基于光合法和生物量法分析塔里木沙漠公路防护林带碳汇估算差异性
Differences in carbon sink estimation between photosynthetic and biomass methods in the Tarim Desert Highway shelterbelt
通讯作者: 王克林(1989-),男,贵州松桃人,高级工程师,研究方向为新能源,(E-mail)wangkl-tlm@petrochina.com.cn
收稿日期: 2024-01-15
| 基金资助: |
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Corresponding authors: WANG Kelin (1989-), male, from Songtao, Guizhou, senior engineer, research direction: organic chemistry and ecological restoration, (E-mail)wangkl-tlm@petrochina.com.cn
Received: 2024-01-15
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作者简介 About authors
李汝勇(1966-),男,河北南皮人,教授级高级工程师,研究方向为新能源,(E-mail)liry-tlm@petrochina.com.cn
【目的】研究基于光合法和生物量法分析塔里木沙漠公路防护林带碳汇估算差异性,为干旱荒漠区人工林管护和碳储量的评估提供科学依据。【方法】以新疆塔克拉玛干沙漠公路沿线人工防护林为研究对象,对比光合速率模型和生物量模型,估算防护林带3种主要建林植物各自光合速率及筛选最优生物量模型,进而估算其固碳能力及碳储量。【结果】3种植物在光合固碳模型中,单位叶面积固碳量差异显著,表现为梭梭 > 沙拐枣 > 柽柳;3种植物生物量最优模型均为幂函数,预测值与实测值回归决定系数在90%以上。光合固碳法估算得到的沙漠公路防护林带总固碳量为567 431.68 t,生物量法估算的值为565 083.75 t,2种方法估算得到的固碳量相当。【结论】3种植物固氮量差异显著(梭梭 > 沙拐枣 > 柽柳),模型效果精确可靠。
关键词:
【Objective】 Desert highway shelterbelts play a major role in wind prevention and sand fixation, as well as oxygen release and carbon fixation. By investigating vegetation along the Tarim Desert Highway and obtaining corresponding measured data, this study aims to further reveal the ecological and environmental effects and artificial ecosystem service functions of desert highway shelterbelts, providing a scientific basis for artificial forest management and carbon storage assessment in arid desert areas. 【Methods】 In this study, we compared the photosynthetic rate model with the biomass model to estimate the photosynthetic rate and the optimal biomass model of each of the three main forest-building plants in the shelterbelt, and then estimated their carbon sinksink capacity and carbon storage, taking the planted shelterbelt along the highway in the Tarim Desert as an object of study. 【Results】 There were significant differences in carbon fixation per unit leaf area among the three plants in the photosynthetic carbon fixation model, which were in the order of Haloxylon ammodendron > Calligonum mongolicum > Tamarix ramosissima. The optimal biomass models of the three plants were all power functions. The validation results showed that the regression determination coefficients between the predicted and measured values exceeded 90%, indicating high precision and reliability of the models. The total carbon sfixation of the desert highway shelterbelt estimated by the photosynthetic method was 567,431.68 tons, and the value estimated by the biomass method was 565,083.75 tons, indicating that the carbon sink estimated by the two methods was comparable. 【Conclusion】 There were significant differences in nitrogen fixation among the 3 species(Haloxylon ammodendron > Calligonum mongolicum > Tamarix ramosissima),indicating high precision and reliability of the models.
Keywords:
本文引用格式
李汝勇, 任久明, 雷霆, 王克林, 刘鹏程, 李江涛.
LI Ruyong, REN Jiuming, LEI Ting, WANG Kelin, LIU Pengcheng, LI Jiangtao.
0 引言
【研究意义】森林通过固碳释氧功能缓解气候变化,林业碳汇研究的关注度日益提升[1-2]。森林作为陆地生态系统的主体,是大气CO2重要的吸收汇。除依靠天然林的自我恢复外更需依靠人工林发展才能与气候变化相适应[3]。人工造林通过增加森林面积、提升森林蓄积量,进而提升森林生态系统碳储量。以灌木为主体植被类型的干旱和半干旱地区约占世界陆地面积的三分之一,是森林生态系统的重要组成部分,在森林固碳和缓解全球气候变化发挥着重要作用[4]。【前人研究进展】我国森林面积达到2.08×108 hm2,其中人工林保存面积达6 933×104 hm2,占全国林地面积的36%,是全球森林资源增长最快的国家[5-6]。发展林草碳汇面临森林面积的增加难度加大[7]。【本研究切入点】塔里木油田公司目前绿化面积达到4 300 hm2左右,其中主要的沙漠公路绿化面积约3 100 hm2[8]。但有关沙漠公路防护林与碳相关的研究文献较少且均为土壤碳分布方面的,而人工林生态系统固碳能力和碳储量的相关研究尚未见报道。植被固碳方面的研究大多集中在森林,需针对荒漠地区灌丛的固碳研究,尤其是对干旱荒漠地区人工防护林的。需研究基于光合法和生物量法分析塔里木沙漠公路防护林带碳汇估算差异性。【拟解决的关键问题】采用常用光合法和生物量法,结合实测数据分析两种方法的差异性,研究并对比2种方法对碳储量的计算是否一致,为沙漠人工林生态系统固碳能力和碳储量评估提供科学可靠的参考。
1 材料与方法
1.1 材料
以新疆塔里木沙漠公路(37°~42°N和82°~85°E)[9]沿线人工防护林为研究对象。年降水量11~50 mm,潜在蒸散量高达3 638.6 mm;年平均气温12.7℃,极端最高气温可达45.6℃,极端最低气温为-22.2℃[10];年日照时数累计为2 854.2 h,年平均风速2.5 m/s,最大瞬时风速为24 m/s,年起沙风时数550~800 h,浮尘扬沙天气频繁[11]。沙漠公路其防护林带全长436 km,其呈南北走向,贯穿整个塔克拉玛干沙漠,防护林带植被群落成活率稳定时长,以柽柳(Tamarix chinensis)、梭梭(Haloxylon ammodendron)和沙拐枣(Calligonum mongolicum)等适应性强、耐风蚀、耐旱、耐沙埋的木本植物作为主要建设树种[12]。
1.2 方法
1.2.1 样本采集
2023年5月中旬采样,沿沙漠公路从北向南均匀设置10个样地S1~S10,每个样地尺寸为50 m×50 m,样地之间间隔为45 km。在每个样地内设置一个10 m×10 m的样方,在每个样方内随机选择个体大小接近,生长健康的沙拐枣、柽柳和梭梭各3棵重复测量其株高(Height,H)、冠幅直径(Crown length,L)、冠幅面积(Canopy,C)和光合作用参数(采用便携式光合测定系统LI-6400XT,LI-COR,USA),总计270株。表1
表1 样方植被特征
Tab.1
| 样方 编号 Sample number | 植被频度 Vegetation frequency(%) | 平均 株高 Average plant height (m) | 平均冠幅 Average crown width (m) | 平均 胸径 Average breast diameter (cm) | 坐标 Coordinate | 海拔 Altitude (m) | ||||
|---|---|---|---|---|---|---|---|---|---|---|
| 梭梭 Haloxylon ammod- endron | 沙拐枣 Calligonum mongolicum | 柽柳 Tamarix chinensis | 东西 East and West | 南北 South and North | 经度 E Longitude | 纬度 N Latitude | ||||
| S1 | 54.85 | 10.30 | 34.85 | 1.47 | 2.01 | 1.96 | 4.29 | 84°18'2.41″ | 40°45'15.64″ | 932 |
| S2 | 60.54 | 37.90 | 1.56 | 1.93 | 2.04 | 2.05 | 5.77 | 84°20'11.11″ | 40°10'40.40″ | 951 |
| S3 | 78.66 | 19.00 | 2.34 | 1.84 | 2.31 | 1.94 | 3.28 | 83°59'58.32″ | 39°35'13.45″ | 1 020 |
| S4 | 76.56 | 13.68 | 9.76 | 1.79 | 1.89 | 1.96 | 2.74 | 83°43'55.20″ | 39°14'27.94″ | 1 066 |
| S5 | 62.43 | 35.50 | 2.07 | 2.04 | 2.05 | 1.88 | 3.23 | 83°35'29.07″ | 39°0'41.45″ | 1 096 |
| S6 | 75.65 | 18.81 | 5.54 | 1.15 | 1.78 | 1.56 | 1.92 | 83°26'41.32″ | 38°47'27.80″ | 1 142 |
| S7 | 70.60 | 22.00 | 7.40 | 1.19 | 1.35 | 1.54 | 2.56 | 83°16'35.85″ | 38°32'41.31″ | 1 164 |
| S8 | 67.85 | 30.95 | 1.20 | 1.67 | 2.02 | 1.84 | 2.77 | 83°8'27.49″ | 38°10'50.59″ | 1 217 |
| S9 | 72.50 | 24.22 | 3.28 | 1.16 | 1.24 | 1.30 | 1.82 | 83°1'20.77″ | 37°49'52.84″ | 1 269 |
| S10 | 72.68 | 14.50 | 12.82 | 1.99 | 2.05 | 1.70 | 4.31 | 82°54'17.15″ | 37°39'24.41″ | 1 314 |
在每个50 m×50 m每个样方中取1株植物整株连根尽可能完全挖出,将植株分成根、干、枝、叶4部分,随后将其带回实验室,把样品放入烘箱用105°C烘10 min杀青,85°C烘干至恒重,分别称取植株各部分的干重,其和为该植株总生物量,作为检验生物量模型的实际生物量值。
1.2.2 光合固碳法
采用便携式光合测定系统分别对10个样方内待测植株的净光合速率和叶片温度进行测定,选择2 cm×3 cm的标准叶室,使用自然光辐射(以研究区当日的辐射强度为准)。每天8:00~18:00,每隔2 h测定1次。每棵植株测3次作为重复,每次测量记录5个瞬时值,分别计算各样方内3种不同植株的平均值。
根据每种植物净光合速率日变化曲线,采用简单积分法计算测试植物在测定当日的净同化量[13]。
P=Σ
式中,P为测定日单位叶面积的净同化总量(mmol/(m2·d));pi为初测点的瞬时光合作用速率;pi+1为i+1测点的瞬时光合作用速率(μmol/(m2·s));ti为初测点的瞬时时间;ti+1为t+1测点的时间(h);j为测试次数;3 600为3 600 s/h;1 000为1 mmol 等于1 000 μmol。
1.2.3 生物量模型建立和检验
一次函数经验公式:
W=a+bX.
指数函数经验公式:
W=aebX.
幂函数经验公式:
W=aXb.
式中,W表示生物量;a、b、c为方程拟合参数;e为自然对数的底;X为自变量(LH和V)。
采用预测值与实测值的回归决定系数R2、平均相对误差(RMA)和总相对误差(RS)检验[17]。选用3种灌木树种的部分预测值和实测值进行回归分析。
总相对误差:
RMA=
平均相对误差:
RS=
式中,Xi代表实测值;Xi代表预测值;n代表样本数量。
1.2.4 生物量固碳法
通过碳储量与生物量的关系(生物量乘以含碳率),估算人工林群落植被碳储量[18],植被碳储量公式:
Q=0.5W总.
式中,Q为碳储量(t);W总为全株生物量(t);采用IPCC推荐的灌木林含碳率平均值0.50[19]。
生物量法固碳计算公式:
G碳=3.67Q.
式中,GC为固碳量(t);CO2与C的摩尔质量比约为3.67。
1.3 数据处理
数据使用Microsoft Office 2016(Microsoft,Washington,USA),整理数据并制表。采用单因素方差分析中的最小显著差异法(LSD)进行分析比较,当P>0.05为无显著差异;用线性回归模拟植被特征因子与植株总生物量方程,利用F检验和t检验对方程进行筛选;数据处理在SPSS 24.0(IBM,New York,USA)中完成,使用Origin 2022(OriginLab,Massachusetts,USA)绘制图片。
2 结果与分析
2.1 沙漠公路防护林带3种木本植物光合速率日变化特征
研究表明,3种沙漠公路防护林带木本植物的光合速率日变化均呈明显的“单峰”曲线,峰值出现在12:00左右,其中柽柳的峰值光合速率最高,梭梭与沙拐枣在不同时间点交替变化趋势,两者的光合速率日变化无明显差异。柽柳的日平均光合速率和单位叶面积固碳量明显高于梭梭和沙拐枣(P<0.05),而梭梭和沙拐枣之间的差异则不显著(P>0.05) 。图1
图1
图1
沙漠公路防护林带3种木本植物光合速率日变化特征、日平均光合速率及固碳量比较
Fig.1
Comparisons of diurnal variation characteristics of photosynthetic rate, daily average photosynthetic rate and carbon sequestration of three kinds of woody plants in desert highway shelter forest
2.2 生物量固碳
2.2.1 生物量模型挑选及检验
研究表明,3种灌木生物量最优生物量模型均为幂函数;V是梭梭和柽柳生物量方程的最佳预测变量,LH是沙拐枣生物量方程的最佳预测变量,3种灌木的生物量最优估算模型如下:柽柳生物量估算最优模型:W = 2.866 3V0.726 5;梭梭生物量估算最优模型:W = 2.798 2V0.973 6;沙拐枣生物量估算最优模型:W = 6.034 9(LH)0.769 6。
表2 沙漠公路防护林带3种木本植物生物量回归模型参数
Tab.2
| 模型 Model | 树种 Tree species | 自变量 Independent variable | R2 | SEE | P |
|---|---|---|---|---|---|
| 一次函数 W=a+bX | 柽柳 | LH | 0.934 | 0.270 | <0.001 |
| 梭梭 | 0.617 | 2.543 | <0.001 | ||
| 沙拐枣 | 0.912 | 0.333 | 0.036 | ||
| 柽柳 | V | 0.937 | 0.170 | <0.001 | |
| 梭梭 | 0.925 | 0.225 | <0.001 | ||
| 沙拐枣 | 0.875 | 0.273 | 0.002 | ||
| 指数函数 W=aebX | 柽柳 | LH | 0.661 | 3.753 | 0.002 |
| 梭梭 | 0.610 | 2.732 | 0.1518 | ||
| 沙拐枣 | 0.861 | 1.200 | <0.001 | ||
| 柽柳 | V | 0.902 | 1.155 | <0.001 | |
| 梭梭 | 0.880 | 2.719 | 0.003 | ||
| 沙拐枣 | 0.899 | 2.231 | 0.011 | ||
| 幂函数 W=aXb | 柽柳 | LH | 0.931 | 0.862 | <0.001 |
| 梭梭 | 0.898 | 0.833 | <0.001 | ||
| 沙拐枣 | 0.956 | 0.742 | <0.001 | ||
| 柽柳 | V | 0.941 | 0.634 | <0.001 | |
| 梭梭 | 0.965 | 0.929 | <0.001 | ||
| 沙拐枣 | 0.799 | 0.923 | <0.001 |
注:C为冠幅面积(m2)、L为冠幅宽度(m)、H为株高(m)和V = C·H为植株体积(m3),R2为判别系数、SEE为估计标准误、P为回归检验显著水平。
Note:C is crown area (m2), L is crown width (m), H is plant height (m) and V = C·H is plant volume (m3), R2 is discriminant coefficient, SEE is estimation standard error, P is regression test significance level
图2
图2
生物量模型拟合
注:C为冠幅面积( m2)、L为冠幅直径(m)、H为株高(m)和V = C·H为植株体积( m3);a、b为一次函数模型;c、d为指数函数模型;e、f为幂函数模型
Fig.2
Biomass model fitting
Note: C is crown area ( m2), L is crown width (m), H is plant height (m) and V = C·H is plant volume ( m3); a, b are linear function models ; c and d are exponential function models ; e and f are power function models
2.2.2 生物量模型固碳量
研究表明,单株固碳量上3种植物有显著差异,并且梭梭 > 沙拐枣 > 柽柳。
2.3 光合法与生物量法固碳量比较
研究表明,3种植物的单位叶面积年固碳量,柽柳 > 沙拐枣 > 梭梭,但梭梭依靠种植面积最广的优势成为固碳量最高的物种(25 181.52 t/a),远超沙拐枣与柽柳年固碳量之和。沙漠公路建林16年后整体防护林带的总固碳量约为567 431.68 t。3种植物的个体生物量存在显著差异,其固碳能力也存在显著差异。其中,柽柳单株生物量为8.72 kg,沙拐枣单株生物量为11.67 kg,梭梭单株生物量为19.62 kg,与其他2种植物相比,梭梭具有更大的单株生物量并且具有更大的固碳能力。防护林内柽柳为147×104株,梭梭为1 260×104株,沙拐枣为413×104株,柽柳总固碳量23 500.4 t,梭梭总固碳量453 222 t,沙拐枣88 361.35 t,防护林总固碳量约为565 083.75 t。防护林总固碳量约为567 431.68 t,生物量法估算防护林总固碳量约为565 083.75 t,光合固碳法所得数值略高于生物量法,估算结果差异不大,均具有一定的参考价值及科学性。表3~4,图3~4
表3 沙漠公路防护林带3种木本植物光合固碳法估算总固碳量
Tab.3
| 树种 Tree species | 单位叶面积年固碳量 Carbon sequestration per unit area per year ( kg/(m2·a)) | 植被覆盖面积 The area covered by vegetation (hm2) | 种植时长 Planting duration (a) | 年均固碳量 Average annual carbon sequestration ( t/a) | 总固碳量 Total carbon sequestration (t) |
|---|---|---|---|---|---|
| 柽柳Tamarix chinensis | 2.20 | 166.06 | 16 | 3 653.32 | 58 453.12 |
| 梭梭Haloxylon ammodendron | 1.95 | 1291.36 | 16 | 25 181.52 | 402 904.32 |
| 沙拐枣Calligonum mongolicum | 2.02 | 328.20 | 16 | 6 629.64 | 106 074.24 |
| 合计Total | 35 464.48 | 567 431.68 |
表4 沙漠公路防护林带3种木本植物生物量固碳法估算总固碳量
Tab.4
| 树种 Tree species | 生物量 Biomass (kg/株) | 株数 Number of plants (104株) | 总生物量 Total biomass (t) | 碳含量 Carbon content (kg/kg) | CO2/C (g/mol) | 碳储量 Carbon storage (t) | 总固碳量 Total carbon sequestration (t) |
|---|---|---|---|---|---|---|---|
| 柽柳Tamarix chinensis | 8.72 | 147 | 12 818.4 | 0.5 | 3.667 | 6 409.2 | 23 500.4 |
| 梭梭Haloxylon ammodendron | 19.62 | 1260 | 247 212 | 0.5 | 3.667 | 123 606 | 453 222 |
| 沙拐枣Calligonum mongolicum | 11.67 | 413 | 48 197.1 | 0.5 | 3.667 | 24 098.55 | 88 361.35 |
| 合计Total | 154 113.75 | 565 083.75 |
图3
图3
3种木本植物生物量实测生物量与预测生物量比较
注:a代表柽柳、b代表梭梭、c代表沙拐枣,图中虚线代表95%置信区间上下限。R2为回归模型决定系数,RS为总相对误差,RMA为平均相对误差
Fig.3
Comparisons of measured biomass and predicted biomass of three types of woody plants
Note: a represents T. ramosissima, b represents H. ammodendron, and c represents C. mongolicum. The dotted line in the figure represents the upper and lower limits of the 95 % confidence interval. R2 is the determination coefficient of the regression model, RS is the total relative error, and RMA is the average relative error
图4
图4
沙漠公路防护林带3种木本植物生物量法固碳量
Fig.4
Carbon sequestration of three kinds of woody plants in desert highway shelterbelt by biomass method
3 讨论
3.1 3种防护林植物的光合速率在一天中呈现出“单峰”曲线,即在正午(12:00)达到最高峰值。就单位叶面积的固碳能力而言,柽柳具有最高的固碳能力;从单株的固碳能力来看,梭梭表现最强,柽柳次之。贾宏涛等[20]对准葛尔盆地南缘荒漠区的柽柳、梭梭和沙拐枣进行了固碳能力分析,通过比较最大光合速率的大小来衡量固碳能力,并得出了柽柳作为首选树种的结论。试验研究的结论与其相吻合。然而,仅仅用这一数值来衡量植被的固碳能力可能会高估植被整体固碳量。是因为光合速率和单位叶面积固定CO2量反映了灌丛叶片光合固碳能力的强弱[21],而单株固碳量则综合考虑了灌丛个体角度上的固碳能力。因此,在沙漠公路人工林防护林培育的选择上,梭梭作为优势物种,并适当增加柽柳的种植面积,以提升整个防护林的固碳能力。试验结果发现,3种木本种植面积存在差异,从而导致不同灌丛单位叶面积固定CO2量和单株固碳量的规律不一致。因此,完善碳汇系统固碳能力核算方法至关重要。
3.2 赵成义[22]利用植株的株高H和基径D构建了用于荒漠地区梭梭和柽柳生物量估测的方程,但其因变量的选择与试验结果不完全一致。这是因为荒漠植物的生长受气候、土壤和降水等因素的紧密影响,因此即使是同一物种在不同环境下的生物量模型也会有所差异。此外,赵梦颖等[23]、杨昊天等[24]认为幂函数模型是最适合用于估算灌木生物量的模型,与研究得出的结论一致。然而,党晓宏[25]在其对库布其沙漠北缘的沙拐枣和柽柳的研究以及魏小平[26]在民勤荒漠绿洲过渡带的沙拐枣和梭梭的研究中选择的最佳生物量模型并非幂函数模型,与研究结果存在一定差异。是由于沙漠公路地区的极端气候条件,导致了植物呈现出形态特征的差异。
4 结论
3种植物固碳量具有显著差异,表现为梭梭 > 沙拐枣 > 柽柳。3种植物生物量最优模型均为幂函数,其中柽柳生物量估算最优为幂指数模型,预测值与实测值回归决定系数在90%以上,模型效果精确可靠。另外,光合固碳法估算得到的沙漠公路防护林带总固碳量为567 431.68 t,生物量法估算的值为565 083.75 t,2种方法估算得到的固碳量相当。
参考文献
发挥森林固碳功能减缓全球气候变暖
[J].
Give full play to the function of forest carbon fixation and slow down global warming
[J].
华北落叶松人工林和天然林径向生长对气候变化的响应
[J].
Response of the radial growth of Larix principis-rupprechtii plantations and natural forests to climate change
[J].
干旱和半干旱地区灌木下土壤 “肥岛”研究进展
[J].世界许多干旱、半干旱地区草地生态系统逐渐被灌木生态系统取代,这种取代过程的发展是由灌木冠幅下土壤中“肥岛”的形成和灌木的扩散相互作用直接造成的,这种“肥岛”的形成和灌木的扩散之间的反馈作用能够改变该系统中的植被组成、结构和土壤养分分布格局,从而改变该生态系统的结构和功能,文中从“肥岛”的概念和形成机制出发,对“肥岛”现象形成的原因、“肥岛”现象的研究意义、研究方法、灌木扩散与“肥岛”之间的相互关系及生物对“肥岛”的响应进行了总结,并分析了“肥岛”研究中应注意的问题,希望为中国干旱、半干旱区域土地退化的成因和过程以及植被恢复的研究提供一些参考。
A research review on “fertile islands” of soils under shrub canopy in arid and semi-arid regions
[J].Due to the inclemency of climate and soil conditions and the intense disturbance of human beings, the soil resources heterogeneity in arid and semi-arid grassland ecosystems worldwide was gradually increased during the last century. The interaction between soil heterogeneity and shrubs induced the autogenic development of "fertile islands" and the increasing spread of shrubs in the grassland ecosystems. The development of "fertile islands" around individual shrubs could change the vegetation composition and structure, as well as the distribution patterns of soil resources, and thus, reinforced the changes of the ecosystem function and structure from a relative stable grassland ecosystem to a quasi-stable shrubland ecosystem. The study of "fertile islands" phenomenon would help us to understand the causes, consequences and processes of desertification in arid and semi-arid areas. In this paper, the causes of "fertile islands", its study methods and significance and its relationship with shrub spreading as well as the responses of vegetation to it were summarized. The problems which might occur in the study of this phenomenon were also pointed out. Our aim was to offer some references to the study of land desertification processes and vegetation restoration in the arid and semi-arid regions.
第八次全国森林资源清查结果
[J].
The eighth national forest resources inventory results
[J].
重视森林资源保护强化森林资源管理
[J].
Attach importance to forest resources protection and strengthen forest resources management
[J].
加强森林资源管理不断提升森林质量
[J].
Strengthen management of forest resources and improve the quality of forests
[J].
塔中沙漠公路零碳示范工程案例研究
[J].
Research on the case of zero carbon demonstrate project in Tazhong Desert highway
[J].
塔里木沙漠公路防护林带根灌节水试验研究
[J].根灌技术直接把水分灌溉到一定深度的植物根系土壤层,是一项新的节水灌溉技术;在塔里木沙漠公路防护林带灌溉中,首次开展了根灌对土壤水分作用与影响的节水试验研究,并与传统的沙漠公路防护林带滴灌技术进行对比。研究结果表明,根灌技术比滴灌技术更加节水,其主要优点表现在增加土壤含水量、增加土壤层的湿润深度、提高灌水效率、节省灌水时间等。而且,根灌技术能有效地抑制滴灌造成的地表土壤水分的蒸发损失、地表土壤的盐分积累。根灌技术比滴灌要节水30%以上,是一项更高效的节水灌溉技术。
Root irrigation experiments used in the protective forest belt along the Tarim Desert highway
[J].<FONT face=Verdana>Root irrigation is an irrigation technique supplying water directly to a certain depth of soil layer where the plant root distributes, and it is a relatively new water-saving irrigation technique. Root irrigation water-saving experiment was first conducted in the protective forest belt along the Tarim Desert highway in this study. The effect of root irrigation on soil water content was investigated in the experiment and at the same time a comparative experiment with the drip irrigation technique, which was a predominant technique in the irrigation of the forest belt along the Tarim Desert highway, was made. The study results show that the root irrigation technique can save more water than drip irrigation technique does, and its advantages are mainly manifested in the significant increase in soil water content and soil moisture depth, the improvement of irrigation efficiency and the decrease of irrigation duration time. Root irrigation can also effectively reduce the evaporation loss of surface water and salt accumulation in surface soil layer caused by drip irrigation. Root irrigation technique is a more effective water-saving irrigation technique because it can save 30% or more irrigation water compared to drip irrigation technique.</FONT>
塔里木沙漠公路风沙危害形成研究
[J].
The formation of the blown sand disaster to the Tarim Desert highway, Xinjiang, China
[J].
水分条件对塔里木沙漠公路防护林植物幼苗生长及生物量分配的影响
[J].
Effects of water conditions on seedling growth and biomass distribution of shelterbelt in Tarim Desert highway
[J].
塔里木沙漠公路防护林造林树种生长动态研究
[J].
Study on dynamic growth of forestation trees on talimu desert highway
[J].
枸杞叶片净光合速率与其它生理参数及环境微气象因子的关系
[J].
Relationship between leaf net photosynthesis rate of Lyciumbarbarum L. and it’s environmental micrometeorological factors
[J].
浑善达克沙地3种灌木生物量的预测模型
[J].
Prediction model for biomass of 3 shrubs in Hunshandake sandy land
[J].
帽儿山地区6种灌木地上生物量估算模型
[J].
Estimation model for biomass of typical shrubs in Maoershan Area, Heilongjiang
[J].
荒漠灌木生物量多尺度估测——以梭梭为例
[J].灌木是荒漠生态系统重要的组成部分,其生物量估算与分配特征是研究荒漠生态系统结构、功能、物质和能量流动的重要指标。但目前关于荒漠灌木生物量的研究仍较缺乏。破坏性的生物量估测方法不适宜在生态系统脆弱的荒漠地区大面积使用,因此通过模型法对灌木生物量进行多尺度估测具有重要意义。本研究以准噶尔荒漠生态系统建群种——梭梭为例,选择多种植物外部形态特征参数,利用相关生长模型(幂函数),分别在单株、样方及区域尺度对梭梭的地上(AGB)和地下生物量(BGB)进行建模和估算。结果表明,以植冠体积(CH)为指标的估测模型(AGB=0.3628×CH<sup>0.9605</sup>)能较好地反映梭梭单株地上生物量累计特征,而单株地下生物量可通过模型BGB=0.8737×AGB<sup>0.9394</sup>得到。样方内梭梭总冠幅面积(TC)是估测样方(0.1 hm<sup>2</sup>)总生物量(TAGB=0.6757×TC<sup>1.1343</sup>, TBGB=0.6384×TC<sup>1.0959</sup>)的有效参数。在大尺度上(区域),利用梭梭相对盖度(RC)估测其生物量密度(DAGB=0.0921×RC<sup>1.1343</sup>, DBGB=0.0796×RC<sup>1.0959</sup>)具有良好效果,进而结合区域面积得到梭梭总生物量。研究表明,相对盖度的方法从生物量密度的角度解决了尺度转换问题,使用时没有尺度限制。未来还可以通过航拍、遥感等手段快速获取相关区域梭梭群落相对盖度,结合上述模型准确估测其地上、地下生物量。
Multi-scale biomass estimation of desert shrubs: a case study of Haloxylonammodendron in the Gurbantunggut Desert, China
[J].
青藏高原典型人工林幼树生物量模型构建
[J].森林生物量计算是全球碳储量估算的基础,现已纳入全球国家森林清单项目。普遍的森林碳汇计量采用的材积源生物量法针对胸径5 cm以上的树木,幼树(胸径<6 cm,树高>0.3 m)的碳汇量并未被完整计入其中,导致生态系统碳汇能力被低估。基于青藏高原137株5种典型人工林幼树的实测生物量数据,以地径代替胸径作为预测变量,采用加权广义最小二乘法建立独立生物量模型,选择比例总量直接控制及代数和控制2种结构形式的相容性生物量模型,并通过加权非线性似乎不相关回归进行方程组估算,建立了整株及各组分的相容性生物量方程。结果表明: 二元相容性模型优于一元以及独立模型,对整株生物量来说,R<sup>2</sup>达到0.90~0.99,两种相容性模型对于不同树种来说各有优势但精度差距可以忽略,从林业生产实践角度考虑,比例总量直接控制生物量模型更有实践意义,从遥感技术的变量提取角度考虑,本研究构建了更适于遥感估算的幼树生物量模型,其整体上拟合精度高,可以准确地进行类似气候环境中的幼树整株和各组分生物量的估算。
Developing biomass estimation models of young trees in typical plantation on the Qinghai-Tibet Plateau, China
[J].Calculation of forest biomass is the basis for global carbon stock estimation, which has been included in national forest inventory projects. The volume-derived biomass method is generally used for trees with diameter at breast height (DBH) larger than 5 cm in most forest carbon sink measurement, which omits young trees (diameter at breast height <6 cm, height >0.3 m) and thus may underestimate ecosystem carbon sink capacity. Based on the biomass data of 137 young trees in five typical plantations on the Tibetan Plateau, independent biomass models were developed using the weighted generalized least squares method, with basic diameter as the predictor instead of DBH. Additive biomass models of controlling directly by proportion functions and controlling by the sum of equations were selected. Additive biomass models for the whole plant and each component were developed by applying weighted nonlinear seemingly uncorrelated regression. The results showed that the binary additive biomass model (<i>R</i><sup>2</sup> reached 0.90-0.99) performed better than the monadic biomass models and independent biomass models for the estimation of total biomass. For different tree species, two forms of the additive models had their own advantages, with neglectable difference in accuracy. From the perspective of forestry production, models of controlling directly by proportion functions were more practical. From the perspective of predictors extraction by remote sensing technology, suitable young tree biomass models were developed for remote sensing estimation. In this study, the additive model had high overall fitting accuracy and could accurately estimate the whole plant and component biomass of young trees in similar climatic environments.
黑龙江省森林碳汇价值评价及碳汇潜力分析
[J].
Evaluation of forest carbon sink value and analysis of carbon sink potential in Heilongjiang Province
[J].
干旱区退耕还林高固碳效率树种筛选
[J].
Screening of tree species with high-efficiency carbon sequestration for returning cultivated land to forest in arid area
[J].
扬州古运河风光带绿地树种固碳释氧效应初步研究
[J].
Carbon fixation and oxygen release of landscaping trees along the Grand Canal in Yangzhou
[J].
几种荒漠植物地上生物量估算的初步研究
[J].在调查植物样方的基础上,利用植株冠幅特征如冠幅长与宽、株高、基径、新生枝条数、总枝条数等作为变量建立了估算典型荒漠植物地上生物量的模型.利用植株冠幅长与宽所建拟合方程对估算琵琶柴灌丛生物量的精确度较高,经验证,预测值与实测值的相关系数为0.9989,相对误差在4.79%~10.12%之间.利用植株株高、基径所建拟合方程对估算梭梭、多枝柽柳生物量计算值与实测值的相关系数在0.9418以上,显著性检验表明相关系数均为极显著.经验证,预测值与实测值的相关系数分别为0.9902和0.9875,相对误差分别为6.87%~19.22%和7.49%~18.47%.研究表明,在大面积荒漠植物生物量研究中,利用植株冠幅特征作为变量来估算琵琶柴灌丛地上生物量方法简便可行,用来估算梭梭、多枝柽柳等灌木地上生物量时存在一定误差.
Estimation of aboveground biomass of desert plants
[J].Based on the research of plant quadrate in Sangong River Basin in Xinjiang, the fitted equations were given, which could be used to estimate the aboveground biomass of typical desert plant by using the thicket characteristics such as length of crown diameter, width of crown diameter, number of basal branch, length of new branch, basal diameter (D) and plant height (H) as parameters. Using the length of crown diameter and the width of crown diameter as parameters, the fitted equation was set up and tested for estimating the aboveground biomass of Reaumuria soongorica Maxim. It had a relatively high accuracy and a fine linear relationship between the predicted values and measured values. Its coefficient and relative standard deviation was 0.9989 and 4.79%-10.12%, respectively. The results indicated that the fitted equation was easy and available for estimating the aboveground biomass of Reaumuria soongorica Maxim in large scale. The fitted equations were also set up and tested for estimating the aboveground biomass of Haloxylon ammodendron and Tamarix ramosissima by using the basal diameter and height of plant as the parameters. The coefficients and relative standard deviations of these equations were 0.9902, 0.9875 and 6.87%-19.22%, 7.49%-18.47%, respectively. Therefore, estimating the biomass of Reaumuria soongorica in large scale through crown characteristics was available, and estimating the biomass of Halaxylon Ammodendron and Tamarix ramosissima through crown characteristics would produce certain error.
内蒙古26种常见温带灌木的生物量模型
[J].
Models for estimating the biomass of 26 temperate shrub species in Inner Mongolia, China
[J].
腾格里沙漠东南缘4种灌木的生物量预测模型
[J].灌木生物量模型是预测灌木生物量最有效的方法。选择腾格里沙漠南缘荒漠生态系统中常见的4种灌木(驼绒藜(Ceratoides latens)、盐爪爪(Kalidium foliatum)、珍珠猪毛菜(Salsola passerina)、红砂(Reaumuria soongarica))为研究对象,以株高(H)和冠幅(C)的复合因子灌木体积(V)为自变量,通过回归分析,分别构建了4种灌木和混合物种的叶、新生枝、老龄枝、地上部分、地下部分和整株生物量的预测模型。通过决定系数(R2)、估计值的标准误(SEE)和回归检验显著水平(p<0.05)筛选出了最优的生物量估测模型。结果显示:4种灌木的生物量模型主要以幂函数W=aVb为最优模型,少数以三次函数W=a+bV+cV2+dV3为最优模型。灌木生物量与V之间呈极显著的相关关系(p<0.001),决定系数较高,分别为:叶片(0.775<R2<0.866),新生枝(0.694<R2<0.840),老龄枝(0.819<R2<0.916),地上部(0.832<R2<0.917),地下部分(0.74<R2<0.808),全株(0.811<R2<0.912),说明预测模型可以应用于此4种灌木的生物量估算。不同物种之间及不同器官之间的生物量模型存在差异,在实际使用中,要根据物种来选择相应的模型。生物量模型的建立有助于全面估算荒漠生态系统的生物量,并进一步评估生态系统不同碳库的碳存储量与碳循环。为有效提高荒漠草地碳储量、合理实施生态系统管理和人为干预提供科学依据。
Biomass estimation models of four shrub species at southeastern edge of the tengger desert
[J].Biomass estimation modeling is one of the most important methods in biomass estimation of shrubs. In this paper, shrubs volume (V) was used as independent variable to establish the models between V and the leaf, current year branch, aging branch, above-ground, under-ground and total biomass for four single common shrubs and their mixed samples in desert area, respectively, at the southeastern edge of the Tengger Desert, China. The optimal models were selected according to the largest determination coefficient (R2), the smallest standard error of estimate(SEE) and significance level (p<0.05). Results showed that the optimal biomass models for all organs, above-ground, under-ground and the whole plant of single species and mixed species were mostly expressed by power functions (W=aVb), only a few can be expressed by cubic equations (W=a+bV+cV2+dV3). The p values of all models reached a significant level (p<0.05) and R2 ranged between 0.69-0.92. Those models can be used to estimate actual biomass of shrubs due to their good effectiveness. However, there existed differences in optimal models among different species or organs. Models should be chosen according to the practical conditions in estimating biomass of shrubs. The effects of mixed models are lower than that of single species. The optimal biomass models are expected to contribute to estimate biomass and carbon storage of different carbon pools for desert ecosystems.
库布其沙漠北缘8种荒漠灌丛生物量预测模型研究
[J].
The biomass estimation models for eight desert shrub species in northern edge of the Hobq Desert
[J].
Estimation of above-and below-ground biomass of dominant desert plant species in an oasis-desert ecotone of Minqin, China
[J].<p>Most desert soil management decisions are based on quantitative measu rements of the biomass of the dominant plant species. The biomass of the dominant plant species in a typical oasis_desert ecotone (ODE) of Minqin was measured in 82 plots (10 m×10 m). The results showed that the distribution and total cover was approximately 16.12%. Above and belowground biomass of five dominant desert species (Nitraria tangutorum, Calligonuum mongolicum, Haloxylon ammoden dron, Agriophyllum squarrosum and Halogeton arachnoideu) was measured by excavation. Linear regressions were used to analyze the relationships among all the biomass components for each plant (fresh and dry weight of aboveand below_ground biomass) and the basal diameter, total height and canopy cover. Best fit models were constructed for each species using 80% of the data. Our results showed that basal diameter (excluding N. tangutorum) and canopy cover were the best predictors of biomass for all five desert plant species. A validation test using the other 20 % of the data not used for estimating the regression equations indicated that these equations made accurate predictions of desert plant species biomass.</p>
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