外加氮源影响下铁铝氧化物在土壤氮素转化中的作用

土壤中铁铝氧化物在团聚体稳定性和有机碳吸附方面具有重要作用,而氮添加对土壤氮循环影响的变化也可能与其有关,但是目前尚缺乏在氮循环方面的研究.为了探究铁铝氧化物在土壤氮素转化中的作用,选择福建省建瓯罗浮栲森林土壤为研究对象,采用选择性溶提技术准备不同的土壤——未经处理（T1）的土壤和去除游离态铁铝氧化物（T2）土壤、去除非晶质铁铝氧化物（T3）土壤、去除络合态铁铝氧化物（T4）土壤,在这些土壤中添加不同形态氮（40 mg/kg）——丙氨酸（氨基酸态氮,AA）、硫酸铵（铵态氮,AN）、硝酸钠（硝态氮,NAN）和亚硝酸钠（亚硝态氮,NIN）,进行室内培养试验,分析氮含量变化和氮素转化情况.结果表明:①与CK处理相比,AA和AN处理均增加了T1土壤中w（NH₄+-N）,NAN处理增加了w（NO₃--N）,但低于添加量,表明添加氨基酸和铵态氮均会促进氮矿化,添加硝态氮会增加NO₃--N的固定且抑制其硝化.②在CK处理下,与T1土壤相比,T2和T4土壤中w（NH₄+-N）、w（NO₃--N）和w（氨基酸）均降低,但T3土壤中w（NH₄+-N）和w（氨基酸）增加、w（NO₃--N）降低,表明土壤中游离态氧化铁铝和络合态氧化铁铝的存在有助于氮素矿化,非晶质氧化铁铝有助于硝化.③在不同氮处理下,各土壤的氮含量及其转化速率与CK处理规律相似.与CK处理相比,各氮处理均未显著增加T2和T4土壤中w（NH₄+-N）,且AA和AN处理均未影响T2、T3和T4土壤中w（NO₃--N）和w（氨基酸）.结果显示,氮添加并没有改变铁铝氧化物的作用,其中,矿化和氨化作用均表现为游离氧化铁铝>络合氧化铁铝>非晶质氧化铁铝,硝化作用表现为非晶质氧化铁铝>游离氧化铁铝>络合态氧化铁铝.因此,土壤铁铝氧化物的不同存在状态应该是调节氮素转化的重要土壤条件.      

盘锦市近岸海域生物资源现状及几点建议

根据异养细菌丰度、浮游动物、浮游植物与底栖动物的生物量分布及种类组成等现场调查结果和近期海洋渔业生产资料，论述了盘锦市近岸海域生物资源现状。并根据该地区油气资源开发和海洋生物资源（尤其是经济贝类资源）保护的需要提出了几点建议。     

Seasonal changes of endogenous ABA and cytokininsin environmental adaptation of differentecotypes of reed plants

ＳｅａｓｏｎａｌｃｈａｎｇｅｓｏｆｅｎｄｏｇｅｎｏｕｓＡＢＡａｎｄｃｙｔｏｋｉｎｉｎｓｉｎｅｎｖｉｒｏｎｍｅｎｔａｌａｄａｐｔａｔｉｏｎｏｆｄｉｆｆｅｒｅｎｔｅｃｏｔｙｐｅｓｏｆｒｅｅｄｐｌａｎｔｓＷａｎｇＨｏｎｇｌｉａｎｇ，ＺｈａｎｇＣｈｅｎｇｌｉ...     

酞酸酯对人与环境的危害

酞酸酯是一种增塑剂，随着时间的推移，可由塑料中转移到外环境，现已成为地球上最为广泛存在的环境污染物。该文较系统地介绍了酞酸酯的理化性质，毒性和致癌作用，以及其对环境的影响，环境行为，动物的吸收，分布、代谢和排泄等等，最后还对酞酸酯的有关毒性评价作了部分介绍。     

Short-duration hydrothermal fermentation of food waste: preparation of soil conditioner for amending organic-matter-impoverished arable soils

Environmental Science and Pollution Research - Soil conditioners can be used to compensate for the insufficient soil nutrition and organic matter (OM) of arable soils. However, the traditional...     

饱和持水量条件下不同氮添加对森林土壤氮素净转化的影响

为了研究在饱和持水量条件下不同氮沉降形态和水平对森林土壤氮素净转化及土壤N₂O排放的影响,选取中亚热带地带性森林红壤为研究对象,采用室内模拟试验方法,设置110%饱和持水量（WHC）的土壤水分,添加不同形态氮[（NH₄）₂SO₄、NaNO₃、NH₄NO₃]和不同含量[0 mg/kg（CK）、20.0 mg/kg（LN）、66.7 mg/kg（HN）,以干土计]的氮素,进行为期14 d的室内培养（20℃）.结果表明,与CK相比,（NH₄）₂SO₄和NaNO₃处理对土壤净氮矿化和氨化的影响不大,而（NH₄）₂SO₄处理的净硝化量在高氮水平下为负值,说明硝化很弱,但该处理的净氨化量高于其他处理,特别是NaNO₃处理的净氨化量较高,认为很可能存在NO₃--N异化还原为铵（DNRA）.NaNO₃处理能显著提高土壤净硝化量而显著降低w（SON）（SON为土壤可溶性有机氮）,NH₄NO₃处理同时降低了土壤w（NH₄+-N）和w（NO₃--N）,表现为氮固定作用,并且高氮水平的土壤w（MBN）（MBN为微生物量氮）显著高于低氮水平;NaNO₃和NH₄NO₃处理的土壤N₂O排放速率和培养周期内的累积排放量均显著高于CK,并且高氮水平显著高于低氮水平,而（NH₄）₂SO₄处理与CK相当,并且高氮水平下的N₂O累积排放量低于低氮水平.研究显示,在过饱和土壤水分条件下,混合形态氮对土壤氮素净转化格局影响较大,含NO₃-形态氮明显促进土壤N₂O的排放,尤其是高氮水平.研究结果可为评价全球气候变化下特别是降雨情况下沉降氮形态对土壤氮素转化的影响提供重要参考.      

Fenton试剂处理汽车油漆废渣

采用Fenton试剂处理汽车油漆废渣。考察了FeSO_4用量、H_2O_2用量、反应温度、反应时间对处理效果的影响。实验结果表明,在FeSO_4用量为20.5 mg/g、H_2O_2用量为0.6 g/g、反应温度为80 ℃、反应时间为3 h的最优条件下,清漆渣、色漆渣、底漆渣3种漆渣的干基减量率均为20%左右,湿基减量率分别为67.9%、48.2%和64.2%,3种产物的脱水性能均有不同程度的提高,处理后废液的COD均为2 000 mg/L左右。采用Fenton试剂处理后的清漆渣产物粒径与原料相似,产物颗粒球形度高,表面粗糙,内部为多孔结构,产物作为固体燃料时燃烧更充分。Fenton试剂处理未对漆渣中的树脂主体产生较大的破坏。     

三峡库区典型小流域氮磷流失特征

为揭示三峡库区农业非点源物氮、磷流失的一般规律,以三峡库区秭归县的张家冲小流域为研究对象,自2005年1月至2006年4月,在自然降雨条件下,同步观测降雨、地表径流量,并对2次降雨径流的全过程进行了氮、磷浓度的测定,对降雨过程中径流量及污染物浓度随降雨-径流变化过程进行了监测研究.结果表明,长期干旱后的初期降雨径流中的氮、磷浓度明显高于雨季径流中的浓度,且氮、磷浓度变化与流量变化呈现出大致相同的趋势.降雨初期,氮、磷浓度随径流量的增大而升高;随着流量的继续增大,浓度呈现出下降趋势.对浓度随流量变化过程的监测表明,与基流中的浓度相比,总氮和硝态氮的浓度变化幅度较小,而氨氮和总磷浓度变化的幅度较大,其最大值分别是其最小值的10和67.5倍.溶解性的氨氮排放主要受降雨条件的制约,而径流中的磷主要是以颗粒态存在通过对径流量和氮、磷排放负荷的多项式回归分析表明,TN、TP、NH4 -N和NO3--N的排放负荷和径流量之间存在着多项式关系,R2分别为0.9545、0.9740、0.9677和0.9504.     

A modeling assessment of association between East Asian summer monsoon and fate/outflow of α-HCH in Northeast Asia

Using a dynamic numerical atmospheric transport model for organochlorine pesticides (OCPs), the relationship between the East Asian summer monsoon and the fate of α-hexachlorocyclohexane (α-HCH), a banned OCP, in the atmosphere over Northeast Asia was investigated and assessed. The modeled temporal and spatial patterns and variability of α-HCH air concentrations during the summer months of 2005 revealed a strong link between this chemical in the atmosphere over Northeast Asia and the East Asian summer monsoon. At lower atmospheric levels, easterly and southeasterly winds blowing from relatively cold ocean surface convey α-HCH air concentration from southeast China to northeast China. A monsoon front extending from southeast China to Japan, characterized by a strong wind convergence, carried the air concentration to a high elevation of the atmosphere where it was delivered by southerly monsoon flow to northern China and North Pacific Ocean. This summer monsoon associated northward atmospheric transport caused a reversal of the soil/air exchange from outgassing to net deposition during spring–summer period. The modeled wet deposition fluxes of α-HCH agreed well with the changes in the typical summer monsoon rain bands, designated as Meiyu in China, Changma in Korea, and Baiu in Japan. The major wet deposition flux paralleled with the monsoon front as well as the monsoon rain bands. The temporal change in the fluxes exhibits abrupt northward advances, which is associated with a stepwise northward and northeastward advance of the East Asian summer monsoon. The modeled α-HCH outflow in the atmosphere from China occurs mostly in the summer months and through northeast China, featured strongly by the evolution of the summer month. This study suggests that the East Asian summer monsoon provides a major atmospheric pathway and summer outflows to α-HCH over East Asia.     

Endosulfan in China 1—gridded usage inventories

Background, aim, and scope  Endosulfan, an organochlorine pesticide (OCP), is genotoxic in mammalian cells and generally considered to be toxic and classified by the World Health Organization and the US Environmental Protection Agency as priority pollutants and a nominator for inclusion in a future iteration of the persistent organic pollutants treaty. Endosulfan is a currently used pesticide and still being used worldwide. The general trend of total global endosulfan use has increased continuously since the first year when this pesticide was applied. It is critical to create national endosulfan usage/emission inventories for China to carry out source–receptor relation analysis, risk assessment, and other research related to endosulfan in this country. Chinese inventories have been published for some OCPs, such as technical HCH and lindane, DDT, and chlordane; for endosulfan, however, there has not been any usage inventory available on any scales (national or provincial), although endosulfan has been widely used since 1994 in this country. This is the first part of the work. The goal of this paper is to quantify the historical production and usage of endosulfan in China and to compile gridded historical usage inventories of endosulfan for this country. Based on these usage inventories, emission and residue inventories will be created, which is the goal of the second part of the work. Materials and methods  Due to the lack of national production and usage information of endosulfan in China, a method to estimate the use of endosulfan was developed. First, information of crops on which endosulfan is applied and average endosulfan use and annual application frequencies of endosulfan on these crops were collected. Secondly, usage of endosulfan on each crop was estimated using the national cropland area for each province from Chinese government reports. Finally, with the help of GIS (geographic information system), the usage data of this insecticide was allocated to a grid system, with a 1/4° longitude by 1/6° latitude resolution, with a size for each grid cell of approximately 25 km by 25 km. Results and discussion  The use of endosulfan in agriculture in China started on cotton in 1994, and on wheat, tea, tobacco, apples, and other fruits in 1998. Endosulfan usage on cotton, wheat, tea, tobacco, and apples in China has been estimated to be approximately 25,700 t between 1994 and 2004. The province with the highest usage of endosulfan is Henan Province, with a total usage reaching 4,000 t, followed by the uses in Xinjiang Autonomous Region (3,200 t), Shandong Province (3,000 t), Hebei Province (2,100 t), and Anhui Province (1,900 t). Gridded usage inventories of endosulfan at a 1/4° longitude by 1/6° latitude resolution have been created, which indicate that the intensive endosulfan use was in the south of Hebei Province, west of Shandong Province, east of Henan Province, north of Anhui Province, east of Jiangsu Province, and some areas in Yunnan Province and Xinjiang Autonomous Region. General agreement has been found between the usage data from our estimation and the small amount of usage data published in China. Conclusions  This is the first national gridded endosulfan usage inventory produced for China. The annual applications of endosulfan from 1994 to 2004 in China were estimated based on the total areas of major crops, on which endosulfan was applied, and spatial distribution of the application was generated at provincial and prefecture levels. With the help of GIS, endosulfan usage based on prefecture was transferred to a 1/4° longitude by 1/6° latitude gridding system. The satisfaction of the inventories was supported by the consistence between the estimation of the annual usage and the reported annual production of endosulfan. Recommendations and perspectives  This gridded endosulfan usage inventory created in this study will be improved upon availability of new information of endosulfan. The usage inventories can be used to create gridded emission and residue inventories for this insecticide. It is believed that this work will pave the way for further endosulfan studies in China and beyond.