植物生态学报 ›› 2014, Vol. 38 ›› Issue (5): 491-498.DOI: 10.3724/SP.J.1258.2014.00045
马洋1,2,3,王雪芹1,*(),张波1,2,3,刘进辉1,2,3,韩章勇1,2,3,唐钢梁1,2,3
收稿日期:
2013-11-25
接受日期:
2014-03-05
出版日期:
2014-11-25
发布日期:
2014-05-13
通讯作者:
王雪芹
基金资助:
MA Yang1,2,3,WANG Xue-Qin1,*(),ZHANG Bo1,2,3,LIU Jin-Hui1,2,3,HAN Zhang-Yong1,2,3,TANG Gang-Liang1,2,3
Received:
2013-11-25
Accepted:
2014-03-05
Online:
2014-11-25
Published:
2014-05-13
Contact:
WANG Xue-Qin
摘要:
塔克拉玛干沙漠南缘风沙活动十分频繁, 风蚀和沙埋是该地区自然植被生长发育的重要影响因子。该文以塔克拉玛干沙漠南缘策勒绿洲-沙漠过渡带为研究区, 以该区域主要建群种植物骆驼刺(Alhagi sparsifolia)为研究对象, 对一次强沙尘天气过后沙丘表面5种不同风蚀沙埋状况的骆驼刺植物进行标定(包括10 cm风蚀、5 cm风蚀、不蚀不积、10 cm沙埋、30 cm沙埋), 天晴后测定其叶水势、叶片含水量、光合参数和叶绿素荧光等参数, 分析研究自然环境条件下风蚀和沙埋对骆驼刺水分和光合作用的影响。结果表明: (1)风蚀显著降低了骆驼刺叶水势和叶片含水量, 进而导致植物气孔导度降低, 并引起植物光合速率和蒸腾速率的下降。风蚀的植物水分利用效率低于沙埋, 特别是在10 cm风蚀深度明显降低。 (2)沙埋增加了骆驼刺的叶水势、叶片含水量和气孔导度, 并引起植物光合速率和蒸腾速率的上升, 水分利用效率也得到提升。(3)风蚀条件下骆驼刺所受胁迫增加, 但可以通过增加活性反应中心的数量和光化学效率来抵消胁迫造成的不利影响。沙埋条件下骆驼刺受胁迫减轻, 反应中心吸收的光能和用于光化学反应的能量随着沙埋程度增加而减小, 这是骆驼刺适应风沙环境的一种生存策略。(4)与5 cm风蚀以及10 cm沙埋相比, 10 cm风蚀显著抑制骆驼刺的生长, 30 cm沙埋则会显著促进骆驼刺的生长。
马洋,王雪芹,张波,刘进辉,韩章勇,唐钢梁. 风蚀和沙埋对塔克拉玛干沙漠南缘骆驼刺水分和光合作用的影响. 植物生态学报, 2014, 38(5): 491-498. DOI: 10.3724/SP.J.1258.2014.00045
MA Yang,WANG Xue-Qin,ZHANG Bo,LIU Jin-Hui,HAN Zhang-Yong,TANG Gang-Liang. Effects of wind erosion and sand burial on water relations and photosynthesis in Alhagi sparsifolia in the southern edge of the Taklimakan Desert. Chinese Journal of Plant Ecology, 2014, 38(5): 491-498. DOI: 10.3724/SP.J.1258.2014.00045
图1 风蚀和沙埋对骆驼刺水势和叶片含水量的影响(平均值±标准偏差)。CK, 对照; MB, 10 cm沙埋; ME, 5 cm风蚀; SB, 30 cm沙埋; SE, 10 cm风蚀。不同字母表示差异显著 (p < 0.05)。
Fig. 1 Effect of wind erosion and sand burial on water potential and leaf water content in Alhagi sparsifolia (mean ± SD). CK, control; MB, sand burial depth of 10 cm; ME, wind erosion depth of 5 cm; SB, sand burial depth of 30 cm; SE, wind erosion depth of 10 cm. Different lower-case letters indicate significant differences (p < 0.05).
图2 风蚀和沙埋对骆驼刺光合参数的影响(平均值±标准偏差)。CK, MB, ME, SB, SE同图1。
Fig. 2 Effect of wind erosion and sand burial on photosynthetic parameters in Alhagi sparsifolia (mean ± SD). CK, MB, ME, SB, SE see Fig. 1.
参数 Parameter | 处理 Treatment | ||||
---|---|---|---|---|---|
SE | ME | CK | MB | SB | |
Fv/Fm | 0.76 ± 0.01* | 0.77 ± 0.01 | 0.79 ± 0.01 | 0.82 ± 0.02* | 0.84 ± 0.01** |
ABS/RC | 2.42 ± 0.19** | 2.31 ± 0.14 | 2.21 ± 0.17 | 2.04 ± 0.14* | 1.82 ± 0.17** |
TR0/RC | 1.83 ± 0.14 | 1.78 ± 0.09 | 1.76 ± 0.12 | 1.67 ± 0.09 | 1.53 ± 0.12* |
ET0/RC | 1.15 ± 0.17 | 1.12 ± 0.08 | 1.10 ± 0.09 | 1.09 ± 0.07 | 1.04 ± 0.09 |
ψ0 | 0.62 ± 0.05 | 0.63 ± 0.04 | 0.63 ± 0.04 | 0.65 ± 0.02 | 0.68 ± 0.02** |
φE0 | 0.47 ± 0.03* | 0.48 ± 0.03 | 0.50 ± 0.04 | 0.53 ± 0.03* | 0.57 ± 0.02** |
RC/CS | 774.29 ± 74.28** | 827.49 ± 63.60* | 936.95 ± 83.66 | 1057.84 ± 113.21* | 1265.13 ± 153.23** |
表1 风蚀和沙埋对骆驼刺叶绿素荧光参数的影响(平均值±标准偏差)
Table 1 Effect of fluorescence parameters in Alhagi sparsifolia under wind erosion and sand burial (mean ± SD)
参数 Parameter | 处理 Treatment | ||||
---|---|---|---|---|---|
SE | ME | CK | MB | SB | |
Fv/Fm | 0.76 ± 0.01* | 0.77 ± 0.01 | 0.79 ± 0.01 | 0.82 ± 0.02* | 0.84 ± 0.01** |
ABS/RC | 2.42 ± 0.19** | 2.31 ± 0.14 | 2.21 ± 0.17 | 2.04 ± 0.14* | 1.82 ± 0.17** |
TR0/RC | 1.83 ± 0.14 | 1.78 ± 0.09 | 1.76 ± 0.12 | 1.67 ± 0.09 | 1.53 ± 0.12* |
ET0/RC | 1.15 ± 0.17 | 1.12 ± 0.08 | 1.10 ± 0.09 | 1.09 ± 0.07 | 1.04 ± 0.09 |
ψ0 | 0.62 ± 0.05 | 0.63 ± 0.04 | 0.63 ± 0.04 | 0.65 ± 0.02 | 0.68 ± 0.02** |
φE0 | 0.47 ± 0.03* | 0.48 ± 0.03 | 0.50 ± 0.04 | 0.53 ± 0.03* | 0.57 ± 0.02** |
RC/CS | 774.29 ± 74.28** | 827.49 ± 63.60* | 936.95 ± 83.66 | 1057.84 ± 113.21* | 1265.13 ± 153.23** |
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