新疆农业科学 ›› 2024, Vol. 61 ›› Issue (8): 2014-2022.DOI: 10.6048/j.issn.1001-4330.2024.08.022
李汝勇1(), 任久明1, 雷霆1, 王克林1(
), 刘鹏程1, 李江涛2
收稿日期:
2024-01-15
出版日期:
2024-08-20
发布日期:
2024-09-19
通信作者:
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作者简介:
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
基金资助:
LI Ruyong1(), REN Jiuming1, LEI Ting1, WANG Kelin1(
), LIU Pengcheng1, LI Jiangtao2
Received:
2024-01-15
Published:
2024-08-20
Online:
2024-09-19
Correspondence author:
WANG Kelin (1989-), male, from Songtao, Guizhou, senior engineer, research direction: organic chemistry and ecological restoration, (E-mail) wangkl-tlm@petrochina.com.cnSupported by:
摘要:
【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。
中图分类号:
李汝勇, 任久明, 雷霆, 王克林, 刘鹏程, 李江涛. 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[J]. 新疆农业科学, 2024, 61(8): 2014-2022.
LI Ruyong, REN Jiuming, LEI Ting, WANG Kelin, LIU Pengcheng, LI Jiangtao. Differences in carbon sink estimation between photosynthetic and biomass methods in the Tarim Desert Highway shelterbelt[J]. Xinjiang Agricultural Sciences, 2024, 61(8): 2014-2022.
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 |
表1 样方植被特征
Tab.1 Quadrat vegetation characteristics
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 |
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
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 |
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 Parameters of biomass regression model of three kinds of woody plants in desert highway shelterbelt
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 |
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
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 Estimation of total carbon sequestration by photosynthetic carbon fixation method of three kinds of woody plants in desert highway shelterbelt
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 |
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 |
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 Estimation of total carbon sequestration by biomass method of three kinds of woody plants in desert highway shelterbelt
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 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
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