Ecology and Environment ›› 2024, Vol. 33 ›› Issue (2): 167-179.DOI: 10.16258/j.cnki.1674-5906.2024.02.001
• Research Article [Ecology] • Next Articles
ZHAI Yongguang1,*(), WANG Xiaoni1, HAO Lei2, QI Wenchao3, WANG Yasong1, GENG Jiayu1, LAN Qiongqiong4, WANG Zhiguo5
Received:
2023-10-20
Online:
2024-02-18
Published:
2024-04-03
翟涌光1,*(), 王晓妮1, 郝蕾2, 戚文超3, 王雅崧1, 耿佳玉1, 兰穹穹4, 王志国5
通讯作者:
*
作者简介:
翟涌光(1986年生),男,副教授,博士,研究方向为遥感大数据处理和环境监测。E-mail: ychia@imau.edu.cn
基金资助:
CLC Number:
ZHAI Yongguang, WANG Xiaoni, HAO Lei, QI Wenchao, WANG Yasong, GENG Jiayu, LAN Qiongqiong, WANG Zhiguo. Multi-time Scale Analysis of Net Ecosystem Productivity Pattern in Inner Mongolia from 2001 to 2020[J]. Ecology and Environment, 2024, 33(2): 167-179.
翟涌光, 王晓妮, 郝蕾, 戚文超, 王雅崧, 耿佳玉, 兰穹穹, 王志国. 2001-2020年内蒙古净生态系统生产力格局多时间尺度分析[J]. 生态环境学报, 2024, 33(2): 167-179.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2024.02.001
站点 名称 | 库布齐- 草地 | 库布齐- 林场 | 内蒙 | 科尔沁 | 锡林浩特 | 四子王 | 多伦- 耕地 | 多伦- 草地 | 锡林郭勒- 荒漠草原 | 锡林郭勒- 典型草原 | 东乌草原 |
---|---|---|---|---|---|---|---|---|---|---|---|
纬度 | 40.38 | 40.54 | 44.53 | 43.29 | 43.55 | 41.79 | 42.05 | 42.05 | 44.09 | 44.13 | 45.56 |
经度 | 108.55 | 108.69 | 116.67 | 122.28 | 116.67 | 111.89 | 116.67 | 116.28 | 113.57 | 116.33 | 117.00 |
年份 | 2006 | 2006‒2010 | 2004‒2008 | 2011‒2012 | 2011‒2012 | 2010‒2011 | 2005‒2006 | 2005‒2006 | 2003‒2010 | 2003‒2010 | 2005‒2007 |
植被 | 干旱草地 | 林地 | 草地 | 草地 | 围封草地 | 干旱草地 (禁牧) | 耕地 | 耕地 | 荒漠草原 | 草地 | 典型草原 |
土壤 | 沙质土壤 | 沙质土壤 | 暗栗钙土 | 栗色土壤 | 栗钙土 | 淡栗钙土 | 栗色土壤 | 栗色土壤 | 棕色钙质土壤 | 栗色土壤 | 栗色土壤 |
Table 1 Flux sites basic information
站点 名称 | 库布齐- 草地 | 库布齐- 林场 | 内蒙 | 科尔沁 | 锡林浩特 | 四子王 | 多伦- 耕地 | 多伦- 草地 | 锡林郭勒- 荒漠草原 | 锡林郭勒- 典型草原 | 东乌草原 |
---|---|---|---|---|---|---|---|---|---|---|---|
纬度 | 40.38 | 40.54 | 44.53 | 43.29 | 43.55 | 41.79 | 42.05 | 42.05 | 44.09 | 44.13 | 45.56 |
经度 | 108.55 | 108.69 | 116.67 | 122.28 | 116.67 | 111.89 | 116.67 | 116.28 | 113.57 | 116.33 | 117.00 |
年份 | 2006 | 2006‒2010 | 2004‒2008 | 2011‒2012 | 2011‒2012 | 2010‒2011 | 2005‒2006 | 2005‒2006 | 2003‒2010 | 2003‒2010 | 2005‒2007 |
植被 | 干旱草地 | 林地 | 草地 | 草地 | 围封草地 | 干旱草地 (禁牧) | 耕地 | 耕地 | 荒漠草原 | 草地 | 典型草原 |
土壤 | 沙质土壤 | 沙质土壤 | 暗栗钙土 | 栗色土壤 | 栗钙土 | 淡栗钙土 | 栗色土壤 | 栗色土壤 | 棕色钙质土壤 | 栗色土壤 | 栗色土壤 |
NEP | 1月 | 2月 | 3月 | 4月 | 5月 | 6月 | 7月 | 8月 | 9月 | 10月 | 11月 | 12月 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
NEP>0 | 0 | 0 | 71.7% | 91.5% | 100% | 100% | 100% | 100% | 90.8% | 59.4% | 0 | 0 |
NEP<0 | 100% | 100% | 28.3% | 8.50% | 0 | 0 | 0 | 0 | 9.20% | 40.6% | 100% | 100% |
平均值(以C计)/(g∙m−2∙month−1) | −2.67 | −2.93 | −1.13 | 8.23 | 26.2 | 37.3 | 45.8 | 41.9 | 16.5 | −0.460 | −3.10 | −2.68 |
Table 2 Monthly mean values and the percentage of NEP in Inner Mongolia from 2001 to 2020
NEP | 1月 | 2月 | 3月 | 4月 | 5月 | 6月 | 7月 | 8月 | 9月 | 10月 | 11月 | 12月 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
NEP>0 | 0 | 0 | 71.7% | 91.5% | 100% | 100% | 100% | 100% | 90.8% | 59.4% | 0 | 0 |
NEP<0 | 100% | 100% | 28.3% | 8.50% | 0 | 0 | 0 | 0 | 9.20% | 40.6% | 100% | 100% |
平均值(以C计)/(g∙m−2∙month−1) | −2.67 | −2.93 | −1.13 | 8.23 | 26.2 | 37.3 | 45.8 | 41.9 | 16.5 | −0.460 | −3.10 | −2.68 |
月份 | 极显著 减少% | 显著 减少% | 无明显 变化% | 显著 增加% | 极显著 增加% |
---|---|---|---|---|---|
1 | 0 | 0 | 100 | 0 | 0 |
2 | 0 | 0 | 100 | 0 | 0 |
3 | 0 | 2.00×10−2 | 99.3 | 0.690 | 4.00×10−2 |
4 | 0 | 0.730 | 59.9 | 26.2 | 13.2 |
5 | 0 | 17.9 | 11.4 | 63.9 | 6.79 |
6 | 0 | 30.7 | 12.7 | 51.4 | 5.26 |
7 | 0 | 37.9 | 4.35 | 54.0 | 3.74 |
8 | 0 | 34.0 | 1.27 | 57.8 | 6.98 |
9 | 0 | 3.27 | 39.7 | 45.9 | 11.2 |
10 | 0 | 0.400 | 95.8 | 3.51 | 0.250 |
11 | 0 | 0 | 100 | 0 | 0 |
12 | 0 | 0 | 100 | 0 | 0 |
Table 3 The percentage of NEP in monthly in Inner Mongolia from 2001 to 2020
月份 | 极显著 减少% | 显著 减少% | 无明显 变化% | 显著 增加% | 极显著 增加% |
---|---|---|---|---|---|
1 | 0 | 0 | 100 | 0 | 0 |
2 | 0 | 0 | 100 | 0 | 0 |
3 | 0 | 2.00×10−2 | 99.3 | 0.690 | 4.00×10−2 |
4 | 0 | 0.730 | 59.9 | 26.2 | 13.2 |
5 | 0 | 17.9 | 11.4 | 63.9 | 6.79 |
6 | 0 | 30.7 | 12.7 | 51.4 | 5.26 |
7 | 0 | 37.9 | 4.35 | 54.0 | 3.74 |
8 | 0 | 34.0 | 1.27 | 57.8 | 6.98 |
9 | 0 | 3.27 | 39.7 | 45.9 | 11.2 |
10 | 0 | 0.400 | 95.8 | 3.51 | 0.250 |
11 | 0 | 0 | 100 | 0 | 0 |
12 | 0 | 0 | 100 | 0 | 0 |
植被类型 | 1月 | 2月 | 3月 | 4月 | 5月 | 6月 | 7月 | 8月 | 9月 | 10月 | 11月 | 12月 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
常绿针叶林 | −19.0* | −1.20* | 71.0 | 760* | 1.00×103* | 910* | 56.0* | 660* | 620* | 250* | −7.10 | −17.0* |
落叶针叶林 | −39.0 | −200 | 390 | 1.10×104 | −3.20×103 | −7.30×103 | −2.26×104* | −2.75×104* | 6.30×103 | 1.30×103 | −490* | −140 |
落叶阔叶林 | −2.10×103* | −1.70×103* | −4.70×103 | 5.42×104* | 1.25×105* | 1.58×105* | 1.12×105* | 6.63×104 | 6.99×104* | 1.09×104* | −1.20×103 | −2.00×103* |
混交林 | 190 | 180 | 540 | 7.40×103* | −57.0 | −1.70×103 | −7.70×103 | −1.11×104* | 2.40×103 | 1.30×103 | 280* | 33.0 |
灌木林 | −270* | −290* | −110* | −57.0 | −350* | −860* | −880* | −560* | −160 | −260* | −290* | −260* |
草地 | −4.10×103 | 1.12×104 | 1.14×105* | 4.58×105* | 4.04×105* | 3.99×105 | 1.84×105 | 4.47×105 | 5.33×105* | 1.05×105* | 1.45×104* | −1.30×103 |
耕地 | −3.10×103* | 690 | 9.90×103 | 3.57×104* | 3.21×104 | 1.33×105* | 9.74×104* | 7.44×104* | 9.25×104* | 1.12×104* | −910 | −2.70×103* |
荒漠 | 2.30×103 | 2.50×103 | 7.70×103 | 5.19×104 | −1.17×104 | −2.23×104 | −1.52×104 | −1.12×104 | 1.58×104 | 220 | 3.40×103* | 850 |
Table 4 Inter-annual change of total NEP (in terms of C) in twelve monthls for 8 vegetation types in Inner Mongolia from 2001 to 2020 Mg?month?1
植被类型 | 1月 | 2月 | 3月 | 4月 | 5月 | 6月 | 7月 | 8月 | 9月 | 10月 | 11月 | 12月 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
常绿针叶林 | −19.0* | −1.20* | 71.0 | 760* | 1.00×103* | 910* | 56.0* | 660* | 620* | 250* | −7.10 | −17.0* |
落叶针叶林 | −39.0 | −200 | 390 | 1.10×104 | −3.20×103 | −7.30×103 | −2.26×104* | −2.75×104* | 6.30×103 | 1.30×103 | −490* | −140 |
落叶阔叶林 | −2.10×103* | −1.70×103* | −4.70×103 | 5.42×104* | 1.25×105* | 1.58×105* | 1.12×105* | 6.63×104 | 6.99×104* | 1.09×104* | −1.20×103 | −2.00×103* |
混交林 | 190 | 180 | 540 | 7.40×103* | −57.0 | −1.70×103 | −7.70×103 | −1.11×104* | 2.40×103 | 1.30×103 | 280* | 33.0 |
灌木林 | −270* | −290* | −110* | −57.0 | −350* | −860* | −880* | −560* | −160 | −260* | −290* | −260* |
草地 | −4.10×103 | 1.12×104 | 1.14×105* | 4.58×105* | 4.04×105* | 3.99×105 | 1.84×105 | 4.47×105 | 5.33×105* | 1.05×105* | 1.45×104* | −1.30×103 |
耕地 | −3.10×103* | 690 | 9.90×103 | 3.57×104* | 3.21×104 | 1.33×105* | 9.74×104* | 7.44×104* | 9.25×104* | 1.12×104* | −910 | −2.70×103* |
荒漠 | 2.30×103 | 2.50×103 | 7.70×103 | 5.19×104 | −1.17×104 | −2.23×104 | −1.52×104 | −1.12×104 | 1.58×104 | 220 | 3.40×103* | 850 |
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