甘氨酸厂氨氮废水治理的工艺及实验研究

运用多效真空蒸发兼热泵技术回收甘氨酸厂高氨氮废水中的氯化铵,通过实验找到了治理此废水的最佳真空度,克服了采用常规蒸发方法的能耗大、料液对设备腐蚀性强的缺点。最后运用吹脱法对蒸发冷凝水进行了治理,通过实验得到了吹脱的最佳工艺参数吹脱时间6h、pH125、吹脱温度60℃,为运用生化法彻底解决甘氨酸厂高氨氮工业废水的污染难题奠定了基础。     

3种人工湿地基质材料对氨氮的吸附特性

对陶粒、石英砂和砾石这3种人工湿地基质材料进行了氨氮（NH₄⁺-N）吸附特性研究.通过扫描电镜和BET比表面积分析仪对材料进行表征分析,发现陶粒表面相比石英砂和砾石更为粗糙,内部孔隙也较发达,陶粒（18.97 m²·g^-1）比表面积高于石英砂和砾石.在纯氨氮溶液和模拟污水厂出水一级B标准的混合溶液中,3种基质对NH₄⁺-N的吸附能力均表现为：陶粒>砾石>石英砂.陶粒对NH₄⁺-N的饱和吸附容量在混合溶液中最大（63.55 mg·g^-1）.陶粒对NH₄⁺-N的吸附过程符合伪二级动力学模型（在纯氨氮溶液中R²为0.99、在混合溶液中R²为0.98）.在纯氨氮溶液中运用Freundlich和Langmuir模型对等温吸附试验结果进行拟合,发现Freundlich模型（R²=0.93）描述陶粒的吸附特性比Langmuir模型更为精确（R²为0.93）,表明陶粒对NH₄⁺-N的吸附为多层吸附.综上所述,陶粒的吸附容量较强,在混合溶液中吸附容量较纯氨氮溶液增大了31%,适用于作为人工湿地基质填料.     

高效液相色谱法测定全氟辛酸铵

全氟辛酸铵是聚四氟乙烯生产废水中的重要污染物,本文采用高效液相色谱对全氟辛酸铵进行定量分析,通过流动相的离子抑制法,达到了满意的检测效果。     

氨氧化木质素作为硝化抑制剂的研究

通过室内培养实验对氨氧化木质素(AOL)的硝化抑制作用进行了探讨。在相同条件下,分别加AOL和DCD处理的铵态氮质量分数都要比未加硝化抑制剂处理的高;相应地,在开始阶段硝态氮质量分数也要比未加硝化抑制剂处理的低。研究结果表明,AOL作为硝化抑制剂是有效果的。     

磷酸铵镁沉淀法脱氨机理、应用及沉淀剂循环

铵根离子可以和镁盐、磷酸根在适当的条件下生成磷酸铵镁沉淀,利用这一反应可以去除水中的氨氮.本文从磷酸铵镁的性质、反应机理、反应条件及沉淀剂循环利用等方面,对这一方法进行了介绍和总结,并对今后该技术发展提出了建议.     

生物电化学措施下SBBR中的亚硝酸盐累积性能及微生物学特征

针对常温下生活污水短程硝化难以实现且稳定性差的难题,探究了生物电化学措施对序批式生物膜反应器(SBBR)中NO₂⁻-N的累积性能及微生物学特征的影响。对SBBR施加生物电化学措施后,通过调控外加电极电势可实现其中电极氨氧化作用的发生及强化,且不同的外加阳极电势会显著影响系统中NH₄⁺-N的转化效果、氧化产物类型及菌群结构。随着外加阳极电势由0.00增至0.50 V,SBBR中电极氨氧化作用的强度逐步提高,系统的NH₄⁺-N氧化效率(AOE)与NO₂⁻-N累积效率(NiAE)分别增至(97.07±1.20)%和(92.79±2.12)%;当外加阳极电势≥0.80 V后,SBBR中NH₄⁺-N的氧化产物因工作电极上的析氧反应转而以NO₃⁻-N为主,电极氨氧化作用的强度因电势不断升高而受到抑制,系统的AOE随之恶化。将外加阳极电势恒定为0.50 V,生物电化学强化型SBBR在常温下处理生活污水时可取得理想的NH₄⁺-N转化效率(AOE=(99.33±0.11)%)与较高水平的亚硝酸盐累积量(NiAE=(88.08±2.07)%),此时系统中的电极氨氧化作用可得到较大程度的强化,其电活性生物膜中的优势菌属包括Nitrosomonas(33.54%)、Geobacter(15.24%)和Empodebacter(16.88%),三者在NH₄⁺-N厌氧氧化过程中起关键作用。     

共价接枝聚季铵盐型杀生剂的制备及工艺优化

研制了一种表面接枝的聚季铵盐型高分子杀生剂,并考察了其对水溶液中的各种菌体的杀生效果,通过对活化剂和硅胶载体的优化,确定了最佳制备方案。结果表明,可以使用价格低廉的-γ氯丙基三甲氧基硅烷代替4-溴丁酰氯作为活化剂,载体硅胶的选择范围广泛,可以采用比表面积大、价格低廉的硅胶作为载体。扫描电镜和红外光谱检测表明杀生功能基团已共价接枝到载体硅胶上。杀生性能检测表明该杀生剂可以在低浓度、短时间内降低水溶液中的大肠杆菌、金黄色葡萄球菌以及真菌的活菌量。显微镜观察发现,杀生剂的灭藻过程是杀生剂表面吸附(藻体)、接触、灭藻。结果表明,新型固定化高分子杀生剂具有较强的抗细菌和抗真菌的能力,对藻类也具有杀灭作用,是一种高效、广普、性质稳定的水处理杀生剂。     

EGSB-BAF集成系统实现厌氧氨氧化、甲烷化和短程硝化反硝化

将膨胀颗粒污泥床(EGSB)和曝气生物滤池(BAF)集成,EGSB出水进入BAF进行短程硝化,BAF出水外回流至EGSB反应器为后者提供亚硝态氮,在不需外部投加亚硝态氮的条件下,实现厌氧氨氧化、甲烷化和短程硝化反硝化的耦合, 系统地处理ρ(氨氮)为50 mg/L和ρ(COD_Cr)为500 mg/L的合成废水.结果表明:当外回流比为200%时,系统CODCr,氨氮和总氮的去除率分别为92.4%,97.4%和80.6%;出水ρ(氨氮),ρ(亚硝态氮),ρ(硝态氮)和ρ(COD_Cr)分别为1.05,4.30,2.56和35.3 mg/L;COD_Cr,总氮和氨氮的去除负荷速率分别为1.770,0.137和0.164 kg/(m3·d). 与传统的活性污泥过程相比,EGSB-BAF集成系统回收甲烷1.03 　L/d,占系统COD_Cr去除量的37.0%;在系统总氮的去除过程中,厌氧氨氧化途径占35.9%,短程反硝化途径占47.4%,全程反硝化途径占16.7%.      

Is The Ca + K + Mg/Al Ratio in the Soil Solution a Predictive Tool for Estimating Forest Damage?

The ratio between (Ca +K +Mg) and Al in nutrientsolution has been suggested as a predictive tool forestimating tree growth disturbance. However, the ratiois unspecific in the sense that it is based on severalelements which are all essential for plant growth;each of these may be growth-limiting. Furthermore,aluminium retards growth at higher concentrations. Itis therefore difficult to give causal and objectivebiological explanations for possible growthdisturbances. The importance of the proportion ofbase-cations to N, at a fixed base-cation/Al ratio, isevaluated with regard to growth of Picea abies.The uptake of elements was found to be selective;nutrients were taken up while most Al remained insolution. Biomass partitioning to the roots increasedafter aluminium addition with low proportions of basecations to nitrogen. We conclude that the low growthrates depend on nutrient limitation in thesetreatments. Low growth rates in the high proportionexperiments may be explained by high internal Alconcentrations. The results strongly suggest thatgrowth rate is not correlated with the ratio in therooting medium and question the validity of usingratios as predictive tools for estimating forestdamage. We suggest that growth limitation of Picea abies in the field may depend on lowproportions of base cations to nitrate. It istherefore important to know the nutritional status ofthe plant material in relation to the growth potentialand environmental limitation to be able to predict andestimate forest damage.     

Effect of ammonium on nitrous oxide emission during denitrification with different electron donors

Nitrous oxide(N2O) emission during denitrification is receiving intensive attention due to its high potential to cause greenhouse effects.In this study,denitrifiers were acclimated in sequencing batch reactors with methanol or acetate as the electron donor and nitrate as the electron acceptor.The effects of ammonium on N2O emission were examined in batch experiments with various electron donors.With the addition of ammonium,N2O emission increased under all the examined conditions compared to experiments without ammonium addition.With different electron donors,the highest ratio of N2O emission to the removed oxidized nitrogen was 0.70% for methanol,5.34% for acetate,and 34.79% for polyhydroxybutyrate.