Abstract

Forest application of biosolids offers a potential environmentally friendly alternative to landfilling. This two-year investigation was designed to analyze the effects of elevated soil metal concentration resulting from the land application of biosolids on the symbiotic, nitrogen (N) fixing relationship between Alnus rubra Bong. (red alder) and Frankia. High metal biosolids and a modern-day composted biosolid applied at high loading rates of 250, 500, and 1000 Mg ha-1, were used to represent a worst-case scenario for metal contamination. The high metal biosolids were obtained before the current regulations were formulated and had been lagooned prior to use in this study. Total cadmium (Cd), lead (Pb) and zinc (Zn) in the high metal biosolids were 45, 958, and 2623 mg kg-1 respectively. These metal concentrations are above current regulatory limits in the US. The compost was made using biosolids that are currently produced and had Cd, Pb and Zn of 0.8, 20 and 160 mg kg-1 respectively. Trees were harvested and analyzed for rate of N fixation (as measured by acetylene reduction activity), biomass, and foliar metals. Soils were analyzed for available N, total carbon and N, pH and total Cd, Pb and Zn. Rates of N fixation were not affected by soil amendment. In year 2, shoot biomass of trees grown in both the compost and high metal amendments were higher than the control. Shoot biomass increased with increasing amount of compost amendments, but decreased with increasing amount of high metal amendments. There was no relationship between soil metal concentration and plant biomass. Foliar Cd and Pb were below detection for all trees and foliar Zn increased with increasing amount of both compost and high metal amendment, with concentrations of 249 mg kg-1 for trees grown in the compost amendment and 279 mg kg-1 for the high metal amendment. The results from this study indicate that the growth of A. rubra benefited from both types of biosolids used in the study and that the Alnus/Frankia relationship was not negatively impacted by metal concentrations resulting from the high metal biosolids amendments.

Highlights

  • As a result of pre-treatment regulations, metal concentrations in biosolids in the US have been greatly reduced over historic levels

  • The 25 year-old biosolids had been lagooned prior to the start of this study and were used to represent high metal biosolids. They were produced in King County using an anaerobic stabilization process prior to the US Environmental Protection Agency (USEPA) code of federal registry (CFR) Part 503 regulations that set limits on metal concentrations in biosolids for land application (USEPA, 1999)

  • Metal concentrations were similar for the control and compost treatments and increased with increased loading of high metal biosolids

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Summary

Introduction

As a result of pre-treatment regulations, metal concentrations in biosolids in the US have been greatly reduced over historic levels. In the UK limits for total zinc (Zn) in biosolids were set to protect Rhizobium leguminosarum biovar trifolii (Giller et al, 1999; McGrath & Chaudri, 1999) This action was taken because R. leguminosarum was considered an indicator organism (Smith, 1997). Results from a long-term study at the Woburn Market Garden using repeated, high-loading applications of biosolids showed that R. leguminosarum had lost its ability to fix nitrogen (N) (Chander & Brookes, 1993). This decline was attributed to soil Zn concentrations. These results are not definitive as other long-term studies looking at R. leguminosarum have not seen the same effect (Giller et al, 1998; Obbard & Jones, 1993; Smith, 1997)

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