北京市典型土著沉水植物对水体中硝酸盐和正磷酸盐的耐受性研究

以北京市3种典型土著沉水植物轮叶黑藻、狐尾藻和金鱼藻为研究对象,构建模拟水生生态系统,研究3种沉水植物对水体中NO₃^-和PO₄^3-的耐受性并确定其耐受范围.同时,对植物体内过氧化氢酶、丙二醛、叶绿素和蛋白质4种指标进行检测.结果表明,轮叶黑藻对NO₃^-具有较强的耐受性,耐受浓度可达8 mg·L^-1,金鱼藻和狐尾藻次之,耐受浓度为3~5 mg·L^-1;狐尾藻对PO₄^3-的耐受性最差,耐受浓度约为0.2 mg·L^-1,轮叶黑藻和金鱼藻的耐受性相当,当PO₄^3-浓度达到0.4 mg·L^-1时开始出现显著胁迫.因此,在本研究的实验条件下,当水体NO₃^-浓度<5 mg·L^-1、PO₄^3-浓度<0.2 mg·L^-1时,建议3种沉水植物同时种植;当NO₃^-浓度>5 mg·L^-1时,建议种植轮叶黑藻;当PO₄^3-浓度为0.2~0.4 mg·L^-1时,建议种植轮叶黑藻和金鱼藻.研究结果可为北京市再生水补给河湖水库的水生态修复及其沉水植物群落的构建提供一定的理论指导.     

都江堰灵岩山3种人工林优势物种叶片的有机组分特征

叶片的有机组分特征不仅是植物光合产物分配策略和养分回收的重要参数,而且是衡量凋落叶分解难易程度的重要指标.为探究不同植物群落叶片间有机组分的差异,以华西雨屏区人工林的优势乔、灌、草植物作为对象,收集其成熟叶及凋落叶,研究其水溶性组分(water soluble component,WSC)、有机溶性组分(organic...     

共和盆地沙质荒漠化过程植被群落特征变化

青海共和盆地是我国西部荒漠化比较严重地区之一。荒漠化不仅表现为植被结构和功能的退化,也伴随着土壤性质的退化。作者对共和盆地典型荒漠化区域设置样带进行植被、土壤调查,利用TWINSPAN对研究区植被进行数量分类,在此基础上确定荒漠化发展阶段类型及所包含的植被群落类型,分析了不同荒漠化发展阶段的植被群落组成、盖度、生物量及土壤质地、有机质和全氮含量。结果表明：研究区荒漠化梯度划分为未退化草地、轻度退化草地、轻度沙化草地、中度退化草地、中度沙化草地。随着荒漠化的发展,群落组成从简单趋于复杂再到简单;群落盖度逐渐减小,其中未退化草地样方的平均盖度达到48．40％4±3．25％,而中度沙化草地的平均盖度仅为15．34％±2．78％;轻度干扰下样方群落生物量先增加,随着干扰加剧,生物量逐渐减小,轻度退化草地地上、地下及总生物量均最高,中度沙化草地的均最低;土壤0-20cm,20-40cm层有机质和全氮含量逐渐减小,粒度组成也发生明显变化。沙化对土壤有机质、全氮含量及粒度组成的影响显著。     

三江平原湿地植物物种空间分异规律的探讨

研究了三江平原典型湿地在地形、水分等因素制约下的植物物种空间分异规律,包括垂直分异规律和水平分异规律。首先,按照地形和水分的分异组合特点,把湿地生境分为较干燥生境、季节积水生境和常年积水生境。然后,在各个生境内采用样方法和样线法调查植物物种。调查分为20世纪70年代、80年代和2003年3个时期,范围包括三江平原的典型湿地植物群落。数据分析时采用了生境组合法。即把3个不同的生境组合成一个水分(或地形)梯度带,根据频度和多度指标筛选出主要物种,然后按照其空间位置,列出主要植物物种沿水分梯度带的分布序列。研究发现:三江平原湿地不同生境的植物物种组合和垂直分异差别明显。较干燥生境的植被类型以岛状林群落为代表,乔木、灌木和草本植物层次分明。季节性积水生境的植被类型以小叶章群落为代表,是典型的湿草甸植物群落,垂直结构不明显。常年积水生境以毛果苔草群落为代表,植物群落层次也比较明显。植物物种水平分异规律,基本上可由植物物种空间分布序列图来代表。随着地势降低,水分增多,乔、灌植物,湿草甸植物,水生草本植物在特定的空间依次出现。     

人工马褂木林下草本植物物种多样性与林分郁闭度的关系

通过对崇明岛5年生人工马褂木林下草本植物分布及生长状况的调查,研究了不同郁闭度下草本植物物种多样性与林分郁闭度的关系.结果表明:在马褂木幼龄林中,随着林分郁闭度的增大,林下草本植物种数呈先增加后减少的趋势,郁闭度为0、(0,0.2]、(0.2,0.4]、(0.4,0.6]、(0.6,0.8]、(0.8,1.0]下的草本植物种数分别为16、16、19、15、9和7种;林下草本植物的平均盖度、平均密度与林分郁闭度在α=0.01水平上呈显著负相关(r盖度-郁闭度=-0.964 3,r密度-郁闭度=-0.981 5);林分郁闭度为(0.2,0.4]林下草本植物多样性指数最高,其中辛普森指数为0.754 8,香农-威纳指数为1.327 3,均匀度指数为0.880 6.     

Occurrence and migration of microplastics and plasticizers in different wastewater and sludge treatment units in municipal wastewater treatment plant

● Reduce the quantifying MPs time by using Nile red staining. ● The removal rate of MPs and PAEs in wastewater and sludge were investigated. ● MPs and PAEs were firstly analyzed during thermal hydrolysis treatment. ● The removal of PAEs from wastewater and sludge was mainly biodegradation. Microplastics (MPs) and plasticizers, such as phthalate esters (PAEs), were frequently detected in municipal wastewater treatment plants (MWTP). Previous research mainly studied the removal of MPs and PAEs in wastewater. However, the occurrence of MPs and PAEs in the sludge was generally ignored. To comprehensively investigate the occurrence and the migration behaviors of MPs and PAEs in MWTP, a series of representative parameters including the number, size, color, shape of MPs, and the concentrations of PAEs in wastewater and sludge were systematically investigated. In this study, the concentrations of MPs in the influent and effluent were 15.46±0.37 and 0.30±0.14 particles/L. The MP removal efficiency of 98.1% was achieved and about 73.8% of MPs were accumulated in the sludge in the MWTP. The numbers of MPs in the sludge before and after digestion were 4.40±0.14 and 0.31±0.01 particles/g (dry sludge), respectively. Fourier Transform Infrared Spectroscopy (ATR FT-IR) analysis showed that the main types of MPs were polyethylene terephthalate (PET), polypropylene (PP), polyethylene (PE), and polystyrene (PS). Six PAEs, including phthalate (DMP), diethyl phthalate (DEP), diisobutyl phthalate (DIBP), ortho dibutyl phthalate (DBP), butyl benzyl phthalate (BBP), and bis(2-ethyl) hexyl phthalate (DEHP), were detected in the MWTP. The concentrations of total PAEs (ΣPAEs) in the influent and effluent were 76.66 and 6.28 µg/L, respectively. The concentrations of ΣPAEs in the sludge before and after digestion were 152.64 and 31.70 µg/g, respectively. In the process of thermal hydrolysis, the number and size of MPs decreased accompanied by the increase of the plasticizer concentration.     

天津市纪庄子污水处理厂恶臭气体排放研究

2011年,在天津市纪庄子污水处理厂内采集空气样品,并对其中恶臭气体的浓度、扩散模式、影响范围及污水厂内各主要构筑物间相关系数进行了分析研究。结果表明,污水处理厂格栅处恶臭气体浓度最高,为4.31 ng/mL,其中95.61%为H2S气体,其他构筑物恶臭气体浓度范围为0.09～0.32 ng/mL,恶臭气体浓度较前处理工艺相比有大幅度减少;各主要构筑物排放的恶臭气体符合高斯气体扩散模式,恶臭影响范围为厂界外100 m以内;格栅处恶臭气体的排放对于厂界处恶臭气体浓度的贡献度最大,为42.68%;格栅、初沉池、脱水机房、二沉池之间的相关度在90%以上。     

重金属污染土壤植物修复及进展

土壤污染是当今面临的一个重要环境问题。常规的土壤污染物理化学治理技术 ,如客土换土法、冲洗法、热处理、固化、玻璃化、动电修复法等 ,由于其技术要求高或经济成本高昂 ,对土壤结构的扰动破坏较严重 ,因而 ,大规模推广应用存在较大问题。重金属超累积植物的不断发现 ,使人们认识到有可能利用植物于土壤污染的治理修复。自 2 0世纪 90年代起 ,植物修复成为环境污染治理研究领域的一个前沿性课题。研究表明 ,通过植物的吸收、挥发、根滤、稳定等作用 ,可以净化土壤或水体中金属污染物 ,达到净化环境的目的。近 10年来 ,在超累积植物的找寻培育、植物根际微生物共存体系研究、植物对重金属的耐忍性、超量吸收及其解毒机制以及植物修复的工艺技术方面已有不少研究 ,并取得长足的进展 ,现代分子生物学的发展以及基因工程技术的应用有可能使植物修复技术取得根本性的突破。     

Emission characterization of unintentionally produced persistent organic pollutants from iron ore sintering process in China

Emission of unintentionally produced persistent organic pollutants (Unintentional POPs), including polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), polychorinated biphenyls (PCBs), hexachlorobenzene (HxCBz) and pentachlorobenzene (PeCBz), were investigated in four typical iron ore sintering plants in China. The emission factors and annual mass releases of the Unintentional POPs were calculated. The results indicated that PCDFs contributed more than 60% to the overall toxic equivalent quantity (TEQ) values, while the contribution of the dl-PCBs is relatively low, and only in the range of 8-9%. The dominant congeners of PCDD/Fs and dl-PCBs contributing most to the total TEQ were 1,2,3,7,8-PeCDD, 2,3,4,7,8-PeCDF and PCB-126. With regard to the TEQ contributions, the most abundant homologues were PeCDFs and HxCDD/Fs, followed by PeCDDs and non-ortho dl-PCB, whereas HpCDD/Fs, OCDD/Fs and mono-ortho dl-PCBs almost made no contributions. Due to the massive use of recycled waste in the feeding materials, the average emission factor of PCDD/Fs and dl-PCBs of the four plants was 3.95 μg WHO-TEQ ton⁻¹. Based on the results, the annual release of PCDD/Fs and dl-PCBs in 2007-2009 were estimated to be 2070 g, 2212 g, and 2307 g WHO-TEQ, respectively.     

日本森林大气中过氧化物的浓度及其对森林植物的影响

为了研究森林衰退的原因,于2000,2001和2002年的8月,分别选择出现森林衰退的日本奥日光白根山落叶树森林和未出现森林衰退的长野县大芝高原红松森林设立监测点,对光化学氧化剂臭氧(O3)和过氧化物的浓度进行监测,同时利用人工气候室对森林植物山毛榉和白桦进行了50′10-9O3、100′10-9O3和50′10-9O3+2′10-9~3′10-9过氧化物(过氧化氢(H2O2)及甲基过氧化氢(MHP))的暴露实验.野外监测结果表明,监测期间奥日光和长野的O3平均浓度相同,奥日光的H2O2及MHP平均浓度均高于长野;大气中的H2O2和MHP总是与O3共存,并且其浓度随O3浓度的增加而增加.暴露实验结果表明,暴露于50′10-9O3+2′10-9~3′10-9过氧化物的山毛榉和白桦出现了不同于O3暴露的叶片伤害症状;与100′10-9O3相比,50′10-9O3+2′10-9~3′10-9过氧化物导致植物出现了严重的叶片伤害和显著的光合速率下降.研究结果表明,除O3外,大气中的过氧化物也是导致森林衰退的原因之一.