Skip to main content

Advertisement

Log in

The Effect of Soil Bacteria and Perlite on Plant Growth and Soil Properties in Metal Contaminated Samples

  • Research Paper
  • Published:
Water, Air, and Soil Pollution Aims and scope Submit manuscript

Abstract

In order to achieve remediation of contaminated substrates, phyto-extraction in pot experiments utilizing lettuce seedlings as universal accumulator plants was investigated. As test substrates, mine tailings from Shiheung and Okdong mines in Korea (particularly high in Pb, Zn, Cu, and Cd), as well as samples from historic mining site at Oberzeiring in Austria (particularly high in Pb, Sb and As) were used, and compared with adjacent farmland soils. After 21 days of growth in the test substrate, the lettuce plants were harvested, and the adjacent soils parted in bulk and root soils. Special soil bacteria, adapted to high Cd levels (Exiguobacter sp.) and capable of adsorbing large amounts of cadmium from solution, as well as perlite (Samson Perlite Inc.) were added to the test substrates before plant growth. Speciation changes in the solids were investigated by sequential leaching, utilizing neutral MgCl2 (exchangeable), 0.16 M acetic acid, hydroxylamine pH 2, oxalate pH 3, H2O2 oxidation, and reflux with aqua regia. Plant growth induced differentiation between root and bulk soils, the differences were more pronounced for the non-contaminated controls. The iron-hydroxide phase increased about 30%, and also the amount of iron-hydroxide bound Be, Cd, Co, Cu, Mg, Mo, Sb and V concentrations, coming mainly from less mobile fractions. The Mn hydroxide phase, however (hydroxylamine), remained rather constant. After plant growth, the root soils were significantly lower in available P, and significantly higher in available Ca, Mn, and Na than the corresponding bulk soils. Addition of Cd-adapted soil bacteria led to a severe decrease of plant yield, but metal uptake changed in both directions. Exchangeable P in both root and bulk soil decreased, and Be, Co, Cr, Fe, K, Li, Mg, Mn, Ni, and Sr in the residual organic fraction increased. This can be interpreted as competition for nutrients, dissolution of residuals by bacterial action, and adsorption to a tightly bound biomass. Addition of perlite hardly affected the plant yield, and again metal uptake changed in both directions, but led to a decrease of siderophilic elements in the Fe- and Mn hydroxides of the bulk soil. In the root soil, perlite addition above all decreased available K, P and As, with respect to the untreated samples. Bacteria addition to perlite treated soils shifted some elements from weak acid mobile towards less available fractions.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Subscribe and save

Springer+
from $39.99 /Month
  • Starting from 10 chapters or articles per month
  • Access and download chapters and articles from more than 300k books and 2,500 journals
  • Cancel anytime
View plans

Buy Now

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Similar content being viewed by others

References

  • Anon (1977) ABC des Kopfsalat-Anbaus im Frühbeet und Kleingewächshaus. Obst und Garten, (3), 113–114.

  • Ahn, J. S., Kim, J. H., Kim, J. G., Song, Y. G., & Moon, H.- S. (2003). Laboratory investigation of the geochemical behaviour of metals in paddy soils contaminated with mine tailings. Water, Air and Soil Pollution, 150, 23–42.

    Article  CAS  Google Scholar 

  • BMLF (1999). Guideline: Richtlinien für die sachgerechte Düngung, Bundesministerium für Land- und Forstwirtschaft, Wien 1999. Vienna, Austria: Federal Ministry of Agriculture and Forestry (guidelines for appropriate fertilization).

    Google Scholar 

  • Chon, H. T., Ahn, J. S., & Jung, M. C. (1998). Heavy metal contamination in the vicinity of some base metal mines in Korea; A review. Geosystem Engineering, 1(2), 74–83, Ch.

    Google Scholar 

  • Chon, H. T., Ahn, J. S., & Jung, M. C. (2005). Heavy metal contamination around the abandoned Au–Ag and base metal mine sites in Korea. Korea Society of Economic and Environmental Geology, 38(2), 101–111.

    Google Scholar 

  • Dai, J., Becquer, Th., Rouiller, J. H., Reversat, G., Bernhard-Reversat, F., & Lavelle, P. (2004). Influence of heavy metals on C and N mineralisation and microbial biomass in Zn-, Pb-, Cu-, and Cd-contaminated soils. Applied Soil Ecology, 25(2), 99–109.

    Article  Google Scholar 

  • Ebner, F., Gaisberger, G., & Prochaska, W. (2002). Schwermetalle in landwirtschaftlich genutzten Böden im Blahbachtal östlich Oberzeiring. Report for the Project P 3. Mining University Leoben, Austria.

  • Ehrendorfer, K. (1957). Die Salatmethode. Die Bodenkultur, 9, 275–297.

    CAS  Google Scholar 

  • Gaisberger, G., Ebner, F., Prochaska, W., & Sager, M. (2003). Environmental impact of historic mining and metallurgy to soils (Oberzeiring – Eastern Alps). In Eliopoulos, et al. (Ed.), Mineral Exploration and Sustainable Development (25–28). Rotterdam: Millpress.

    Google Scholar 

  • Kandeler, E., Kampichler, C., & Horak, O. (1996). Influence of heavy metals on the functional diversity of soil microbial communities. Biology and Fertility of Soils, 23, 299–306.

    CAS  Google Scholar 

  • Khan, A. G., Kuek, C., Chaudhry, T. M., & Hayes, W. J. (2000). Role of plants, mycorrhizae and phytochelators in heavy metal contaminated land remediation. Chemosphere, 41, 197–207.

    Article  CAS  Google Scholar 

  • Krug, H., Liebig, H. P., & Stützel, H. (2002). Gemüseproduktion. Stuttgart-Hohenheim: Eugen Ulmer Verlag.

    Google Scholar 

  • Lee, S. Y. (2002). The effects of chelating agents and metal speciations in phytoremediation. Seoul National University, Master Thesis.

  • Lee, J. S., & Chon, H. T. (2003). Exposure assessment of heavy metals on abandoned metal mine areas by ingestion of soil, crop plant and groundwater. Journal de Physics IV France, 107, 757–760.

    Article  CAS  Google Scholar 

  • Mench, M., & Martin, E. (1991). Mobilization of cadmium and other metals from two soils by root exudates of Zea mays L., Nicotiana tabacum L., and Nicotiana rustica L. Plant and Soil, 132, 187–196.

    CAS  Google Scholar 

  • Park, J. H. (2003). Seoul National University, Master Thesis.

  • Puschenreiter, M., & Wenzel, W. W. (2003). Rhizosphären- Management zur Optimierung von Nährstoff- und Schadstoffgehalt in der Pflanze. Mitteilungen der Österreichischen Bodenkundlichen Gesellschaft, 69, 97.

    Google Scholar 

  • Shetty, K. G., Hetrick, B. A. D., & Schwab, A. P. (1995). Effects of mycorrhizae and fertilizer amendments on zinc tolerance of plants. Environmental Pollution, 88, 307–314.

    Article  CAS  Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to M. Sager.

Rights and permissions

Reprints and permissions

About this article

Cite this article

Sager, M., Park, J.H. & Chon, H.T. The Effect of Soil Bacteria and Perlite on Plant Growth and Soil Properties in Metal Contaminated Samples. Water Air Soil Pollut 179, 265–281 (2007). https://doi.org/10.1007/s11270-006-9230-y

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s11270-006-9230-y

Keywords