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.     

土壤Pb,Zn复合污染对作物吸收重金属的影响

以褐土为供试土壤,用小白菜作指示植物,通过模拟试验研究了土壤Pb,Zn复合污染对植物吸收重金属的影响。结果表明,在土壤Pb,Zn复合污染条件下,土壤中Pb的存在对蔬菜吸收Zn未产生明显影响,而土壤中Zn的存在则对蔬菜吸收Pb产生抑制作用。同时,分析复合污染条件下Pb,Zn在蔬菜体内的分布,表明小白菜主要将重金属Pb积累于根部,而Zn则是更多的被小白菜积累在地上部位。     

蚯蚓与植物联合去除猪粪中的Cu,Zn污染研究

由于饲料添加剂的使用,畜禽粪便中的重金属污染已非常普遍,尤其是Cu,Zn污染最为显著。为此,利用蚯蚓对腐熟猪粪进行处理,再通过植物对蚓粪中Cu,Zn吸收的方法,进行了消除猪粪中重金属的研究。结果表明,蚯蚓对猪粪Zn有较强的吸收能力,富集系数为1.43;而对Cu的吸收能力相对较弱,富集系数为0.61。植物对Cu,Zn的吸收贡献不大,但可以作为饲料返回到动物体内,从而减少饲料添加剂中Cu,Zn的含量。通过蚯蚓与植物的联合处理,能有效地降低腐熟猪粪中Cu,Zn的含量。     

氮锌配施对不同玉米品种灌浆期生理特性和籽粒氮锌含量的影响

提高粮食作物中可食部分的锌生物有效性是解决人体缺锌的重要措施。为研究氮锌肥料施用对玉米籽粒锌营养的影响,本研究以郑单958和谷神玉66为试验材料,在大田条件下研究3个氮水平(90、180 和225 kg N·hm^-2)和2个喷锌处理(0和4.5 kg·hm^-2 ZnSO₄·7H₂O)下玉米籽粒产量和氮锌含量以及灌浆期叶片生理特性的变化。结果表明,吐丝后,与施氮量90 kg·hm^-2处理相比,施氮量180和225 kg·hm^-2处理提高了吐丝后穗位叶SPAD值及硝酸还原酶(NR)、谷氨酰胺合成酶(GS)、碳酸酐酶(CA)、超氧化物歧化酶(SOD)活性和灌浆后期PSⅡ综合性能指数(PI),降低了丙二醛(MDA)含量。施锌能提高吐丝后穗位叶CA、SOD、过氧化物酶(POD)、过氧化氢酶(CAT)活性和灌浆后期SPAD值和PI,降低MDA含量。2个品种相比,谷神玉66灌浆后期穗位叶SPAD值、叶片初始荧光(F_o)和最大荧光(F_m)较高,而灌浆前期穗位叶PI和吐丝后NR、CA、SOD以及POD活性则以郑单958较高。施氮量为90 kg·hm^-2时,玉米籽粒产量平均为8.55 t·hm^-2,随着施氮量增加,玉米籽粒产量显著提高。籽粒中氮含量以施氮量180 kg·hm^-2时最高,为14.85 g·kg^-1。施氮量90和180 kg·hm^-2时,籽粒锌含量平均为27.2 mg·kg^-1,显著高于施氮量225 kg·hm^-2处理。与不施锌相比,喷锌后玉米籽粒产量未有显著变化,籽粒中氮、锌含量分别增加了11.7%和18.0%。郑单958籽粒产量较谷神玉66提高了3.8%,籽粒氮锌含量则分别减少了11.9%和5.3%。综合来看,施氮量为180 kg N·hm^-2时,与喷施ZnSO₄·7H₂O 4.5 kg·hm^-2 配合施用能够增强玉米灌浆期叶片SPAD和荧光特性,提高氮锌代谢关键酶活性,增强氧自由基清除系统酶活性,减弱膜脂过氧化作用的伤害,促进籽粒中氮、锌的吸收和累积。本研究结果可为玉米生产中优化锌生物强化措施提供理论依据。     

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.     

重金属锌对猪粪堆肥过程中氧化还原类酶活性的影响

以猪粪和秸秆为主要试验材料,添加不同浓度重金属Zn,采取发酵罐处理方法,在好氧高温条件下研究了重金属Zn对猪粪堆肥过程中多酚氧化酶、脱氢酶活性的变化,以及堆腐过程堆体温度、堆料pH值、胡敏酸E4/E6值的变化。结果表明：（1）低量重金属Zn处理（L）较不添加重金属Zn（CK）和添加高量重金属Zn（H）堆料升温快、温度高、高温持续时间长。（2）重金属Zn的加入对堆料的pH值影响不大,不是影响堆肥进程的直接原因。（3）H处理在整个堆肥过程中E4/E6值均高于L和CK,表明高浓度Zn处理抑制腐殖质的缩合和芳构化。（4）L处理的多酚氧化酶活性大多数时间高于H处理的活性,说明低量重金属Zn更好地促进了木质素的降解及其产物的转化。（5）从整个堆肥过程来看,3个不同处理的脱氢酶活性表现出一定的不稳定性,可能是重金属对脱氢酶活性有抑制作用的同时发生＂抗性酶活性＂现象。     

锌污染对猪粪堆腐过程中微生物群落的影响

利用Biolog微平板技术,对不同浓度重金属Zn影响下堆料微生物群落多样性进行了研究。结果表明,较低浓度Zn处理（Zn含量为400mg·kg^-1）的堆料升温快,高温持续时间长。微生物群落多样性指数和微生物群落主成分分析（PCA）指标均表明不同浓度重金属处理的堆料微生物群落有明显不同,Zn含量为400mg·kg^-1的堆料微生物活性高,有利于增加群落的丰富度和功能多样性,与Zn含量为1000mg·kg^-1的堆料、对照组堆料起分异作用的碳源主要为多聚物类和糖类。     

湘西花垣矿区蔬菜重金属污染现状及健康风险评价

对湘西花垣锰矿、铅锌矿区的部分蔬菜及其种植土壤进行了调查和重金属含量分析,通过污染指数法和经蔬菜途径重金属暴露接触对人体的健康风险进行了系统评价。结果表明,与非矿区比较,两矿区蔬菜、土壤Pb、Zn和Cd含量较高,矿区土壤Pb、Zn、Cd含量均超过GB15618—1995《土壤环境质量标准》二级标准（pH〈6.5）的污染警戒值;矿区蔬菜Pb、Zn和Cd含量均超过国家蔬菜重金属元素限量标准,分别为限量标准的2.0～10.75、0.9～2.5倍和2.2～19.8倍;两矿区蔬菜受到了Pb、Cd的严重污染,Zn的轻-中度污染。重金属暴露接触对人体的风险评估结果表明,两矿区居民通过蔬菜途径摄入的Pb和Cd对其健康存在较大的潜在风险,且对儿童的健康风险高于成年人。因此,矿区土壤上种植蔬菜会对食用这些蔬菜的当地居民产生一定的健康风险,应采取合适的治理措施进行矿区污染土壤的修复。     

Effect of Conditioning Zinc Sulfate Heptahydrate (ZnSHH) with Zinc Oxide (ZnO) and Neem Oil on Growth,Productivity, Zinc Biofortification of Grain and Zinc Uptake by Basmati Rice

Commercial grade zinc (Zn) sulfate hepta hydrate (ZnSHH) is the most widely used source of Zn in India and several other countries for amelioration of Zn deficiency in crops. However, it releases water of hydration at temperature above 30°C and forms lumps on storage, which make it difficult to handle it and apply in fields. Therefore, conditioning of ZnSHH with ZnO and neem oil reduces the release of water of hydration and prevents lumps formation and can be well stored. Field experiments were conducted at the research farm of the Indian Agricultural Research Institute, New Delhi, India during rice growing seasons (July-November) of 2009 and 2010 to study the effect of conditioning ZnSHH with ZnO and neem oil on growth, productivity and Zn fortification of rice (Oryza sativa) grain and uptake by Basmati rice ‘Pusa 1121’. The experiment was conducted in a randomized block design with 3 replications comprised of 9 treatments of Zn fertilization. The present study shows that when conditioned with 2% ZnO and 4% neem oil ZnSHH improved yield attributes, grain and straw yields, Zn uptake and partial factor productivity (PFP), agronomic efficiency (AE), recovery efficiency (RE), and physiological efficiency (PE) of Zn in Basmati rice ‘Pusa 1121’. In general, ZnO was inferior to ZnSHH. Application of ZnSHH conditioned with 2% ZnO and 4% neem oil can be a better source of Zn for transplanted puddled Basmati rice on Zn deficient soils.