Relationship between the Water Body Chlorophyll-a and Water Quality Factors of Wetlands Baiguishan R Relationship between the Water Body Chlorophyll-a and Water Quality Factors of Wetlands Baiguishan R

Relationship between the Water Body Chlorophyll-a and Water Quality Factors of Wetlands Baiguishan R

  • 期刊名字:农业科学与技术(英文版)
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  • 论文作者:SHE Oiu-sheng,TIAN Xun,WANG Gu
  • 作者单位:Department of Biological Engineering
  • 更新时间:2020-07-08
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论文简介

Agricutural Science & Technology, 2011, 12(4): 581 -583.591Copyright 02011, Information Institute of HAAS. Al rights reseved.Resources and EnvironmentRelationship between the Water Body Chlorophyll-aand Water Quality Factors of Wetlands BaiguishanReservoirSHE Qiu-sheng, TIAN Xun, WANG Guo-zhen, JI Xlao-cun, L Jlu-xuan, ZHAO Zhen "Department of Biological Engineering, Henan University of Uban Construction, Pingdingshan 467036Abstract [Objective] The aim was to explore the relationship between water body Chloroplhl-a and water quality factors of wetiands Baiguis-han reservoir. [Method ] Chlorophyl-a and water quality factors of water quality of Wellands BaiGuishan Reservoir was studied, the analysis ofthe relationship on water quality of Wetlands Baiguishan Reservoir was made by use of trophic status indices and SPSS17.0 statistical analysis.[ Result] Total phosphorus was an important factor of influence Chloropyl-a in reservoir, water body had slight eutrophication phenomenon inreservoir of July to October in 2010. [ Conchusioo ] Comprehensive management should be strengthened so as to improve the water quality ofshan WetlandBaiguishan VKey words Wetlands Baiguishan Resrvir;hoplyl-a; Water quality factors; RelationshipThe wetlands Baiguishan ( the Reservoir which was buit selected for fve sampling points: east, wsst, north andatifcially in 1965) is located in the mainstream of Huaihe Riv-south, and middle from Baiuishan wetland area (Fig. 1).er, the southwest area of Pingdingshan City, which is a floodThe sampling time and frequency: May 2010 to Octobercontrol, giving agricultural irigation, industrial and urban wa-2010, once a month.ter supply reservoir. Baiguishan wetland reservoir is an impor-tant part of the wetland resources in Henan Province. It pro-vides the drinking water to the local people, and plays an im-” Northportant role in maintaining ecological balance system and theSouthCenterprotection of biological diversity. In adition, it is the regulatorBaiguishan Reservoirof south-to-north water diversion project. Therefore, the stud-Westasties on dynamic monitoring of Baiuishan wetland reservoir cannot only provide the scientific basis for water qualiy protectionand ecological environment protection policies, but also enrichFlg.1 Sampling distribution of Baiguishan wetiand areathe ecological research database of midline of the south-to-Selection of monitorng projectnorth water diversion project.According to the national lake eutrophication surveyPhytoplankton plays an important role in the process ofstandard', and with reference to the surface water environ-material circulation, energy conversion in lake ecosystems,ment quality standards ( GB3838-2002) and other standard,and the Chloropyll-a (Chla) content in water is an evaluationaccording to the specific circumstances of Baiguishan wetlandof phytoplankton biomass, which is also the important index of area, the ammonia nitrogen (NHy-_N) . total phosphorus (TP)productivity and the number of algae, an important parameterand dissolved oxygen (OD), potassium permanganate indexof eutrophication. Therefore, we monitor the environmental(CODm) and chlorophyl a were detected and analyzed.factors index of wettand resevoir, survey the eutrophicationNutrition evaluationssituation and using mutiple stepwise regression analysis, findBased on the content of Chiorophyl-a, potassium pemanout the environmental factors which is significant correlationganate index, phosphorus index, according to the nutrition indexwith Chlorophyll-a and establish forecasting model to providecalculation formula to calculate TU (Chla), TU(COD) andthe scientific basis for the corresponding countermeasures to TU( TP), refer to the relative weight clculation fommula andprevent and control it.comprehensive nutritin exponential formulae, calculate compre-hensive nutritin index fomula; TU (Z) =TU (E) =Z W, xMaterials and MethodsTU(), the nutrtive ratio type of reservoir Baiguishan wet-Sampling place and sampling timeland was evaluated2lOn the basis of Water quality-guidance on sampling tech-Statistical analysesniques( GB1299891), according to the geographical charac-May to October,teristics and combined with the reservoir situation, surround-2010,中国煤化工n satistics method,ing humanity of Baiguishan wetland area, five directions werefour enTIYH.CNMHGhe ammonia nitrogenand phlate index and dis-Received: March 12, 2011Accepted: Apil5, 2011solved oxygen and algae Chlorophl-a) for stepwise regres-Supported by Natural Science Study Fund from the Department ofsion analysis, and the stepwise regression equation was e昭Education of Henan ( 2010B610002).tablished, and it was found that the significant environmental# Corresponding author. E-mail; zhaozhen@hnqj. edu. cnfactor that infuenced algae Chorplyl-a. Four environment582Agricultural Science & Technology Vol. 12, No.4, 2011factors were used as independent variables and algae Chloro-phyl-a was used as dependent variable to cary out statisticalLanalysis with SPSS 17. 0 and conclude the multiple stepwiseregression equation and complex correlation coefficient.. 。CanterResults and AnalysisTime-space distribution of physical and chemical indexesAccording to Surface Water Environment Quality Stand-aards( GB383888-2002 ) in China 91 , the test reults of monito-ring ammonia nitrogen, total phosphorus, potassium perman-MalyJuneJuly Agst Septa ber Octoberganate index and dissolved oxygen were shown in Fig.2 -5.Fig.4 Time-space distribution of Total PThe results showed that:①in monitored time, the ammonianitrogen and potassium permanganate indexes were growingup gradually, reaching the highest in August and declining af-ter;②in May to October of 2010, total phosphorus contentwas increasing, and reaching to its top in July;③the content- Canterof dissolved oxygen were declining, lowest in August and ris-ing after;④the dissolved oxygen saturation locus might occurdue to lower water temperature, less oxygen consumed bymicroorganisms in water and oxygen in water produced byphotosynthetic bacteria; ⑤from regional perspective, the mo~nitoring indicators in the west and south of the BaiguishanJueJuly lgst Septa her lctoberWetlands were higher.Fig.5 Time-space ditribution of dissolved oxygenTime-space distribution of Chlorophyl-a contentThe content of chloroplylla was detected, and the testresults in Fig. 6 showed that: ①with the temperature grow-+ Southing, Chioropl-a content overall showed a rising trend, andreaching to its top in August;②it declines greatly in Septem-- xCanterber, which might be due to the rainfall and upstream food dis-charge;③the average content of Chlorophyl-a in the sixmonths showed the trend of south reservoir >midle reservoir >west reservoir > north reservoir > east reservoir, Chlorophyll-acontent was higher in southwest than which in northeast ofBaiguishan wetland reservoir.July Lgst Sepcamber QctoberFig.6 Time-space distribution of Chlorophyl-a8number of alga is. In practical work, it's always regarded asthe main factor of water eutrophication. However, due to the6一Catercomplexity of the water ecological system and the eutrophica-tion process, multiple factor evaluation methods are adoptedto evaluate the water eutrophication. Integrated nutrition stateindex is based on mtti-factor evaluation index of Chorpyl-a.An average TLI value of the Baiguishan Wetlands in May -Jurehuly lgst Soptaber QctoberOctober of 2010 was shown in Fig. 7. Besides, Table 1showed the grading standards of lake nutrition state. It couldFig.2 Time-space distribution of permanganate indexbe concluded from Fig.7 that:①the TLIvalue of the Baiguis-han Wetlands in comprehensive nutritin state in May to June7[and in Moderate nutrition state, July to October in slight eu-trophication status; 2 in monitoring time, integrated TLI valuewas increased gradully, which was the highest in August and. -Oater圭declining after;③from its influencing situation, total phos-phorus content was the major factor of integrated nutrtionstate index of water.Table 1 Grading of Lakes nutrition stateTUva中国煤化工ilybgst Spcaiber CcokcTU<3fYHCNMHGFig.3 Time-space distribution of Ammonia nitrogen content30≤7Evaluation of comprehensive nutrition state of Baiguis-50< TU≤60Mild europhication60< TU≤70Medium eutrophicationhan wetland areaChlorophyl-a is overall target rflecting how much theTU>70Severe eutrophicationSHE Qiu-sheng et al. Relationship between the Water Body Chloroplyl-a and Water Qulity Factors of Wetands Baiguishan Reservoir583Linear correlation matrix between Chorophyll-a and20 [Physical-chemical factors of Baiguishan wetland area00工L (CTD)The linear relationship analysis of five parameters: Chlo.LIOrophylIl-a, ammonia nitrogen and phosphorus, potassium per-30manganate index and dissolved oxygen was carried out, and50the result was shown in Table 2. It was found that Chloroplyll-a2and ammonia nitrogen, phosphorus and potassium permanga-nate index showed positive correlation, and the correlation be-20tween total P and Chloropll-a was significant, so the totalphosphorus was more likely the restrictive factor to algalJuneJulylupust Septatber Octobergrowth of Baiguishan wetland area.Fig.7 Comprehensive nutition state index of Baiguishan wet-land areaTable2 Linear crrelation cofficient A of physical and chemical factors and chlorophy a of BaiguishanIndexChlorophy/l-aAmmonia nitrogenTotal PPemanganate indexDissolved oxygenChlorophyll A0.453*10.545"0.291Permanganate index0.377*0.848**0.3590.444"-0.493*。means signiticanty related (P<0.05), * * means extremely signiticant correlation(P<0.01).Stepwise regression analysis of physical-chemical factorsphosphorus and potassium permanganate index were shownand algae Chlorophyll-a of Baiguishan wetland areain Fig. 9: Choroplyl-a had a significant difterence betweenFour factors of five sampling places were used to carryammonia nitrogen, phosphorus and potassium permanga-out stepwise regression analysis of physical-chemical factorsnate index, and chlorophyll an increased significantly whenand algae Chlorophyll-a of Baiguishan wetland area, and thetotal phosphorus concentration increased.screening independent variable was selected at the significant+ Relativity of Mmonislevel critical value 95% and establish comprehensive regres-. nitroeg ind chorpyllsion equation:gesphonus andehoroblChla =0.72 x(NH-N) +3.34 *(TP) -0.35*(CODm) +10index and chlorophyil-a1.348y-0235 2x+ 14220The regression equation of the three variable factors was, R-0.1417y-0313 Tx+L 0101analyzed successively: water quality factor, establish ammo-nia nitrogen, phosphorus and potassum permanganate index. B-t2045●of Baiguishan wetland reservoir. It was found that the mutiplecorrelation coeffcient was 0. 636, comprehensive F value wasy-0078 lbx+0.396 s5. 888, while P value was 0.003.“”-0.2972。It could be concluded from Fig.8 that the average Chloro-phll-a concentration of return simulaton value curves was rel10立14ative coincident with the measured in monitoring time, theUhit i/Ltemperature was high in August and October, and there was aFlg. 9 Water Chorophll-a content and ammonia nitrogen,low ebb in September, which mainly related to flooo dischargephosphorus and potassium pemanganate indexof ZhaoPingTai reservoir and too much rantall+ Masured ValueConclusion+ Predictive ValueThe analysis of the chlorophyll a and water quality fac-tors of Baiguishan wetland area from May to October of 2010showed that:①the south side had a higher Chorophyll-alevel than other areas, the results were geared to the high目3content element such as the nitrogen and phosphorus con-sistent and in south side;②Chloropyl-a and ammonia ni-trogen, phosphorus and potassium permanganate index hadpositive correlation, and the total phosphorus was signifi-August Septanber Octobercant;③Based on the content of Chlorophl-a, potassiumFig.8 Compare the average Chloropll-a concentration ofpermar中国煤化工,according to theretum simulation value curves relative with the meas-nutritio_Iculate TU, the TLured in monitoring timevalue CYC N M H G mild eutrophicationRelations between water chlorophyll a and water qualitystatus.factor of Baiguishan wetland reservoirTo improve the water quality of Baiguishan wetland, weWater Choroplyll-a content and ammonia nitrogen,(下转第591页)ZHENG Kai et al. Risk Assessment and Zoning of Agicultural Drought Disaster in Helongiang Province591astrous condition of drought in China(中国早灾的地理分布特征与灾出版社), 2007: 236 - 2390.情分析)[J]. Joumal of Arid Land FResources & Environment(千旱[7] ZHANG W(张丽娟), U WL(李文亮). ZHANG DY(张冬有). Mete-区资源与环境), 1999, 5(4): 1-7.orological disaster risk assessment method based on information[2] U KR(李克让), YIN SM(尹思明), SHA WY(沙万英). Charactersdiftuon theory(基1信息扩散理论的气象灾害风险评估方法)[J].of time - space of recent drought in China(中国现代干旱灾害的时cienta Geographica Sinica(地理科学)。2009 29(2): 251 -252.空特征)[J]. Geographical Research(地理研究),1996, 15(3):6 [8] GUW, HAAKAWA SJ, suzuk YN. Regional division of agricutur-al meteorological disasters using fuzzy cluster analysis[J]. J Agroc[3] WANG WK(王文楷). ZHANG ZY(张霞字). Discussion on the reMeteorol, 1993, 48; 339 -347.gional distribution law of drought and flood in Henan and hazard reduction measures(河南省气涝灾害的地域分异规律和威火对策研[9] ZHANG L, WANG x, U FS, et al. Efects of enhanced utraviolet究)[J]. Joumal of Catastrophology(灾害学), 196, 11(4): 74-radiation-B on maize in arid regions of middle-high elevation[J].78.Agricultural Science & Technology, 2009, 10(1):11 -14, 73.,[4] YUAN L(袁林). on the regular pattemns of the historical droughts [10] WANG MN(王美娜), YANG ZY(杨志勇)。ZHENG MM(郑苗苗).in Shaanxi Province(陕西历史早火发生规律研究)[J]. Joumal ofDiscussion on etfects of白Nino event on climate in Shenyang(试Catastophology(灾害学), 1993, 8(4):40-43.论8 nino事件对沈阳气候的影响)[J]. Joumal of Anhui Agricul-[5] U ZY(李祚泳), DENG XM(邓新民). Study on fractal features oftural Sciences(安徽农业科学), 2011, 39(6): 3523 -3526, 3529.time series of dryness/ wetness/disasters in Sichuan Province(四[11] WEI CB, ZHANG P. QINY, et al. Physiological responses of Yox-川旱捞灾时间分布水列的分形特征研究)[J]. Joumal of Catastro-ing Liy leat and bulb to drought stress[J]. Agriculurad Science &phology(灾害学), 1994(3): 88 -91.Technoloo 2010.1133-35.586] ZHANG Ja(张继权),u Y(李字). Quniatve methods and appli[12] ZHAO YH(赵永华),LU G(刘耿). Eoc-enironmental problemnscations of risk assessment and management on main meterolog-in the upper reaches of Min River(岷江上:游地区的生态环境问题研cal disasters(主要气象灾害风险评价与管理的数量化方法及其应用)究)[J]. Joumal of Anhui Agicultural Sciences(安徽农业科学),[M]. Biig: Bejing Normal University Press(北京:北京师范大学2011, 39(6): 3508 -3511.Responsible editor: DUAN Yong-boResponsible proofreader: WU Xiao-yan.(上接第583页)泊富营养化评价方法及分级标准)[J]. Enironmental Monitoring Inshould combine the actual situation, and it is advisable to[3] TANG GM(唐相明)。Reasons of ftshore shallow river dssolved axy-China(中国环境监测), 2002, 18(5):47 -49.take the fllwing measures:①using biological technology,gen supersaturated(近海河殷溶解氧过饱和原因戊析)[J]. Marinemanaging eutrophication water;②afforestation, preventingEnvironmental Science(每洋环境科学), 1994, 13(1):21 -26, 31.soil erosion, reducing the incoming of organic matter in therunoff and farmland of swamp-side, actively promoting no[4] U s, CHEN s, ZHANG JW. Environment ichanges analysis ofphosphorus catharsis things in upstream;③strengtheningEopgianao ane Qungete 1Agriutural Saience&Technology, 2009, 10(6):178-the water quality monitoring, mastering water quality change[5] xu X(徐信), ZH CY(支崇远),.CHENL(体FS) 。Aopieationin time and making reasonable management measures.diatoms in water qulity monitoring and reconstuction of palaeoenir.onment(硅算在水质监侧和古环境重建中的应用)[J]. Joural of Anhui Agicltural Sciences(安徽农业科学), 2011, 39(9): 5216 -5217,References[1] JIN xC金相b1), πU QY(屠清瑛). suvey noms of lake etrophica [6] uU QX(刘清学),HUO SL(霍守亮). ZAN FY(夠逢字), etal. Inves-tion(湖泊席营养化调杏规范)[M]. Bejing: China Enironmental Sc-tigation and evaluation on the etrphicain of lakes in Anhui Prov-ence Press(北京:中国境科学出版社),1995.ince(安徽省湖的席营养化现状调查与评价)[J]. Joumal of Anhui Ag2] WANG MC(王明翠),UU XQ(刘雪岸),ZHANG JH(张建辉).riutural Sciences(安徽农业科学), 2011, 39(8): 4626 -4629.Evaluate method and dassification standard on lake eutrophication(湖Responsible editor: U Ting-tingResponsible profreader: WU Xlao-yan(上接第488页)ALA改变了油菜幼苗体内ABA的含量(摘要)张树杰,李玲,张春雷* ,李光明(中国农业科学院油料作物研究所,农业 部油料作物生物学重点开放实验室,农业部作物生理生态与裁培重点开放实验室.湖北武汉430062)[目的]本文的目的是为了揭示ALA处理对冬油菜( Basscas nopus L )幼苗生长的影响及作用机理。[方法]采用营养液培养的方法研究ALA溶液淡种对中双9号油菜幼苗生长及体内ABA含量的影响。实验设置4个处理,分别用0.25.50和75 mg/L ALA(CK AI、A2和A3)溶液浸种6 h。[结果]除了A3处理使油菜幼苗f重轻微降低之外,ALA浸种使油菜幼苗(根系和地上部)千重.净光合速率.蒸腾速率和气孔导度较对照显著增加。与对照相比,ALA浸种使油菜幼苗体内和木质部伤流液中ABA含量出现不同程度的增加。[结论]提高体内ABA含量叮能是ALA浸种处理促进冬油菜幼苗在冬前低温阶段生长的主要原因。关键词Brassica napus L. ;营养液培养;木质部伤流液;光合作用;植物激素基金项目科技支撑计划项 目(00BADA8B01)和公益性行业专项项目(0000中国煤化工作者简介张树杰 (1972 -).男.陕西延安人,助理研究员,主要从事油莱生理生态与:MYHCNMHG收稿日期20110208修回日期2011403-28

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