Sengar Rakesh Singh, Gautam Madhu, Sengar Rajesh Singh, Garg Sanjay Kumar, Sengar Kalpana, Chaudhary Reshu
Institute of Management Studies, C-238, Bulandshahr Road, Indl, Area, Lal Quan, G.T. Road, Ghaziabad, India.
Rev Environ Contam Toxicol. 2008;196:73-93. doi: 10.1007/978-0-387-78444-1_3.
Lead is a metallic pollutant emanating from various environmental sources including industrial wastes, combustion of fossil fuels, and use of agrochemicals. Lead may exist in the atmosphere as dusts, fumes, mists, and vapors, and in soil as a mineral. Soils along roadsides are rich in lead because vehicles burn leaded gasoline, which contributes to environmental lead pollution. Other important sources of lead pollution are geological weathering, industrial processing of ores and minerals, leaching of lead from solid wastes, and animal and human excreta. Lead is nondegradable, readily enters the food chain, and can subsequently endanger human and animal health. Lead is one of the most important environment pollutants and deserves the increasing attention it has received in recent decades. The present effort was undertaken to review lead stress effects on the physiobiochemical activity of higher plants. Lead has gained considerable attention as a potent heavy metal pollutant because of growing anthropogenic pressure on the environment. Lead-contaminated soils show a sharp decline in crop productivity. Lead is absorbed by plants mainly through the root system and in minor amounts through the leaves. Within the plants, lead accumulates primarily in roots, but some is translocated to aerial plant parts. Soil pH, soil particle size, cation-exchange capacity, as well as root surface area, root exudation, and mycorrhizal transpiration rate affect the availability and uptake of lead by plants. Only a limited amount of lead is translocated from roots to other organs because there are natural plant barriers in the root endodermis. At lethal concentrations, this barrier is broken and lead may enter vascular tissues. Lead in plants may form deposits of various sizes, present mainly in intercellular spaces, cell walls, and vacuoles. Small deposits of this metal are also seen in the endoplasmic reticulum, dictyosome, and dictyosome-derived vesicles. After entering the cells, lead inhibits activities of many enzymes, upsets mineral nutrition and water balance, changes the hormonal status, and affects membrane structure and permeability. Visual, nonspecific symptoms of lead toxicity are stunted growth, chlorosis, and blackening of the root system. In most cases, lead inhibition of enzyme activities results from the interaction of the metal with enzyme -SH groups. The activities of metalloenzymes may decline as a consequence of displacement of an essential metal by lead from the active sites of the enzymes. Lead decreases the photosynthetic rate of plants by distorting chloroplast ultrastructure, diminishing chlorophyll synthesis, obstructing electron transport, and inhibiting activities of Calvin cycle enzymes.
铅是一种金属污染物,来自各种环境源,包括工业废物、化石燃料燃烧和农用化学品的使用。铅在大气中可能以粉尘、烟雾、雾气和蒸气的形式存在,在土壤中则以矿物质的形式存在。路边的土壤富含铅,因为车辆燃烧含铅汽油,这导致了环境铅污染。铅污染的其他重要来源是地质风化、矿石和矿物的工业加工、固体废物中铅的浸出以及动物和人类排泄物。铅不可降解,很容易进入食物链,随后可能危及人类和动物健康。铅是最重要的环境污染物之一,近几十年来受到了越来越多的关注。目前的工作是对铅胁迫对高等植物生理生化活性的影响进行综述。由于人类活动对环境的压力不断增加,铅作为一种强大的重金属污染物受到了相当大的关注。受铅污染的土壤作物生产力急剧下降。铅主要通过根系被植物吸收,少量通过叶片吸收。在植物体内,铅主要积累在根部,但也有一些会转移到地上部分。土壤pH值、土壤颗粒大小、阳离子交换能力以及根表面积、根系分泌物和菌根蒸腾速率都会影响植物对铅的有效性和吸收。只有有限量的铅从根部转移到其他器官,因为根内皮层存在天然的植物屏障。在致死浓度下,这个屏障会被打破,铅可能进入维管组织。植物中的铅可能形成大小不一的沉积物,主要存在于细胞间隙、细胞壁和液泡中。在内质网、高尔基体和高尔基体衍生的小泡中也可以看到这种金属的小沉积物。进入细胞后,铅会抑制许多酶的活性,扰乱矿物质营养和水分平衡,改变激素状态,并影响膜结构和通透性。铅毒性的可见、非特异性症状是生长受阻、黄化和根系变黑。在大多数情况下,铅对酶活性的抑制是由于金属与酶的-SH基团相互作用。金属酶的活性可能会因铅从酶的活性位点取代必需金属而下降。铅通过扭曲叶绿体超微结构、减少叶绿素合成、阻碍电子传递和抑制卡尔文循环酶的活性来降低植物的光合速率。