HEAVY METALS ON FLUVIAL SEDIMENTS FROM A TOBACCO PLANTATION IN THE SOUTH OF BRAZIL

 

Torres, JPM1*; Lima, RG2, Etges, V2; Turci, SR3; Ferreira, MA2, Hermes, N2 and Malm, O1.

 

1Laboratorio de Radioisótopos Eduardo Penna Franca, Instituto de Biofísica Carlos Chagas Filho, UFRJ, Rio de Janeiro, Brazil (jptorres@biof.ufrj.br or jpmtorres@uol.com.br).

2Curso de Mestrado em Desenvolvimento Regional, UNISC, Rio Grande do Sul, Brazil

3COMPREV, INCA, Rio de Janeiro, Brazil.

 

Abstract

 

Tobacco is one of the main exportation products of the south of Brazil. Its production relies on several agrochemicals. These products (e.g. phosphorous fertilizers and ditiocarbamate fungicides) are know to have considerable amounts of metals like Zn, Cd and Mn in their composition. Another product have also copper in its composition.

To proceed a first approach to the environmental quality of a watershed were tobacco is being cultivated for more than 30 years, fluvial sediments were collected at 9 locations in the Rio Pardinho basin, near the town of Santa Cruz do Sul, RS. After total digestion of the samples, the final extracts were ressuspended in HCl 0,1 N and analyzed by means of FASS (Varian 1475). Enrichment factors using Fe as a conservative element was used to express the obtained results. In most of the samples, the heavy metal levels were low. Only cadmium showed a small enrichment in one of the analyzed sediments. 

 

Introduction

 

            Beside dozens of organic substances, several products now in use in agriculture, especially fertilizers, algaecides and fungicides, contain heavy metals like Zn, Cd, Mn and Cu in its constitution. In tropical areas, the environmental fate of these compounds after agrochemical application is only sparsely understood.

            In order to understand the effects of intensive cultivation of tobacco (that use each year large amounts of such products), the ecosystem health of a small river in the South Brazil is being investigated by a multidisciplinary group (IDRC, 1999). In Brazil, especially in the south, the agricultural development is based in small to medium size properties that resembles quite well the old 18’s situation in Europe. In fact, a great contingent of population of these areas consist nowadays of descendents of Germans and Italians that immigrated to Brazil in the last years of 1800. 

 

Study area

 


           

Figure 1 – Study area in the south part of Brazil (adapted from Lobo and Costa, 1997).

 

The Pardinho River (ca. 50 Km long) is a tributary of the Pardo. They belong to the Jacuí River watershed, the largest freshwater basin of Rio Grande do Sul State (Figure 1). The weather in this region may be very cold especially in strong winters. Probably due to a high precipitation index, in the past most of this riverbanks were covered with tropical forests that once were part of the Atlantic forest that covered most part of the Brazilian coast. Although the German colonization of these upper part of the area is rather recent (150 years), older Portuguese settlements (e.g. Rio Pardo) where established in the middle of the 17th. Century (Etges, 1991).

The riverheads, located at Sinimbu and Boqueirão do Leão municipalities (Figure 1) are a mix of river rapids and plateaus with more or less limited floodplains, that may be covered during the raining season. Traditional tobacco cultivation usually using animal traction is wide spread along the course of the River and spare bottles of different pesticides are commonly found in the riverbanks.

 

Material and methods

 

Bottom sediments from 7 locations along the Pardinho River were collected using a polyethylene scoop, and stored in plastic bags that were stored in iceboxes during their transport to the Radioisotopes Laboratory in Rio de Janeiro. The sediments were sieved in 200 mesh sieves and the fraction smaller than 74 mm (clay + silt + fine sand) were analyzed for their total content of heavy metals (Cd, Cu, Cr, Fe, Mn, Ni and Zn) after digestion in Teflonâ bombs with strong acids (HF, NNO3 and HClO4), the final extracts were ressuspended in HCl 0,1 N and the metal determination were done by conventional flame AAS (Varian 1475). Reagent blanks and certified reference materials were analyzed in each batch of 10 samples (All samples were analyzed in triplicates) (Fiszman et al, 1984).


 

Results and discussion

 

The results, expressed as mg/kg (ppm) of dry sediment are presented in table 1.

 

 

Table 1- Total heavy metal contents (ppm) of the sediments of the Pardinho River watershed.

 

 

Cd

Cu

Cr

Fe

Mn

Ni

Zn

Sinimbu 1

0.55

68.8

106.0

73996

1393

69.0

70.0

Sinimbu 2

1.05

56.8

88.5

71871

1083

54.8

75.0

Rio Pardinho

0.60

57.8

101.8

69121

1015

53.5

78.3

Santa Cruz do Sul 1

0.45

42.0

158.3

79183

1132

76.0

64.3

Santa Cruz do Sul 2

0.48

42.3

38.5

47558

925

25.3

61.8

Santa Cruz do Sul 3

0.35

40.3

73.3

57996

1157

41.0

58.8

Rio Pardo

0.15

8.8

12.0

10656

191

7.8

16.3

Mean crust**

0.20

55.0

100.0

56300

950

75.0

70.0

Average shale**

0.30

33.0

90.0

41000

770

52.0

95.0

Background RPS*

0.01

36

53.0

62388

1235

29.0

104.0

* Paraiba do Sul riverheads (Malm et al, 1986).

** Forstner and Wittman,1981.

 

All of the observed results are within the same order of magnitude of the mean crust value or the average shale, thus they cannot be considered polluted. However, when the results are expressed by enrichment factor using Fe as a conservative element, the results for cadmium found near the town of Sinimbu showed some enrichment (> 4). The net concentration, around 1 ppm, tough not very high, are similar the one that can be found in other rivers and in shallow bays near industrialized areas of Brazil (Lacerda et al, 1982; Torres, 1992). This concentration, observed near the riverheads of a non-industrialized area (present study) may be reflecting anthropogenic inputs of these toxic metal that is present as impurities of different fertilizers.

            The same pattern of a mild cadmium contamination was observed in other areas in where the same kind of fertilizers are used (De Boo, 1990).

 


 

References

 

1.      IDRC-Canada, 1999. Project Grant No. 50386. Tobacco growing and ecosystem effects.

 

2.      Etges, VE. 1991. Sujeição e resistência: os camponeses gauchos e a indústria do fumo. Edunisc. Rio Grande do Sul, Brasil.

 

3.      Lobo EA and Costa, AB, 1997. Revista Tecnológica, UNISC 1(1)11-36.

 

4.      Fisman, M; Pfeiffer, WC and Lacerda LD. 1984. Environmental Technology Letters. 5:

5.      567-575.

 

6.      Malm, 0, Pfeiffer, WC; Fiszman, M and Azcue, 1988. The Science of the Total Environment. 75: 201-209.

 

7.      Forstner, U, and Wittman, GTW. 1981. Metal Pollution in the Aquatic Environment. Springer-Verlag, Berlin.

 

8.      Lacerda, LD; Pfeiffer, WC and Fiszman, M. 1982. Ciência e Cultura, 34(7)921-924.

 

9.      Torres, JPM. M.Sc. Thesis. IBCCF-CCS-UFRJ. 114 pp.

 

10.  De Boo, W. 1990. Cadmium in Agriculture. Toxicological and Environmental Chemistry. 27:55-63.