Human activity in the last century has led to a significant increase in nitrogen (N) emissions and atmospheric deposition. This N deposition has reached a level that has caused or is likely to cause alterations to the structure and function of many ecosystems across the United States. One approach for quantifying the deposition of pollution that would be harmful to ecosystems is the determination of critical loads. A critical load is defined as the input of a pollutant below which no detrimental ecological effects occur over the long-term according to present knowledge. The objectives of this project were to synthesize current research relating atmospheric N deposition to effects on terrestrial and freshwater ecosystems in the United States, and to estimate associated empirical N critical loads. The receptors considered included freshwater diatoms, mycorrhizal fungi, lichens, bryophytes, herbaceous plants, shrubs, and trees. Ecosystem impacts included: (1) biogeochemical responses and (2) individual species, population, and community responses. Biogeochemical responses included increased N mineralization and nitrification (and N availability for plant and microbial uptake), increased gaseous N losses (ammonia volatilization, nitric and nitrous oxide from nitrification and denitrification), and increased N leaching. Individual species, population, and community responses included increased tissue N, physiological and nutrient imbalances, increased growth, altered root : shoot ratios, increased susceptibility to secondary stresses, altered fire regime, shifts in competitive interactions and community composition, changes in species richness and other measures of biodiversity, and increases in invasive species. The range of critical loads for nutrient N reported for U.S. ecoregions, inland surface waters, and freshwater wetlands is 1–39 kg N·ha−1·yr−1, spanning the range of N deposition observed over most of the country. The empirical critical loads for N tend to increase in the following sequence for different life forms: diatoms, lichens and bryophytes, mycorrhizal fungi, herbaceous plants and shrubs, and trees. The critical load approach is an ecosystem assessment tool with great potential to simplify complex scientific information and communicate effectively with the policy community and the public. This synthesis represents the first comprehensive assessment of empirical critical loads of N for major ecoregions across the United States.
展开▼
机译:上个世纪的人类活动已导致氮(N)排放和大气沉积的显着增加。氮的沉积已达到已经或可能导致美国许多生态系统结构和功能发生变化的水平。量化对生态系统有害的污染沉积的一种方法是确定关键负荷。临界负荷定义为污染物的输入,根据目前的知识,在污染物的长期输入下,不会产生有害的生态影响。该项目的目的是综合目前有关大气N沉积与对美国陆地和淡水生态系统影响的研究,并估算相关的经验N临界负荷。所考虑的受体包括淡水硅藻,菌根真菌,地衣,苔藓植物,草本植物,灌木和树木。生态系统的影响包括:(1)生物地球化学反应和(2)个别物种,种群和社区反应。生物地球化学反应包括增加的氮矿化和硝化作用(以及植物和微生物吸收氮的有效性),增加的气态氮损失(氨挥发,硝化作用和反硝化作用产生的一氧化氮和一氧化二氮)以及增加的氮淋滤。个体物种,种群和社区的反应包括组织氮增加,生理和养分失衡,生长增加,根比率改变,对次要胁迫的敏感性增加,火势改变,竞争性相互作用和群落组成的变化,物种丰富度和生物多样性的其他衡量标准,以及入侵物种的增加。据报道,美国生态区,内陆地表水和淡水湿地中养分N的临界负荷范围为1–39 kg N·ha-1·yr-1,覆盖了美国大部分地区的N沉降范围。对于N的经验性临界负荷,对于不同的生命形式,依次按以下顺序增加:硅藻,地衣和苔藓植物,菌根真菌,草本植物,灌木和树木。关键负荷方法是一种生态系统评估工具,具有极大的潜力,可简化复杂的科学信息并与政策界和公众进行有效沟通。该综合报告是对美国主要生态区域的N经验临界负荷的首次全面评估。
展开▼