Heavy metal dispersion detected in soils and plants alongside roads in Hungary

被引:12
作者
Daniel, P [1 ]
Kovacs, B [1 ]
Prokisch, J [1 ]
Gyori, Z [1 ]
机构
[1] Debrecen Agr Univ, Cent Chem Lab, H-4027 Debrecen, Hungary
来源
CHEMICAL SPECIATION AND BIOAVAILABILITY | 1997年 / 9卷 / 03期
关键词
contamination; roadside area; heavy metals; leaded fuel; soil-plant relationship; HHPN-ICP;
D O I
10.1080/09542299.1997.11083292
中图分类号
Q5 [生物化学]; Q7 [分子生物学];
学科分类号
071010 ; 081704 ;
摘要
Soil and plant samples from roadside areas contaminated with toxic by-products of vehicular traffic (for example, lead compounds from leaded fuel, metal contaminants derived from spare parts) were analysed in the case of five Hungarian sampling sites. The analyses were carried out with a new analytical method which is based on the use of a high performance sample introduction unit in the conventional ICP spectrometry. By using this system, significantly lower detection limits were obtained related to the conventional ICP-AES method. The analysis results showed a close correlation between the daily mean volume of traffic and metals accumulated in the soil samples. On the other hand, using this method similar heavy metal profiles were gained, ie. the total and plant-available heavy metal concentrations were the highest in the 0-1 m region from the road, and the further sampling points (0-90 m) showed significantly lower and lower heavy metal contents until at about 90 m distance from the road, where heavy metal contamination reached such a low value that can be considered to be the environmental background level. A similar trend was also recognised in plants; the plants very near to the road surface accumulated very high amounts of lead, cadmium and other heavy metals derived from vehicular traffic. The results revealed different behaviours of contaminants in different conditions inside the roadside areas (soil pH and heavy metal content, species and abundance of flora at the different sampling points, etc.). For example, total and available concentrations were apparently low only in one sampling site where each sampling point of the cross-section showed acid soil medium. Generally, acid pH means higher mobility of heavy metals, which was verified in our study too, as low concentrations in soil are associated with high accumulation factors in plants. Both single-and two-factor ANOVA results showed that total and available lead contents were not significantly different between sampling sites, therefore they were considered as traffic as the main contaminating source produced near the same lead content in different conditions. Single-factor ANOVAs showed significant differences, meanwhile two-factor ANOVAs did not show significant differences among mean lead contents detected in plants sampled in the five sites. These different results for lead showed that with the increase of variables (from one to two factors) the mathematical differences between lead contents became less and less significant. It calls for paying attention to the evaluation of bioindication and requires use of all the available variables in order to gain precise results from sampled areas. Some plants such as Echinocloa crus-galli, Clematis recta, Artemisia vulgaris, Crepis biennis, Portulaca oleracea and Lathyrus pratensis were found to be good indicators, as they accumulated three or four different heavy metals in high concentrations. in addition to their sensitive indicating ability, the majority of these plants are weeds of cereals in arable lands, and so are easily available in roadside areas.
引用
收藏
页码:83 / 93
页数:11
相关论文
共 16 条
[1]  
ARKOSI I, 1990, KRONYEZETGAZALKODASI, V3, P27
[2]   HIGH-PRESSURE NEBULIZATION - A NEW WAY OF SAMPLE INTRODUCTION FOR ATOMIC SPECTROSCOPY [J].
BERNDT, H .
FRESENIUS ZEITSCHRIFT FUR ANALYTISCHE CHEMIE, 1988, 331 (3-4) :321-323
[3]  
BUTLER E. J., 1957, JOUR COMP PATHOL AND THERAP, V67, P378, DOI 10.1016/S0368-1742(57)80038-1
[4]  
CSATHO P, 1994, REV TAKI
[5]  
Hamilton R. S., 1991, STUDIES ENV SCI, V44
[6]  
Kadar I., 1995, TALAJ NOVENY ALLAT E
[7]   A study of plant sample preparation and inductively coupled plasma emission spectrometry parameters [J].
Kovacs, B ;
Gyori, Z ;
Prokisch, J ;
Loch, J ;
Daniel, P .
COMMUNICATIONS IN SOIL SCIENCE AND PLANT ANALYSIS, 1996, 27 (5-8) :1177-1198
[8]  
KOVACS B, 1995, METAL COMPOUNDS ENV, P82
[9]  
KOVACS B, 1996, 39 MAG SPEKTR VAND, P31
[10]  
LAKANEN E, 1982, FAO SOILS B, P10