptability to Cd stress in mining reclamation soils is still unclear. The present work studied the Cd immobilization and microbial community changes in a mining reclamation soil displaying extreme Cd contaminatio...     

结石通片对小鼠的急性毒性试验及其对乙二酰胺致大鼠肾结石的作用研究

[目的]研究结石通片对小鼠的急性毒性作用,对健康大鼠的利尿作用,以及对乙二酰胺致大鼠肾结石的调节作用.[方法]取ICR小鼠40只,雌、雄各半,随机分为对照组与给药组,每组20只,观察结石通片给药前后小鼠的体重变化和死亡情况;另取SD大鼠36只,雌、雄各半,分为对照组、低剂量组(给予5％结石通片溶液)和高剂量组(给予10...     

乐果、铜和锌对水生生物的联合毒性研究

为通过不同生物等级的模式生物研究乐果、铜和锌的联合毒性,以明亮发光杆菌和斑马鱼胚胎为受试模式生物,通过混合毒性指数法（MTI法）评价了乐果、铜和锌的联合毒性效应。结果表明：明亮发光杆菌毒性测试显示,暴露测试15 min时,乐果、铜和锌的EC₅₀值分别为123、0.53 mg·L^-1和1.71 mg·L^-1;暴露测试30 min时,EC₅₀值分别为122、0.50 mg·L^-1和1.54 mg·L^-1。乐果-铜和乐果-锌暴露15 min测得的MTI分别为0.69和0.60。斑马鱼胚胎毒性测试显示,暴露72 h后乐果、铜和锌的LC50值分别为0.31、1.67 mg·L^-1和369 mg·L^-1。乐果-铜和乐果-锌暴露72 h后测得的MTI分别为0.70和0.75。研究表明,乐果和铜、锌分别混合后的联合毒性均有所增强,整体毒性表现为部分相加作用,因此两类物质在环境中的残留会对水生生物及其他生物造成潜在危害。     

有机胂添加剂对蛋白核小球藻及大型蚤的急性毒性研究

为评估有机胂添加剂对水环境的影响,以蛋白核小球藻、大型蚤为研究对象,研究了洛克沙胂、阿散酸对蛋白核小球藻和大型蚤的急性毒性.结果表明:洛克沙胂、阿散酸对蛋白核小球藻的24、48、72、96 h的半数有效抑制浓度(EC50)分别为:190.55、263.03、346.74、389.05 mg·L-1;239.88、308.18、418.12、410.40 mg·L-1(以原型药物计);均大于100 mg·L-1,在水环境中为低毒级化合物(急性Ⅲ化学物质以下).对大型蚤24 h-EC50分别是49.77、83.70 mg·L-1;48 h-EC50分别是39.00、57.48 mg·L-1,48 h-LC50分别是44.19、61.97 mg·L-1(均以原型药物计);依据蚤类急性活动抑制毒性分级标准,它们属于中毒级化合物.     

农药废水对秀丽隐杆线虫毒性效应及其主要有毒组分

应用battery生物测试法,检测研究农药废水对秀丽隐杆线虫的生命周期、繁殖速率、生殖能力、头摆和身体弯曲频率等影响的生物毒性,及其引发生物毒性的主要有机污染物。结果表明,在已经达到国家废水排放标准[GB 8978—1996]情况下,处理出水对受试动物仍然存在致毒效应;线虫的世代周期对进水的毒性最为敏感,产卵数量对出水的毒性最为敏感;进水毒性主要来自易受酸性调节影响的有机污染物,出水毒性主要来自易受碱性调节影响的有机污染物。结果表明,该项生物测试的毒性参数,可用于指示存在于低CODCr废水中的生物毒性;所用的毒性鉴别评价（TIE）方法,可用于鉴别废水中引发致毒效应的关键污染物。废水中悬浮颗粒污染物的生物毒性至关重要,尚未研究,有待继续。     

Effect of Lime and Flooding on Phosphorus Availability and Rice Growth on Two Acidic Lowland Soils

Abstract

Loss of soil‐water saturation may impair growth of rainfed lowland rice by restricting nutrient uptake, including the uptake of added phosphorus (P). For acidic soils, reappearance of soluble aluminum (Al) following loss of soil‐water saturation may also restrict P uptake. The aim of this study was to determine whether liming, flooding, and P additions could ameliorate the effects of loss of soil‐water saturation on P uptake and growth of rice. In the first pot experiment, two acid lowland soils from Cambodia [Kandic Plinthaqult (black clay soil) and Plinthustalf (sandy soil)] were treated with P (45 mg P kg^?1 soil) either before or after flooding for 4 weeks to investigate the effect of flooding on effectiveness of P fertilizer for rice growth. After 4 weeks, soils were air dried and crushed and then wet to field capacity and upland rice was grown in them for an additional 6 weeks. Addition of P fertilizer before rather than after flooding depressed the growth of the subsequently planted upland rice. During flooding, there was an increase in both acetate‐extractable Fe and the phosphate sorption capacity of soils, and a close relationship between them (r²=0.96–0.98). When P was added before flooding, Olsen and Bray 1‐extractable P, shoot dry matter, and shoot P concentrations were depressed, indicating that flooding decreased availability of fertilizer P. A second pot experiment was conducted with three levels of lime as CaCO₃ [to establish pH (CaCl₂) in the oxidized soils at 4, 5, and 6] and four levels of P (0, 13, 26, and 52 mg P kg^?1 soil) added to the same two acid lowland rice soils under flooded and nonflooded conditions. Under continuously flooded conditions, pH increased to over 5.6 regardless of lime treatment, and there was no response of rice dry matter to liming after 6 weeks' growth, but the addition of P increased rice dry matter substantially in both soils. In nonflooded soils, when P was not applied, shoot dry matter was depressed by up to one‐half of that in plants grown under continuously flooded conditions. Under the nonflooded conditions, rice dry matter and leaf P increased with the addition of P, but less so than in flooded soils. Leaf P concentrations and shoot dry matter responded strongly to the addition of lime. The increase in shoot dry matter of rice with lime and P application in nonflooded soil was associated with a significant decline in soluble Al in the soil and an increase in plant P uptake. The current experiments show that the loss of soil‐water saturation may be associated with the inhibition of P absorption by excess soluble Al. By contrast, flooding decreased exchangeable Al to levels below the threshold for toxicity in rice. In addition, the decreased P availability with loss of soil‐water saturation may have been associated with a greater phosphate sorption capacity of the soils during flooding and after reoxidation due to occlusion of P within ferric oxyhydroxides formed.     

柠檬酸对西瓜幼苗铝毒害的缓解作用

为了探究柠檬酸对西瓜幼苗铝毒害的缓解作用,本试验采用水培法,以早春红玉(耐铝型,HY)和早蜜王(铝敏感型,ZM)2个西瓜品种为材料,用不同柠檬酸浓度(200、400、800、1 200μmol·L~(-1))处理铝胁迫(1 500μmol·L~(-1))下的西瓜幼苗,研究不同柠檬酸浓度对西瓜幼苗生长和生理特性的影响。结果表明,铝胁迫对HY和ZM幼苗的生长和生理均产生了明显的毒害作用,与HY相比,ZM受毒害的程度更大。加入柠檬酸后,铝对HY和ZM的毒害作用得到了有效的缓解,且缓解效果存在浓度差异,在一定浓度范围内(≤800μmol·L~(-1)),随着柠檬酸浓度增加缓解效果增强,其中以800μmol·L~(-1)效果最佳;当浓度增至1 200μmol·L~(-1)时,缓解效果反而减弱。柠檬酸对ZM的缓解作用强于HY,同时随着处理时间的延长柠檬酸缓解效果越明显。综上所述,柠檬酸能够有效缓解铝对西瓜幼苗的毒害作用,以400~800μmol·L~(-1)解毒效果最佳。本研究结果为明确柠檬酸缓解西瓜铝毒害作用机制以及西瓜优质高产栽培提供了理论依据。     

水稻根尖边缘细胞对铁毒的形态生理响应

以水稻(Oryza sativa L.)品种Azucena（铁耐性）和IR64（铁敏感）为材料,研究了Fe2+毒胁迫下附着于根尖边缘细胞(即原位边缘细胞)的数目、存活率,根尖细胞形态结构、根尖保护酶活性的变化。结果显示,Fe2+ 毒对根边缘细胞的产生有抑制作用。相对于敏感性品种而言,一定浓度Fe2+(100~200 μmol/L)有利于耐性品种边缘细胞的产生;Fe2+ 毒对边缘细胞有致死效应,随Fe2+浓度的提升,边缘细胞的存活率呈下降趋势,根尖外围细胞壁增厚,并出现细胞程序性死亡特征(敏感性品种)。同时,Fe2+ 毒对根尖保护酶活性有一定的影响,200~400 μmol/L Fe2+处理下,耐性品种POD、CAT、SOD活性都超过对照;敏感品种只有SOD活性超过对照。说明Fe2+毒胁迫下,水稻根尖通过增加边缘细胞数目、提高细胞拒铁作用,维持较高水平的POD、CAT和SOD活性来对抗Fe2+毒,缓解铁毒害。