天堂国产午夜亚洲专区-少妇人妻综合久久蜜臀-国产成人户外露出视频在线-国产91传媒一区二区三区

持久性有機(jī)污染物的森林過濾效應(yīng)研究

發(fā)布時(shí)間:2019-07-03 16:53
【摘要】:持久性有機(jī)污染物(POPs)是一類半揮發(fā)、難降解且具有很強(qiáng)親脂憎水性的有機(jī)化合物。這類化合物大多由人類活動(dòng)產(chǎn)生并排放至自然環(huán)境,可在大氣中長(zhǎng)距離遷移導(dǎo)致全球范圍的污染。在主要POPs一次污染源削減和現(xiàn)今全球氣候變化背景下,認(rèn)識(shí)和掌握POPs的二次污染規(guī)律,有助于更客觀理解POPs全球分布現(xiàn)狀和歸趨!叭蛘麴s模型”一直以來被視為最經(jīng)典的POPs環(huán)境歸趨模型,然而近年來質(zhì)疑該模型的聲音越來越多,季風(fēng)和大氣環(huán)流、降解和生物遷移都是影響POPs環(huán)境命運(yùn)的重要因素。POPs的“森林過濾效應(yīng)”已被廣為接受,但目前相關(guān)研究并不多。全球森林對(duì)于POPs的固定作用及POPs全球傳輸?shù)挠绊懘蠖嘀挥心P湍M研究,缺乏在林區(qū)的實(shí)測(cè)研究;赑OPs長(zhǎng)距離傳輸?shù)目赡苄院痛竺娣e森林的可得性,藏東南森林是研究POPs森林過濾效應(yīng)的天然實(shí)驗(yàn)室。因此,本研究工作首先選擇青藏高原東南緣的貢嘎山東坡海螺溝無人區(qū)開展“冷凝捕集效應(yīng)”和“森林過濾效應(yīng)”的對(duì)比研究。通過對(duì)比不同海拔高度、不同環(huán)境介質(zhì)中多氯聯(lián)苯(PCBs)污染水平、組成和空間分布特征,結(jié)合對(duì)環(huán)境參數(shù)(溫度、降雨、土壤有機(jī)碳)的統(tǒng)計(jì)分析,定量獲取兩種效應(yīng)對(duì)PCBs高山富集的貢獻(xiàn)值。結(jié)果表明,貢嘎山東坡土壤中PCBs的組成與分布主要受大氣傳輸和森林土壤有機(jī)碳的影響,土壤有機(jī)碳對(duì)土壤PCBs濃度變化的貢獻(xiàn)率有75%,與由溫度控制的發(fā)生高海拔富集的“全球蒸餾模型”假設(shè)不符,“森林過濾效應(yīng)”在PCBs山地富集中所起的作用較山地“冷凝捕集效應(yīng)”更大,兩種效應(yīng)的平均貢獻(xiàn)率分別為65%和35%。森林過濾效應(yīng)對(duì)不同類別POPs的影響程度可能不同。因此,論文的第二部分,考察了鹵系阻燃劑(HFRs)在貢嘎山東坡土壤的分布情況,利用分子組成比率和氣團(tuán)后向軌跡模型判斷了HFRs的可能來源,并分析了HFRs空間分布的影響因子。結(jié)果表明,貢嘎山東坡森林土壤中可以檢測(cè)出低揮發(fā)性的BDE209和新型溴系阻燃劑(NBFRs)十溴二苯基乙烷(DBDPE)、2-乙基己基-2,3,4,5-四溴苯酸鹽(TBB)、1,2-雙(2,4,6-三溴苯氧基)乙烷(TBE)和氯系阻燃劑德克隆(DP),其中DBDPE在大氣和土壤中的濃度分別達(dá)到171 pg/m3和1450 pg/g干重,是相對(duì)含量最高的單體,NBFRs在HFRs中的比重因此最高。HFRs濃度沿海拔梯度呈整體下降趨勢(shì),BDE47、BDE99和BDE209在山地環(huán)境的遷移能力從高到低依次為BDE47BDE99BDE209,DBDPE濃度沿海拔梯度波動(dòng)較大,推測(cè)其環(huán)境穩(wěn)定性較差。森林土壤的HFRs主要富集在有機(jī)質(zhì)含量高的O層,高山草甸土壤的HFRs在C層的含量最高,可能與高山地表徑流攜帶HFRs從山頂向山腳遷移有關(guān)。HFRs的海拔分布主要受大氣傳輸和人類活動(dòng)遠(yuǎn)近程度影響,與環(huán)境溫度和土壤有機(jī)質(zhì)的相關(guān)性較差。森林過濾效應(yīng)強(qiáng)度與植被覆蓋類型和土壤有機(jī)碳含量密切相關(guān)。然而,在全球氣候變化和人類活動(dòng)雙重壓力下,土地利用/覆蓋類型在時(shí)間和空間尺度發(fā)生快速變化,從而劇烈改變地表覆蓋狀態(tài)和土壤有機(jī)碳儲(chǔ)量。我國(guó)是人工林面積最多的國(guó)家,熱帶地區(qū)天然林向人工林變化情況嚴(yán)峻,其中地力衰退引起的土壤碳流失可能導(dǎo)致“老”POPs的二次遷移。因此,論文的第三部分選取海南島儋州市的蘭洋國(guó)營(yíng)林場(chǎng)開展天然林和人工林土壤富集POPs的比較研究。通過考察不同林型(天然林、橡膠林、桉樹林)和林齡(5齡橡膠、15齡橡膠、25齡橡膠)土壤中POPs的污染水平、組成和空間分布特征,結(jié)合對(duì)土壤理化性質(zhì)(pH、土壤有機(jī)碳、碳氮比)的統(tǒng)計(jì)分析,闡明桉樹和橡膠樹種植對(duì)POPs環(huán)境歸趨的影響。結(jié)果表明,熱帶天然森林對(duì)POPs的持留能力顯著高于熱帶人工林,橡膠林對(duì)POPs的持留能力隨膠林的增加而增加;谙嚓P(guān)性分析和界面平衡分析,再次強(qiáng)調(diào)土壤有機(jī)碳對(duì)POPs分布的影響,并指出人工林POPs向土壤中的滲濾強(qiáng)度較天然林大。這些新認(rèn)識(shí),有助于更客觀理解POPs全球分布現(xiàn)狀和歸趨。
[Abstract]:Persistent organic pollutants (POPs) are a class of organic compounds that are semi-volatile, difficult to degrade and have very strong lipophilicity. Most of these compounds are produced and discharged to the natural environment by human activities, and long-distance migration in the atmosphere can lead to global pollution. In the context of primary POPs reduction and current global climate change, it is helpful to understand and master the law of secondary pollution of POPs and help to understand the current situation and trend of POPs global distribution more objectively. The "global distillation model" has been regarded as the most classic POPs model, but in recent years it has been questioned that the sound of the model is increasing, and the circulation, degradation and biological migration of the monsoon and the atmosphere are important factors that affect the fate of the POPs. The "forest filtering effect" of POPs has been widely accepted, but the current research is not much relevant. The effect of global forest on the fixed function of POPs and the global transmission of POPs is only a model simulation study, and there is a lack of the actual study in the forest area. Based on the possibility of long-distance transmission of POPs and the availability of large-area forest, the forest in the southeast is the natural laboratory for studying the filtering effect of POPs. Therefore, the research work first selected the comparative study of the "condensation trapping effect" and the "forest filtering effect" in the uninhabited area of the east slope of the Gongga Mountain in the southeast of the Qinghai-Tibet Plateau. By comparing the pollution level, composition and spatial distribution of polychlorinated biphenyls (PCBs) in different environmental media, the contribution of two effects to the high mountain enrichment of PCBs was obtained by statistical analysis of environmental parameters (temperature, rainfall and soil organic carbon). The results show that the composition and distribution of PCBs in the Dongpo soil of Gongga Mountain are mainly influenced by the atmospheric transmission and the organic carbon of the forest, and the contribution rate of soil organic carbon to the change of the concentration of the soil PCBs is 75%, which is not in conformity with the "global distillation model" of the high-altitude enrichment caused by the temperature control. The effect of the "forest filtering effect" on the enrichment of the PCBs in the mountainous region is larger than that of the mountain "condensation trapping effect", and the average contribution rate of the two effects is 65% and 35%, respectively. The effect of forest filtration on different categories of POPs may be different. The second part of the thesis is to study the distribution of the halogen-based flame retardant (HFRs) in the east slope of the Gongga Mountain. The possible sources of the HFRs are determined by the molecular composition ratio and the air mass, and the influence factors of the spatial distribution of the HFRs are also analyzed. The results show that the low-volatility BDE209 and the novel brominated flame retardant (NBFRs) decabromodiphenyl ethane (DBDPE),2-ethylhexyl-2,3,4,5-tetrabromobenzene (TBB), 1,2-bis (2,4,6-tribromophenoxy) ethane (TBE) and chlorine-based flame retardant (DP) can be detected in the forest soil in the east slope of the Gongga Mountain. The concentration of the DBDPE in the atmosphere and the soil reaches 171 pg/ m3 and 1450 pg/ g dry weight, respectively, is the highest relative content, and the specific gravity of the NBFRs in the HFRs is therefore the highest. The concentration of HFRs decreased as a whole along the altitude gradient, and the migration ability of BDE47, BDE99 and BDE209 in the mountain environment was BDE47BDE99BDE209 in order from high to low, and the concentration of DBDPE was large along the altitude gradient, and the environmental stability of BDE47, BDE99 and BDE209 was relatively poor. The HFRs of the forest soil are mainly enriched in the O-layer with high organic matter content. The highest in the C-layer of the high-alpine meadow soil, it is possible to carry the HFRs from the top of the mountain to the mountain-foot migration from the top of the mountain. The altitude distribution of the HFRs is mainly influenced by the atmospheric transmission and the near-far of the human activity, and the correlation between the ambient temperature and the organic matter of the soil is poor. The intensity of the forest filtration effect is closely related to the vegetation cover type and the soil organic carbon content. However, under the dual pressure of global climate change and human activity, the type of land use/ cover changes rapidly in terms of time and space, thus dramatically changing the surface coverage and soil organic carbon reserves. In the country with the largest plantation area, the change of natural forest in the tropics to the plantation is serious, and the loss of soil carbon due to the decline of soil fertility can lead to the secondary migration of the "old" POPs. Therefore, the third part of the thesis is to select the comparative study of the soil-enriched POPs of natural forest and plantation in the Lanyang State-owned Forest Farm in Lanzhou, Hainan, China. The pollution level, composition and spatial distribution of POPs in different forest types (natural forest, rubber forest, eucalyptus forest) and forest age (5-year-old rubber,15-year-old rubber and 25-year-old rubber) were investigated, and the statistical analysis of soil physical and chemical properties (pH, soil organic carbon, carbon-nitrogen ratio) was combined. The effects of the planting of eucalyptus and rubber tree on the environment of the POPs were clarified. The results showed that the retention capacity of the tropical natural forest on the POPs was significantly higher than that of the tropical forest, and the retention capacity of the rubber forest to the POPs was increased with the increase of the rubber forest. Based on the correlation analysis and the analysis of the interface balance, the effect of soil organic carbon on the distribution of POPs is emphasized, and it is pointed out that the percolation intensity of the PPs in the soil is larger than that of the natural forest. These new understandings have contributed to a more objective understanding of the current status and trend of the global distribution of POPs.
【學(xué)位授予單位】:中國(guó)科學(xué)院研究生院(廣州地球化學(xué)研究所)
【學(xué)位級(jí)別】:博士
【學(xué)位授予年份】:2016
【分類號(hào)】:X173;X592

【相似文獻(xiàn)】

相關(guān)期刊論文 前10條

1 王芬 ,楊逸淇;全球總動(dòng)員圍剿POPs[J];環(huán)境導(dǎo)報(bào);2003年23期

2 ;Take actions against Persistent Organic Pollutants (POPs)[J];Journal of Environmental Sciences;2004年06期

3 ;聯(lián)合國(guó)環(huán)境規(guī)劃署POPs分析示范實(shí)驗(yàn)室落戶中國(guó)科學(xué)院生態(tài)環(huán)境研究中心[J];環(huán)境化學(xué);2006年06期

4 王芬;;全球總動(dòng)員圍剿POPs[J];生命世界;2006年05期

5 林科;;聯(lián)合國(guó)POPs實(shí)驗(yàn)室落戶中科院[J];農(nóng)藥市場(chǎng)信息;2006年23期

6 馮文;張鵬;張建揚(yáng);;紡織品中持久性有機(jī)污染物(POPs)的分析[J];紡織導(dǎo)報(bào);2008年01期

7 彭麗;;我國(guó)POPs污染場(chǎng)地治理刻不容緩[J];農(nóng)藥市場(chǎng)信息;2008年12期

8 丁峰;沈偉;顧金利;賈學(xué)敏;吳相山;方武均;;POPs污染及其治理方法[J];科技情報(bào)開發(fā)與經(jīng)濟(jì);2009年08期

9 安泉;;潛伏的殺手——POPs(二)[J];環(huán)境;2010年02期

10 安泉;;潛伏的殺手——POPs(三)[J];環(huán)境;2010年03期

相關(guān)會(huì)議論文 前10條

1 王謀;;寧夏持久性有機(jī)污染物(POPs)防治的有關(guān)問題探討[A];持久性有機(jī)污染物論壇2011暨第六屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2011年

2 朱麗波;李申杰;楊炳建;慎迪飛;;寧波POPs地方履約應(yīng)對(duì)策略初探[A];持久性有機(jī)污染物論壇2009暨第四屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2009年

3 任智輝;裴國(guó)霞;張琦;張巖;;逸度模型應(yīng)用于POPs研究中若干問題的探討[A];持久性有機(jī)污染物論壇2010暨第五屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2010年

4 周隆超;黃俊;鄧述波;余剛;;歐盟POPs科研支撐的理論模型及在我國(guó)的應(yīng)用前景[A];持久性有機(jī)污染物論壇2010暨第五屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2010年

5 任南琪;劉麗艷;齊虹;李一凡;;大尺度環(huán)境(區(qū)域和全球)中POPs研究[A];持久性有機(jī)污染物論壇2010暨第五屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2010年

6 呂俊崗;劉瀟威;李凌云;李衛(wèi)建;買光熙;王璐;;土壤中POPs污染現(xiàn)狀與化學(xué)分析技術(shù)研究進(jìn)展[A];全國(guó)耕地土壤污染監(jiān)測(cè)與評(píng)價(jià)技術(shù)研討會(huì)論文集[C];2006年

7 石毓民;;使用美國(guó)EPA方法大量快速分析土壤,油和水中POPs樣品[A];持久性有機(jī)污染物論壇2006暨第一屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2006年

8 鄭濤;楊曉東;;鋼鐵工業(yè)持久性有機(jī)污染物(POPs)狀況及控制措施[A];持久性有機(jī)污染物論壇2006暨第一屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2006年

9 孫玉艷;徐鐵兵;馬躍濤;王宇青;;POPs危害與管理對(duì)策分析[A];環(huán)境與健康:河北省環(huán)境科學(xué)學(xué)會(huì)環(huán)境與健康論壇暨2008年學(xué)術(shù)年會(huì)論文集[C];2008年

10 侯貴光;吳舜澤;逯元堂;朱建華;張建成;韓文亞;劉軍民;王桂娟;;POPs公約履約資金渠道研究[A];持久性有機(jī)污染物論壇2010暨第五屆持久性有機(jī)污染物全國(guó)學(xué)術(shù)研討會(huì)論文集[C];2010年

相關(guān)重要報(bào)紙文章 前10條

1 記者 王繁泓;削減和淘汰POPs項(xiàng)目啟動(dòng)[N];中國(guó)化工報(bào);2001年

2 趙曉強(qiáng);構(gòu)筑POPs公約數(shù)字基石[N];中國(guó)化工報(bào);2002年

3 李宏乾;我國(guó)POPs控制工作逐步啟動(dòng)[N];中國(guó)化工報(bào);2004年

4 記者 姜虹;我防治POPs污染面臨雙重挑戰(zhàn)[N];中國(guó)化工報(bào);2005年

5 本報(bào)記者 王玲;狙擊POPs[N];經(jīng)濟(jì)日?qǐng)?bào);2004年

6 李禾;POPs:你還不了解的隱形“殺手”[N];科技日?qǐng)?bào);2004年

7 莊國(guó)泰;關(guān)于推進(jìn)我國(guó)POPs公約履約工作的思考[N];中國(guó)環(huán)境報(bào);2006年

8 徐曉白;POPs廢物和污染場(chǎng)地危害及其控制[N];中國(guó)環(huán)境報(bào);2007年

9 王秀蘭;首個(gè)POPs環(huán)境安全“973”項(xiàng)目啟動(dòng)[N];中國(guó)化工報(bào);2004年

10 李宏乾;淘汰POPs需加緊開發(fā)適用技術(shù)[N];中國(guó)化工報(bào);2004年

相關(guān)博士學(xué)位論文 前6條

1 劉昕;持久性有機(jī)污染物的森林過濾效應(yīng)研究[D];中國(guó)科學(xué)院研究生院(廣州地球化學(xué)研究所);2016年

2 趙玉麗;大氣持久性有機(jī)污染物在樹木表皮中的富集機(jī)制初探及其在大氣污染時(shí)空分辨監(jiān)測(cè)中的應(yīng)用[D];廈門大學(xué);2008年

3 王泰;海河河口水環(huán)境中POPs的污染特征及來源解析[D];清華大學(xué);2010年

4 朱剛兵;基于β-環(huán)糊精和納米碳材料的POPs電化學(xué)傳感研究[D];湖南大學(xué);2013年

5 丁輝;大沽排污河POPs歸趨行為[D];天津大學(xué);2005年

6 劉小真;鄱陽湖流域底質(zhì)重金屬及殺蟲劑類POPs垂直污染分布特征[D];南昌大學(xué);2008年

相關(guān)碩士學(xué)位論文 前10條

1 康凱;重慶市POPs分布和排放狀況的初步研究[D];重慶大學(xué);2009年

2 曲穎群;吉林省主要土壤類型中持久性有機(jī)污染物(POPs)的研究[D];東北師范大學(xué);2010年

3 梁寶翠;陜西省POPs污染綜合防治對(duì)策研究[D];西北大學(xué);2012年

4 弓俊微;重慶市廢棄殺蟲劑類POPs調(diào)查及前處理方案研究[D];重慶大學(xué);2009年

5 蔡蘇芬;吉林省持久性有機(jī)污染物(POPs)污染狀況及防治對(duì)策研究[D];吉林大學(xué);2012年

6 李冬梅;西安市蔬菜基地持久性有機(jī)污染物(POPs)殘留狀況研究[D];陜西師范大學(xué);2008年

7 劉華林;河口持久性有機(jī)污染物(POPs)多介質(zhì)分配特征及影響機(jī)制研究[D];華東師范大學(xué);2005年

8 張安;海產(chǎn)品中POPs的暴露水平及其風(fēng)險(xiǎn)分析[D];大連海事大學(xué);2013年

9 迭慶杞;典型地區(qū)環(huán)境中二惡英類POPs的時(shí)空分布特征及其環(huán)境行為研究[D];中國(guó)環(huán)境科學(xué)研究院;2014年

10 吳方國(guó);富營(yíng)養(yǎng)化與POPs協(xié)同關(guān)系的多介質(zhì)環(huán)境化學(xué)模型[D];重慶大學(xué);2004年

,

本文編號(hào):2509537

資料下載
論文發(fā)表

本文鏈接:http://sikaile.net/kejilunwen/nykj/2509537.html


Copyright(c)文論論文網(wǎng)All Rights Reserved | 網(wǎng)站地圖 |

版權(quán)申明:資料由用戶a758f***提供,本站僅收錄摘要或目錄,作者需要?jiǎng)h除請(qǐng)E-mail郵箱bigeng88@qq.com