英语翻译IntroductionSince the beginning of the twentieth century,air pollution has worsened as a consequence of urbanization and industrialization,together with the rapid growth of motorized transportation and population.Of the main components of

英语翻译IntroductionSince the beginning of the twentieth century,air pollution has worsened as a consequence of urbanization and industrialization,together with the rapid growth of motorized transportation and population.Of the main components of
英语翻译
Introduction
Since the beginning of the twentieth century,air pollution has worsened as a consequence of urbanization and industrialization,together with the rapid growth of motorized transportation and population.Of the main components of air pollu- tants,an important group to be considered is that of heavy metals,mostly associated with airborne particulate matter.This is particularly true in city centers,where vehicle engines,as well as the heat- ing systems inside buildings,represent the most important sources of air pollution (Sawidis et al.
1995; Monaci et al.2000).
\x05Environmental monitoring methods are based on expensive and sophisticated measuring sys- tems.Since the element composition of vascular plants,bryophytes and lichens can change as a consequence of pollution,a complementary use of their parts as biomonitors may be an appropriate alternative (Bargagli 1998; Bari et al.2001).The organisms most frequently used for monitoring metal pollutants are lower plants,such as mosses,and lichens (Conti and Cecchetti 2001; Adamo et al.2003; Figueira et al.2002) due to their con- siderable ability to accumulate metals.However,since these organisms are rare in urban areas with high degrees of pollution,in recent years,the use of vascular plants has been introduced to monitor heavy metal pollution (Sawidis et al.1995).The aim of this work is to test the diff erent heavy metal accumulation capabilities in a sper- matophyte and two lichens transplanted to an urban area in order to quantify the suitability of different taxa for monitoring airborne heavy metals.\x05
since these organisms are rare in urban areas with high degrees of pollution,in recent years,the use of vascular plants has been introduced to monitor heavy metal pollution (Sawidis et al.1995).
The aim of this work is to test the diff erent heavy metal accumulation capabilities in a sper- matophyte and two lichens transplanted to an urban area in order to quantify the suitability of diff erent
different后面还有一句话taxa for monitoring airborne heavy metals.

英语翻译IntroductionSince the beginning of the twentieth century,air pollution has worsened as a consequence of urbanization and industrialization,together with the rapid growth of motorized transportation and population.Of the main components of
Since the beginning of the twentieth century,air pollution has worsened as a consequence of urbanization and industrialization,together with the rapid growth of motorized transportation and population.Of the main components of air pollu- tants,an important group to be considered is that of heavy metals,mostly associated with airborne particulate matter.This is particularly true in city centers,where vehicle engines,as well as the heat- ing systems inside buildings,represent the most important sources of air pollution (Sawidis et al.从一开始的第二十个世纪,大气污染的恶化,因此城市化和工业化的快速增长,加上机动交通与人口.主要部件的空气污染剂,一个重要的群体,被认为是重金属,大多与空气中的颗粒物.尤其是在城市中心,在汽车发动机,以及热系统内的建筑物,是最重要的空气污染源（sawidis等人.1995; Monaci et al.2000).1995monaci等人.2000）.Environmental monitoring methods are based on expensive and sophisticated measuring sys- tems.Since the element composition of vascular plants,bryophytes and lichens can change as a consequence of pollution,a complementary use of their parts as biomonitors may be an appropriate alternative (Bargagli 1998; Bari et al.2001).The organisms most frequently used for monitoring metal pollutants are lower plants,such as mosses,and lichens (Conti and Cecchetti 2001; Adamo et al.2003; Figueira et al.2002) due to their con- siderable ability to accumulate metals.However,since these organisms are rare in urban areas with high degrees of pollution,in recent years,the use of vascular plants has been introduced to monitor heavy metal pollution (Sawidis et al.1995).The aim of this work is to test the diff erent heavy metal accumulation capabilities in a sper- matophyte and two lichens transplanted to an urban area in order to quantify the suitability of different taxa for monitoring airborne heavy metals.环境监测方法的基础是昂贵和复杂的测量系统方案.由于元素组成的维管束植物,苔藓和地衣可以改变由于污染的后果,补充使用其部分biomonitors可能是一个适当的替代（巴尔伽利1998；巴里等人.2001）.最常见的微生物用于监测金属污染物较低的植物,如苔藓,地衣和切凯蒂（达2001；阿达莫等.2003图片等.2002）由于其控制siderable能力积累金属.然而,因为这些生物体是罕见的在城市地区的高程度的污染,近年来,使用血管植物介绍了监测重金属污染（sawidis等人.1995）.这项工作的目的是测试不同重金属的积累能力的精子-matophyte和地衣移植到城市地区,以量化的适合不同类群监测空气中重金属.since these organisms are rare in urban areas with high degrees of pollution,in recent years,the use of vascular plants has been introduced to monitor heavy metal pollution (Sawidis et al.1995).由于这些生物体是罕见的在城市地区的高程度的污染,近年来,使用血管植物介绍了监测重金属污染（sawidis等人.1995）.The aim of this work is to test the diff erent heavy metal accumulation capabilities in a sper- matophyte and two lichens transplanted to an urban area in order to quantify the suitability of diff erenttaxa for monitoring airborne heavy metals.这项工作的目的是测试不同重金属的积累能力的精子-matophyte和地衣移植到城市地区,以量化的适宜性差异erenttaxa监测空气中重金属.

简介
二十世纪初以来，空气污染恶化，城市化和工业化的结果，连同机动运输和人口的快速增长。空气污染活性剂，要考虑的一个重要组的主要组成部分是相关的重金属，主要是颗粒物。这是特别是在城市中心，汽车发动机，以及在建筑物内的加热系统，代表空气污染的最重要来源（Sawidis等。
1995年; Monaci等。 2000年）。
环境监测方法的基础上价格昂贵和复杂的测量系统中。由于元素...

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简介
二十世纪初以来，空气污染恶化，城市化和工业化的结果，连同机动运输和人口的快速增长。空气污染活性剂，要考虑的一个重要组的主要组成部分是相关的重金属，主要是颗粒物。这是特别是在城市中心，汽车发动机，以及在建筑物内的加热系统，代表空气污染的最重要来源（Sawidis等。
1995年; Monaci等。 2000年）。
环境监测方法的基础上价格昂贵和复杂的测量系统中。由于元素组成的维管束植物，苔藓植物和地衣可以改变污染的后果，biomonitors及其零部件的互补使用可能是一个合适的替代品（Bargagli 1998年，巴里等人，2001年）。金属污染物监测中使用最频繁的生物体是较低的植物，如苔藓，地衣（Conti和Cecchetti 2001年的Adamo等，2003;等。菲盖拉2002年），由于其浓度相当的能力，积累金属。然而，由于这些微生物在城市地区，污染程度高，近年来，罕见，已使用的维管束植物监测重金属污染（Sawidis等，1995），这项工作的目的是测试差异erent一个sper matophyte和两个移植到市区，以量化为监测空气中的重金属不同类群的适用性地衣的重金属积累能力。
因为这些生物体是在城市地区，污染程度高，近年来罕见的，使用维管束植物已被引入到监测重金属污染（Sawidis等，1995）。
这项工作的目的是为了测试一个sper matophyte和移植到市区两个地衣不同重金属的积累能力，以量化的差异erent的适用性

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从二十世纪之初,空气污染已经恶化了作为一个后果是城市化和工业化的用地,连同机动运输的快速增长和人口。空气中的主要内容pollu——在印度的城市里漫步,一组重要要考虑是重金属颗粒物主要相关的事情。这是非常正确的。在城市的中心,那里的汽

介绍
自从二十世纪之初,空气污染已经恶化了作为一个后果是城市化和工业化的用地,连同机动运输的快速增长和人口。空气中的主要内容pollu——在印度的城市里漫步,一组重要要考虑是重金属颗粒物主要相关的事情。这是非常正确的。在城市的中心,那里的汽车发动机,以及热- ing系统内的建筑,代表了空气污染的重要来源(Sawidis丁晓萍。
1995;Monaci丁晓萍。2000)。
环...

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介绍
自从二十世纪之初,空气污染已经恶化了作为一个后果是城市化和工业化的用地,连同机动运输的快速增长和人口。空气中的主要内容pollu——在印度的城市里漫步,一组重要要考虑是重金属颗粒物主要相关的事情。这是非常正确的。在城市的中心,那里的汽车发动机,以及热- ing系统内的建筑,代表了空气污染的重要来源(Sawidis丁晓萍。
1995;Monaci丁晓萍。2000)。
环境监测的方法是基于昂贵和复杂的测量系统-等方面。自从元素组成的维管植物,苔藓植物和地衣可以改变造成的污染、相辅相成的利用他们的部分可能是一个合适的选择biomonitors(Bargagli巴里丁晓萍。1998;2001)。最常用于生物监测重金属低等植物中,如苔藓、地衣(孔蒂和Cecchetti报道丁晓萍。2001;2003;Figueira丁晓萍。2002)由于他们的能力——siderable欺诈积累金属。然而,由于这些生物体中是很少见的城市地区高程度的污染,近年来,使用了维管植物重金属污染监测(Sawidis丁晓萍。1995)。这项工作的目的是为了测试比较不同的重金属积累能力在一个sper - matophyte和两个地衣移植到一个城市地区,以量化不同类群的适用性进行监测空降重金属
因为这些生物是罕见的在城市地区高程度的污染,近年来,使用了维管植物重金属污染监测(Sawidis丁晓萍。1995)。
这项工作的目的是为了测试不同的重金属积累的差异,在固相萃取能力

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