Ecotoxicology of Air Pollutants CIEMAT (Ed.70), Avda. Complutense 40, 28040, Madrid, Spain.
Environ Pollut. 2017 Jan;220(Pt A):186-195. doi: 10.1016/j.envpol.2016.09.038. Epub 2016 Oct 15.
Ozone (O) critical levels (CLe) are still poorly developed for herbaceous vegetation. They are currently based on single species responses which do not reflect the multi-species nature of semi-natural vegetation communities. Also, the potential effects of other factors like the nitrogen (N) input are not considered in their derivation, making their use uncertain under natural conditions. Exposure- and dose-response relationships were derived from two open-top chamber experiments exposing a mixture of 6 representative annual Mediterranean pasture species growing in natural soil to 4 O fumigation levels and 3 N inputs. The Deposition of O and Stomatal Exchange model (DOSE) was modified to account for the multi-species nature of the canopy following a big-leaf approach. This new approach was used for estimating a multi-species phytotoxic O dose (POD). Response relationships were derived based on O exposure (AOT40) and flux (POD) indices. The treatment effects were similar in the two seasons: O reduced the aboveground biomass growth and N modulated this response. Gas exchange rates presented a high inter-specific variability and important inter-annual fluctuations as a result of varying growing conditions during the two years. The AOT40-based relationships were not statistically significant except when the highest N input was considered alone. In contrast, POD relationships were all significant but for the lowest N input level. The influence of the N input on the exposure- and dose-response relationships implies that N can modify the O CLe. However, this is an aspect that has not been considered so far in the methodologies for establishing O CLe. Averaging across N input levels, a multi-species O CLe (CLe) is proposed POD = 7.9 mmol m, accumulated over 1.5 month with a 95% confidence interval of (5.9, 9.8). Further efforts will be needed for comparing the CLe with current O CLe based on single species responses.
臭氧 (O) 临界水平 (CLe) 对于草本植被仍未得到充分发展。它们目前基于单一物种的反应,不能反映半自然植被群落的多物种性质。此外,在推导臭氧临界水平时,没有考虑氮 (N) 输入等其他因素的潜在影响,使得它们在自然条件下的使用不确定。暴露和剂量反应关系是从两个开顶式气室实验中得出的,该实验将 6 种代表地中海一年生牧场物种的混合物暴露在 4 种臭氧熏蒸水平和 3 种 N 输入下,这些物种在自然土壤中生长。臭氧沉积和气孔交换模型 (DOSE) 进行了修改,以根据树冠的多物种性质采用大叶片方法进行核算。这种新方法用于估计多物种臭氧毒性剂量 (POD)。根据臭氧暴露 (AOT40) 和通量 (POD) 指数得出响应关系。这两个季节的处理效果相似:臭氧降低了地上生物量的生长,而 N 调节了这种反应。由于两年间生长条件的变化,气体交换率呈现出高度的种间变异性和重要的年际波动。基于 AOT40 的关系除了在单独考虑最高 N 输入时没有统计学意义。相比之下,除了最低 N 输入水平外,POD 关系均具有统计学意义。N 输入对暴露和剂量反应关系的影响表明,N 可以改变臭氧临界水平。然而,到目前为止,在建立臭氧临界水平的方法中还没有考虑到这一点。在平均 N 输入水平下,提出了一种多物种臭氧临界水平 (CLe),即 POD = 7.9 mmol m,在 1.5 个月内累积,95%置信区间为 (5.9, 9.8)。需要进一步努力将 CLe 与基于单一物种反应的当前臭氧 CLe 进行比较。