Monson R K, Harley P C, Litvak M E, Wildermuth M, Guenther A B, Zimmerman P R, Fall R
Department of Environmental, Population, and Organismic Biology, University of Colorado, 80309, Boulder, CO, USA.
Atmospheric Chemistry Division, National Center for Atmospheric Research, 80307, Boulder, CO, USA.
Oecologia. 1994 Sep;99(3-4):260-270. doi: 10.1007/BF00627738.
Isoprene emission from plants represents one of the principal biospheric controls over the oxidative capacity of the continental troposphere. In the study reported here, the seasonal pattern of isoprene emission, and its underlying determinants, were studied for aspen trees growing in the Rocky Mountains of Colorado. The springtime onset of isoprene emission was delayed for up to 4 weeks following leaf emergence, despite the presence of positive net photosynthesis rates. Maximum isoprene emission rates were reached approximately 6 weeks following leaf emergence. During this initial developmental phase, isoprene emission rates were negatively correlated with leaf nitrogen concentrations. During the autumnal decline in isoprene emission, rates were positively correlated with leaf nitrogen concentration. Given past studies that demonstrate a correlation between leaf nitrogen concentration and isoprene emission rate, we conclude that factors other than the amount of leaf nitrogen determine the early-season initiation of isoprene emission. The late-season decline in isoprene emission rate is interpreted as due to the autumnal breakdown of metabolic machinery and loss of leaf nitrogen. In potted aspen trees, leaves that emerged in February and developed under cool, springtime temperatures did not emit isoprene until 23 days after leaf emergence. Leaves that emrged in July and developed in hot, midsummer temperatures emitted isoprene within 6 days. Leaves that had emerged during the cool spring, and had grown for several weeks without emitting isoprene, could be induced to emit isoprene within 2 h of exposure to 32°C. Continued exposure to warm temperatures resulted in a progressive increase in the isoprene emission rate. Thus, temperature appears to be an important determinant of the early season induction of isoprene emission. The seasonal pattern of isoprene emission was examined in trees growing along an elevational gradient in the Colorado Front Range (1829-2896 m). Trees at different elevations exhibited staggered patterns of bud-break and initiation of photosynthesis and isoprene emission in concert with the staggered onset of warm, springtime temperatures. The springtime induction of isoprene emission could be predicted at each of the three sites as the time after bud break required for cumulative temperatures above 0°C to reach approximately 400 degree days. Seasonal temperature acclimation of isoprene emission rate and photosynthesis rate was not observed. The temperature dependence of isoprene emission rate between 20 and 35°C could be accurately predicted during spring and summer using a single algorithm that describes the Arrhenius relationship of enzyme activity. From these results, it is concluded that the early season pattern of isoprene emission is controlled by prevailing temperature and its interaction with developmental processes. The late-season pattern is determined by controls over leaf nitrogen concentration, especially the depletion of leaf nitrogen during senescence. Following early-season induction, isoprene emission rates correlate with photosynthesis rates. During the season there is little acclimation to temperature, so that seasonal modeling simplifies to a single temperature-response algorithm.
植物释放异戊二烯是对大陆对流层氧化能力的主要生物地球化学控制之一。在本研究中,我们对生长在科罗拉多州落基山脉的白杨树叶异戊二烯排放的季节模式及其潜在决定因素进行了研究。尽管净光合速率为正,但在叶片出现后的4周内,异戊二烯排放的春季开始时间有所延迟。叶片出现后约6周达到最大异戊二烯排放速率。在这个初始发育阶段,异戊二烯排放速率与叶片氮浓度呈负相关。在秋季异戊二烯排放下降期间,排放速率与叶片氮浓度呈正相关。鉴于以往的研究表明叶片氮浓度与异戊二烯排放速率之间存在相关性,我们得出结论,除了叶片氮含量之外的其他因素决定了异戊二烯排放的早期开始。异戊二烯排放速率在季节后期的下降被解释为由于代谢机制的秋季分解和叶片氮的损失。在盆栽白杨树上,2月出现并在凉爽的春季温度下发育的叶片直到叶片出现后23天才释放异戊二烯。7月出现并在炎热的仲夏温度下发育的叶片在6天内释放异戊二烯。在凉爽的春季出现并生长了几周而未释放异戊二烯的叶片,在暴露于32°C的2小时内可被诱导释放异戊二烯。持续暴露于温暖温度导致异戊二烯排放速率逐渐增加。因此,温度似乎是异戊二烯排放早期诱导的重要决定因素。我们研究了科罗拉多前山海拔梯度(1829 - 2896米)上树木的异戊二烯排放季节模式。不同海拔的树木表现出芽萌发、光合作用和异戊二烯排放开始的交错模式,与温暖春季温度的交错开始一致。在三个地点中的每一个,异戊二烯排放的春季诱导都可以预测为芽萌发后累积温度高于0°C达到约400度日所需的时间。未观察到异戊二烯排放速率和光合速率的季节温度适应性。在春季和夏季,使用描述酶活性的阿伦尼乌斯关系的单一算法可以准确预测20至35°C之间异戊二烯排放速率对温度的依赖性。从这些结果可以得出结论,异戊二烯排放的早期季节模式受当时温度及其与发育过程的相互作用控制。后期季节模式由对叶片氮浓度的控制决定,特别是衰老期间叶片氮的消耗。在早期季节诱导之后,异戊二烯排放速率与光合速率相关。在季节期间,对温度的适应性很小,因此季节建模简化为单一的温度响应算法。