重庆地票交易时空特征及其与人口流动的耦合态势

从地票复垦生产和落地使用双边视角,采用区位基尼系数、热点分析、重心演变等方法探寻地票交易特征动态变化过程及其与人口流动的耦合态势。研究表明：（1）重庆主城区地票流入极功能弱化;渝西地区正成为新的地票流入极;渝东北、渝东南地区发展为以产出地票为主、兼具地票使用需求的复合区域。（2）渝东北、渝东南分别是地票复垦生产的主极核和次极核。渝西地区呈爆发式产出剧增。（3）地票流与人口流呈“偏离—一致—偏离”耦合态势。差异化的落地政策刺激了人口流出区地票使用积极性,造成地票流入偏离城镇人口流入轨迹;渝西地区受需求驱动大规模生产地票、渝东北和渝东南剩余农村闲置建设用地资源潜力有限,造成地票流出偏离乡村人口流出轨迹。     

盐酸羟胺/铁基MOFs/过硫酸盐体系降解磺胺嘧啶

使用盐酸羟胺（HA）促进Fe （Ⅲ）/Fe （Ⅱ）循环,强化铁基金属有机骨架（Fe-MOFs）/过硫酸盐（PS）体系降解水中磺胺嘧啶（SDZ）.通过X射线衍射（XRD）、扫描电子显微镜（SEM）、傅立叶变换红外光谱（FTIR）和X射线光电子能谱仪（XPS）对Fe-MOFs进行结构和形貌的表征.探究了溶液初始pH值、PS浓度、Fe-MOFs投加量、HA浓度、SDZ浓度、共存离子、腐殖酸等对SDZ去除效果的影响,并考察了该体系的实际应用前景.结果表明,Fe-MOFs/PS/HA体系在较宽的初始pH值范围（3~6）内,对于SDZ的180min去除率可达到90.1%以上.适量的HA可以促进Fe-MOFs/PS体系降解SDZ的性能.自由基清扫实验和电子顺磁共振实验表明,Fe-MOFs/PS/HA体系降解SDZ的过程中产生了SO₄^-·、·OH、O₂^-·以及¹O₂.在本文考察范围内,Fe-MOFs/PS/HA体系对SDZ的降解性能随pH值（pH=3~6）升高逐渐下降;随着PS、HA、Fe-MOFs浓度的升高,SDZ去除率呈现率先上升后下降的趋势.氯离子、腐殖酸等因素对该体系应用于实际地表水存在负面作用,但HA可以强化该体系在自然环境下降解SDZ的效果.循环实验结果表明,Fe-MOFs具有良好的重复使用性,表现出了良好的应用潜力.     

微塑料对结冰过程中环境因子迁移的影响

为探究结冰过程中微塑料赋存对典型环境因子(总氮、总磷、盐度、化学需氧量、悬浮物)等分布及迁移规律的影响,采用室内模拟的方式研究不同条件下(结冰比例、结冰温度及方式、初始浓度)各典型环境因子在冰-水相间的分布及迁移规律,采用物质分配系数(K)表征环境因子的迁移能力。结果表明,结冰过程中冰体对环境因子具有排斥作用,不同条件下微塑料赋存对环境因子的分布规律均有一定程度的影响,由于微塑料自身特性致使原本应迁移至冰下水体中的环境因子部分滞留于冰体中,导致冰体中环境因子浓度的提高,为对照组冰体中环境因子浓度的1.13~1.49倍;同时使冰下水体中环境因子浓度下降,为对照组冰下水体中环境因子浓度的0.73~0.93倍;微塑料的赋存同时导致环境因子分配系数K值提高0.04~0.18,致使环境因子向冰下水体迁移的能力下降,但微塑料的赋存并未改变结冰过程中环境因子由冰体向冰下水体迁移的趋势,微塑料对于环境因子的携带作用小于冰体对环境因子的排斥作用;同时不同条件下结冰过程中微塑料对环境因子分布与迁移机理的影响均可以从结晶学角度与共晶理论得到解释。     

长期冻融循环下固化铅锌镉复合重金属污染土抗剪强度及浸出特征研究

为了评估长期冻融循环后(最长90d (次))固化复合重金属污染土的的抗剪强度及浸出特征,采用水泥、生石灰和粉煤灰按比例混合的复合固化剂固化/稳定化铅锌镉复合重金属污染土进行三轴压缩试验及毒性特征浸出程序试验.结果表明,固化污染土体的内摩擦角仅在冻融循环3次内有明显增加,增加率高达96.3%;粘聚力在冻融循环30次内总体趋势不断下降,之后无显著变化,最终下降率达到54.23%;Pb²⁺、Zn²⁺、Cd²⁺浸出浓度与冻融循环次数呈正比;EC值与冻融循环次数在总体上正相关;长期冻融循环作用后浸出液的pH值降低.并通过扫描电子显微镜,进一步探究长期冻融循环下固化污染土抗剪强度及浸出特征的劣化机理,结果显示在冻融循环后期固化土体内生成了大量的延迟钙矾石,这些延迟钙矾石在形成过程中的膨胀作用是引起抗剪强度损失、重金属浸出浓度升高的主要原因.     

两亲性壳聚糖制备优化及其气浮除藻研究

对壳聚糖（CTS）进行了两亲改性,通过响应曲面实验对比各因素对取代度影响的显著程度且优选出最佳的制备条件,并采用3种两亲性CTS进行了表面改性气浮（PosiDAF）除藻实验,对比了不同条件下的除藻效果且探究除藻机理.结果表明,两亲性CTS水溶性增强,但热稳定性降低;对响应值影响的显著程度为：碳链长度>反应时间>反应温度>原料投加比;以丁基N-2羟丙基三甲基壳聚糖氯化铵（C4-HTCC）为改性剂,投加量为1.0mg/L时改性气浮除藻效果最佳,可达93.47%,源于其改性的微气泡具有较强的静电吸引作用.     

Mechanisms of Pb(II) coprecipitation with natrojarosite and its behavior during acid dissolution

Lead (Pb) coprecipitation with jarosite is common in natural and engineered environments, such as acid mine drainage (AMD) sites and hydrometallurgical industry. Despite the high relevance for environmental impact, few studies have examined the exact interaction of Pb with jarosite and the dissolution behavior of each phase. In the present work, we demonstrate that Pb mainly interacts with jarosite in four modes, namely incorporation, occlusion, physically mixing, and chemically mixing. For comparison, the four modes of Pb-bearing natrojarosite were synthesized and characterized separately. Batch dissolution experiments were undertaken on these synthetic Pb-bearing natrojarosites under pH 2 to simulate the AMD environments. The introduction of Pb decreases the final Fe releasing efficiency of jarosite-type compounds from 18.18% to 3.45%-5.01%, showing a remarkable inhibition of their dissolution. For Pb releasing behavior, PbSO₄ dissolves in preference to Pb-substituted natrojarosite, i.e., (Na, Pb)-jarosite, which primarily results in the sharp increase of Pb releasing concentration (> 40 mg/L). PbSO₄ occlusion by jarosite-type compounds can significantly reduce the release of Pb. The results of this study could provide useful information regarding Fe and Pb cycling in acidic natural and engineered environments.     

Competing pathways of cresol formation in toluene photooxidation: OH-toluene adducts react with NO2 or with O2?

Methyl-hydroxy-cyclohexadienyl radicals (OTAs) are the key products of the photooxidation of toluene, with implications for the fate of toluene. Hence, we investigated the photooxidation mechanisms and kinetics of three main OTAs (o-OTA, m-OTA, and p-OTA) with NO₂ using quantum chemical calculations as well as the fate of OTAs under the different concentration ratios of NO₂ and O₂. The mechanism results show that the pathway of H-abstraction by NO₂ to anti-HONO (anti-H-abstraction) is more favorable than the syn-H-abstraction pathway, because the strong interaction between OTAs and NO₂ is formed in the transition states of the anti-H-abstraction pathways. The branching ratios of the anti-H-abstraction pathways are more than 99% in the temperature range of 216−298 K. The total rate constant of the OTA-NO₂ reaction is 9.9 × 10⁻¹² cm³/(molecule∙sec) at 298 K, which is contributed about 90% by o-OTA + NO₂, and the main products are o-cresol and anti-HONO. The half-lives of the OTA-NO₂ reaction in some polluted areas of China are 35 times longer than those of the OTA-O₂ reaction. In the atmosphere, the NO₂- and O₂- initiated reactions of OTAs have the same ability to form cresols as [NO₂] is up to 142.1 ppmV, which is impossible to achieve. It implies that under the experimental condition, the [NO₂]/[O₂] should be controlled to be less than 7.8 × 10⁻⁵ to simulate real atmospheric oxidation of toluene. Our results reveal that for the photooxidation of toluene, the yield of cresol is not affected by the concentration of NO₂ under the atmospheric environment.     

Remediation of preservative ethylparaben in water using natural sphalerite: Kinetics and mechanisms

As a typical class of emerging organic contaminants(EOCs), the environmental transformation and abatement of preservative parabens have raised certain environmental concerns. However, the remediation of parabens-contaminated water using natural matrixes(such as, naturally abundant minerals) is not reported extensively in literature. In this study, the transformation kinetics and the mechanism of ethylparaben using natural sphalerite(NS) were investigated. The results show that around 63% of ethy...     

Formation of sulfur oxide groups by SO2 and their roles in mercury adsorption on carbon-based materials

The presence of SO₂ display significant effect on the mercury (Hg) adsorption ability of carbon-based sorbent. Yet the adsorption and oxidation of SO₂ on carbon with oxygen group, as well as the roles of different sulfur oxide groups in Hg adsorption have heretofore been unclear. The formation of sulfur oxide groups by SO₂ and their effects on Hg adsorption on carbon was detailed examined by the density functional theory. The results show that SO₂ can be oxidized into SO₃ by oxygen group on carbon surface. Both C-SO₂ and C-SO₃ can improve Hg adsorption on carbon site, while the promotive effect of C-SO₂ is stronger than C-SO₃. Electron density difference analyses reveal that sulfur oxide groups enhance the charge transfer ability of surface unsaturated carbon atom, thereby improving Hg adsorption. The experimental results confirm that surface active groups formed by SO₂ adsorption is more active for Hg adsorption than the groups generated by SO₃.     

典型工程纳米材料对微藻的毒性效应研究进展

近年来,随着纳米技术的快速发展,工程纳米材料由于其良好的物理化学特性而广泛应用于各行各业。然而,在生产、使用和丢弃含有工程纳米材料产品的过程中不可避免地导致纳米材料释放到水环境中。工程纳米材料已在世界多地的水环境中被检测到,给水生态系统和人体健康带来潜在风险。由于水环境的复杂性,工程纳米材料在水体中的环境行为、毒性效应等生态风险还未得到充分的研究。本文以微藻为模型生物,总结了典型工程纳米材料,包括纳米金属、纳米氧化物、碳纳米材料以及量子点的毒性效应。探讨了工程纳米材料在水中的环境行为以及与其它污染物的复合毒性效应,讨论了工程纳米材料自身理化性质和环境因素对其毒性的影响。从生理指标和组学指标出发分析了工程纳米材料对微藻的毒性机制,并展望了工程纳米材料毒性研究的发展方向,以期为工程纳米材料的毒性评价提供一定的理论依据,促进纳米材料的绿色发展。