宋婭妮,呼 和,程云湘,侯扶江,常生華
(1.草地農(nóng)業(yè)生態(tài)系統(tǒng)國(guó)家重點(diǎn)實(shí)驗(yàn)室 農(nóng)業(yè)部草牧業(yè)創(chuàng)新重點(diǎn)實(shí)驗(yàn)室 蘭州大學(xué)草地農(nóng)業(yè)科技學(xué)院,甘肅 蘭州 730020;2.甘肅省農(nóng)業(yè)科學(xué)院土壤肥料與節(jié)水研究所,甘肅 蘭州 730070)
自工業(yè)革命至20世紀(jì),全球平均氣溫上升0.6 ℃,并預(yù)計(jì)到21世紀(jì)末將上升1.4~5.8 ℃[1]。大氣中主要的3種溫室氣體是二氧化碳(CO2)、甲烷(CH4)和氧化亞氮(N2O),它們濃度的年增量分別為1.5 mL·m-3、4 μL·m-3、0.8 μL·m-3[2],其濃度的持續(xù)上升不僅造成全球變暖[3],而且對(duì)陸地生態(tài)系統(tǒng)碳、氮循環(huán)有一定的影響作用[4]。CO2是造成全球變暖最主要的溫室氣體,科學(xué)家預(yù)言,大氣中CO2每增加1倍,全球平均氣溫將上升1.5~4.5 ℃[5]。CH4是僅次于CO2的具有化學(xué)活性的溫室氣體,比CO2具有更強(qiáng)吸收紅外線輻射的能力[6],大氣中70%~90%的CH4來(lái)自地表生物源[7],CH4雖然在大氣中滯留時(shí)間較短,但具有最高的年增長(zhǎng)率[8]。N2O是一種既有溫室效應(yīng)又可以破壞臭氧層的溫室氣體[9],N2O雖然在3種主要溫室氣體中占有最低的百分?jǐn)?shù)和年增長(zhǎng)率,但具有比CO2和CH4高出百倍的增溫勢(shì),同時(shí)在大氣中滯留的時(shí)間更長(zhǎng)[10]。草地是我國(guó)最大的陸地生態(tài)系統(tǒng),約占陸地總面積的43.7%[11],是溫室氣體的主要來(lái)源之一[12],草地生態(tài)系統(tǒng)中溫室氣體通量的變化直接影響大氣中溫室氣體含量,同時(shí)對(duì)地球生物圈碳、氮的化學(xué)循環(huán)具有一定的影響作用[13],其功能的正常發(fā)揮對(duì)全球以及區(qū)域性生態(tài)系統(tǒng)有著及其重要的平衡作用[14]。當(dāng)陸地生態(tài)系統(tǒng)中氣候條件發(fā)生變化時(shí),草地生態(tài)系統(tǒng)的反饋調(diào)節(jié)機(jī)制對(duì)大氣化學(xué)成分的變化有一定的調(diào)節(jié)作用[15]。
放牧是草地生態(tài)系統(tǒng)的主要利用方式之一,同時(shí)也是影響草地群落的重要因素[16-17],對(duì)塑造草地植物群落的組成和結(jié)構(gòu)有十分重要的意義[18]。放牧對(duì)草地生態(tài)系統(tǒng)具有正負(fù)兩方面的影響,集中體現(xiàn)在植被和土壤[19]。適度的放牧可以有效地促進(jìn)草地生產(chǎn)力的提高和生物多樣性的維持[20],但是過(guò)牧?xí)斐刹莸卮竺娣e退化、草地初級(jí)生產(chǎn)力和土壤理化性質(zhì)逐漸惡化[21-22]。就草地植物生產(chǎn)力而言,國(guó)內(nèi)外研究均表明,放牧對(duì)其影響主要與土壤因子的資源供給密切相關(guān)[23],在資源供給充足的情況下,放牧的作用明顯;相反,放牧的作用受到一定程度的削弱[24]。就草地土壤理化性質(zhì)而言,放牧通過(guò)家畜采食、踐踏影響土壤的物理結(jié)構(gòu)(如緊實(shí)度、滲透率)[25],同時(shí)采食活動(dòng)及畜體對(duì)營(yíng)養(yǎng)物質(zhì)的轉(zhuǎn)化和排泄物歸還等影響,導(dǎo)致土壤化學(xué)成分的變化[26],而草地土壤的物理變化和化學(xué)變化之間也相互作用、相互影響[27]。放牧、施氮、土壤水分和溫度的變化是導(dǎo)致草地生態(tài)系統(tǒng)溫室氣體通量變化的幾種常見(jiàn)因素,其中放牧既是草地生態(tài)系統(tǒng)的主要利用方式,又是影響該生態(tài)系統(tǒng)的主要因素[28-29],放牧對(duì)溫室氣體的調(diào)控有兩種作用:1)放牧使草地生態(tài)系統(tǒng)的碳庫(kù)發(fā)生變化,這種變化作用對(duì)全球碳循環(huán)有著修復(fù)作用,并且對(duì)全球溫室氣體的排放有直接的影響作用[30];2)放牧通過(guò)改變系統(tǒng)土壤的理化性質(zhì)、微生物和有機(jī)物質(zhì)含量等作用,間接影響草地生態(tài)系統(tǒng)-大氣溫室氣體通量的交換[31],這種交換通量的季節(jié)變化主要受年度氣候變化控制[32]。放牧對(duì)草地溫室氣體排放的影響因素很多,如放牧模式、放牧強(qiáng)度和放牧動(dòng)物等。放牧行為明顯減少了草地植物的地上和地下生物量[33],進(jìn)而通過(guò)影響植物的光合作用,影響CO2的排放[34];放牧強(qiáng)度的影響主要表現(xiàn)為,隨著放牧強(qiáng)度的增加,草地植物的地上和地下有機(jī)碳、土壤微生物生物量碳的含量逐漸減少,造成了整個(gè)生態(tài)系統(tǒng)碳庫(kù)的流失[35];放牧動(dòng)物在采食過(guò)程中對(duì)土壤的踐踏,使土壤形成有利于甲烷菌活躍活動(dòng)的厭氧區(qū)[36],雖然放牧動(dòng)物的糞尿斑對(duì)土壤碳庫(kù)有一定的補(bǔ)償作用,但同時(shí)也是溫室氣體的一種源和匯[37-38]。目前,國(guó)內(nèi)外就放牧對(duì)溫室氣體的影響主要做了以下研究:通過(guò)比較不同放牧模式、放牧強(qiáng)度和放牧動(dòng)物對(duì)溫室氣體通量的影響,集中以不同區(qū)域和草地類型為基礎(chǔ),從生態(tài)系統(tǒng)中各種不同因子的響應(yīng)特征、氣體交換規(guī)律及碳氮元素平衡和生態(tài)功能特征等方面說(shuō)明溫室氣體的增加或減少;放牧動(dòng)物排泄物的研究從宏觀和微觀兩個(gè)角度出發(fā),宏觀主要通過(guò)植物的光合、呼吸作用和碳、氮元素的循環(huán)轉(zhuǎn)移分析排放通量的增加或減少,微觀主要從土壤微生物角度出發(fā)研究生態(tài)系統(tǒng)中微生物的敏感性、不同微生物菌群的多元回歸及活性變化和不同試驗(yàn)處理下微生物的分布特征等對(duì)溫室氣體通量變化的貢獻(xiàn)。本文從放牧的不同角度出發(fā)綜述草地生態(tài)系統(tǒng)中3種主要溫室氣體的排放情況,主要為草地生態(tài)系統(tǒng)的優(yōu)化利用提供科學(xué)的理論依據(jù),對(duì)全球溫室氣體的減排有一定的指導(dǎo)作用,同時(shí)為準(zhǔn)確評(píng)估草地-大氣之間溫室氣體交換通量做出一定的科學(xué)貢獻(xiàn)。
放牧模式分為自由放牧和劃區(qū)輪牧兩種,放牧模式不能改變溫室氣體的源和匯,同時(shí)對(duì)它們吸收、排放的季節(jié)動(dòng)態(tài)無(wú)顯著的影響,放牧對(duì)溫室氣體的影響主要通過(guò)土壤溫室氣體通量的變化表現(xiàn)。馬秀枝[39]通過(guò)研究開(kāi)墾與放牧對(duì)內(nèi)蒙古草原溫室氣體通量變化時(shí)發(fā)現(xiàn),自由放牧平均增加了27%的CH4吸收通量,但其季節(jié)動(dòng)態(tài)沒(méi)有改變;自由放牧使N2O的平均釋放通量增加了1倍。齊玉春等[40]在研究放牧對(duì)溫帶典型草原含碳溫室氣體CO2、CH4通量特征的影響時(shí)發(fā)現(xiàn),與禁牧草原相比,自由放牧和輪牧兩種放牧制度均沒(méi)有改變土壤-大氣間CO2、CH4氣體通量的源匯,土壤通量的季節(jié)變化形式也沒(méi)有變化;在植物生長(zhǎng)季,放牧促進(jìn)了土壤對(duì)CH4的氧化吸收,同時(shí)在春季凍融期增加了CH4的正排放,放牧增加了土壤CH4通量的年變幅。Wilson[41]通過(guò)研究放牧對(duì)草原溫室氣體通量的變化發(fā)現(xiàn),在凈生態(tài)系統(tǒng)中放牧對(duì)CH4吸收通量的變化有著顯著的作用,同時(shí)放牧可以增強(qiáng)CO2的排放。李玉娥等[42]通過(guò)研究休牧對(duì)高寒矮嵩草(Kobresiahumilis)草甸溫室氣體排放的影響發(fā)現(xiàn),夏季休牧增加了CO2、N2O的排放通量降低了CH4的吸收通量,綜合3種溫室氣體的增溫勢(shì)發(fā)現(xiàn),采取夏季休牧措施可以降低草地對(duì)大氣溫室氣體的貢獻(xiàn)。王躍思等[43]研究放牧對(duì)內(nèi)蒙古草原溫室氣體排放的影響時(shí)發(fā)現(xiàn),自由放牧降低了羊草(Leymuschinensis)草原對(duì)CH4的吸收和對(duì)N2O的排放,但顯著增加了CO2的排放量。隨著放牧強(qiáng)度的增加,草原溫室氣體排放強(qiáng)度呈線性迅速增長(zhǎng),與自由放牧相比,禁牧作用可以有效降低草原溫室氣體的排放。合理的劃區(qū)輪牧管理措施既可以減少整個(gè)草地生態(tài)系統(tǒng)溫室氣體的排放,又可以為整個(gè)生態(tài)系統(tǒng)的減排提供一定的科學(xué)依據(jù),對(duì)整個(gè)生態(tài)系統(tǒng)的可持續(xù)發(fā)展有著十分重要的意義。
通過(guò)對(duì)不同區(qū)域、不同草原類型和不同利用方式下3種溫室氣體通量變化比較(表1)發(fā)現(xiàn),不同區(qū)域、不同草原類型在不同放牧制度下,CO2排放均表現(xiàn)出降低的趨勢(shì),但CH4吸收和N2O排放通量變化趨勢(shì)不一致,自由放牧通??梢栽黾覥H4的吸收、降低N2O的排放??赡艿脑蚴牵煌瑓^(qū)域的自由放牧和輪牧的劃分標(biāo)準(zhǔn)不一致;不同區(qū)域的水熱條件差異明顯,而CH4吸收和N2O排放與土壤含水量和溫度均呈正相關(guān)關(guān)系[49]。
表1 不同區(qū)域、不同利用方式下溫室氣體的變化情況Table 1 Changes in greenhouse gases in different areas and utilization patterns
不同的放牧強(qiáng)度主要通過(guò)影響土壤溫度、水分含量和有機(jī)碳氮含量而影響草地生態(tài)系統(tǒng)溫室氣體的排放,放牧強(qiáng)度主要表現(xiàn)在土壤緊實(shí)度和植物地上地下生物量的變化。周培[50]以內(nèi)蒙古草原為研究對(duì)象,通過(guò)分析不同放牧強(qiáng)度下荒漠草原和草甸草原溫室氣體的排放發(fā)現(xiàn),不同放牧強(qiáng)度均表現(xiàn)為CH4吸收和CO2、N2O排放,在中度放牧下草原的CH4吸收和CO2、N2O排放達(dá)到最大值,輕度和重度放牧CH4吸收、CO2排放降到最小值;研究不同草原類型進(jìn)行不同放牧強(qiáng)度放牧?xí)r發(fā)現(xiàn),在重牧、中牧、輕牧3種放牧強(qiáng)度下,放牧均不能改變CH4、CO2兩種溫室氣吸收、排放的源和匯,由于地域和草原植被類型的水熱條件是N2O排放的主要影響條件,所以其源和匯的確定沒(méi)有代表意義。曹娜[51]以內(nèi)蒙古典型半干旱羊草草原為研究對(duì)象,利用同步直接測(cè)定法分析不同放牧強(qiáng)度下氦環(huán)境的培養(yǎng)氣體發(fā)現(xiàn),不同放牧強(qiáng)度均表現(xiàn)為CH4吸收和CO2、N2O排放,隨著放牧強(qiáng)度的增加,CH4吸收和N2O排放均減少,放牧強(qiáng)度對(duì)CO2的排放影響不明顯。Cardoso等[52]以南美熱帶牧場(chǎng)為研究對(duì)象,研究不同地區(qū)、不同季節(jié)、不同放牧強(qiáng)度下溫室氣體通量的變化,認(rèn)為不同放牧強(qiáng)度下均表現(xiàn)為CH4吸收和CO2、N2O排放,但是在不同的地區(qū)3種溫室氣樣的變化通量有著明顯的差異,水熱條件成為其主要的影響因素。
放牧強(qiáng)度對(duì)溫室氣體的影響主要表現(xiàn)為,輕度放牧可以增加CO2的排放、降低CH4的吸收、對(duì)N2O的排放作用不明顯;中度放牧可以增加CO2和N2O的排放、降低CH4的吸收;重度放牧可以降低CO2的排放和CH4吸收、增加N2O的排放(表2)。綜上所述:隨著放牧強(qiáng)度的增加,CH4的吸收呈現(xiàn)降低的趨勢(shì);N2O的排放呈現(xiàn)出增加的趨勢(shì);CO2的排放在適度范圍內(nèi)表現(xiàn)出增加的趨勢(shì),但在重度放牧?xí)r卻逐漸降低。
表2 不同區(qū)域、不同放牧強(qiáng)度下溫室氣體的變化Table 2 Changes in greenhouse gases under different grazing intensities in different areas
CO2和N2O均為排放,CH4為其吸收?!硎驹黾樱硎窘档?,-表示不明顯。
CO2and N2O are discharged, and CH4is absorbed;↑, increased; ↓, reduced; - , no obvious.
1.3.1動(dòng)物種類 反芻動(dòng)物是草地上常見(jiàn)的放牧動(dòng)物,放牧動(dòng)物主要通過(guò)采食、踐踏影響土壤的物理結(jié)構(gòu)(如緊實(shí)度、滲透率),改變了土壤的氣體交換速率、氧化環(huán)境和微生物的活力,從而影響溫室氣體的排放通量[58]。動(dòng)物生態(tài)系統(tǒng)是非人為CO2溫室氣體排放的主要來(lái)源[59],據(jù)統(tǒng)計(jì),由家畜及其排泄物產(chǎn)生的CH4和N2O分別占人為排放總量的20%和55%[60],而反芻動(dòng)物(牛、羊)對(duì)CH4的貢獻(xiàn)占全球釋放總量的15%~25%[61-62]。以內(nèi)蒙古呼和浩特市為例,CH4與N2O的排放量前5位的家畜分別是奶牛、綿羊、肉牛、山羊、豬,分別占全市溫室氣體排放總量的72.06%、15.45%、4.30%、4.24%、2.78%[63]。目前常采用對(duì)性別比例、出欄周期、不同放牧動(dòng)物比例和放牧動(dòng)物的優(yōu)化管理等現(xiàn)代科學(xué)手段人為減少溫室氣體排放[64]。Chen等[65]以內(nèi)蒙古草原為研究對(duì)象,研究不同載畜量與溫室氣體的排放的關(guān)系,結(jié)果表明:在適牧范圍內(nèi),較高的載畜量對(duì)氮循環(huán)具有正效應(yīng)刺激作用,隨載畜量的增加N2O的排放量減少。丁丹[66]在研究牛羊混合放牧對(duì)內(nèi)蒙古荒漠草原溫室氣體通量的影響時(shí)發(fā)現(xiàn),3種放牧方式(牛單牧、羊單牧、牛羊混合放牧)中牛羊混合放牧釋放的CO2量比牛單牧、羊單牧少,而CH4多。汪詩(shī)平等[67]以4歲和7歲閹牦牛一生CH4排放總量作比較,研究放牧閹牦牛提前出欄CH4排放強(qiáng)度減排時(shí)發(fā)現(xiàn),牦牛提前出欄有較大的CH4減排潛力。張亮等[68]在研究傳統(tǒng)放牧模式下青藏高原高寒牧區(qū)藏系綿羊溫室氣體排放時(shí)發(fā)現(xiàn),在傳統(tǒng)放牧模式下CH4的排放主要由腸道發(fā)酵產(chǎn)生,在此過(guò)程中產(chǎn)生的CH4占溫室氣體排放總量的79%,而糞便排放的CH4僅占1%;在傳統(tǒng)放牧系統(tǒng)下不同生產(chǎn)環(huán)節(jié)的溫室氣體排放中,建群繁殖種群和生產(chǎn)羔羊占65%,35%是由放牧期進(jìn)行交易的羊產(chǎn)生的,其中母羊的貢獻(xiàn)高達(dá)46%。
綜上所述,研究放牧動(dòng)物對(duì)草地生態(tài)系統(tǒng)溫室氣體的影響發(fā)現(xiàn),放牧動(dòng)物對(duì)CH4和N2O有著顯著的作用,主要原因是不同放牧動(dòng)物、不同放牧動(dòng)物管理和不同載畜量主要影響草地土壤的緊實(shí)度,草地土壤緊實(shí)度的變化直接影響土壤孔隙度并提高厭氧型微生物的活性呼吸類型,進(jìn)而影響其對(duì)CH4吸收和N2O排放的通量。
1.3.2動(dòng)物排泄物 放牧動(dòng)物的排泄物,一方面本身的排放量和厭氧降解的過(guò)程直接產(chǎn)生溫室氣體,另一方面通過(guò)間接影響草地植物群落的光合作用和土壤的呼吸作用,從而影響溫室氣體的排放[69]。放牧動(dòng)物的排泄物不僅對(duì)草地退化有一定的影響作用,同時(shí)對(duì)整個(gè)草地生態(tài)系統(tǒng)溫室氣體的排放通量有重要的貢獻(xiàn)作用。放牧動(dòng)物排泄物的氮轉(zhuǎn)化(氮的礦化、硝化與反硝化、氮的氨化)過(guò)程是整個(gè)草地生態(tài)系統(tǒng)氮素循環(huán)的關(guān)鍵,土壤動(dòng)物和微生物在氮的礦化過(guò)程具有顯著的促進(jìn)作用[70]。放牧草地上家畜糞尿有非常高的可溶性氮和有效碳濃度,并以糞斑斑塊的形式散落在放牧區(qū)域,這些斑塊可能是影響產(chǎn)生N2O和CH4吸收的活躍位點(diǎn)[71]。據(jù)統(tǒng)計(jì),全球動(dòng)物糞斑N2O的年排放量為1.0 g[72],約占全球N2O排放總量的7%[73];全球動(dòng)物糞斑CH4的年排放總量為25 Tg,占已知人為因素排放總量的5.5%~8.0%[74]。動(dòng)物糞便在厭氧處理下,分別由兩大類群的微生物起作用,最終轉(zhuǎn)化為CH4、NH3等[75];在好氧處理下,由好氧微生物和兼性微生物起作用,有機(jī)物被轉(zhuǎn)化為CO2、H2O等[76]。放牧動(dòng)物及其糞尿斑對(duì)草地生態(tài)系統(tǒng)溫室氣體的貢獻(xiàn),已成為該系統(tǒng)溫室氣體排放的研究熱點(diǎn)之一[50-76]。
Ma等[77]在研究?jī)?nèi)蒙古典型草原上綿羊糞便對(duì)溫室氣體(CO2、CH4和N2O)通量短期影響時(shí)發(fā)現(xiàn),動(dòng)物糞便補(bǔ)丁在草原溫室氣體中扮有重要角色,雖然高氮和可用碳沉淀在小地區(qū),在秋季草原退化后,糞便的作用在評(píng)估總溫室氣體排放時(shí)可以被忽略;放牧動(dòng)物的排泄物在短時(shí)間內(nèi)迅速轉(zhuǎn)變?yōu)镃H4和N2O的弱源,從而對(duì)整個(gè)生態(tài)系統(tǒng)溫室氣體的排放有一定的影響作用。葛世棟[78]在研究高寒草甸糞斑的溫室氣體排放時(shí)發(fā)現(xiàn),牛糞斑覆蓋后的高寒草甸生態(tài)系統(tǒng)中CO2、CH4和N2O的排放隨著時(shí)間的推移,總體上呈現(xiàn)先增加后降低的單峰趨勢(shì),但3種溫室氣體出現(xiàn)峰值的時(shí)間不同,其中CO2排放的波動(dòng)幅度較大;在整個(gè)研究過(guò)程中3個(gè)月內(nèi)的全球變暖潛勢(shì)相對(duì)于未覆蓋牛糞斑的增加了39.2%。姜圓圓[79]發(fā)現(xiàn),在放牧綿羊排泄物逐漸降解的過(guò)程中,草地生態(tài)系統(tǒng)溫室氣體的排放通量明顯增加,主要原因是增強(qiáng)了草地的源,減弱了草地的匯,充分說(shuō)明放牧家畜排泄物對(duì)內(nèi)蒙古荒漠草原溫室氣體排放具有重要的貢獻(xiàn)。陸日東[80]在探究影響奶牛糞便排放溫室氣體因子時(shí)發(fā)現(xiàn),不同翻蓋、不同堆放方式和不同溫度處理下奶牛糞便溫室氣體的排放具有顯著的差異性,其中溫度是影響其排放通量的主要因子,其結(jié)果表明,隨著溫度的不斷升高,溫室氣體的排放通量逐漸增強(qiáng)。
隨著溫室氣體CO2、CH4、N2O產(chǎn)生機(jī)理的深入研究,放牧對(duì)草地生態(tài)系統(tǒng)溫室氣體排放的影響在國(guó)內(nèi)外已經(jīng)展開(kāi)了廣泛地研究,逐漸由大尺度的宏觀環(huán)境條件的研究向微觀精確微生物領(lǐng)域深入,由單因素到多因素再到各種因素互相作用的研究,研究?jī)?nèi)容不斷深入、研究方法逐漸成熟、研究成果持續(xù)更新。目前,有關(guān)放牧對(duì)草地生態(tài)系統(tǒng)溫室氣體排放通量的研究較多,主要集中在比較不同放牧模式、不同放牧強(qiáng)度和不同放牧動(dòng)物下溫室氣體通量的變化,探討不同放牧作用下影響溫室氣體通量變化的主要植被和土壤理化性質(zhì)因子。由于各種因素的影響,放牧作用對(duì)草地生態(tài)系統(tǒng)溫室氣體通量的變化缺乏準(zhǔn)確性評(píng)估,所得的試驗(yàn)資料缺乏可比性,評(píng)估標(biāo)準(zhǔn)不一致等;未來(lái)放牧對(duì)草地生態(tài)系統(tǒng)溫室氣體通量影響的研究應(yīng)從以下方面進(jìn)行重點(diǎn)研究。1)進(jìn)一步加強(qiáng)不同放牧模式對(duì)草地生態(tài)系統(tǒng)溫室氣體通量變化的研究,在一定區(qū)域范圍內(nèi)建立一套具有可比性的方法,找到適合當(dāng)?shù)貎?yōu)化減排的放牧管理模式。2)增加不同放牧強(qiáng)度梯度的研究,以彌補(bǔ)3種強(qiáng)度劃分下大尺度上的空白和不足。3)加強(qiáng)不同放牧動(dòng)物組合及排泄物對(duì)土壤成分及其微生物影響的研究,減少生長(zhǎng)季反芻動(dòng)物的采食、踐踏和糞尿斑等形成的厭氧區(qū)域,尤其對(duì)CH4和N2O的吸收排放有著顯著作用。除了基本的放牧方式對(duì)溫室氣體通量差異及物理環(huán)境的影響之外,應(yīng)著重研究微生物的土壤理化特性、生物特性對(duì)草地生態(tài)系統(tǒng)溫室氣體通量的影響。4)探討草地生態(tài)系統(tǒng)溫室氣體減排對(duì)策及技術(shù)措施的評(píng)價(jià)標(biāo)準(zhǔn)和方法,提出溫室氣體減排對(duì)策和技術(shù)措施。
References:
[1] 張衛(wèi)建,許泉,王緒奎,卞新民.氣溫上升對(duì)草地土壤微生物群落結(jié)構(gòu)的影響.生態(tài)學(xué)報(bào),2004,24(8):1742-1747.
Zhang W J,Xu Q,Wang X K,Bian X M.Impacts of experimental atmospheric warming on soil microbial community structure in a tallgrass prairie.Acta Ecologica Sinica,2004,24(8):1742-1747.(in Chinese)
[2] Laan S V D,Neubert R E M,Meijer H A J.A single gas chromatograph for accurate atmospheric mixing ratio measurements of CO2,CH4,N2O,SF6,CO.Atmospheric Measurement Techniques & Discussions,2009,2(2):549-559.
[3] Jones S K,Helfter M C,Anderson M C,Campbell C.The nitrogen,carbon and greenhouse gas budget of a grazed,cut and fertilised temperate grassland.Biogeosciences Discussions,2017,14:1-55.
[4] 王璐,蔣躍林.農(nóng)田土壤溫室氣體排放研究進(jìn)展.中國(guó)農(nóng)業(yè)與技術(shù),2012,13(8):1738-1743.
Wang L,Jiang Y L.Advances in greenhouse gases emission in farmland soils.Agricultural Science & Technology,2012,13(8):1738-1743.(in Chinese)
[5] Intergovermental Panel on Climate Change.Summary for Policy Makers.In Climate Change 2007:The Physical Science Basis.Contribution of Working Group to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change,2007:710-719.
[6] Benson R G,Scanlon T J,Czerepuszko P A.Thermography camera tuned to detect absorption of infrared radiation in a selected spectral bandwidth.US:US8653461,2014.
[7] 翟洋洋.隴東黃土高原農(nóng)田土壤的溫室氣體排放特征.蘭州:蘭州大學(xué)碩士學(xué)位論文,2015.
Zhai Y Y.Greenhouse gases emission of farm soil eastern Gansu Loess Plateau.Master Thesis.Lanzhou:Lanzhou University,2015.(in Chinese)
[8] Mosier A R,Pendall P,Morgan J A.Soil-atmosphere exchange of CH4,CO2,NOx,and N2O in the colorado shortgrass steppe following five years of elevated CO2and N fertilization.Atmospheric Chemistry & Physics,2003,3(3):2691-2706.
[9] 嚴(yán)迎燕.短程同步硝化反硝化過(guò)程的N2O釋放特性及其微生物群落特征研究.廣州:華南理工大學(xué)碩士學(xué)位論文,2014.
Yan Y Y.Study on the N2O emission characteristics and microbial community succession during the shortcut simultaneous nitrification and denitrification process.Master Thesis.Guangzhou:South China University of Technology,2014.(in Chinese)
[10] 王明星,張仁健,鄭循華.溫室氣體的源與匯.氣候與環(huán)境研究,2000,5(1):75-79.
Wang M X,Zhang R J,Zheng X H.Sources and sinks of green house gases.Climatic & Environmental Research,2000,5(1):75-79.(in Chinese)
[11] Jia B,Zhou G,Wang F,Wang Y,Weng E.Effects of grazing on soil respiration ofLeymuschinensis,Steppe.Climatic Change,2014,82(1/2):211-223.
[12] Novak S M,Fiorelli J L.Greenhouse gases and ammonia emissions from organic mixed crop-dairy systems:A critical review of mitigation options.Agronomy for Sustainable Development,2010,30(2):215-236.
[13] Soussana J F,Allard V,Pilegaard K,Ambusb P.Full accounting of the greenhouse gas(CO2,N2O,CH4)budget of nine European grassland sites.Agriculture Ecosystems & Environment,2007,121(1/2):121-134.
[14] 馬鋼.高寒草甸生態(tài)系統(tǒng)CO2和N2O排放對(duì)土壤干濕交替的響應(yīng).蘭州:甘肅農(nóng)業(yè)大學(xué)碩士學(xué)位論文,2014.
Ma G.Responses of CO2and N2O emissions to alternating wetting and drying in alpine meadow eco-system.Master Thesis.Lanzhou:Gansu Agricultural University,2014.(in Chinese)
[15] 牛書(shū)麗,萬(wàn)師強(qiáng),馬克平.陸地生態(tài)系統(tǒng)及生物多樣性對(duì)氣候變化的適應(yīng)與減緩.中國(guó)科學(xué)院院刊,2009,24(4):421-427.
Niu S L.Wan S Q,Ma K P.Acclimation and mitigation of terrestrial ecosystem and biodiversity to climate change.Bulletin of Chinese Academy of Sciences,2009,24(4):421-427.(in Chinese)
[16] 王長(zhǎng)庭,龍瑞軍,丁路明.草地生態(tài)系統(tǒng)中物種多樣性、群落穩(wěn)定性和生態(tài)系統(tǒng)功能的關(guān)系.草業(yè)科學(xué),2005,22(6):1-7.
Wang C T,Long R J,Ding L M.Species diversity,community stability and ecosystem function-extension of the continuous views.Pratacultural Science,2005,22(6):1-7.(in Chinese)
[17] Su R,Cheng J,Chen D,Bai Y,Jin H.Effects of grazing on spatiotemporal variations in community structure and ecosystem function on the grasslands of Inner Mongolia,China.Scientific Reports,2017,7(1):40.
[18] 張亮,韓靜艷,王道涵.草地生態(tài)系統(tǒng)土壤呼吸對(duì)放牧干擾的響應(yīng)研究進(jìn)展.生態(tài)科學(xué),2017,36(2):201-207.
Zhang L,Han J Y,Wang D H.Review on responses of soil respiration to stock grazing in grassland ecosystems.Ecological Science,2017,36(2):201-207.(in Chinese)
[19] 崔偉,趙凌平,趙芙蓉.封育和放牧對(duì)黃土高原典型草原芽庫(kù)的影響.草業(yè)科學(xué),2017,34(1):9-15.
Cui W,Zhao L P,Zhao F R.Effects of fencing and grazing management on bud bank in a semiarid steppe on the Loess Plateau.Pratacultural Science,2017,34(1):9-15.(in Chinese)
[20] 寶音賀希格.放牧對(duì)草地生態(tài)系統(tǒng)的影響.畜牧與飼料科學(xué),2013,34(z1):71-74.
Baoyinhexige.Effect of grazing on grassland ecosystem.Animal Husbandry & Feed Science,2013,34(z1):71-74.(in Chinese)
[21] Li Y,Li Z,Li Z,Geng X,Deng X.Numerical simulation of the effects of grassland degradation on the surface climate in overgrazing area of northwest China.Advances in Meteorology,2013(4):183-186.
[22] 高超.東祁連山不同退化程度高寒草甸草原土壤有機(jī)質(zhì)特性及其對(duì)草地生產(chǎn)力的影響.蘭州:甘肅農(nóng)業(yè)大學(xué)碩士畢業(yè)論文,2007.
Gao C.Study on the characteristics of soil organic matter of alpine meadow under different degradation degrees in eastern Qilian Mountains and its effect on productivity.Master Thesis.Lanzhou:Gansu Agricultural University,2007.(in Chinese)
[23] Allen D E,Pringle M J,Page K L,Dalal R C.A review of sampling designs for the measurement of soil organic carbon in Australian grazing lands.Rangeland Journal,2010,32(2):227-246.
[24] Kuijper D P J,Bakker J P.Top-down control of small herbivores on salt-marsh vegetation along a productivity gradient.Ecology,2005,86(4):914-923.
[25] Zhou Z C,Gan Z T,Shangguan Z P.Effects of grazing on soil physical properties and soil erodibility in semiarid grassland of the northern Loess Plateau(China).Catena,2010,82(2):87-91.
[26] Pang X Y,Bao W K,Wu N.The effects of clear-felling subalpine coniferous forests on soil physical and chemical properties in the eastern Tibetan Plateau.Soil Use & Management,2011,27(2):213-220.
[27] 張亮,沈潮,鄧杰.放牧干擾對(duì)草地土壤理化性質(zhì)的影響.防護(hù)林科技,2016(12):1-4.
Zhang L,Shen C,Deng J.Effects of grazing disturbance on soil physical and chemical properties in grassland.Protection Forest Science and Technology,2016(12):1-4.(in Chinese)
[28] Ishizuka S,Tsuruta H,Murdiyarso D.An intensive field study on CO2,CH4,and N2O emissions from soils at four land-use types in Sumatra,Indonesia.Global Biogeochemical Cycles,2002,16(3):11-22.
[29] Solomon S.Climate change 2007 the physical science basis:Work group I contribution to the fourth assessment report of the Intergovernmental Panel on Climate Change,2007:710-719.
[30] 李鳳霞,李曉東,周秉榮,祁棟林,王力,傅華.放牧強(qiáng)度對(duì)三江源典型高寒草甸生物量和土壤理化特征的影響.草業(yè)科學(xué),2015,32(1):11-18.
Li F X,Li X D,Zhou B R,Qi D L,Wang L,Fu H.Effects of grazing intensity on biomass and soil physical and chemical characteristics in alpine meadow in Tthree the source Rivers Source.Pratacultural Science,2015,32(1):11-18.(in Chinese)
[31] 管雄明.放牧對(duì)內(nèi)蒙古典型草原土壤甲烷通量變化及相關(guān)微生物的影響.杭州:浙江大學(xué)碩士學(xué)位論文,2016.
Guan X M.Effect of grazing on methane flux and related microbes in Inner Mongolia grassland soils.Master Thesis.Hangzhou:Zhejiang University,2016.(in Chinese)
[32] 衛(wèi)智軍,烏日?qǐng)D,達(dá)布希拉圖,蘇吉安,楊尚明.荒漠草原不同放牧制度對(duì)土壤理化性質(zhì)的影響.中國(guó)草地學(xué)報(bào),2005,27(5):6-10.
Wei Z J,Wuritu,Dabuxilatu,Su J A,Yang S M.The influence of different grazing systems on soil physical and chemical properties in desert steppe.Grassland of China,2005,27(5):6-10.(in Chinese)
[33] 梁茂偉,梁存柱,白雪,苗百嶺,王英舜,包桂榮,王譞.一年生植物功能群對(duì)放牧草原生物量和土壤呼吸的影響.草業(yè)科學(xué),2016,33(12):2407-2417.
Liang M W,Liang C Z,Bai X,Miao B L,Wang Y S,Bao G R,Wang X.Effects of annual plant functional group on biomass and soil respiration in agrazing community of a typical steppe grassland.Pratacultural Science,2016,33(12):2407-2417.(in Chinese)
[34] Sillen W M A,Dieleman W I J.Effects of elevated CO2and N fertilization on plant and soil carbon pools of managed grasslands:A meta-analysis.Biogeosciences,2012,9(6):2247-2258.
[35] 蒲寧寧,孫宗玖,范燕敏,楊合龍.放牧強(qiáng)度對(duì)昭蘇草甸草原土壤有機(jī)碳及微生物碳的影響.新疆農(nóng)業(yè)大學(xué)學(xué)報(bào),2013,36(1):66-70.
Pu N N,Sun Z J,Fan Y M,Yang H L.Influence of grazing intensity on the soil organic carbon and microbial biomass carbon of meadow steppe in Zhaosu area.Journal of Xinjiang Agricultural University,2013,36(1):66-70.(in Chinese)
[36] 李華偉.放牧條件下內(nèi)蒙古白絨山羊甲烷排放量的測(cè)定.呼和浩特:內(nèi)蒙古農(nóng)業(yè)大學(xué)碩士學(xué)位論文,2008.
Li H W.Measurement of methane emission from grazing Inner Mongolia Cashmere goats.Master Thesis.Hohhot:Inner Mongolia Agricultural University,2008.(in Chinese)
[37] 高英志,韓興國(guó),汪詩(shī)平.放牧對(duì)草原土壤的影響.生態(tài)學(xué)報(bào),2004,24(4):790-797.
Gao Y Z,Han X G,Wang S P.The effects of grazing on grassland soils.Acta Ecologica Sinica,2004,24(4):790-797.(in Chinese)
[38] Zhang F,Diao Q Y.Research progress on greenhouse gas emissions of animal husbandry and emission reduction measures.Journal of Domestic Animal Ecology,2015,36(11):81-85.
[39] 馬秀枝.開(kāi)墾和放牧對(duì)內(nèi)蒙古草原土壤碳庫(kù)和溫室氣體通量的影響.北京:中國(guó)科學(xué)院植物研究所博士學(xué)位論文,2006.
Ma X Z.Effects of cultivation and grazing on soil carbon pool and greenhouse gases fluxes in the Inner Mongolia steppes.PhD Thesis.Beijing:Institute of Botany,The Chinese Academy of Sciences,2006.(in Chinese)
[40] 齊玉春,董云社,楊小紅,耿元波,劉立新,李明峰.放牧對(duì)溫帶典型草原含碳溫室氣體CO2、CH4通量特征的影響.資源科學(xué),2005,27(2):103-109.
Qi Y C,Dong Y S,Yang X H,Geng Y B,Liu L X,Li M F.Effects of grazing on carbon dioxide and methane fluxes in typical temperate grassland in Inner Mongolia,China.Resources Science,2005,27(2):103-109.(in Chinese)
[41] Wilson R,Müller C,Moser G,Wilson D.To graze or not to graze?Four years greenhouse gas balances and vegetation composition from a drained and a rewetted organic soil under grassland.Agriculture Ecosystems & Environment,2016,222:156-170.
[42] 李玉娥,秦曉波,李文福,林而達(dá),高清竹,萬(wàn)運(yùn)帆,石峰.夏季休牧對(duì)高寒矮嵩草草甸溫室氣體排放的影響.農(nóng)業(yè)工程學(xué)報(bào),2007,23(4):206-211.
Li Y E,Qin X B,Li W F,Lin E D,Gao Q Z,Wan Y F,Shi F.Impacts of no grazing in summer on greenhouse gas emissions fromKobresiahumilisalpine meadow.Transactions of the Chinese Society of Agricultural Engineering,2007,23(4):206-211.(in Chinese)
[43] 王思躍,胡玉瓊,紀(jì)寶明,劉廣仁.薛敏.放牧對(duì)內(nèi)蒙古草原溫室氣體排放的影響.中國(guó)環(huán)境科學(xué),2002,22(6):490-494.
Wang Y S,Hu Y Q,Ji B M,Liu G R,Xue M.Research of grazing effects on greenhouse gas emission in Inner Mongolia grasslands.China Environmental Science,2002,22(6):490-494.(in Chinese)
[44] 王躍思,胡玉瓊,紀(jì)寶明,劉廣仁,薛敏.半干旱草原溫室氣體排放/吸收與環(huán)境因子的關(guān)系研究.大氣科學(xué)進(jìn)展,2003,20(1):295-310.
Wang Y S,Hu Y Q,Ji B M,Liu G R,Xue M.An investigation on the relationship between emission/uptake of greenhouse gases and environmental factors in semiarid grassland.Advances in Atmospheric Sciences,2003,20(1):295-310.(in Chinese)
[45] 賀桂香,李凱輝,宋韋,公延明,劉學(xué)軍,胡玉昆,田長(zhǎng)彥.新疆天山高寒草原不同放牧管理下的CO2,CH4和N2O通量特征.生態(tài)學(xué)報(bào),2014,34(3):674-681.
He G X,Li K H,Song W,Gong Y M,Liu X J,Hu Y K,Tian C Y.The fluxes of carbon dioxide,methane and nitrous oxide in alpine grassland of the Tianshan Mountains,Xinjiang.Acta Ecologica Sinica,2014,34(3):674-681.(in Chinese)
[46] Soussana J F,Allard V,Pilegaard K,Ambus P,Amman C.Full accounting of the greenhouse gas(CO2,N2O,CH4)budget of nine European grassland sites.Agriculture Ecosystems & Environment,2007,121(1):121-134.
[47] Moore J L,Howden S M,Mckeon G M,Carte J O,Scanlan J C.The dynamics of grazed woodlands in southwest Queensland,Australia,and their effect on greenhouse gas emissions.Environment International,2001,27(2/3):147-153.
[48] Howden S M,White D H,Mckeon G M,Scanlan J C,Carter J O.Methods for exploring management options to reduce greenhouse gas emissions from tropical grazing systems.Climatic Change,1994,27(1):49-70.
[49] 陳先江,王彥榮,侯扶江.草地生態(tài)系統(tǒng)溫室氣體排放機(jī)理及影響因素.草業(yè)科學(xué),2011,28(5):722-728.
Chen X J,Wang Y R,Hou F J.Mechanisms and controlling factors of grassland ecosystem greenhouse gas emissions.Pratacultural Science,2011,28(5):722-728.(in Chinese)
[50] 周培.不同放牧強(qiáng)度對(duì)內(nèi)蒙古草原溫室氣體通量影響.呼和浩特:內(nèi)蒙古農(nóng)業(yè)大學(xué)碩士學(xué)位論文,2011.
Zhou P.Effects of the different grazing intensity on greenhouse gas fluxes of Inner Monoglia grassland.Master Thesis.Huhhot:Inner Mongolia Agricultural University,2011.(in Chinese)
[51] 曹娜.放牧強(qiáng)度對(duì)半干旱草原土壤N2、N2O、NO、CO2和CH4排放的影響.楊凌:西北農(nóng)林科技大學(xué)碩士學(xué)位,2015.
Cao N.Effect of grazing intensity on the emissions of N2,N2O,NO,CO2,CH4in temperate semiarid steeps.Master Thesis.Yangling:North West Agriculture and Forestry University,2015.(in Chinese)
[52] Cardoso A D S,Brito L D F,Janusckiewicz E R,Morgado E D S,Barbero R P.Impact of grazing intensity and seasons on greenhouse gas emissions in tropical grassland.Ecosystems,2017,20:845-859.
[53] 萬(wàn)運(yùn)帆,李玉娥,高清竹,段敏杰,旦久羅布,白瑪玉珍,韋蘭亭.夏季放牧強(qiáng)度對(duì)藏北草原溫室氣體排放的影響.草業(yè)科學(xué),2010,27(11):1-6.
Wan Y F,Li Y E,Gao Q Z,Duan M J,Danjiuluobu,Baimayuzhen,Wei L T.Effect of summer grazing intensity on GHG emission in the north Tibet steppe.Pratacultural Science,2010,27(11):1-6.(in Chinese)
[54] 朱二雄,詹偉,胡驥,彭長(zhǎng)輝,鄭群英,楊剛,何奕忻,朱單,朱求安,陳槐.不同放牧強(qiáng)度對(duì)高寒草甸生態(tài)系統(tǒng)呼吸的早期影響.應(yīng)用與環(huán)境生物學(xué)報(bào),2016,22(4):561-566.
Zhu E X,Zhan W,Hu J,Peng C H,Zheng Q Y,Yang G,He Y X,Zhu D,Zhu Q A,Chen H.Early influence of the grazing intensity on ecosystem respiration of alpine meadows.China Journal of Applied Environment Biology,2016,22(4):561-566.(in Chinese)
[55] 周培,韓國(guó)棟,王成杰,劉瑞香,姜圓圓,唐士明.不同放牧強(qiáng)度對(duì)內(nèi)蒙古荒漠草地生態(tài)系統(tǒng)含碳溫室氣體交換的影響.內(nèi)蒙古農(nóng)業(yè)大學(xué)學(xué)報(bào)(自然科學(xué)版),2011,32(4):59-64.
Zhou P,Han G D,Wang C J,Liu R X,Jiang Y Y,Tang S M.Effects of stocking rates on carbon fluxin the desert grassl and ecological system of inner mongolia Journal of Inner Mongolia Agricultural University(Natural Science Edition),2011,32(4):59-64.(in Chinese)
[56] Bell M J,Cullen B R,Eckard R J.The influence of climate,soil and pasture type on productivity and greenhouse gas emissions intensity of modeled beef cow-calf grazing systems in southern Australia.Animals,2012,2(4):540-558.
[57] Chai L,Kr R.Greenhouse gases and ammonia emissions from grazing beef cattle in Alberta and Ontario Canada.PloS One,2015,10(4):S10.
[58] 張成霞,南志標(biāo).放牧對(duì)草地土壤理化特性影響的研究進(jìn)展.草業(yè)學(xué)報(bào),2010,19(4):204-211.
Zhang C X,Nan Z B.Research progress on effects of grazing on physical and chemical characteristics of grassland soil.Acta Prataculturae Sinica,2010,19(4):204-211.(in Chinese)
[59] 王躍思,薛敏,黃耀,劉廣仁,王明星,紀(jì)寶明.內(nèi)蒙古天然與放牧草原溫室氣體排放研究.應(yīng)用生態(tài)學(xué)報(bào),2003,14(3):372-376.
Wang Y S,Xue M,Huang Y,Liu G R,Wang M X,Ji M B.Greenhouse gases emission or uptake in Inner Mongolia natural and free-grazing grasslands.Chinese Journal of Applied Ecology,2003,14(3):372-376.(in Chinese)
[60] 林巧燕,布仁巴音,汪詩(shī)平.反芻家畜及其排泄物對(duì)N2O和CH4排放的貢獻(xiàn).生態(tài)學(xué)雜志,2011,30(11):2604-2612.
Lin Q Y,Burenbayin,Wang S P.Contributions of ruminants and their excreta to N2O and CH4emissions.Chinese Journal of Ecology,2011,30(11):2604-2612.(in Chinese)
[61] 程勝利,肖玉萍,楊保平.反芻動(dòng)物甲烷排放現(xiàn)狀及調(diào)控技術(shù)研究進(jìn)展.中國(guó)草食動(dòng)物科學(xué),2013,33(5):56-59.
Cheng S L,Xiao Y P,Yang B P.Research progress in methane emission from ruminant and control techniques.China Herbivores Science,2013,33(5):56-59.(in Chinese)
[62] 王胤晨,袁揚(yáng),張錦華,何光中,韓勇,周文章.反芻動(dòng)物瘤胃甲烷產(chǎn)生的營(yíng)養(yǎng)調(diào)控.中國(guó)畜牧獸醫(yī)文摘,2015,41(7):100-104.
Wang Y C,Yuan Y,Zhang J H,He G Z,Han Y,Zhou W Z.Nutritional regulation of rumen methane production in ruminantanimals.Chinese Absstracts of Animal Husbandry and Veterinary Medicine,2015,41(7):100-104.(in Chinese)
[63] 王月,張東方,丁瑩,荊紅俊,娜仁花.內(nèi)蒙古呼和浩特市家畜溫室氣體排放量估算.家畜生態(tài)學(xué)報(bào),2014(10):68-73.
Wang Y,Zhang D F,Ding Y,Jing H J,Narenhua.Greenhouse gas emission by livestocks in hohhot.Acta Ecologiae Animalis Domastici,2014(10):68-73.(in Chinese)
[64] 郭小偉,杜巖功,林麗.青藏高原北緣3種高寒草地的CH4、CO2和N2O通量特征的初步研究.草業(yè)科學(xué),2016,33(1):27-37.
Guo X W,Du Y G,Lin L.CH4,CO2and N2O flux among three types of alpine meadow in the north regions of Qinghai-Tibetan Plateau.Pratacultural Science,2016,33(1):27-37.(in Chinese)
[65] Chen W,Wolf B,Brüggemann N,Butterbach-Bahl K,Chen X Z.Annual emissions of greenhouse gases from sheepfolds in Inner Mongolia.Plant and Soil,2011,340(1):291-301.
[66] 丁丹.牛羊混合放牧對(duì)內(nèi)蒙古荒漠草原溫室氣體通量的影響.呼和浩特:內(nèi)蒙古農(nóng)業(yè)大學(xué)碩士學(xué)位論文,2015.
Ding D.Effects of cattle and sheep mixed-grazing on GHG fluxes during the growing season in Inner Monoglia desert steppe.Master Thesis.Huhhot:Inner Mongolia Agricultural University,2015.(in Chinese)
[67] 汪詩(shī)平,Andreas Wilke,汪亞運(yùn),白玲.放牧閹牦牛提前出欄甲烷排放強(qiáng)度減排潛力探討.環(huán)境科學(xué),2014(8):3225-229.
Wang S P,Wilkes A,Wang Y Y,Bai L.Discussion on reduction potential of CH4emission intensity for early off-take practice of grazing yak.Environmental Science,2014,35(8):3225-3229.(in Chinese)
[68] 趙亮,陳懂懂,徐世曉,趙新全,李奇.傳統(tǒng)放牧模式下青藏高原高寒牧區(qū)藏系綿羊溫室氣體排放研究.家畜生態(tài)學(xué)報(bào),2016,37(8):36-44.
Zhao L,Chen D D,Xu S X,Zhao X Q,Li Q.Life cycle assessment of greenhouse gas emission from tibetan sheep under traditional grazing management on the alpine grassland of Qinghai-Tibetan Plateau.Journal of Domestic Animal Ecology,2016,37(8):36-44.(in Chinese)
[69] 朱玲玲,戎郁萍,王偉光,馬磊.放牧對(duì)草地生態(tài)系統(tǒng)CO2凈氣體交換影響研究概述.草地學(xué)報(bào),2013,21(1):3-10.
Zhu L L,Rong Y P,Wang W G,Ma L.Effects of grazing on the net ecosystem exchange of carbon dioxide in grassland ecosystems(Research Review).Acta Agrestia Sinica,2013,21(1):3-10.(in Chinese)
[70] 劉忠寬,汪詩(shī)平,韓建國(guó),陳佐忠,王艷芬.放牧家畜排泄物N轉(zhuǎn)化研究進(jìn)展.生態(tài)學(xué)報(bào),2004,24(4):775-783.
Liu Z K,Wang S P,Han J G,Chen Z Z,Wang Y F.Nitrogen turnover from grazing livestock excreta:A review.Acta Ecologica Sinica,2004,24:775-783.(in Chinese)
[71] 王成杰,汪詩(shī)平,周禾.放牧家畜甲烷氣體排放量測(cè)定方法研究進(jìn)展.草業(yè)學(xué)報(bào),2006,15(1):113-116.
Wang C J,Wang S P,Zhou H.Review on advancements in measurement methods of methane emissions from grazing animals.Acta Prataculturae Sinica,2006,15(1):113-116.(in Chinese)
[72] 葛世棟,徐田偉,李冰,曹慧,趙亮,徐世曉.高寒草甸糞斑的溫室氣體排放.草業(yè)科學(xué),2014,31(1):39-47.
Ge S D,Xu T W,Li B,Cao H,Zhao L,Xu S X.Effects of yak dung on greenhouse gas emission during growing season in the alpine meadow.Pratacultural Science,2014,31(1):39-47.(in Chinese)
[73] Khalil M A K,Rasmussen R A.The global sources of nitrous oxide.Journal of Geophysical Research,1992,97(D13):14651-14660.
[74] Houghton J T,Callander B A,Vamey S K.The Supplementary Report to the IPCC Scientific Assessment,2015:141-141.
[75] 劉德江.家畜糞便厭氧消化特性與應(yīng)用研究.楊凌:西北農(nóng)林科技大學(xué)碩士學(xué)位論文,2004.
Liu D J.Study on property and applicantion of anaerobic digestion on for livetock dung.Master Thesis.Yangling:North West Agriculture and Forestry University,2004.(in Chinese)
[76] Mats O,Ingvar S.Effects of a transient oxic period on mineralization of organic matter to CH4and CO2in anoxic peat incubations.Geomicrobiology Journal,1998,15(4):325-333.
[77] Ma X Z,Wang S P,Wang Y F,Jiang G M,Nyren P.Short-term effects of sheep excrement on carbon dioxide,nitrous oxide and methane fluxes in typical grassland of Inner Mongolia.New Zealand Journal of Agricultural Research,2006,49(3):285-297.
[78] 葛世棟.糞斑覆蓋對(duì)高寒草地溫室氣體排放的影響.西寧:中國(guó)科學(xué)院西北高原生物研究所博士學(xué)位論文,2013.
Ge S D.Effects of fecal coverage on greenhouse gas emission in alpine grassland.PhD Thesis.Xining:Northwest Plateau Institute of Biology,Chinese Acadeng of Sciences,2013.(in Chinese)
[79] 姜圓圓.放牧綿羊排泄物養(yǎng)分降解及其對(duì)溫室氣體排放的貢獻(xiàn).呼和浩特:內(nèi)蒙古農(nóng)業(yè)大學(xué)碩士學(xué)位論文,2012.
Jiang Y Y.The study on nutrient degradation and contribution to greenhouse gas emission of grazing sheep excreta.Master Thesis.Huhhot:Inner Mongolia Agricultural University,2012.(in Chinese)
[80] 陸日東.奶牛糞便溫室氣體排放及影響因子研究.北京:中國(guó)農(nóng)業(yè)科學(xué)院碩士學(xué)位論文,2007.
Lu R D.Emissions of greenhouse gases from dairy manure and influencing factors.Master Thesis.Beijing:Chinese Academy of Agricultural Sciences(CAAS),2007.(in Chinese)