Abstract

The effect of traffic on the content of lead and cadmium in grass morphological parts—leaves, shoots, and inflorescences—was studied. The samples were taken on a part of the European route E30 (Siedlce by road). The following plants were tested: Dactylis glomerata, Arrhenatherum elatius, and Alopecurus pratensis. During the flowering of grasses, the plant material was collected at distances of 1, 5, 10, and 15 m from the edge of the road, on the strip of road with a length of 9 km. In the collected plant parts, the content of lead and cadmium using the atomic absorption spectroscopy (AAS) method was determined. The effect of distance from the road on the content of lead and cadmium was evaluated using regression equations. Average lead content in the above parts of tested grass species was 3.56, while cadmium 0.307 mg kg−1 dry matter (DM). Lead content in plants of Alopecurus pratensis (average 4.11 mg kg−1 DM) was significantly higher than in other grasses. The lowest cadmium content, significantly different from the other species, was found in plants of Arrhenatherum elatius (0.251 mg kg−1 DM). Distance of sampling sites from the roadway significantly affects the differences in the content of cadmium and lead in plants. Analyzed aboveground plant organs of studied grasses were significantly different in contents of lead and cadmium. There were species differences in the proportions of cadmium concentration in various organs of plants. The obtained results indicate the possibility of species composition selection of grassland sward in areas with a higher risk of heavy metals associated with dust sedimentation.

Highlights

  • Grasses are typical cover of soils adjacent to the roadway

  • Average lead content in the aboveground parts of tested grass species amounted to 3.56 mg kg−1 dry matter (DM; Table 1)

  • The lead content found in different grass species from a variety parts of Poland reported by Klocek et al (2003) ranged from 0.6 to 15 mg kg−1 DM

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Summary

Introduction

Grasses are typical cover of soils adjacent to the roadway They are subjected to continuous operation of stressful factors caused by the exploitation of the roads. Roadsides receive considerable amounts of these traffic-generated pollutants (Garcia and Milan 1998) The effect of these factors is the change of physical and chemical conditions of their growth and bioaccumulation of elements deposited into the environment. Large quantities of these elements and fresh emission affect the increase of their content in the plants growing along the road. Their content in the plants is, mainly related with bioaccumulation potential specific for each species.

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