白洋淀多环芳烃与有机氯农药季节性污染特征及来源分析

为研究白洋淀表层水体中多环芳烃(polycyclic aromatic hydrocarbons,PAHs)和有机氯农药(organochlorine pesticides,OCPs)的季节性污染特征及来源,分析了白洋淀12个监测断面春、夏两季表层水体中17种PAHs和15种OCPs的浓度.结果表明,白洋淀春季表层水体中PAHs总浓度范围是35.38~88.06 ng·L~(-1),平均值为46.57 ng·L~(-1),夏季表层水体中PAHs总浓度范围是25.64~301.41 ng·L~(-1),平均值为76.23 ng·L~(-1);白洋淀春季表层水体中OCPs总浓度范围是0.69~4.50 ng·L~(-1),平均值为1.77 ng·L~(-1);夏季表层水体中OCPs总浓度范围是0.11~3.20 ng·L~(-1),平均值为0.90 ng·L~(-1).白洋淀春、夏两季表层水体中PAHs季节性污染特征表现为前塘、关城和安新桥等3个断面夏季PAHs总浓度要远高于春季,而其他9个断面则均表现为春季略高于夏季;OCPs季节性污染特征表现为关城断面夏季OCPs总浓度高于春季,而其他11个监测断面均表现为春季高于夏季.从白洋淀春、夏两季表层水体PAHs和OCPs组成特征来看,春季各监测断面PAHs主要以三环芳烃为主,占PAHs总浓度的比例为45.92%~61.36%(平均为52.60%);夏季安新桥、前塘和关城等3个监测断面主要以二环芳烃萘(Naphthalene,Nap)为主,其浓度分别占PAHs总浓度的比例高达84.91%、91.04%和78.10%,其他9个监测断面主要以三环芳烃为主,占PAHs总浓度的比例为37.14%~53.90%(平均为48.94%);白洋淀表层水体中只有HCHs和DDTs有不同程度检出,且呈现出以HCHs为主的污染特征,其中,春季各监测断面表层水体中HCHs均以β-HCH为主,占HCHs总浓度的29.94%~100%,平均比例为59.87%,而夏季大张庄、郭里口等5个监测断面表层水体中HCHs以β-HCH为主,占HCHs总浓度的57.55%~80.23%,平均比例为61.98%,其他断面以α-HCHs和δ-HCH为主.分析白洋淀春、夏两季表层水体中PAHs和OCPs的来源,PAHs同分异构体比值显示其PAHs主要来源于燃烧源,部分监测断面还存在石油源;而OCPs同分异构体比值显示其OCPs主要来源于环境残留和大气的长距离传输.白洋淀表层水体中PAHs和OCPs浓度不超过不同国家和组织制定的相关水质标准,但安新桥和圈头两个监测断面表层水体中α-HCH、p,p'-DDD浓度超过了美国环保署制定的人体健康水质基准,表明α-HCH和p,p'-DDD可能会对白洋淀淀区居民产生潜在有害影响.     

滹沱河冲洪积扇地下水中挥发性有机物的分布特征与健康风险

为研究滹沱河冲洪积扇地下水中VOCs(volatile organic compounds,挥发性有机物)的污染现状,于2014年9月在滹沱河冲洪积扇地区采集44个地下水样品,采用吹扫捕集-气相色谱-质谱法分析了25种VOCs的质量浓度,并对其分布特征和健康风险进行了讨论. 结果表明,研究区44个采样点均有VOCs检出,其中氯仿、二氯甲烷检出率为100%. 检出的VOCs中,ρ(氯仿)平均值最高,范围为15.4~52 195.9 ng/L;其次为ρ(四氯化碳)(nd~17 145.8 ng/L). VOCs的分布与工业布局密切相关,受制药企业排污影响,ρ(氯仿)、ρ(苯乙烯)、ρ(苯)、ρ(甲苯)、ρ(乙苯)、ρ(二甲苯)等均在G2-1采样点最高;而在石家庄石化炼制产业密集区域,地下水中检出的VOCs种类、检出频次及含量均较高. 研究显示,研究区地下水VOCs的非致癌风险指数介于1.8×10-5~4.7×10-2之间,均远小于1;G2-22采样点地下水VOCs的致癌风险指数最高,为1.1×10-5,处于可接受水平,但四氯化碳的污染现状值得关注.      

武汉典型饮用水水源中典型POPs污染特征与健康风险评估

为了揭示武汉典型饮用水水源中典型持久性有机污染物(POPs)的污染特征与风险水平,采用固相萃取-气相色谱-质谱定性定量分析法,对武汉长江及其支流上18个典型集中式饮用水水源地,共26个采样点水体中多环芳烃(PAHs)、有机氯农药(OCPs)和多氯联苯(PCBs)浓度进行了检测,分析了 POPs的污染水平,并开展健康风险评估.结果表明,26个采样点均有PAHs检出,除苯并[k]荧蒽检出率为88.46％外,其他15种单体检出率均为100.00％,多环芳烃累积ρ(∑PAHs)检出范围为57.04～475.79 ng·L-1,平均值为173.86 ng·L-1.PAHs污染程度总体较低,PAHs主要以中低环芳烃为主,来源于以石油源为主的混合源.共有8种OCPs被检出,(∑OCPs)范围为ND-4.57 ng.L-1,平均值为0.78 ng·L-1,OCPs浓度水平相对较低.共有24种PCBs被检出,ρ(∑PCBs)范围为ND-77.49 ng·L-1,平均值为9.88 ng·L-1,PCBs主要以不易降解的高氯联苯为主,部分点位PCBs浓度超过我国地表水环境质量标准限值,HeptaCBs-180物质需要引起持续关注.健康风险评估结果显示,研究区域内PAHs和PCBs的致癌风险指数均处于10-6～10-4,对人体可能产生潜在的致癌风险;OCPs和PCBs的非致癌风险指数均小于1,不会对人体产生非致癌风险.     

长江下游支流水体中多环芳烃的分布及生态风险评估

长江下游地区是我国一个典型的化学工业园区聚集地,化工园区企业生产过程中产生和排放的多环芳烃通过大气沉降、地表径流等方式进入支流水体,并最终汇入长江.本研究选择了典型的支流水体,开展了多环芳烃的分布特征、源解析和生态风险评估研究.结果表明多环芳烃单体以低环为主,总浓度为37.27～285.88 ng·L~(-1),平均值为78.31 ng·L~(-1).PAHs单体浓度范围0～61.35 ng·L~(-1),检出率最低单体为苯并[k]荧蒽和苯并[a]芘,其检出率均为75%.苯并[a]芘是毒性当量因子最大的PAHs,其浓度范围为0～11.08 ng·L~(-1).根据我国《生活饮用水水源水质标准》(CJ 3020-1993)规定,饮用水中苯并[a]芘的限值为10 ng·L~(-1),其中研究区域内无锡市的一个水样(S12)中浓度超出了标准限值,长江下游支流水体的PAHs浓度总体处于低至中等的污染水平.根据比值法和主成分分析的源解析结果,水体中多环芳烃主要受化工排放、汽车尾气的影响,还有部分来自燃煤.生态风险评估结果显示,水体的生态风险处于中等水平,从长期的环境暴露角度出发,应当考虑采取相应地控制措施,防止进一步污染.研究结果可为长江下游支流水环境中多环芳烃风险评估以及化工园区的污染控制提供参考.     

轿车内苯系物的健康风险评价

为分析车内苯系物污染对不同性别驾乘人员的致癌风险和非致癌风险,对65辆轿车内空气中ρ(苯)、ρ(甲苯)、ρ(乙苯)和ρ(二甲苯)进行评价;提出车内苯的基本致癌风险浓度与危险致癌风险浓度概念及其计算公式,并与国内外相关标准中苯系物浓度标准限值进行对比分析. 结果表明:65辆轿车内空气中苯系物H_fz(综合非致癌指数)的最大值为0.44,低于US EPA(美国国家环境保护局)规定的非致癌风险基本值(1),对乘客与司机均不存在非致癌风险;但苯对司机H_za(致癌指数)的平均值为129.3×10-6,致癌风险较高;苯对男性乘客、女性乘客、男性司机与女性司机的C_wx(危险致癌风险浓度)分别为450.0、470.0、67.5和70.4 μg/m3. GB/T 27630—2011《乘用车内空气质量评价指南》中苯浓度标准限值对司机H_za的平均值为1.59×10-4,大于US EPA规定的苯致癌风险危险值(1×10-4),构成致癌危害;苯系物浓度标准限值对司机H_fz的平均值为1.15,构成非致癌危害. 轿车内空气中ρ(苯)、ρ(甲苯)、ρ(乙苯)和ρ(二甲苯)的合理限值分别为0.068、1.000、1.350和1.350 mg/m3.      

农药企业场地土壤中苯系物污染风险及管理对策

苯系物主要包括苯、甲苯、乙苯、二甲苯和苯乙烯等,是一类重要的环境污染物,可以通过呼吸道、消化道和皮肤等进入人体,对人体产生健康危害.采用吹扫捕集-气相色谱/质谱联用对河北省3个代表性农药企业场地内外土壤的苯系物进行分析,研究了土壤中苯系物的污染特征与健康风险.结果表明,A、B、C这3个企业场地土壤中的苯系物,除苯和苯乙烯外,甲苯、乙苯、二甲苯均有检出.苯系物总含量分别在673.50~32363.50 ng·g-1、nd~6 461.80 ng·g-1、461.70~8 740.80ng·g-1之间.检出的甲苯和乙苯含量(4619.50~7234.30 ng·g-1和364.60~7944.60 ng·g-1)超过加拿大工业用地指导值(370 ng·g-1和82 ng·g-1),场地A生产区灰尘中二甲苯含量甚至超过荷兰土壤干预值(17000 ng·g-1).对于场地外,区域Ⅰ(A周边)和区域Ⅱ(B、C周边)土壤苯系物浓度分别在nd~645.81 ng·g-1和nd~309.13 ng·g-1之间,均低于加拿大农业用地指导值.A、B、C场地内土壤中苯系物非致癌风险分别在2.90E-06~1.32E-04、nd~4.30E-05、1.29E-06~5.64E-05之间,远小于1,说明各场地土壤苯系物不存在明显的非致癌风险.场地外区域Ⅰ和Ⅱ苯系物的总非致癌风险分别在nd~2.02E-06和nd~1.10E-06之间,远低于1,同时也低于对应场地内非致癌风险的平均值.苯系物非致癌风险较高的区域主要集中在场地的下风向,此外,村庄和城镇周边土壤苯系物的非致癌风险略高于其他区域.整体来看,各场地内土壤和灰尘已受到不同程度的污染,场地外的农业用地环境质量也有所下降.据此,提出了企业环境管理和职工安全防护的具体对策建议.     

多功能型城市人工湿地水体汞分布特征及其量变分析

以重庆某集接纳生活污水处理厂出水、水质净化、休闲娱乐为一体的城市湿地公园为研究对象,根据水流流向设点采样,分析了湿地公园内污水处理区、湖泊深度净化区中总汞(THg)和甲基汞(MeHg)的分布特征,并探讨了其源汇关系.结果表明,污水处理区出水THg质量浓度范围为1. 98～38. 03 ng·L~(-1)[平均值为(9. 10±5. 84) ng·L~(-1)],出水MeHg质量浓度范围为0. 09～0. 84 ng·L~(-1)[平均值为(0. 34±0. 08) ng·L~(-1)];湖泊深度净化区THg质量浓度范围为0. 37～85. 69 ng·L~(-1)[平均值为(6. 76±2. 29) ng·L~(-1)],MeHg质量浓度范围为0. 04～1. 47 ng·L~(-1)[平均值为(0. 35±0. 17) ng·L~(-1)],人为活动对汞浓度的干扰较为明显.水体总汞、甲基汞垂直分布规律具有一致性,均表现出表层深层.通过物料衡算,表明该湿地系统水体总汞每年降低155. 50 g,水体甲基汞每年降低1. 65 g,对下游水体具有保护作用.     

河北衡水湖湿地汞污染现状及生态风险评价

以河北衡水湖湿地为调查对象,采用均匀设点采样分析,研究了衡水湖湿地大气、表层水和土壤/沉积物中总汞含量及其分布特征;同时采用地积累指数法和潜在生态风险指数法进行衡水湖湿地汞污染的生态风险评价.结果表明:衡水湖湿地大气总汞含量变化范围为1.0~5.0 ng·m~(-3),平均值为(2.9±0.85)ng·m~(-3);表层水总汞含量变化范围为0.010~0.57μg·L~(-1),平均值为(0.081±0.053)μg·L~(-1);土壤/沉积物总汞含量变化范围为0.001 0~0.058 mg·kg~(-1),平均值为(0.027±0.013)mg·kg~(-1).衡水湖湿地汞污染分布特征为,表层水总汞浓度岸边显著高于湖中(P0.05),湖中沉积物总汞浓度显著高于岸边土壤(P0.05);岸边大气总汞浓度与土壤总汞浓度呈正相关关系;高浓度汞富集总伴随剧烈的人为活动.地积累指数法表明衡水湖湿地地区汞污染为清洁程度;潜在生态风险指数法表明衡水湖湿地地区汞污染风险为低生态风险.     

长江南京段水源水中抗生素的赋存特征与风险评估

利用固相萃取-液相色谱-串联质谱技术(SPE-HPLC-MS/MS)分析了长江南京段水源水中抗生素的赋存特征.结果表明,16个采样点累计质量浓度范围为13. 37～780. 5 ng·L~(-1),平均值为92. 95 ng·L~(-1),共检出4种磺胺类、3种氟喹诺酮类、1种四环素类、5种大环内酯类和1种氯霉素类抗生素,平均质量浓度为0. 14～49. 91 ng·L~(-1),其中恩诺沙星(ERX)和克拉霉素(CLR)的检出率为100%,克林霉素(CLI)检出质量浓度最高(739. 44 ng·L~(-1)).与国内部分河流、湖泊相比,长江南京段水体中的抗生素浓度处于较低水平.生态风险评估结果表明,点位S2具有最大的联合风险熵值(0. 31),磺胺甲恶唑(SMX)、强力霉素(DOX)和罗红霉素(ROX)的环境风险熵值具有低等风险水平; 9种抗生素对不同年龄段人群的健康风险指数HQ在2. 22×10-6和4. 86×10-3之间,同时CLI和DOX为主要的潜在健康风险因素.     

成都市大气环境VOCs污染特征及其健康风险评价

于2012年9月,在成都市分别选取代表城市大气环境和路边大气环境的两个采样点对大气中挥发性有机物(VOCs)进行采样,对不同大气环境中VOCs的浓度水平与变化特征、组成和反应活性进行分析,并对其中的芳香烃化合物进行健康风险评价.结果表明,成都市城市大气环境和路边大气环境中TVOCs的平均质量浓度分别为(108.57±52.43)μg·m~(-3)和(132.61±49.31)μg·m~(-3),不同大气环境中各烃类物质浓度均呈现出烷烃芳香烃烯烃炔烃的趋势;城市和路边大气环境中芳香烃和烯烃对臭氧生成潜势(OFP)贡献较大,关键物种均为间/对二甲苯、甲苯、乙烯、邻二甲苯和丙烯;不同大气环境中的苯、甲苯、乙苯和二甲苯(BTEX)对人体的非致癌风险和危害指数均小于1,对暴露人群不存在非致癌风险;致癌物质苯对人体的致癌风险高于安全阈值1.00E-06,对暴露人群可能存在致癌风险.     

Evaluation of phytoextracting cadmium and lead by sunflower, ricinus, alfalfa and mustard in hydroponic culture

Soil contaminated with heavy metals cadmium(Cd)and lead(Pb)is hard to be remediated.Phytoremediation may be a feasible method to remove toxic metals from soil,but there are few suitable plants which can hyperaccumulate metals.In this study,Cd and Pb accumulation by four plants including sunflower(Helianthus annuus L.),mustard(Brassica juncea L.),alfalfa(Medicago sativa L.), ricinus(Ricinus communis L.)in hydroponic cultures was compared.Results showed that these plants could phytocxtract heavy metals, the ability of accumulation differed with species,concentrations and categories of heavy metals.Values of BCF(bioconcentration factor)and TF(translocation factor)indicated that four species had dissimilar abilities of phytoextraction and transportation of heavy metals.Changes on the biomass of plants,pH and Eh at different treatments revealed that these four plants had distinct responses to Cd and Pb in cultures.Measurements should be taken to improve the phytoremediation of sites contaminated with heavy metals,such as pH and Eh regulations,and so forth.     

Oxidation of As(Ⅲ) by potassium permanganate

The oxidation of As(Ⅲ) with potassium permanganate was studied under conditions including pH, initial As(Ⅲ) concentration and dosage of Mn(Ⅶ). The results have shown that potassium permanganate was an effective agent for oxidizing of As(Ⅲ) in a wide pH range. The pH value of tested water was not a significant factor affecting the oxidation of As(Ⅲ) by Mn(Ⅶ). Although theoretical redox analyses suggest that Mn(Ⅶ) should have better performance in oxidization of As(Ⅲ) within lower pH ranges, the experimental results show that the oxidation efficiencies of As(Ⅲ) under basic and acidic conditions were similar, which may be due to the adsorption of As(Ⅲ) on the Mn(OH)2 and MnO2 resulting from the oxidation of As(Ⅲ).     

Distribution and ecological effect of mercury in Laogang landfill, Shanghai, China

Laogang landfill near Shanghai is the largest landfill in China, and receives about 10000 t of daily garbage per day, Samples of topsoil and plants were analyzed to evaluate mercury pollution from the landfill. For topsoil samples, there were significant correlations among total mercury （HgT）, combinative mercury （Hgc） and gaseous mercury （HgG）, and content of total organic carbon （TOC）, but, no significantly relationship was found between Hg content and filling time. Hg content changes in vertical profiles with time showed that the average Hgv of profiles 1992, 1996, and 2000 was similar, but their average HgG was quite different. HgT was significantly correlated with Hgc in profile 1992 and 2000, and Hgv was significantly correlated with Hg6 in profile 1996. HgG/Hgv ratio in profile samples decreased in the order of （HgG,/HgT）1992〉（HgG/HgT）1996〉〉（HgG/HgT）2000. A simple outline of Hg release in landfill could be drawn： with increasing of filling time, degradation undergoes different biodegradation, accordingly, gaseous mercury goes through small, more, and small proportion to total mercury. Distribution of Hg in plants was inhomogeneous, following the order of leaf〉root〉stem. The highest value of leaf may be associated with higher atmospheric Hg from landfill. Ligneous plants （e.g. Phyllostachys glanca, Prunus salicina and Ligustrum lucidum） are capable of enriching more Hg than herbaceous plants.     

EDTA-enhanced phytoremediation of lead contaminated soil by Bidens maximowicziana

Phytoremediation is a potential cleanup technology for the removal of heavy metals from contaminated soils.Bidens maximowicziana is a new Pb hyperaccumulator,which not only has remarkable tolerance to Pb but also extraordinary accumulation capacity for Pb.The maximum Pb concentration was 1509.3 mg/kg in roots and 2164.7 mg/kg in overground tissues.The Pb distribution order in the B. maximowicziana was:leaf>stem>root.The effect of amendments on phytoremediation was also studied.The mobility of soil Pb and the Pb concentrations in plants were both increased by EDTA application.Compared with CK(control check),EDTA application promoted translocation of Pb to overground parts of the plant.The Pb concentrations in overground parts of plants was increased from 24.23-680.56 mg/kg to 29.07-1905.57 mg/kg.This research demonstrated that B.maximowicziana appeared to be suitable for phytoremediation of Pb contaminated soil,especially,combination with EDTA.     

Decomposition of alachlor by ozonation and its mechanism

Decomposition and corresponding mechanism of alachlor, an endocrine disruptor in water by ozonation were investigated. Results showed that alachlor could not be completely mineralized by ozone alone. Many intermediates and final products were formed during the process, including aromatic compounds, aliphatic carboxylic acids, and inorganic ions. In evoluting these products, some of them with weak polarity were qualitatively identified by GC-MS. The information of inorganic ions suggested that the dechlorination was the first and the fastest step in the ozonation of alachlor.     

Enzymatic oxidation of aqueous pentachlorophenol

The influence of the nonionic surfactant Tween 80 on pentachlorophenol （PCP） oxidation catalyzed by horseradish peroxidase was studied. The surfactant was tested at concentrations below and above its critical micelle concentration （CMC）. Enhancement of PCP removal was observed at sub-CMCs. The presence of Tween 80 in the reaction mixture reduced enzyme inactivation which occurred through a combination of free radical attack and sorption by precipitated products. A simple first-order model was able to simulate time profiles for enzyme inactivation in the presence or absence of Tween 80. At supra-CMCs, the surfactant caused noticeable reductions in PCP removal, presumably through micelle partitioning of PCP which precluded the hydrophobic PCP molecule from interacting with the enzyme.     

Chlorobenzenes in waterweeds from the Xijiang River （Guangdong section） of the Pearl River

The Xijiang River is the major source of water for about 4.5 millions of urban population and 28.7 millions of rural population. The water quality is very important for the health of the rural population. The concentration and distribution of chlorobenzenes (CBs) in both water and waterweeds collected from 4 stations in the Xijiang River (Gangdong section) of the Pearl River in April and November were determined. The result showed that nearly every congener of CBs was detected. The total contents of CBs (∑CBs) in the river water ranged from 111.1 to 360.0 ng/L in April and from 151.9 to 481.7 ng/L in November, respectively. The pollution level of CBs in the water in April was higher than that in November. The contents of ∑ CBs in waterweeds ranged from 13.53×102 μg/g to 38.27×102μg/g dry weight (dw). There was no significant difference between April and November in waterweeds. The distribution of CBs in roots, caulis, and leaves of Vallisneria spiralis L. showed different patterns. The leaves mainly contained low-molecular-weight CBs(DCBs), whereas the roots accumulated more PCBs and HCBs. The average lgBCFlip (bioconcentration factor) of CBs ranged from 0.64 to 3.57 in the waterweeds. The spatial distribution character of CBs in the Xijiang River was: Fengkai County ＜ Yunan County ＜Yun'an County ＜ Gaoyao County according to the ∑CBs, and the pollution deteriorated from the upstream to the downstream of the Xijiang River. Further analysis demonstrated that the discharge of waste containing CBs may be the main source of CBs pollution in the Xijiang River.     

Degradation of 2,4-dichlorophenol with a novel TiO2/Ti-Fe-graphite felt photoelectrocatalytic oxidation process

Degradation of 2,4-dichlorophenol(2,4-DCP)was studied in a novel three-electrode photoelectrocatalytic(PEC)integrative oxidation process,and the factors influencing the degradation rate,such as applied current,flow speed of O_2,pH,adscititious voltage and initial 2,4-DCP concentration were investigated and optimized.H_2O_2 was produced nearby cathode and Fe~(2 )continuously generated from Fe anode in solution when current and O_2 were applied,so,main reactions,H_2O_2-assisted TiO_2 PEC oxidation and E-Fenton reaction,occurred during degradation of 2,4-DCP in this integrative system.The degradation ratio of 2,4-DCP was 93% in this integrative oxidation process,while it was only 31% in E-Fenton process and 46% in H_2O_2-assisted TiO_2 PEC process.So,it revealed that the degradation of 2,4-DCP was improved greatly by photoelectrical cooperation effect.By the investigation of pH,it showed that this integrative process could work well in a wide pH range from pH 3 to pH 9.     

Effect of copper on the degradation of pesticides cypermethrin and cyhalothrin

The influence of coexisting copper (Cu) ion on the degradation of pesticides pyrethroid cypermethrin and cyhalothrin in soil and photodegradation in water system were studied.Serial concentrations of the pesticides with the addition of copper ion were spiked in the soil and incubated for a regular period of time,the analysis of the extracts from the soil was carried out using gas chromatography (GC).The photodegradation of pyrethroids in water system was conducted under UV irradiation.The effect of Cu~(2 ) on the pesticides degradation was measured with half life (t_(0.5)) of degradation.It was found that a negative correlation between the degradation of the pyrethroid pesticides in soil and Cu addition was observed.But Cu~(2 ) could accelerate photodegradation of the pyrethroids in water.The t_(0.5) for cyhalothrin extended from 6.7 to 6.8 d while for cypermethrin extended from 8.1 to 10.9 d with the presence of copper ion in soil.As for photodegradation,t_(0.5) for cyhalothrin reduced from 173.3 to 115.5 rain and for cypermethrin from 115.5 to 99.0 min.The results suggested that copper influenced the degradation of the pesticides in soil by affecting the activity of microorganisms.However, it had catalyst tendency for photodegradation in water system.The difference for the degradation efficiency of pyrethroid isomers in soil was also observed.Copper could obviously accelerate the degradation of some special isomers.     

基于综合水质标识指数和对应分析法的校园河道水质评价

以三峡大学的校园河道求索溪为研究对象,利用综合水质标识指数法确定求索溪水质类别,分析其水质时空变化规律,并利用对应分析法得出求索溪中不同监测点的主要污染因子.研究结果表明:求索溪整体的综合水质标识指数为7.423,整体水质为劣V类(地表水环境质量标准GB 3838-2002)且黑臭.从时间变化来看,求索溪4月份的水质最差,5月份次之,4、5月份所有监测点的水质都劣于V类且黑臭;8月份水质最好,水质为Ⅳ类;从空间分布来看,8个监测点综合水质标识指数均超过6.0,水质为劣V类,其中6号监测点的水质相对最好,监测点3号的水质相对最差;对应分析法得出求索溪的整体水体污染程度受总氮因子的影响最大,其次为总磷.该研究拟为求索溪及类似校园河道的水环境治理研究提供基础依据和参考.