Sparling D W, Lowe T P
National Biological Service, Patuxent Environmental Science Center, Laurel, MD 20708, USA.
Rev Environ Contam Toxicol. 1996;145:1-127. doi: 10.1007/978-1-4612-2354-2_1.
Aluminum is extremely common throughout the world and is innocuous under circumneutral or alkaline conditions. However, in acidic environments, it can be a major limiting factor to many plants and aquatic organisms. The greatest concern for toxicity in North America occurs in areas that are affected by wet and dry acid deposition, such as eastern Canada and the northeastern U.S. Acid mine drainage, logging, and water treatment plant effluents containing alum can be other major sources of Al. In solution, the metal can combine with several different agents to affect toxicity. In general, Al hydroxides and monomeric Al are the most toxic forms. Dissolved organic carbons, F, PO(3)3- and SO(4)2- ameliorate toxicity by reducing bioavailability. Elevated metal levels in water and soil can cause serious problems for some plants. Algae tend to be both acid- and Al tolerant and, although some species may disappear with reduced pH, overall algae productivity and biomass are seldom affected if pH is above 3.0. Aluminum and acid toxicity tend to be additive to some algae when pH is less than 4.5. Because the metal binds with inorganic P, it may reduce P availability and reduce productivity. Forest die-backs in North America involving red spruce, Fraser fir, balsam fir, loblolly pine, slash pine, and sugar maples have been ascribed to Al toxicity, and extensive areas of European forests have died because of the combination of high soil Al and low pH. Extensive research on crops has produced Al-resistant cultivars and considerable knowledge about mechanisms of and defenses against toxicity. Very low Al levels may benefit some plants, although the metal is not recognized as an essential nutrient. Hyperaccumulator species of plants may concentrate Al to levels that are toxic to herbivores. Toxicity in aquatic invertebrates is also acid dependent. Taxa such as Ephemeroptera, Plecoptera, and Cladocera are sensitive and may perish when Al is less than 1 mg.L-1 whereas dipterans, molluscs, and isopods seem to be tolerant. In Al-sensitive species, elevated levels (approximately 500 micrograms.L-1) affect ion regulation and respiratory efficiency. Toxicity tends to be greatest near a species' threshold of pH sensitivity. At lower pHs, Al may have a slight ameliorative effect by interfering with H+ transport across membranes. Aquatic invertebrates can accumulate very high levels of Al, but most of this appears to be through adsorption rather than assimilation. Aluminum concentrations may be as high as 5000 mg.kg-1 in insects and greater than 17,000 mg.kg-1 in other invertebrates.(ABSTRACT TRUNCATED AT 400 WORDS)
铝在全球极为常见,在中性或碱性条件下是无害的。然而,在酸性环境中,它可能成为许多植物和水生生物的主要限制因素。北美对毒性最为担忧的地区出现在受干湿酸沉降影响的区域,如加拿大东部和美国东北部。酸性矿山排水、伐木以及含有明矾的水处理厂废水可能是铝的其他主要来源。在溶液中,这种金属可与多种不同介质结合以影响毒性。一般来说,氢氧化铝和单体铝是毒性最强的形式。溶解有机碳、氟、磷酸根离子和硫酸根离子通过降低生物可利用性来减轻毒性。水和土壤中金属含量升高会给一些植物带来严重问题。藻类往往既耐酸又耐铝,虽然有些物种可能会随着pH值降低而消失,但如果pH值高于3.0,藻类的总体生产力和生物量很少受到影响。当pH值小于4.5时,铝和酸的毒性对一些藻类往往具有累加作用。由于这种金属与无机磷结合,它可能会降低磷的有效性并降低生产力。北美涉及红云杉、弗雷泽冷杉、香脂冷杉、火炬松、湿地松和糖枫的森林衰退被归因于铝毒性,欧洲大片森林因土壤高铝和低pH值的共同作用而死亡。对农作物的广泛研究已培育出耐铝品种,并积累了大量关于毒性机制及防御方面的知识。尽管铝不被视为必需营养素,但极低水平的铝可能对某些植物有益。植物的超积累物种可能会将铝浓缩到对食草动物有毒的水平。水生无脊椎动物的毒性也取决于酸度。蜉蝣目、襀翅目和枝角类等分类群很敏感,当铝含量低于1毫克/升时可能会死亡,而双翅目、软体动物和等足类似乎具有耐受性。在对铝敏感的物种中,铝含量升高(约500微克/升)会影响离子调节和呼吸效率。毒性往往在物种对pH敏感性的阈值附近最大。在较低的pH值下,铝可能通过干扰氢离子跨膜运输而产生轻微的改善作用。水生无脊椎动物可以积累非常高含量的铝,但其中大部分似乎是通过吸附而非同化作用。昆虫体内的铝浓度可能高达5000毫克/千克,其他无脊椎动物体内则超过17000毫克/千克。(摘要截取自400字)