Krupa S V, Kickert R N
Department of Plant Pathology, University of Minnesota, St Paul, MN 55108, USA.
Environ Pollut. 1989;61(4):263-393. doi: 10.1016/0269-7491(89)90166-8.
There is a fast growing and an extremely serious international scientific, public and political concern regarding man's influence on the global climate. The decrease in stratospheric ozone (O3) and the consequent possible increase in ultraviolet-B (UV-B) is a critical issue. In addition, tropospheric concentrations of 'greenhouse gases' such as carbon dioxide (CO2), nitrous oxide (N2O) and methane (CH4) are increasing. These phenomena, coupled with man's use of chlorofluorocarbons (CFCs), chlorocarbons (CCs), and organo-bromines (OBs) are considered to result in the modification of the earth's O3 column and altered interactions between the stratosphere and the troposphere. A result of such interactions could be the global warming. As opposed to these processes, tropospheric O3 concentrations appear to be increasing in some parts of the world (e.g. North America). Such tropospheric increases in O3 and particulate matter may offset any predicted increases in UV-B at those locations. Presently most general circulation models (GCMs) used to predict climate change are one- or two-dimensional models. Application of satisfactory three-dimensional models is limited by the available computer power. Recent studies on radiative cloud forcing show that clouds may have an excess cooling effect to compensate for a doubling of global CO2 concentrations. There is a great deal of geographic patchiness or variability in climate. Use of global level average values fails to account for this variability. For example, in North America: 1. there may be a decrease in the stratospheric O3 column (1-3%); however, there appears to be an increase in tropospheric O3 concentrations (1-2%/year) to compensate up to 20-30% loss in the total O3 column; 2. there appears to be an increase in tropospheric CO2, N2O and CH4 at the rate of roughly 0.8%, 0.3% and 1-2%, respectively, per year; 3. there is a decrease in erythemal UV-B; and 4. there is a cooling of tropospheric air temperature due to radiative cloud forcing. The effects of UV-B, CO2 and O3 on plants have been studied under growth chamber, greenhouse and field conditions. Few studies, if any, have examined the joint effects of more than one variable on plant response. There are methodological problems associated with many of these experiments. Thus, while results obtained from these studies can assist in our understanding, they must be viewed with caution in the context of the real world and predictions into the future. Biomass responses of plants to enhanced UV-B can be negative (adverse effect); positive (stimulatory effect) or no effect (tolerant). Sensitivity rankings have been developed for both crop and tree species. However, such rankings for UV-B do not consider dose-response curves. There are inconsistencies between the results obtained under controlled conditions versus field observations. Some of these inconsistencies appear due to the differences in responses between cultivars and varieties of a given plant species; and differences in the experimental methodology and protocol used. Nevertheless, based on the available literature, listings of sensitive crop and native plant species to UV-B are provided. Historically, plant biologists have studied the effects of CO2 on plants for many decades. Experiments have been performed under growth chamber, greenhouse and field conditions. Evidence is presented for various plant species in the form of relative yield increases due to CO2 enrichment. Sensitivity rankings (biomass response) are agein provided for crops and native plant species. However, most publications on the numerical analysis of cause-effect relationships do not consider sensitivity analysis of the mode used. Ozone is considered to be the most phytotoxic regional scale air pollutant. In the pre-occupation of loss in the O3 column, any increases in tropospheric O3 concentrations may be undermined relative to vegetation effects. As with the other stress factors, the effects of O3 have been studied both under controlled and field conditions. Thboth under controlled and field conditions. The numerical explanation of cause-effect relationships of O3 is a much debated subject at the present time. Much of the controversy is directed toward the definition of the highly stochastic, O3 exposure dynamics in time and space. Nevertheless, sensitivity rankings (biomass response) are provided for crops and native vegetation. The joint effects of UV-B, CO2 and O3 are poorly understood. Based on the literature of plant response to individual stress factors and chemical and physical climatology of North America, we conclude that nine different crops may be sensitive to the joint effects: three grain and six vegetable crops (sorghum, oat, rice, pea, bean, potato, lettuce, cucumber and tomato). In North America, we consider Ponderosa and loblolly pines as vulnerable among tree species. This conclusion should be moderated by the fact that there are few, if any, data on hardwood species. In conclusion there is much concern for global climate change and its possible effects on vegetation. While this is necessary, such a concern and any predictions must be tempered by the lack of sufficient knowledge. Experiments must be designed on an integrated and realistic basis to answer the question more definitively. This would require very close co-operation and communication among scientists from multiple disciplines. Decision makers must realize this need.
国际上对人类影响全球气候的问题日益关注,这种关注增长迅速且极为严峻。平流层臭氧(O3)减少以及随之而来的紫外线B(UV - B)可能增加是一个关键问题。此外,对流层中二氧化碳(CO2)、氧化亚氮(N2O)和甲烷(CH4)等“温室气体”的浓度正在上升。这些现象,再加上人类对氯氟烃(CFCs)、碳氯化合物(CCs)和有机溴(OBs)的使用,被认为会导致地球臭氧柱的改变以及平流层与对流层之间相互作用的变化。这种相互作用的一个结果可能是全球变暖。与这些过程相反,对流层臭氧浓度在世界某些地区(如北美)似乎正在增加。对流层中臭氧和颗粒物的这种增加可能会抵消这些地区预计的紫外线B增加。目前,用于预测气候变化的大多数通用循环模型(GCMs)是一维或二维模型。令人满意的三维模型的应用受到可用计算机能力的限制。最近关于辐射云强迫的研究表明,云可能具有额外的冷却效应,以补偿全球二氧化碳浓度翻倍的影响。气候存在很大的地理斑块性或变异性。使用全球平均水平未能考虑到这种变异性。例如,在北美:1. 平流层臭氧柱可能会减少(1 - 3%);然而,对流层臭氧浓度似乎在增加(每年1 - 2%),以补偿总臭氧柱中高达20 - 30%的损失;2. 对流层中的二氧化碳、氧化亚氮和甲烷似乎分别以每年约0.8%、0.3%和1 - 2%的速度增加;3. 红斑紫外线B减少;4. 由于辐射云强迫,对流层气温下降。已经在生长室、温室和田间条件下研究了紫外线B、二氧化碳和臭氧对植物的影响。很少有研究(如果有的话)考察了多个变量对植物反应的联合影响。这些实验中有许多存在方法学问题。因此,虽然从这些研究中获得的结果有助于我们理解,但在现实世界和未来预测的背景下,必须谨慎看待这些结果。植物对增强的紫外线B的生物量反应可能是负面的(不利影响)、正面的(刺激作用)或无影响(耐受)。已经为作物和树种制定了敏感性排名。然而,这种紫外线B的排名没有考虑剂量反应曲线。在受控条件下获得的结果与田间观察结果之间存在不一致。其中一些不一致似乎是由于给定植物物种的品种和变种之间的反应差异;以及所使用的实验方法和方案的差异。尽管如此,根据现有文献,提供了对紫外线B敏感的作物和本地植物物种列表。从历史上看,植物生物学家已经研究二氧化碳对植物的影响数十年了。已经在生长室、温室和田间条件下进行了实验。以二氧化碳富集导致的相对产量增加的形式为各种植物物种提供了证据。再次为作物和本地植物物种提供了敏感性排名(生物量反应)。然而,大多数关于因果关系数值分析的出版物没有考虑所使用模式的敏感性分析。臭氧被认为是最具植物毒性的区域尺度空气污染物。在关注臭氧柱损失的情况下,相对于植被影响,对流层臭氧浓度的任何增加可能会被削弱。与其他胁迫因素一样,已经在受控和田间条件下研究了臭氧的影响。目前,臭氧因果关系的数值解释是一个备受争议的话题。许多争议都指向高度随机的臭氧暴露在时间和空间上的动态定义。尽管如此,还是为作物和本地植被提供了敏感性排名(生物量反应)。对紫外线B、二氧化碳和臭氧的联合影响了解甚少。根据植物对单个胁迫因素的反应以及北美的化学和物理气候学文献,我们得出结论,九种不同的作物可能对联合影响敏感:三种谷物作物和六种蔬菜作物(高粱、燕麦、水稻、豌豆、豆类、土豆、生菜、黄瓜和番茄)。在北美,我们认为黄松和火炬松在树种中较为脆弱。由于关于硬木物种的数据很少(如果有的话),这一结论应有所缓和。总之,人们对全球气候变化及其对植被可能产生的影响非常关注。虽然这是必要的,但这种关注和任何预测都必须因缺乏足够的知识而有所缓和。必须在综合和现实的基础上设计实验,以便更明确地回答这个问题。这将需要多个学科的科学家之间非常密切的合作与交流。决策者必须认识到这一需求。