魅力国土空间:重塑区域特色的国土空间规划策略

国土空间规划的提出使我国的规划体系进入到新的发展时期与发展语境,国土空间开发方向已从生产空间为主导转向生态、生活、生产空间相协调。如何将基于“三生空间”概念的传统国土空间认知提升到丰富文化脉络、生态特征、生活基础的复合魅力国土空间,如何对不同区域的发展进行侧重,杜绝对单一发展模式的盲目跟风,是国家和地方面临的共同重大主题。结合国土空间在历史与现实不同时期的发展表征和形成原因,在回溯空间认知过程、反思空间规划实践的基础上,厘清了魅力国土空间的概念与内涵,提出国土空间规划体系下魅力国土空间的关注焦点,从区域发展平衡、管控弹性调整、空间要素流动、发展目标优化等方面阐述了魅力国土空间的作用与功能。     

Ni2+对好氧颗粒污泥系统性能的影响

以城镇污水处理厂A²/O工艺的回流污泥作为接种污泥,在序批式反应器（SBR）中培养好氧颗粒污泥（AGS）,探究Ni²⁺对AGS系统的影响.结果表明：在25℃的条件下,50d左右培养出成熟的AGS,其形态多呈球状或椭球状,外表分布着少量丝状菌,颗粒污泥粒径主要在2~4mm,MLSS达6000mg/L,SVI维持在40~50mL/g.将Ni²⁺作用于培养出的成熟AGS,Ni²⁺在0~2mg/L的浓度范围内会提高AGS的稳定性,使MLSS上升,SVI降低;同时会促进AGS分泌胞外多聚物（EPS）,EPS组成成分中的蛋白质（PN）明显多于多糖（PS）;Ni²⁺对好氧颗粒污泥去除总氮（TN）的抑制程度要大于COD,最终COD去除率可维持在95%以上,TN去除率可维持在70%以上.     

互花米草入侵对长江口湿地土壤碳动态的影响

为了评价互花米草入侵对长江河口湿地土壤碳动态的影响,利用配对的试验设计在长江口崇明东滩湿地的高潮滩和低潮滩各设置1条入侵种互花米草与土著种的配对样线.结果表明,与土著植物相比,互花米草入侵显著增加了长江口湿地的植物碳库、土壤微生物碳、土壤总碳库和有机碳库,而对占土壤总碳库60%以上的无机碳库无显著影响,意味着互花米草入侵导致的土壤总碳库改变主要是通过增加土壤有机碳库来实现的.高潮滩互花米草和芦苇群落的年均土壤呼吸强度分别为（210.02±4.90）,（157.79±6.39）mg/（m²·h）;低潮滩互花米草和海三棱藨草群落年均土壤CO₂排放速率分别为（157.41±5.27）,（110.90±5.16）mg/（m²·h）,表明互花米草入侵显著增加长江口湿地的土壤呼吸.上述结果意味着互花米草入侵同时增加土壤碳输入和碳输出,但入侵也显著增加了土壤碳库表明入侵增加的土壤碳输入显著高于增加的土壤碳输出.本研究表明互花米草入侵可能会增强了长江河口湿地的土壤碳汇强度和固碳能力.但仍然需要长期系统的监测研究,以便全面定量评估互花米草入侵我国滨海湿地的综合生态影响.     

水中Mg~(2+)的测试管快速测定

研制了一种测定水中Mg2 + 的测试管 ,测定范围为 0 .5mg/L～ 2 .0mg/L。该测试管适用于现场应急监测 ,具有快速、简便、抗干扰能力强和价格低廉等特点     

Multimedia model of atrazine in plant-soil-groundwater system with a fugacity approach

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论乌海及周边地区推广气烧石灰竖窑的可行性

本文介绍了使用焦炉煤气做气烧石灰竖窑清洁燃料国内发展概况，阐述了在乌海及周边地区利用丰富石灰石资源和焦炉剩余煤气开展清洁生产、减少环境污染、进行循环经济的必然选择，并从石灰石生产工艺选择，环境效益分析方面进行了讨论。     

MBBR处理制药废水的试验研究

采用二级移动床生物膜反应器(MBBR)处理呋喃铵盐制药废水。在填充比为40%,总水力停留时间为32h时,COD的去除率为88.6%,TN的去除率为25.7%,第二级反应器对NH3-N的去除率为56.2%。     

水中氯仿的活性炭电增强吸附特性

讨论了活性炭在电场作用下对水中微量的三氯甲烷的吸附 ,测定不同控制电位下活性炭的吸附量 ,并讨论了吸附动力学与吸附等温方程 .实验结果表明 :活性炭的吸附量与活性炭上所加的控制电位相关 .在阳极极化时 ,活性炭的吸附量增大 ;在阴极极化时 ,活性炭吸附量减少 .吸附起始浓度为 10 0 μg L的氯仿溶液 ,同样数量的活性炭在阳极极化下可得到最大吸附量 ,其值为无电场时的 1 6倍 .分析了电场影响活性炭吸附的机理 .     

Photocatalytic remediation of γ-hexachlorocyclohexane contaminated soils using TiO2 and montmorillonite composite photocatalyst

TiO2 and montmorillonite composite photocatalysts were prepared and applied in degrading γ-hexachlorocyclohexane(γ-HCH)in soils.After being spiked with γ-HCH,soil samples loaded with the composite photocatalysts were exposed to UV-light irradiation.The results indicated that the photocatalytic activities of the composite photocatalysts varied with the content of TiO2 in the order of 10%＜70%＜50%＜30%.Moreover,the photocatalytic activity of the composite photocatalysts with TiO2 content 30% was higher than that of the pure P25 with the same mass of TiO2.The strong adsorption capacity of the composite photocatalysts and quantum size effect may contribute to its increased photocatalytic activities.In addition,effect of dosage of composite photocatalysts and soil pH on γ-HCH photodegradation was investigated. Pentachlorocyclohexene,trichlorocyclohexene,and dichlorobenzene were detected as photodegradation intermediates,which were gradually degraded with tlle phOtOdegradation evolution.     

Photodegradation of acetochlor in water and UV photoproducts identified by mass spectrometry

The sunlight photodegradation half-lives of 20 mg/L acetochlor were 151, 154 and 169 days in de-ionized water, river water and paddy water, respectively. When exposed to ultraviolet (UV) light, acetochlor in aqueous solution was rapidly degraded. The half-lives were7.1, 10.1, and 11.5 min in de-ionized water, river water and paddy water, respectively. Photopreduets of acetochlor were identified by gas chromatography/mass spectrometry(GC/MS) and found at least twelve photoproducts resulted from dechlorination with subsequent hydrtrxylation and cyclization processes. The chemical structures of ten photoproducts were presumed on the basis of mass spectrum interpretation and literature data. Photoproducts are identified as 2-ethyl-6-methylaniline; N, N-diethylaniline ; 4, 8-dimethyl-2-oxo- 1,2,3,4- tetrahydroquino-line; 2-oxo-N-(2-ethyl-6-methylphenyl)-N-(ethoxymethyl) acetamide; N-(ethoxymethyl)-2‘-ethyl-6‘-methylformanilide; 1-hydroxyaeetyl-2-ethoxyl-7-ethylind ole; 8-ethyl-l-ethoxymethyl-2-oxo-1, 2, 3, 4-tetrahydroquinoline; 4, 8-dimethyl-l-ethoxymethyl-2-oxo-1, 2, 3, 4-tetrahydroquinoline; 2-hydroxy-2‘-ethyl-6‘-methyl-N-(ethoxymethyl) acetanilide and a compound related to acetochlor. The other two photoproducts were detected by GC/MS although their chemical structure was unknown.