Article(id=1208051028902126199, tenantId=1146029695717560320, journalId=1146123166801305609, issueId=1208051024368083510, articleNumber=null, orderNo=null, doi=10.12404/j.issn.1671-1815.2402718, pmid=null, cstr=null, oa=null, hot=null, price=null, onlineType=0, articleFormat=0, articleType=null, articleTypeStr=research-article, receivedDate=1713110400000, receivedDateStr=2024-04-15, revisedDate=1742140800000, revisedDateStr=2025-03-17, acceptedDate=null, acceptedDateStr=null, onlineDate=1765951409792, onlineDateStr=2025-12-17, pubDate=1751040000000, pubDateStr=2025-06-28, doiRegisterDate=null, doiRegisterDateStr=null, onlineIssueDate=1765951409792, onlineIssueDateStr=2025-12-17, onlineJustAcceptDate=null, onlineJustAcceptDateStr=null, onlineFirstDate=null, onlineFirstDateStr=null, sourceXml=null, magXml=null, createTime=1765951409792, creator=13701087609, updateTime=1765951409792, updator=13701087609, issue=Issue{id=1208051024368083510, tenantId=1146029695717560320, journalId=1146123166801305609, year='2025', volume='25', issue='18', pageStart='7455', pageEnd='7883', issueExtLink='null', onlineDate='null', pubDate='null', beforeIssueId=null, nextIssueId=null, price=null, status=1, issueComplete=1, articleOrder=1, issueType=-1, specialIssue=null, createTime=1765951408712, creator=13701087609, updateTime=1765951896766, updator=13701087609, preIssue=null, nextIssue=null, ext={EN=IssueExt(id=1208053071507198943, tenantId=1146029695717560320, journalId=1146123166801305609, issueId=1208051024368083510, language=EN, specialIssueTitle=, coverIllustrator=null, specialIssueEditor=, specialIssueAbout=), CN=IssueExt(id=1208053071507198944, tenantId=1146029695717560320, journalId=1146123166801305609, issueId=1208051024368083510, language=CN, specialIssueTitle=, coverIllustrator=null, specialIssueEditor=, specialIssueAbout=)}, issueFiles=null}, startPage=7778, endPage=7784, ext={EN=ArticleExt(id=1208051030248497868, articleId=1208051028902126199, tenantId=1146029695717560320, journalId=1146123166801305609, language=EN, title=Calculation of Minimum Water Demand of Vegetation in the Lower Reaches of Tarim River Based on Potential Natural Vegetation, columnId=1156262735643005297, journalTitle=Science Technology and Engineering, columnName=Papers·Hydraulic Engineering, runingTitle=null, highlight=null, articleAbstract=
In order to solve the contradiction between ecological maintenance and agricultural production water demand, the minimum water demand for ecological restoration in arid areas was determined. The lower reaches of the Tarim River were selected as the typical study area. Suitable areas for vegetation growth were determined through the PNV (potential natural vegetation) simulation method, while the suitable growth ranges and distribution areas of trees, shrubs, and grasslands were analyzed. The minimum ecological water demand for the lower reaches of the Tarim River was calculated by the multi-year evapotranspiration data from the AET dataset. The results show as follows. The PNV results obtaine in the lower reaches of the Tarim River are dominated by shrubs, forests and grasslands are highly dependent on water resources, mainly distributed around river channels. The forest and grassland in the study area show high growth potential, while the shrub distribution areas far from the river show a degradation trend. According to PNV simulation results, the ecological water demand in the lower reaches of Tarim River is about 11 279.23×104 m3, of which shrubs account for the largest proportion, while woodland and grassland account for 7.4% and 5.36% respectively due to their small areas. The research results provide a new method for ecological restoration and determination of water transport capacity in arid areas, which can clarify the scope of ecological restoration and vegetation types in the basin, and contribute to the management and optimal allocation of regional water resources.
, correspAuthors=Yun-fei LIU, authorNote=null, correspAuthorsNote=null, copyrightStatement=null, copyrightOwner=null, extLink=null, articleAbsUrl=null, sourceXml=null, magXml=null, pdfUrl=null, pdf=null, pdfFileSize=null, pdfExtLink=null, richHtmlUrl=null, mobilePdfUrl=null, reviewReport=null, pdfFirstPage=null, abstractGraph=null, abstractGraphContent=null, abstractVideo=null, citation=null, cebUrl=null, magXmlContent=null, mapNumber=null, authorCompany=null, fund=null, authors=null, authorsList=Zhen-wen WANG, Biao CHEN, Yun-fei LIU), CN=ArticleExt(id=1208051031720698710, articleId=1208051028902126199, tenantId=1146029695717560320, journalId=1146123166801305609, language=CN, title=基于潜在自然植被的塔里木河下游植被最小需水量计算, columnId=1156262735810777459, journalTitle=科学技术与工程, columnName=论文·水利工程, runingTitle=null, highlight=null, articleAbstract=
为解决生态维护与农业生产需水量之间的矛盾,厘定干旱区生态修复最小需水量。以塔里木河下游为典型研究区,通过潜在自然植被(potential natural vegetation, PNV)模拟的方法,得出植被生长适宜区域,并对乔木、灌木和草地的适宜生长区域和面积进行了分析,结合AET数据集的多年蒸散发结果,对塔里木河下游的最小需水量进行了计算,结果表明:塔河下游得出的PNV结果以灌木为主,林地和草地对水资源的依赖程度较高,主要分布在河道周边;研究区内的林地和草地均表现出较高的生长潜力,而距离河道较远的灌木分布区域表现出退化趋势;根据PNV模拟结果计算出的塔里木河下游生态需水量约为11 279.23×104 m3,其中灌木占比最大,而林地和草地由于面积较小,需水量占比分别为7.4%和5.36%。研究结果为干旱区流域生态修复及输水量的确定提供了新的方法,能够明确流域的生态修复范围和植被种类,并有助于区域水资源的管理和优化配置。
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1 Xinjiang Railway Survey and Design Institute Co., Ltd., Urumqi 830011, China, bio=null, bioImg=null, bioContent=null, aboutCorrespAuthor=null), CN=AuthorExt(id=1208085586104128299, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, authorId=1208085584657093372, language=CN, stringName=王振文, firstName=null, middleName=null, lastName=null, prefix=null, suffix=null, authorComment=null, nameInitials=null, affiliation=null, department=null, xref=
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1 新疆铁道勘察设计院有限公司, 乌鲁木齐 830011, bio={"content":"
王振文(1967—),男,汉族,新疆乌鲁木齐人,高级工程师。研究方向:水文与生态地理。E-mail:76990417@qq.com。
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王振文(1967—),男,汉族,新疆乌鲁木齐人,高级工程师。研究方向:水文与生态地理。E-mail:76990417@qq.com。
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2 中国科学院新疆生态与地理研究所, 乌鲁木齐 830011, bio=null, bioImg=null, bioContent=null, aboutCorrespAuthor=null)}, companyList=[AuthorCompany(id=1208085584451572452, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, xref=2, ext=[AuthorCompanyExt(id=1208085584476738277, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, companyId=1208085584451572452, language=EN, country=null, province=null, city=null, postcode=null, companyName=null, departmentName=null, remark=
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2 中国科学院新疆生态与地理研究所, 乌鲁木齐 830011)])])], keywords=[Keyword(id=1208085587257562013, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, orderNo=1, keyword=ecological water demand), Keyword(id=1208085587366613926, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, orderNo=2, keyword=arid area watershed), Keyword(id=1208085587500831668, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, orderNo=3, keyword=PNV (potential natural vegetation)), Keyword(id=1208085587651826631, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, orderNo=4, keyword=evapotranspiration), Keyword(id=1208085587807015900, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, orderNo=1, keyword=生态需水量), Keyword(id=1208085587958010856, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, orderNo=2, keyword=干旱区流域), Keyword(id=1208085588079645686, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, orderNo=3, keyword=PNV(potential natural vegetation)), Keyword(id=1208085588234833922, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, orderNo=4, keyword=蒸散发)], refs=[Reference(id=1208085592626270536, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, doi=null, pmid=null, pmcid=null, year=2019, volume=null, issue=null, pageStart=null, pageEnd=null, url=null, language=null, rfNumber=[1], rfOrder=0, authorNames=刘毅, journalName=塔里木盆地南缘绿洲灌区地表水与地下水联合利用研究, refType=null, unstructuredReference=刘毅.
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Location and land use type of the downstream of the Tarim River in 2020, figureFileSmall=Off1UMGIP85PjTTg2uIHfQ==, figureFileBig=N1HqS9LZtob+99Rnv6O2Fw==, tableContent=null), ArticleFig(id=1208085588612321330, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=图1, caption=
2020年塔里木河下游土地利用分类, figureFileSmall=Off1UMGIP85PjTTg2uIHfQ==, figureFileBig=N1HqS9LZtob+99Rnv6O2Fw==, tableContent=null), ArticleFig(id=1208085588830425157, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, label=Fig.2, caption=
Potential spatial distribution characteristics of forest, shrub and grass in the downstream of the Tarim River, figureFileSmall=3/tawD/PK5zoGnKstkOctQ==, figureFileBig=eLiN/joszBz52f/m95skeQ==, tableContent=null), ArticleFig(id=1208085588994003034, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=图2, caption=
塔河下游林、灌、草潜在空间分布特征 其他是指不透水地面和数据缺失区域
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Spatial distribution of PNDVI of forest, shrub and grass in the downstream of the Tarim River, figureFileSmall=481lXTzCWPh3XyIn+gabnA==, figureFileBig=ljszRmV3MZp8ElKUM938eA==, tableContent=null), ArticleFig(id=1208085589400850557, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=图3, caption=
塔河下游林地、灌木、草地的PNDVI空间分布, figureFileSmall=481lXTzCWPh3XyIn+gabnA==, figureFileBig=ljszRmV3MZp8ElKUM938eA==, tableContent=null), ArticleFig(id=1208085590722056336, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, label=Table 1, caption=
Environmental factor variables
, figureFileSmall=null, figureFileBig=null, tableContent=
| 编号 | 描述 | 编号 | 描述 |
| bio1 | 年均温/℃ | bio17 | 最干季降水量/mm |
| bio2 | 昼夜温差月均温℃ | bio18 | 最暖季降水量/mm |
| bio3 | 等温性/% | bio19 | 最冷季降水量/mm |
| bio4 | 温度季节变化标准差/% | clay | 黏粒含量/(g·kg-1) |
| bio5 | 最暖月最高温度/℃ | sand | 砂粒含量/(g·kg-1) |
| bio6 | 最冷月最低温度/℃ | silt | 粉粒含量/(g·kg-1) |
| bio7 | 年均温变化范围/℃ | sk | 距水库距离/m |
| bio8 | 最湿季均温/℃ | hd | 距河道距离/m |
| bio9 | 最干季均温/℃ | DEM | 数字高程/m |
| bio10 | 最暖季均温/℃ | GW04 | 塔河4月地下水位/m |
| bio11 | 最冷季均温/℃ | GW05 | 塔河5月地下水位/m |
| bio12 | 年均降水量/mm | GW06 | 塔河6月地下水位/m |
| bio13 | 最湿月降水量/mm | GW07 | 塔河7月地下水位/m |
| bio14 | 最干月降水量/mm | GW08 | 塔河8月地下水位/m |
| bio15 | 降水量变异系数/% | GW09 | 塔河9月地下水位/m |
| bio16 | 最湿季降水量/mm | GWD | |
), ArticleFig(id=1208085590881439899, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=表1, caption=
环境因子变量表
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| 编号 | 描述 | 编号 | 描述 |
| bio1 | 年均温/℃ | bio17 | 最干季降水量/mm |
| bio2 | 昼夜温差月均温℃ | bio18 | 最暖季降水量/mm |
| bio3 | 等温性/% | bio19 | 最冷季降水量/mm |
| bio4 | 温度季节变化标准差/% | clay | 黏粒含量/(g·kg-1) |
| bio5 | 最暖月最高温度/℃ | sand | 砂粒含量/(g·kg-1) |
| bio6 | 最冷月最低温度/℃ | silt | 粉粒含量/(g·kg-1) |
| bio7 | 年均温变化范围/℃ | sk | 距水库距离/m |
| bio8 | 最湿季均温/℃ | hd | 距河道距离/m |
| bio9 | 最干季均温/℃ | DEM | 数字高程/m |
| bio10 | 最暖季均温/℃ | GW04 | 塔河4月地下水位/m |
| bio11 | 最冷季均温/℃ | GW05 | 塔河5月地下水位/m |
| bio12 | 年均降水量/mm | GW06 | 塔河6月地下水位/m |
| bio13 | 最湿月降水量/mm | GW07 | 塔河7月地下水位/m |
| bio14 | 最干月降水量/mm | GW08 | 塔河8月地下水位/m |
| bio15 | 降水量变异系数/% | GW09 | 塔河9月地下水位/m |
| bio16 | 最湿季降水量/mm | GWD | |
), ArticleFig(id=1208085591095349423, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, label=Table 2, caption=
Table of NDVI value and vegetation coverage level
, figureFileSmall=null, figureFileBig=null, tableContent=
| NDVI | 植被盖度/% | 植被覆盖水平 |
| NDVI0~1 | NDVI0~255 |
| >0.50 | >191 | >60 | 高植被覆盖 |
| 0.23~0.49 | 156~190 | 30~60 | 中植被覆盖 |
| 0.09~0.22 | 139~155 | 15~30 | 低值被覆盖 |
| <0.08 | <138 | <15 | 裸地或极稀疏植被 |
), ArticleFig(id=1208085591263121600, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=表2, caption=
NDVI值与植被覆盖水平的对应表
, figureFileSmall=null, figureFileBig=null, tableContent=
| NDVI | 植被盖度/% | 植被覆盖水平 |
| NDVI0~1 | NDVI0~255 |
| >0.50 | >191 | >60 | 高植被覆盖 |
| 0.23~0.49 | 156~190 | 30~60 | 中植被覆盖 |
| 0.09~0.22 | 139~155 | 15~30 | 低值被覆盖 |
| <0.08 | <138 | <15 | 裸地或极稀疏植被 |
), ArticleFig(id=1208085591426699467, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, label=Table 3, caption=
Actual and potential distribution area and percentage of forest, shrub and grass in the downstream of the Tarim River
, figureFileSmall=null, figureFileBig=null, tableContent=
植被 类型 | ANV | | PNV |
| 面积/km2 | 占比/% | 面积/km2 | 占比/% |
| 林地 | 0.798 | 0.049 | | 38.837 | 2.40 |
| 草地 | 0.692 | 0.043 | | 23.570 | 1.45 |
| 灌木 | 808.122 | 49.85 | | 641.497 | 39.57 |
| 裸地 | 689.534 | 42.54 | | 795.242 | 49.06 |
), ArticleFig(id=1208085591560917210, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=表3, caption=
塔河下游实际和潜在林、灌、草分布面积和百分比
, figureFileSmall=null, figureFileBig=null, tableContent=
植被 类型 | ANV | | PNV |
| 面积/km2 | 占比/% | 面积/km2 | 占比/% |
| 林地 | 0.798 | 0.049 | | 38.837 | 2.40 |
| 草地 | 0.692 | 0.043 | | 23.570 | 1.45 |
| 灌木 | 808.122 | 49.85 | | 641.497 | 39.57 |
| 裸地 | 689.534 | 42.54 | | 795.242 | 49.06 |
), ArticleFig(id=1208085591711912173, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, label=Table 4, caption=
Area and percentage of actual and potential NDVI of forest, shrub and grass in the downstream of the Tarim River
, figureFileSmall=null, figureFileBig=null, tableContent=
植被 类型 | 植被覆盖 程度 | ANDVI | | PNDVI |
| 面积/km2 | 占比/% | 面积/km2 | 占比/% |
| 林地 | 高植被覆盖 | 0.010 | 0.000 6 | | 4.535 | 0.280 |
| 中植被覆盖 | 0.239 | 0.015 | | 16.151 | 0.996 |
| 低植被覆盖 | 0.365 | 0.023 | | 17.153 | 1.058 |
| 其他 | 1 620.366 | 99.962 | | 1 583.141 | 97.666 |
| 灌木 | 高植被覆盖 | 1.085 4 | 0.067 | | 56.274 | 3.472 |
| 中植被覆盖 | 93.450 | 5.765 | | 63.235 | 3.901 |
| 低植被覆盖 | 332.628 | 20.520 | | 393.892 | 24.299 |
| 其他 | 1 193.817 | 73.648 | | 1 107.579 | 68.328 |
| 草地 | 高植被覆盖 | 0.002 | 0.000 1 | | 6.983 | 0.431 |
| 中植被覆盖 | 0.084 | 0.005 | | 7.151 | 0.441 |
| 低植被覆盖 | 0.297 | 0.018 | | 9.410 | 0.580 |
| 其他 | 1 620.597 | 99.976 | | 1 597.436 | 98.548 |
), ArticleFig(id=1208085591804186871, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=表4, caption=
塔河下游林、灌、草实际与潜在NDVI的面积和百分比
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植被 类型 | 植被覆盖 程度 | ANDVI | | PNDVI |
| 面积/km2 | 占比/% | 面积/km2 | 占比/% |
| 林地 | 高植被覆盖 | 0.010 | 0.000 6 | | 4.535 | 0.280 |
| 中植被覆盖 | 0.239 | 0.015 | | 16.151 | 0.996 |
| 低植被覆盖 | 0.365 | 0.023 | | 17.153 | 1.058 |
| 其他 | 1 620.366 | 99.962 | | 1 583.141 | 97.666 |
| 灌木 | 高植被覆盖 | 1.085 4 | 0.067 | | 56.274 | 3.472 |
| 中植被覆盖 | 93.450 | 5.765 | | 63.235 | 3.901 |
| 低植被覆盖 | 332.628 | 20.520 | | 393.892 | 24.299 |
| 其他 | 1 193.817 | 73.648 | | 1 107.579 | 68.328 |
| 草地 | 高植被覆盖 | 0.002 | 0.000 1 | | 6.983 | 0.431 |
| 中植被覆盖 | 0.084 | 0.005 | | 7.151 | 0.441 |
| 低植被覆盖 | 0.297 | 0.018 | | 9.410 | 0.580 |
| 其他 | 1 620.597 | 99.976 | | 1 597.436 | 98.548 |
), ArticleFig(id=1208085591938404610, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=EN, label=Table 5, caption=
Water demand of forest, shrub and grass with different coverage in the lower reaches of Tarim River
, figureFileSmall=null, figureFileBig=null, tableContent=
植被 类型 | 植被覆盖 程度 | 面积/ km2 | 蒸散发/mm | | 需水量/104m3 |
| 平均值 | 标准差 | 平均值 | 标准差 |
| 林地 | 高植被覆盖 | 4.54 | 266.35 | 33.6 | | 120.79 | 15.24 |
| 中植被覆盖 | 16.15 | 232.17 | 31.33 | | 374.98 | 50.6 |
| 低植被覆盖 | 17.15 | 197.49 | 42.13 | | 338.75 | 72.27 |
| 灌木 | 高植被覆盖 | 56.27 | 232.44 | 27.41 | | 1308.03 | 154.25 |
| 中植被覆盖 | 63.24 | 204.52 | 32.55 | | 1 293.28 | 205.83 |
| 低植被覆盖 | 393.89 | 184.29 | 25.19 | | 7 259.04 | 992.21 |
| 草地 | 高植被覆盖 | 6.98 | 292.35 | 52.23 | | 204.15 | 36.47 |
| 中植被覆盖 | 7.15 | 252.17 | 35.81 | | 180.33 | 25.61 |
| 低植被覆盖 | 9.41 | 212.41 | 44.72 | | 199.88 | 42.08 |
| 总计 | | 11 279.23 | 1 594.56 |
), ArticleFig(id=1208085592143925525, tenantId=1146029695717560320, journalId=1146123166801305609, articleId=1208051028902126199, language=CN, label=表5, caption=
塔河下游不同盖度林、灌、草需水量
, figureFileSmall=null, figureFileBig=null, tableContent=
植被 类型 | 植被覆盖 程度 | 面积/ km2 | 蒸散发/mm | | 需水量/104m3 |
| 平均值 | 标准差 | 平均值 | 标准差 |
| 林地 | 高植被覆盖 | 4.54 | 266.35 | 33.6 | | 120.79 | 15.24 |
| 中植被覆盖 | 16.15 | 232.17 | 31.33 | | 374.98 | 50.6 |
| 低植被覆盖 | 17.15 | 197.49 | 42.13 | | 338.75 | 72.27 |
| 灌木 | 高植被覆盖 | 56.27 | 232.44 | 27.41 | | 1308.03 | 154.25 |
| 中植被覆盖 | 63.24 | 204.52 | 32.55 | | 1 293.28 | 205.83 |
| 低植被覆盖 | 393.89 | 184.29 | 25.19 | | 7 259.04 | 992.21 |
| 草地 | 高植被覆盖 | 6.98 | 292.35 | 52.23 | | 204.15 | 36.47 |
| 中植被覆盖 | 7.15 | 252.17 | 35.81 | | 180.33 | 25.61 |
| 低植被覆盖 | 9.41 | 212.41 | 44.72 | | 199.88 | 42.08 |
| 总计 | | 11 279.23 | 1 594.56 |
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