DB13-T 5920-2024 白洋淀水生態(tài)環(huán)境質(zhì)量綜合評價(jià)技術(shù)規(guī)范

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本文件起草單位：河北省生態(tài)環(huán)境科學(xué)研究院、河北大學(xué)、白洋淀流域生態(tài)環(huán)境監(jiān)測中心、河本文件主要起草人：趙建國、李洪波、董麗、劉存歧、秦長簫、朱永濤、陳新永、劉晶、吳亦1白洋淀水生態(tài)環(huán)境質(zhì)量綜合評價(jià)技術(shù)規(guī)范下列文件中的內(nèi)容通過文中的規(guī)范性引用而構(gòu)成本文件必不可少的條款。其中，注日期的引用HJ710.8生物多樣性觀測技術(shù)導(dǎo)則淡水底棲大型無脊椎HJ710.12生物多樣性觀測技術(shù)導(dǎo)則水生維管植物HJ1098水華遙感與地面監(jiān)測評價(jià)技術(shù)規(guī)范HJ1216水質(zhì)浮游植物的測定0.1HJ1296水生態(tài)監(jiān)測技術(shù)指南湖泊和水地表水環(huán)境質(zhì)量評價(jià)辦法（試行）環(huán)辦〔203.1水生態(tài)環(huán)境質(zhì)量aquaticenvironment以生態(tài)學(xué)理論為基礎(chǔ)，在特定的時(shí)間和空間范圍內(nèi)，水體不同尺度生態(tài)系統(tǒng)的組成要素總的性3.23.3保守系數(shù)conservativecoef保守性是植物物種固守在未受干擾生境中的能力，對每一植物物種的保守性進(jìn)行賦值，稱保守3.43.5底棲大型無脊椎動(dòng)物的相對豐度與其敏感性或耐受性結(jié)合而成的單一指數(shù)或記分值。3.63.723.83.94評價(jià)指標(biāo)體系水生生物評價(jià)從浮游植物、浮游動(dòng)物、水生維管植物、底棲大型無脊椎動(dòng)物、魚類和外來物種浮游植物以浮游植物豐富度指數(shù)進(jìn)行評價(jià)，計(jì)算方法按附錄A.1確定，分級標(biāo)準(zhǔn)及賦分值按表2豐富度指數(shù)（D1）1D1=00浮游動(dòng)物以浮游動(dòng)物豐富度指數(shù)進(jìn)行評價(jià)，計(jì)算方法按附錄A.2確定，分級標(biāo)準(zhǔn)及賦分值按表33豐富度指數(shù)（D2）1D2=00沉水植物質(zhì)量指數(shù)（PQI）PQI≥8.610底棲大型無脊椎動(dòng)物生物指數(shù)（BI）105.1.6魚類土著魚類物種數(shù)(S)104外來物種入侵危害評價(jià)指數(shù)(AIHI)10岸線自然狀況以岸線自然指數(shù)進(jìn)行評價(jià)，計(jì)算方法按附錄A.7確定，分級標(biāo)準(zhǔn)及賦分值按表8確岸線自然指數(shù)（BEI）10水力連通狀況以水力連通指數(shù)進(jìn)行評價(jià)，計(jì)算方法按附錄A.8確定，分級標(biāo)準(zhǔn)及賦分值按表9確水力連通指數(shù)(HCI)10水質(zhì)狀況以年度水質(zhì)類別進(jìn)行評價(jià)，計(jì)算方法按附錄A.9確定，分級標(biāo)準(zhǔn)及賦分值按表10確定。優(yōu)1V類水質(zhì)05營養(yǎng)狀態(tài)以綜合營養(yǎng)狀態(tài)指數(shù)進(jìn)行評價(jià)，計(jì)算方法按附錄A.10確定，分級標(biāo)準(zhǔn)及賦分值按表111105.4水資源評價(jià)全年水位達(dá)標(biāo)月數(shù)量（M）優(yōu)1差05.5物種多樣性評價(jià)物種多樣性評價(jià)以鳥類多樣性綜合指數(shù)進(jìn)行評價(jià)，計(jì)算方法按附錄A.11確定，分級標(biāo)準(zhǔn)及賦分鳥類多樣性綜合指數(shù)（BDI）12＜BDI≤30＜BDI≤1BDI=005.6各評價(jià)指標(biāo)權(quán)重賦值6按照水質(zhì)國控點(diǎn)位布設(shè)，將白洋淀劃分為鴣丁淀區(qū)、南劉莊區(qū)、燒車淀區(qū)、光淀張莊區(qū)、端村6.2調(diào)查區(qū)水生態(tài)環(huán)境質(zhì)量指數(shù)6.3白洋淀水生態(tài)環(huán)境質(zhì)量綜合WEQIz0ng=∑1WEQI?n·································水生態(tài)環(huán)境質(zhì)量綜合指數(shù)(WEQIzong)IV7.1.1.1在白洋淀八個(gè)生態(tài)調(diào)查區(qū)域進(jìn)行7.1.1.3水生維管植物在春夏秋季各監(jiān)測一次，分別計(jì)算各區(qū)域質(zhì)量指數(shù)年平均值進(jìn)行評7.1.1.5魚類在每年春夏秋季各進(jìn)行一次現(xiàn)場調(diào)查，并對當(dāng)?shù)貪O民進(jìn)行社會(huì)調(diào)查，進(jìn)行數(shù)據(jù)補(bǔ)充，7按照白洋淀八個(gè)地表水環(huán)境質(zhì)量國控點(diǎn)位監(jiān)測數(shù)據(jù)，計(jì)算各點(diǎn)位各指標(biāo)年平均值，采用單因子按照鳥類繁殖期、越冬期、遷徙期分別進(jìn)行觀測。每期單獨(dú)核算香農(nóng)維納指數(shù)，取全年最大值7.2監(jiān)測分析方法8A.1浮游植物豐富度指數(shù)（D1）··············································S—總物種數(shù)量。A.3沉水植物質(zhì)量指數(shù)（PQI）A.3.1沉水植物質(zhì)量指數(shù)（PQI）按照公式A.2計(jì)PQI=√n×∑1(ci×Mri)···································Mri—樣區(qū)第i種沉水植物相對密度。Mri=····················································A.4底棲大型無脊椎動(dòng)物生物指數(shù)（BI）底棲大型無脊椎動(dòng)物生物指數(shù)（BI）按照公式BI=∑×ti··································A.5土著魚類物種數(shù)（S）A.6外來物種入侵危害評價(jià)指數(shù)（AIHI）外來物種入侵危害評價(jià)指數(shù)包括外來入侵高等水生植物危害評價(jià)指數(shù)和外來入侵動(dòng)物危害評價(jià)9A.6.2外來入侵高等水生植物危害評價(jià)指數(shù)賦分值（B1）通過實(shí)際調(diào)查發(fā)現(xiàn)“有或無”進(jìn)行賦分，其中A.6.3外來入侵動(dòng)物危害評價(jià)指數(shù)賦分值（B2）A.6.3.1外來入侵動(dòng)物危害評價(jià)指數(shù)按照公式·····································），A.6.4指標(biāo)權(quán)重A.6.5外來物種入侵危害評價(jià)指數(shù)（AIHI）AIHI=∑1Di×Bi··························································A.7岸線自然指數(shù)（BEI）A.7.1一般規(guī)定A.7.2岸線侵蝕比例賦分值（C1）A.7.2.1岸線侵蝕比例（SER）按照SER=································································Lse—受侵蝕岸線長度（mA.7.2.2岸線侵蝕比例分級標(biāo)準(zhǔn)及賦分值見表A.2。岸線侵蝕比例(SER)10A.7.3岸線植被覆蓋度賦分值（C2）A.7.3.1岸線植被覆蓋度（PC）按照公Pc=∑×100··············································PC—岸線植被覆蓋度；Aci—岸段i的植被覆蓋面積（km2Aai—岸段i的岸帶面積（km2Lvci—岸段i的長度（kmL—評價(jià)岸段的總長度（kmA.7.3.2岸線植被覆蓋度分級標(biāo)準(zhǔn)及賦分值見表A.10A.7.5岸線自然指數(shù)（BEI）BEI=∑1Di×ci····················································BEI—岸線自然指數(shù)；水力連通指數(shù)包括阻水堤埝分布密度和淀泊連通指數(shù)A.8.2阻水堤埝分布密度賦分值（E1）·········································ρ—堤埝分布密度（km/km2A.8.2.2阻水堤埝分布密度分級標(biāo)準(zhǔn)及賦分值見表A.5。堤埝分布密度(ρ)10A.8.3淀泊連通指數(shù)賦分值（E2）A.8.3.1淀泊連通指數(shù)（CIS）按照公CIS=············································）；A.8.3.2環(huán)淀河流連通性確定CISn時(shí)，應(yīng)根據(jù)評價(jià)年主流阻隔月數(shù)計(jì)，對于自然月不是所有天數(shù)都處于阻隔狀態(tài)的情況，可將阻隔天數(shù)折算為以月為單位分別確定順暢狀況，取其中的最差狀況采用線性差值方法確定每條環(huán)湖河流連通性賦分。每條環(huán)淀012400A.8.3.3淀泊連通指數(shù)分級標(biāo)準(zhǔn)及賦分值見表A.7。10A.8.5水力連通指數(shù)（HCI）HCI=∑1Di×Ei································A.9年度水質(zhì)類別按照《地表水環(huán)境質(zhì)量評價(jià)辦法（試行）》，對GB3838表1中A.10A.11鳥類多樣性綜合指數(shù)（BDI）A.11.1一般規(guī)定鳥類多樣性綜合指數(shù)包括香農(nóng)維納多樣性指數(shù)、累計(jì)鳥類總物種數(shù)環(huán)比值和相對重要值環(huán)比值A(chǔ).11.2香農(nóng)維納多樣性指數(shù)（H’）H′=?∑EQ\*jc3\*hps15\o\al(\s\up4(s),i)=1pilnpi·························································(A.13)S—鳥類物種數(shù)；Pi—第i種鳥類個(gè)體數(shù)占群落內(nèi)總個(gè)體數(shù)的比例，按照公式A.14計(jì)算?！ぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁi—第i種鳥類個(gè)體數(shù)；N—全部鳥類總個(gè)體數(shù)。A.11.3累計(jì)鳥類總物種數(shù)環(huán)比值（A）累計(jì)鳥類總物種數(shù)環(huán)比值（A）按照公式····························A.11.4相對重要值環(huán)比值（D）·········································D—相對重要值環(huán)比值；In—評價(jià)年相對重要值，按照公式A.17計(jì)算。In-1—評價(jià)年前一年相對重要值，按照公式A.18計(jì)算?！ぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁぁI—評價(jià)年國家一級保護(hù)鳥類物種數(shù)；In?1=···············································S’I—評價(jià)年前一年國家一級保護(hù)鳥類物種數(shù)；A.11.5鳥類多樣性綜合指數(shù)（BDI）BDI=H′×A×D·····BDI—鳥類多樣性綜合指數(shù)；D—相對重要值環(huán)比值?？茖俜N1CeratophyllumL.CeratophyllumdemersumL-12Ceratophyllumdemersumvar.quadrispinumMakino-33BatrachiumS.F.GrayBatrachiumbungei(Stedel)L.Liou-84Batrachiumtrichophyllum(Chaix.)F.Schultz.85PotamogetonL.PotamogetoncrispusL. 26PotamogetonlucensL. 57PotamogetonmaackianusA.Benn. 58PotamogetonmalaianusMiq.49PotamogetonpectinatusL.2PotamogetonpusillusL.-6ZannichelliaL.ZannichelliapalustrisL.7NajadaceaeNajasL.NajasmarinaL.3NajasminorAll. 3HydrillaRich.Hydrillaverticillata(Linn.f.)Royle-2VallisneriaVallisneriaasiaticaMiki.-3MyriophyllumL.MyriophyllumspicatumL.3MyriophyllumverticillatumL.-5UtriculariaL.UtriculariaVulgarisL.-4UtriculariaaureaLour. 6Characharasp 6門綱目屬種1AnnelidaaBranchiura 2AnnelidaaLlimnodrilus--3AnnelidaArhynchobde----4Annelida 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