a国产,中文字幕久久波多野结衣AV,欧美粗大猛烈老熟妇,女人av天堂

黃土丘陵區(qū)深層土壤有機(jī)碳對(duì)土地利用變化的響應(yīng)

發(fā)布時(shí)間:2018-03-07 03:03

  本文選題:深層土壤 切入點(diǎn):有機(jī)碳儲(chǔ)量 出處:《中國科學(xué)院研究生院(教育部水土保持與生態(tài)環(huán)境研究中心)》2015年碩士論文 論文類型:學(xué)位論文


【摘要】:土地利用變化在全球碳平衡及氣候變化中起著重要作用。目前對(duì)黃土高原地區(qū)土壤有機(jī)碳庫雖然已經(jīng)進(jìn)行了大量卓有成效的研究工作,但絕大部分仍是以淺層有機(jī)碳含量或者有機(jī)碳庫大小作為研究對(duì)象,而近期一些研究表明,1m以下的深層土壤積聚的有機(jī)碳十分可觀。該區(qū)天然次生林轉(zhuǎn)變?yōu)槿斯ち旨稗r(nóng)田等植被破壞過程中,土壤有機(jī)碳變化的研究還鮮見報(bào)道,還不足以科學(xué)認(rèn)識(shí)該區(qū)土地利用變化對(duì)土壤有機(jī)碳的影響方式和程度。本文以黃土丘陵區(qū)子午嶺為研究區(qū),以天然喬木林、天然灌木林、人工喬木林、撂荒地、農(nóng)地5種不同土地利用類型為研究對(duì)象,以淺層(0~100cm)土壤為對(duì)照,研究深層土壤有機(jī)碳儲(chǔ)量和有機(jī)碳組分對(duì)土地利用變化響應(yīng)的程度、方式、機(jī)理,以及土地利用變化后年限與土壤有機(jī)碳的關(guān)系。并且對(duì)土壤溶解性有機(jī)碳遷移特征及其動(dòng)態(tài)變化進(jìn)行了研究,進(jìn)一步了解深層有機(jī)碳來源問題。研究取得以下主要結(jié)果:1.黃土丘陵子午嶺林區(qū)天然喬木林、天然灌木林、人工喬木林、撂荒地、農(nóng)地0~200cm有機(jī)碳儲(chǔ)量分別為134.65t?hm-2、96.23t?hm-2、124.98t?hm-2、76.03t?hm-2、82.75t?hm-2,深層(100~200cm)土壤有機(jī)碳儲(chǔ)量分別占0~200cm總有機(jī)碳儲(chǔ)量的33%、29%、31%、34%、42%。2.不同土地利用類型間0~200cm土壤有機(jī)碳含量有一定差異,以天然喬木林和人工林地最高,其次是天然灌木林地,撂荒地和農(nóng)田土壤有機(jī)碳含量最低。不同利用類型間淺層土壤有機(jī)碳含量差異顯著,但深層土壤有機(jī)碳含量差異不大。3.土地利用變化對(duì)土壤有機(jī)碳儲(chǔ)量影響顯著,淺層比深層變化更敏感。天然喬木林轉(zhuǎn)變?yōu)槿斯棠玖、天然喬木林轉(zhuǎn)變?yōu)檗r(nóng)田、天然灌木林轉(zhuǎn)變?yōu)榱袒牡丶稗r(nóng)田四種土地利用轉(zhuǎn)變方式導(dǎo)致淺層土壤有機(jī)碳儲(chǔ)量減少幅度為2%~48%,深層減少幅度為12%~22%。4.天然灌木林地轉(zhuǎn)變?yōu)檗r(nóng)田土壤有機(jī)碳儲(chǔ)量隨著開墾時(shí)間的增長而降低,開墾0~30年,有機(jī)碳含量儲(chǔ)量下降較快,降幅為31%。淺層(0~100cm)土壤有機(jī)碳儲(chǔ)量在開墾30~50年有略微下降,降幅為8%,50年后基本不變。而深層(100~200cm)土壤有機(jī)碳儲(chǔ)量變化幅度較小,介于4%~15%之間。5.不同土地利用類型土壤深層(60~200cm)活性有機(jī)碳占0~200cm活性有機(jī)碳含量的8%~51%。不同土地利用轉(zhuǎn)變方式不僅對(duì)淺層(0~60cm)土壤活性有機(jī)碳有影響,對(duì)深層(60~200cm)也有一定影響。天然喬木林轉(zhuǎn)變?yōu)槿斯棠玖、天然喬木林轉(zhuǎn)變?yōu)檗r(nóng)田、天然灌木林轉(zhuǎn)變?yōu)榱袒牡丶稗r(nóng)田四種土地利用轉(zhuǎn)變方式深層土壤易氧化性碳減少幅度為1%~21%;土壤微生物量碳減少幅度為8%~25%。6.土壤溶解性有機(jī)碳含量隨土壤剖面深度的增加而逐漸降低,與有機(jī)碳含量顯著相關(guān);淺層(0~100cm)和深層(100~200cm)溶解性有機(jī)碳含量分別占0~200cm土層總含量58%和42%。灌木林地DOC淋溶10d后土壤0~200cm整個(gè)土層DOC增加量增幅為23%;入滲30d的淺層(0~100cm)和深層(100~200cm)DOC分別僅增加5%和4%。
[Abstract]:Land use change plays an important role in global carbon balance and climate change. But most of them still study the content of shallow organic carbon or the size of organic carbon pool. Some recent studies have shown that the accumulation of organic carbon in the deep soil below 1 m is considerable. In the process of the natural secondary forest being transformed into artificial forest and farmland, there are few reports on the change of soil organic carbon. This paper takes Ziwuling of loess hilly area as the research area, takes natural tree forest, natural shrub forest, artificial arbor forest, abandoned land, etc. Five different land use types of farmland were studied, and the degree, mode and mechanism of deep soil organic carbon storage and organic carbon components response to land use change were studied. The relationship between soil organic carbon (SOC) and land use change (LUCF), and the characteristics and dynamic changes of soil dissolved organic carbon (SOC) transport were also studied. The main results of the study are as follows: 1. Natural Arbor Forest, Natural shrub Forest, artificial Arbor Forest, abandoned Land, and Agricultural Land (0 ~ 200cm) in the Loess Hilly Ziwuling Forest region are respectively 134.65 t ~ (-1)? Hm-2n 96.23t? Hm-2n 124.98t? Hm-2? 76.03t? Hm-2n 82.75t? The soil organic carbon reserves of 0 ~ 200cm were 3329 ~ 31C ~ (34) ~ (42cm) respectively. There were some differences in soil organic carbon contents between different land use types, among which the natural tree forest and artificial forest land were the highest, followed by natural shrub forest land, the soil organic carbon reserves of 0 ~ (200 ~ 2) cm were higher than that of the natural forest land, and the soil organic carbon storage was 100 ~ (100 ~ (200) cm) of the total organic carbon storage of 0 ~ (200 cm), respectively. The soil organic carbon content of abandoned land and farmland was the lowest. The content of organic carbon in shallow soil was significantly different among different utilization types, but there was no significant difference in organic carbon content in deep soil. 3. Land use change had a significant effect on soil organic carbon storage. The shallow layer is more sensitive than the deep layer change. The natural tree forest turns into the artificial tree forest, the natural tree forest turns into the farmland, The conversion of natural shrub forest to abandoned land and farmland has resulted in the decrease of soil organic carbon reserves in shallow layer by 248%, and in deep layer by 120.22.4. the natural shrub land is transformed into farmland soil organic carbon storage with the opening of soil organic carbon storage. With the increase of reclamation time, During the period of 0 ~ 30 years of reclamation, the content of organic carbon decreased rapidly, the decrease was 31%.) the soil organic carbon reserve decreased slightly from 30 to 50 years, the decrease was 8%, and after 50 years it was basically unchanged.) the change of soil organic carbon storage in the deep layer (100 ~ 100 cm) was relatively small. The content of active organic carbon in 0 ~ 200 cm soil is 80.51% of the total active organic carbon content of 0 ~ 200cm. Different land use transformation patterns not only affect the soil active organic carbon content in shallow layer (0 ~ (60) cm), but also have a significant effect on the soil organic carbon content of 0 ~ 200 cm in different land use types. Natural Arbor Forest is transformed into artificial Arbor Forest and Natural Arbor Forest turns into farmland. Conversion of natural shrub forest to abandoned land and farmland four types of land use transformation methods the extent of reduction of oxidizing carbon in deep soil is 1 / 21, and that of microbial biomass carbon in soil is 8 / 25.6.The content of dissolved organic carbon in soil varies with the depth of soil profile. Increasing and gradually decreasing, There was a significant correlation between organic carbon content and organic carbon content. The content of dissolved organic carbon (DOC) in the soil layer of 0 ~ 200cm was 58% and 42cm, respectively. After 10 days of DOC leaching in shrub land, the increase of DOC in the whole soil layer of 0 ~ 200cm was 23%, while that in the shallow layer of 30d infiltration was 5% and 47.The content of DOC in deep layer (100200cm) increased only 5% and 4cm, respectively.
【學(xué)位授予單位】:中國科學(xué)院研究生院(教育部水土保持與生態(tài)環(huán)境研究中心)
【學(xué)位級(jí)別】:碩士
【學(xué)位授予年份】:2015
【分類號(hào)】:S153.6;F301.2

【引證文獻(xiàn)】

相關(guān)會(huì)議論文 前1條

1 陳安冉;王祖?zhèn)?;土壤中水溶性有機(jī)碳研究進(jìn)展[A];2012中國環(huán)境科學(xué)學(xué)會(huì)學(xué)術(shù)年會(huì)論文集(第三卷)[C];2012年

,

本文編號(hào):1577639

資料下載
論文發(fā)表

本文鏈接:http://www.wukwdryxk.cn/jingjilunwen/nongyejingjilunwen/1577639.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7f8cb***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
亚洲国产一区二区三区在线观看| 中文文字幕一区二区三三| 欧美簧片| 社长ol丝袜人妻秘书| 少妇人妻nph| www一区二区三区| 亚洲免费成人| 变态另类zoz0另类| 内丘县| 中文无码人妻有码人妻中文字幕| 国产又色又爽又黄的视频在线| 亚洲性无码AV中文字幕| 人人妻人人爽人人澡人人| 高清视频大片免费观看| 日韩不卡手机视频在线观看| 欧美成A人片在线观看久| 扒开老师大腿猛进AAA片| 亚洲av电影| 国产女同网| 青青精品| 亚洲偷| 精品一区二区三区波多野结衣| 人人妻人人爽人人澡人人| 人人澡人人澡人人看添av| 87亚洲国产中文在线精品国自产拍 | 欧美无砖专区一中文字| 蜜臀精品国产高清在线观看| 欧美极品少妇×XXXBBB| 亚洲综合图色40p| 最近最新的日本字幕MV| 欧美激情综合网| 国产精品久久久久久久午夜片| 超碰97人妻| 国产成人精品高清在线观看93| 色综合另类小说图片区| 日本少妇内射视频播放舔| 国产欧美va欧美va香蕉在线| 欧美野性肉体狂欢大派对| 国产av综合第一页| ck电影网| 国产精品国产三级国产潘金莲|