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首页> 外文期刊>The Science of the Total Environment >Stomatal uptake of O_3 in a Schima superba plantation in subtropical China derived from sap flow measurements
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Stomatal uptake of O_3 in a Schima superba plantation in subtropical China derived from sap flow measurements

机译:来自树液流量测量的中国亚热带木荷树人工林的O_3气孔吸收

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摘要

Canopy stomatal ozone (O_3) flux (F_(st,O3)) in a plantation of Schima superba, an ecologically and economically important evergreen pioneer tree species in subtropical China, was quantified based on sap flow measurements during a 2-year period. Mean F_(st,O3) and accumulated F_(st,O3) (AF_(st)0) were significantly higher in wet seasons from April to September (4.62 nmol m~(-2) s~(-1) and 35.37 mmol m~(-2), respectively) than in dry seasons from October to March (3.90 nmol m~(-2) s~(-1) and 24.15 mmol m~(-1), respectively), yet comparable between the 2 years of the experiment, being 4.23 nmol m~(-2) s~(-1) and 58.23 mmol m~(-2) in April 2013-March 2014 and 4.29 nmol m~(-2) s~(-1) and 60.80 mmol m~(-2) in April 2014-March 2015, respectively. At the diurnal scale, F_(st,O3) generally peaked in the early to middle afternoon hours (13:00-15:00), while the maximum stomatal conductance (G_(st,O3)) typically occurred in the middle to late morning hours (09:00-11:00). Monthly integrated AF_(st)0 reached the maximum in July, although accumulated O_3 exposure (SUM0) was highest in October. Seasonally or yearly, the accumulated O_3 doses, either exposure-based or flux-based, notably exceeded the currently adopted critical thresholds for the protection of forest trees. These results, on the one hand, demonstrated the decoupling between the stomatal uptake of O_3 and its environmental exposure level; on the other hand, indicated the potential O_3 risk for S. superba in the experimental site. Therefore, the present study endorses the use of sap flow measurements as a feasible tool for estimating F_(st,O3), and the transition from the exposure-based toward flux-based metrics for assessing O_3 risk for forest trees. Further studies are urgently needed to relate stomatal O_3 uptake doses with tree growth reductions for an improved understanding of O_3 effects on trees under natural conditions.
机译:基于2年期间的汁液流量定量研究了一种荷叶人工林冠层气孔臭氧(O_3)通量(F_(st,O3)),它是中国亚热带生态和经济重要的常绿先锋树种。在4月至9月的雨季,平均F_(st,O3)和累积F_(st,O3)(AF_(st)0)显着更高(4.62 nmol m〜(-2)s〜(-1)和35.37 mmol m〜(-2)分别比10月至3月的旱季(分别为3.90 nmol m〜(-2)s〜(-1)和24.15 mmol m〜(-1)),但两者之间具有可比性的实验年份,2013年4月至2014年3月分别为4.23 nmol m〜(-2)s〜(-1)和58.23 mmol m〜(-2)和4.29 nmol m〜(-2)s〜(-1) 2014年4月至2015年3月分别为60.80 mmol m〜(-2)和60.80 mmol m〜(-2)。在昼夜尺度上,F_(st,O3)通常在午后至中午(13:00-15:00)达到峰值,而最大气孔导度(G_(st,O3))通常发生在中晚期。早上(09:00-11:00)。尽管7月的累积O_3暴露量(SUM0)最高,但7月的​​月累积AF_(st)0达到了最大值。季节性或每年累积的O_3剂量,无论是基于暴露的还是基于通量的,都大大超过了目前采用的保护林木的临界阈值。这些结果一方面证明了气孔对O_3的吸收与其环境暴露水平之间的脱钩。另一方面,这表明在实验地点发生超级链球菌的潜在O_3风险。因此,本研究支持使用树液流量测量作为估算F_(st,O3)的可行工具,以及从基于暴露的评估向基于通量的评估森林树木的O_3风险的过渡。迫切需要进一步的研究,以将气孔吸收O_3的剂量与树木生长的减少联系起来,以更好地了解自然条件下O_3对树木的影响。

著录项

  • 来源
    《The Science of the Total Environment》 |2016年第1期|465-475|共11页
  • 作者单位

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

    Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China,Guangdong Provincial Key Laboratory of Applied Botany, South China Botanical Garden, Chinese Academy of Sciences, Xingke Road 523, Tianhe District, Guangzhou 510650, China;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Schima superba; Sap flow; Stomatal conductance; Ozone uptake; Risk assessment;

    机译:木荷液流气孔导度臭氧吸收;风险评估;

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