黄土高原不同植被带人工刺槐林土壤团聚体稳定性及其化学计量特征

为研究黄土高原不同植被带对土壤团聚体稳定性及团聚体化学计量变化特征的影响,本研究选取黄土高原不同植被带人工刺槐林地土壤为研究对象,分析了不同粒径团聚体含量,团聚体化学计量及稳定性指标.结果表明, 2 mm和0. 25～2 mm粒径团聚体含量,机械团聚体的平均重量直径(E_(MWD))和机械团聚体的几何平均直径(E_(GMD))表现为森林带森林草原带草原带,而0. 053～0. 25 mm粒径团聚体含量和可蚀性因子K呈现相反的变化特点;各粒径团聚体有机碳和全氮含量在3个植被带整体表现为森林带显著高于森林草原带和草原带,而全磷含量在各植被带间无明显变化规律;有机碳和全氮含量在草原带以0. 053 mm和0. 25～2 mm粒径占绝对优势,在森林草原带以0. 053～0. 25 mm和0. 25～2 mm粒径为主,而森林带各粒径间均无显著差异;草原带和森林草原带0. 053 mm粒径全磷含量最高,而森林带全磷含量在各粒径间无显著差异;0. 053 mm和0. 053～0. 25 mm粒径团聚体C∶N值以草原带和森林草原带高于森林带,而0. 25～2 mm和 2 mm粒径在3个植被带间无显著差异;各粒径C∶P和N∶P值以森林带显著高于森林草原带和草原带.综上可见,土壤团聚体稳定性和团聚体化学计量在3个植被带间存在较大差异,团聚体稳定性和团聚体有机碳、全氮含量整体表现为森林带显著高于森林草原带和草原带.     

上海城区二次气溶胶的形成:光化学氧化与液相反应对二次气溶胶形成的影响

二次组分是大气细颗粒物中最重要的组成部分之一.本研究旨在探究上海城区大气气溶胶颗粒物中二次组分的贡献及其形成的主要影响因素.利用高分辨率飞行时间气溶胶质谱仪(HR-TOF-AMS)对上海城区春季及夏季的亚微米颗粒物(PM_1)进行实时的在线表征,发现有机物是PM_1中最主要的组成部分,占比为55%;其次是硫酸盐(24%)与硝酸盐(10%).进一步结合正交矩阵因子解析模型(PMF)对有机组分进行了来源解析.结果表明,一次有机气溶胶(POA)与二次有机气溶胶(SOA)分别占总有机物浓度的34%与66%; POA主要来自机动车源与餐饮源的贡献,且在春季和夏季对有机物的贡献趋于稳定.观测期间共观察到3个二次气溶胶显著生成的过程:其中,春季二次组分的显著增长过程以硫酸盐和老化的有机气溶胶在正午时段上升显著为主要特征,主要受光化学氧化过程的促进;夏季二次组分的显著生成过程主要是液相反应与光化学氧化共同促进的结果,如液相反应过程中,硝酸盐浓度与颗粒相水含量有较好的相关性(R~2=0. 72),而光化学氧化期间SOA浓度与大气氧化性(O_x)有较好的相关性.总体而言,二次组分是上海城市大气气溶胶颗粒物中最重要的组成部分,二次有机与无机组分在PM_1颗粒物中占比分别为35. 5%和43%,光化学氧化与液相反应对二次组分的形成有显著的促进作用.     

绿狐尾藻分解及其氮磷释放特征

湿地植物分解释放的有机物、氮和磷等会影响人工湿地对水体污染物的去除效率和出水水质.本研究采用尼龙分解袋法研究绿狐尾藻在水中的分解过程及氮磷释放特征.连续60 d的室内分解实验结果表明,前期(0～4 d)绿狐尾藻干物质质量损失速率快,占初始质量的30%,中后期(4～60 d)损失速率减慢,占31%.拟合的一级动力学分解速率常数为0. 014 2d-1,降解50%的干物质需48. 8 d.水体p H值变化情况:0～4 d从7. 60迅速下降到5. 63;中期趋于稳定;后期p H值回升到7. 03,与空白对照值接近.绿狐尾藻分解实验系统中溶解氧浓度从6. 30 mg·L~(-1)在1 d内快速下降到0. 61 mg·L~(-1),表明该系统一直处于厌氧状态.水中总氮浓度0～2 h迅速增加达到12. 7 mg·L~(-1),2 h～32 d逐渐降低到5. 80 mg·L~(-1),后期略有增加;总磷浓度初期快速升高到18. 4 mg·L~(-1),中后期趋于稳定.有机氮(占总氮65. 7%～94. 7%)和无机磷(占总磷61%～89%)是主要的氮磷存在形态.绿狐尾藻体内总氮含量随分解时间逐渐增加,从24. 3 mg·g~(-1)上升到60. 5 mg·g~(-1);而总磷含量从6. 09 mg·g~(-1)下降到2. 94 mg·g~(-1)后波动稳定,这可能与附着微生物对氮的吸收和固定等因素有关.本研究证实绿狐尾藻分解过程释放的氮磷营养元素会引起水体二次污染,为此采用合理的植物收割管理措施非常必要.     

高温厌氧膜生物反应器处理餐厨废水的启动

以除油后的实际餐厨废水为原料,在高温（50±1）℃条件下利用浸没式纤维膜生物反应器（AnMBR）进行连续厌氧消化试验,以水力停留时间（HRT）20d启动,HRT 15d运行,直到发生膜污染,试验共进行了50d.研究了反应器启动和运行期间的发酵特性和膜过滤性能.研究表明,反应器30d完成了启动,在HRT 15d条件下,甲烷产量达到578L/kgVS_in,COD和挥发性固体（VS）去除率均达到94%以上,膜出水总挥发性脂肪酸（TVFA）浓度为（103±77） mg/L,其中乙酸浓度为（98±28） mg/L.系统pH 8.26,具有良好的稳定性.膜通量设定为9L/（m²·h）,运行30d后发生了明显的膜污染,伴随着反应器内挥发性悬浮固体（VSS）浓度由8.1g/L逐渐增加到18/L.在处理高浓度餐厨废水时,AnMBR可以短时间启动且在8.5kgCOD/（m³·d）的高负荷条件下稳定运行,反应器中污泥浓度和溶解性微生物产物的增加导致膜过滤性能下降是导致膜污染的主要因素.     

区域大气环境模式RegAEMS中二次气溶胶的改进模拟研究

为了提升二次气溶胶的模拟精度,在区域大气环境模式RegAEMS中加入了硫酸盐气溶胶的两种新生成机制（NO₂+SO₂化学过程和过渡金属催化氧化（TMI））以及二次有机气溶胶（SOA）生成的挥发性有机物基集（VBS）方法.模拟了2020年1月上海市两次中度污染过程,并与观测数据进行对比验证.研究发现,两次污染过程硫氧转化率（SOR）均大于0.4,PM_2.5主要组分为SO₄^2-、NO₃^-、NH₄⁺等水溶性离子,占比为61.25%~63.85%.SOA占比为2.92%~3.0%.加入NO₂+SO₂化学过程和过渡金属催化氧化（TMI）后,硫酸盐模拟精度明显提升（相关系数（R）从0.49~0.63提升至0.58~0.67,相对标准偏差（NMB）从-35.0%~-36.5%提升至-17.3%~-14.2%）.两种化学过程在污染发展阶段平均贡献占比为23.3%~27.9%,这可能是造成污染条件下SO₄^2-浓度迅速增加的主要原因.VBS机制能够较好地模拟出SOA的变化趋势（相关系数为0.53~0.56）,由于硫酸盐和SOA生成机理的改进,RegAEMS在PM_2.5的模拟精度上有所提升（相对标准偏差（NMB）从-13.5%~-6.0%提升至-9.0%~-3.3%）.     

新冠期间河北省典型钢铁企业大气污染影响

基于国家气象局气象预报数据,建立了基于AERMOD的钢铁企业污染预报模型,模拟了新冠疫情管控期（2020年2~3月）及解封后期（2020年4~10月）河北省某钢铁企业对大气污染的影响,并结合空气质量实测数据进行模型验证.结果显示,不利风向条件下,该钢铁厂大气污染物排放对当地3个国控站点SO₂、NO_x和PM₁₀的平均浓度贡献占比,在疫情管控期分别为20.19%~33.81%,17.49%~23.46%和2.02%~2.69%,在解封后期分别为13.43%~21.01%,11.09%~20.92%和1.20%~2.22%.由于疫情管控期受其他人为源干扰较少,该钢铁厂SO₂、NO_x和PM₁₀的预报值和三个国控站点实际监测值的相关系数,在新冠疫情管控期（在单个站点中,最高分别为0.43、0.48和0.29）高于解封后期（最高分别为0.42、0.39和0.07）.     

Marine aquaculture regulates dissimilatory nitrate reduction processes in a typical semi-enclosed bay of southeastern China

Marine aquaculture in semi-enclosed bays can significantly influence nutrient cycling in coastal ecosystems. However, the impact of marine aquaculture on the dynamics of dissimilatory nitrate reduction processes (DNRPs) and the fate of reactive nitrogen remain poorly understood. In this study, the rates of DNRPs and the abundances of related functional genes were investigated in aquaculture and non-aquaculture areas. The results showed that marine aquaculture significantly increased the denitrification (DNF) and dissimilatory nitrate reduction to ammonium (DNRA) rates and decreased the rate of anaerobic ammonium oxidation (ANA), as compared with non-aquaculture sites. DNF was the dominant pathway contributing to the total nitrate reduction, and its contribution to the total nitrate reduction significantly increased from 66.72% at non-aquaculture sites to 78.50% at aquaculture sites. Marine aquaculture can significantly affect the physicochemical characteristics of sediment and the abundances of related functional genes, leading to variations in the nitrate reduction rates. Although nitrate removal rates increased in the marine aquaculture area, ammonification rates and the nitrogen retention index in the aquaculture areas were 2.19 and 1.24 times, respectively, higher than those at non-aquaculture sites. Net reactive nitrogen retention exceeded nitrogen removal in the aquaculture area, and the retained reactive nitrogen could diffuse with the tidal current to the entire bay, thereby aggravating N pollution in the entire study area. These results show that marine aquaculture is the dominant source of nitrogen pollution in semi-enclosed bays. This study can provide insights into nitrogen pollution control in semi-enclosed bays with well-developed marine aquaculture.     

Co-metabolic and biochar-promoted biodegradation of mixed PAHs by highly efficient microbial consortium QY1

Polycyclic aromatic hydrocarbons (PAHs), typical representatives of the persistent organic pollutants (POPs), have become ubiquitous in the environment. In this study, a novel microbial consortium QY1 that performed outstanding PAHs-degrading capacity has been enriched. The degradation characteristics of single and mixed PAHs treated with QY1 were studied, and the effect of biochar on biodegradation of mixed PAHs and the potential of biochar in PAHs-heavy metal combined pollution bioremediation were also investigated. Results showed that, in single substrate system, QY1 degraded 94.5% of 500 mg/L phenanthrene (PHE) and 17.8% of 10 mg/L pyrene (PYR) after 7 days, while in PHE-PYR mixture system, the biodegradation efficiencies of PHE (500 mg/L) and PYR (10 mg/L) reached 94.0% and 96.2%, respectively, since PHE served as co-metabolic substrate to have significantly improved PYR biodegradation. Notably, with the cooperation of biochar, the biodegradations of PHE and PYR were greatly accelerated. Further, biochar could reduce the adverse impact of heavy metals (Cd²⁺, Cu²⁺, Cr₂O₇^2?) on PYR biodegradation remarkably. The sequencing analysis revealed that Methylobacterium, Burkholderia and Stenotrophomonas were the dominant genera of QY1 in almost all treatments, indicating that these genera might play key roles in PAHs biodegradation. Overall, this study provided new insights into the efficient bioremediation of PAHs-contaminated site.     

Degradation of poly(butylene adipate-co-terephthalate) by Stenotrophomonas sp. YCJ1 isolated from farmland soil

In recent years, poly (butylene adipate-co-terephthalate) (PBAT) has been widely used. However, PBAT-degrading bacteria have rarely been reported. PBAT-degrading bacteria were isolated from farmland soil and identified. The effects of growth factors on the degradation of PBAT and the lipase activity of PBAT-degrading bacteria were assessed. The degradation mechanism was analyzed using scanning electron microscopy, attenuated total reflection Fourier transform infrared spectroscopy, proton nuclear magnetic resonance, X-ray diffraction, and liquid chromatography-mass spectrometry. The results showed that Stenotrophomonas sp. YCJ1 had a significant degrading effect on PBAT. Under certain conditions, the strain could secrete 10.53 U/mL of lipase activity and degrade 10.14 wt.% of PBAT films. The strain secreted lipase to catalyze the degradation of the ester bonds in PBAT, resulting in the production of degradation products such as terephthalic acid, 1,4-butanediol, and adipic acid. Furthermore, the degradation products could participate in the metabolism of YCJ1 as carbon sources to facilitate complete degradation of PBAT, indicating that the strain has potential value for the bioremediation of PBAT in the environment.     

A2/O与倒置A2/O工艺低温条件下的氨氮去除能力解析

对相同进水、平行运行的A²/O与倒置A²/O工艺的冬季氨氮（NH₄⁺-N）去除能力进行了全面解析.在运行水温为14℃时,倒置A²/O工艺表现出更低的NH₄⁺-N容积去除负荷［0.13 kg·（m³·d）^-1和0.29 kg·（m³·d）^-1］和氨氧化速率（AOR）［0.07 kg·（kg·d）^-1和0.11 kg·（kg·d）^-1］,而26℃时两个工艺则相差无几.两个平行工艺中的氨氧化菌（AOB）种群定量结果几乎始终相等（倒置A²/O工艺为3.2%±0.24%,A²/O工艺为3.4%±0.31%）.克隆文库分析的结果表明,造成低温时倒置A²/O工艺中具有较低氨氮去除能力的原因是其AOB优势种属为AOR较慢的慢生型（K-生长策略）亚硝化螺菌属（Nitrosospira）,而在A²/O工艺中则为AOR较快的快生型（r-生长策略）亚硝化单胞菌属（Nitrosomonas）;而在26℃环境下两个工艺中的优势种属则均为Nitrosomonas.结合对污染物沿程去除过程的全面分析,发现尽管温度是决定AOB优势种属演替的首要原因,但由于倒置A²/O的工艺结构变化造成其好氧单元具有较高的COD负荷和高NH₄⁺-N浓度等不利于AOB生长的因素,决定了其可以在常规城市污水的条件下出现K-生长策略型的优势AOB种属.因此倒置A²/O针对异养菌（聚磷菌与反硝化菌）的工艺构造变化却通过COD负荷等间接影响到自养型氨氧化菌的种群分布与演替,并最终造成工艺在低温条件下硝化能力的减弱.