大通河流域土壤细菌及氮循环功能菌群沿海拔的空间分布

探究土壤微生物的海拔分布格局及其驱动机制对理解气候变化下陆地生态系统的响应至关重要.土壤微生物群落的海拔分布格局随空间尺度有所差异,为此分别沿大通河流域干流流向（海拔梯度1 000 m）和山体坡面（海拔梯度500 m）设置了两种空间尺度的样带,利用高通量测序技术分析土壤细菌群落结构和多样性沿海拔的分布特征,基于FAPROTAX数据库分析氮循环功能类群的海拔分布,探讨驱动土壤细菌群落沿海拔分布的关键环境因子.结果表明:①土壤理化性质沿海拔分布有显著差异,总氮（TN）和硝态氮（NO₃ ^-）含量与海拔正相关（P < 0.01）,土壤容重（BD）、pH与海拔负相关（P < 0.001）;②细菌群落OTU丰度沿海拔升高显著增大（P < 0.01）,丰富度和多样性指数沿海拔增大,但趋势不显著（P > 0.05）;③细菌群落以酸杆菌门（Acidobacteria）、变形菌门（Proteobacteria）和拟杆菌门（Bacteroidetes）为优势门,其相对丰度随海拔升高分别增加、减小和微弱减小;④参与氮循环的功能类群共13种,以硝化作用、好氧氨氧化和好氧亚硝酸盐氧化作用为主,随海拔升高响应规律不同,其中硝化作用细菌丰度显著增加（P < 0.01）,好氧氨氧化和硝酸还原细菌丰度微弱增加,而参与含氮化合物异化还原的细菌丰度先增后减;⑤冗余分析表明海拔（ELEV）、pH和氨氮（NH₄ ⁺）是驱动门水平土壤细菌群落的主要因子,Mantel分析表明土壤细菌氮循环优势类群均受海拔驱动（P < 0.01）.⑥流域和坡面尺度上细菌群落α-多样性沿海拔的规律一致,但土壤性质、氮循环功能菌群丰度和主要环境影响因子均不同.因此从不同空间尺度探究土壤微生物的海拔分布格局具有重要意义.     

地裂缝上内廊式框架结构计算分析

通过查阅大量参考资料,根据地裂缝的成因机制与灾害特征,利用西安地区1989年第三季度—1990年第四季度的地裂缝实测数据,以四层内廊式横向框架结构模型为研究对象,采用SAP2000有限元软件,对地裂缝上的建筑结构进行内力变化和结构变形的分析和对比,从而标识出结构中最容易破坏的构件,为建筑结构设计提供一定的理论参考。     

氧化镁脱硫结垢研究

对氧化镁脱硫法中的结垢问题进行了系统的研究 ,通过对比实验 ,分析了结垢的机理、氧化镁法在防止结垢方面所具有的优势及其原因 ,提出了实际中判断结垢倾向的方法和避免结垢的合理建议。     

Sewage sludge ditch for recovering heavy metals can improve crop yield and soil environmental quality

• Indirect use of sludge in ditches alongside plants was tested in field experiments. • The dried and stabilized sludge in ditches was recovered with heavy metals. • Cd, Pb, Cu and Zn in the planted soil were all in a safe range. • The indirect use of sludge increased plant yield, soil N content and C storage. The treatment and disposal of municipal sewage sludge (MSS) is an urgent problem to be resolved in many countries. Safely using the nutrients within MSS to increase crop yield and enhance the fertility of poor soil could contribute to achieving sustainable development. An indirect use of MSS in ditches alongside Pennisetum hybridum plants was studied in field plots for 30 months and the contents of heavy metals and macronutrients were monitored in soil, sludge and plant samples. We found that the yield of P. hybridum was significantly increased by 2.39 to 2.80 times and the treated plants had higher N content compared with no sludge. In addition, the organic matter (OM) and N contents in the planted soil increased significantly compared with the initial soil. The OM content in the planted soil of the MSS treatment was 2.9 to 5.2 times higher than that with no sludge, and N increased by 2.0 to 3.8 times. However, MSS had no significant effect on the N, P and K contents in the soil at the bottom of the MSS ditch, and the content of heavy metals (Cd, Pb, Cu and Zn) were also within the safe range. Moreover, the moisture content and phytotoxicity of MSS after this indirect use were reduced and the heavy metal contents changed little, which is favorable to the further disposal of recovered MSS. Therefore, this indirect use of MSS is beneficial to agricultural production, soil quality and environmental sustainability.     

Remediation of arsenic contaminated soil by sulfidated zero-valent iron

• Sulfidation significantly enhanced As(V) immobilization in soil by zerovalent iron. • S-ZVI promoted the conversion of exchangeable As to less mobile Fe-Mn bound As. • Column test further confirmed the feasibility of sulfidated ZVI on As retention. • S-ZVI amendment and magnetic separation markedly reduced TCLP leachability of As. In this study, the influences of sulfidation on zero-valent iron (ZVI) performance toward As(V) immobilization in soil were systemically investigated. It was found that, compared to unamended ZVI, sulfidated ZVI (S-ZVI) is more favorable to immobilize As(V) in soil and promote the conversion of water soluble As to less mobile Fe-Mn bound As. Specifically, under the optimal S/Fe molar ratio of 0.05, almost all of the leached As could be sequestrated by>0.5 wt.% S-ZVI within 3 h. Although the presence of HA could decrease the desorption of As from soil, HA inhibited the reactivity of S-ZVI to a greater extent. Column experiments further proved the feasibility of applying S-ZVI on soil As(V) immobilization. More importantly, to achieve a good As retention performance, S-ZVI should be fully mixed with soil or located on the downstream side of As migration. The test simulating the flooding conditions in rice culture revealed there was also a good long-term stability of soil As(V) after S-ZVI remediation, where only 0.7% of As was desorbed after 30 days of incubation. Magnetic separation was employed to separate the immobilized As(V) from soil after S-ZVI amendment, where the separation efficiency was found to be dependent of the iron dosage, liquid to soil ratio, and reaction time. Toxicity characteristic leaching procedure (TCLP) tests revealed that the leachability of As from soil was significantly reduced after the S-ZVI amendment and magnetic separation treatment. All these findings provided some insights into the remediation of As(V)-polluted soil by ZVI.     

农地转用政策与农地转用最优数量——外部性内化视角的实证分析

尽管不少文献对农地转用政策的有效性进行了分析,但我国农地转用政策在农地-市地配置优化中的作用却较少受到关注。论文从外部性内化的视角出发,利用地方政府农地转用模型对土地用途管制、税费政策的作用机制和配置效应进行研究。在考虑多项政策影响的基础上,对湖北省地方政府决策函数进行拟合,并结合近年来农地外部性测算的结果实证分析了农地转用政策的合理性及其对农地转用数量的影响。实证结果表明,土地用途管制和税费政策均能显著地抑制农地转用数量,但政策的影响效果则存在差异。其中,税费政策的数量标准与外部性数量基本一致,但土地用途管制对农地转用的抑制效果已经超出了外部性内化的目标。根据这一结果,结论部分讨论了相应的政策含义及农地转用配置优化的对策建议。     

Monitoring of soil biochemical quality parameters under greenhouse spinach cultivation through animal waste recycling

Under the intensive agricultural system, direct application of animal slurries to soils can provide a sustainable disposal of these wastes by inducing positive changes in soil quality and fertility. However, how animal wastes quantitatively affect the key nutrients (C, N, P and S) transforming soil enzymes is not clearly known. A greenhouse spinach cultivation study demonstrated that pig slurry, either in raw (RS) or processed (aerobically aged) (PS) form, significantly (p?β-glucosidase (23–39%), urease (59–103%), nitrate reductase (73–103%) and dehydrogenase (27–72%)) and microbial growth in soil as compared to the unamended control. However, it did not significantly (p?>?.05) alter the aryl sulphatase enzyme activity. Slurry applications also significantly improved the macro (N, P and K) and micronutrients (Cu, Mn, Zn and Fe) uptake by spinach plant and hence the yield (2.9–3.38 times higher than control). Similarly, compared to chemical fertilisers the application of pig slurries improved soil biological and biochemical parameters as well as plant nutrients uptake. This study demonstrated the closing of global energy and nutrient cycles through land application of animal wastes without compromising the crop yield.     

Distribution of thifluzamide,fenoxanil and tebuconazole in rice paddy and dietary risk assessment

Distribution behaviors of thifluzamide, fenoxanil, and tebuconazole applied to rice were investigated in South China. Analysis was by a modified QuEChERS method with gas chromatography (thifluzamide and fenoxanil) and liquid chromatography mass spectrometry (tebuconazole). Thifluzamide and tebuconazole partitioned mainly into the soil, with half-lives in the paddy soil of 12–14 and 5.3–7.8 days, respectively. Fenoxanil partitioned mainly into the rice plants, with half-lives of 3.3–4.4 days. The half-lives of thifluzamide, fenoxanil, and tebuconazole in paddy water were 0.17–0.89, 1.8–3.0, and 1.6–4.0 days, respectively. The residues in rice grains at the pre-harvest interval of 14 days were all below the established maximum limit values. The dietary risks assessed as hazard quotients at the pre-harvest interval were less than 1.     

冶炼企业周边农田土壤的多环芳烃污染及其细菌群落效应

多环芳烃是一类持久性有机污染物,进入土壤后可能产生多方面生态效应。为研究多环芳烃对土壤微生物的影响,选取南京某冶炼企业周边农田样品,在分析污染物含量基础上,采用高通量测序、定量PCR等方法综合评价了土壤细菌多样性和组成以及多环芳烃降解细菌丰度等特征。17个土壤样品中,多环芳烃总量为0.25~31.08 mg·kg-1,并具有随污染源距离增加而降低的空间分布特征。与土壤理化性质如p H相比较,多环芳烃污染对土壤细菌的总体多样性和群落组成影响不显著。进一步分析发现多环芳烃与潜在降解微生物的相对丰度和降解功能基因(芳香环羟基化双加氧酶,PAH-RHDα)拷贝数显著正相关。污染较重样品的克隆、测序分析表明,土壤中PAH-RHDα基因主要属于革兰氏阳性细菌nid A3/fad A1类群,且与分支杆菌相关序列较为接近。这些结果综合评价了冶炼企业周边农田土壤多环芳烃污染对微生物群落的影响,提示土壤污染在多环芳烃潜在降解细菌中的富集作用,将为后续污染土壤生物修复提供重要科学依据。     

长三角农田土壤中滴滴涕的污染特征与生态风险

以长江三角洲地区农田土壤为研究对象,分析了土壤和蔬菜中滴滴涕(DDTs)的残留水平和空间分布特征,评估了DDTs对土壤生态和人体健康的潜在风险。结果显示,长三角地区农田土壤中DDTs含量范围为0.2~3 520 ng·g-1,平均63.8 ng·g-1,主要残留在土壤耕作层(0~30 cm)。土壤中DDTs及其代谢产物残留量较低,98.5%的点位土壤符合《中国土壤环境质量标准》的二级标准。15%的蔬菜样品中检出DDTs,其浓度为相应土壤DDTs浓度的9%~18%,土壤残留的DDTs通过食物链进入人体导致的健康风险很小。低残留DDTs对土壤微生物的群落结构和多样性无显著影响(-0.25R0.25,0.307P0.979)。应用美国环保署(USEPA)方法评估了土壤中DDTs对人体的健康风险,其中致癌风险级别为非常低,对儿童和成人具有非致癌风险的样品比例分别为1.1%和0.7%。因此,长三角地区大多数点位农田土壤DDTs残留量较低,不会对生态环境和人体健康产生危害。