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Effect of Biosolids on Phytoavailability of Cd in Long-term Amended Soil. U. Kukier 1 , R.L. Chaney 2 , J.A. Ryan 3 ,  W.L. Daniels 1 , R.H. Dowdy 4 , and T. Granato 5 Virginia Tech, Blacksburg, VA; USDA-ARS Beltsville, MD; US EPA Cincinnati, OH
Experimental Design Soil were collected from paired long-term biosolids-amended   and  unamended soils   from controlled field tests in Maryland, Minnesota and Illinois. Soil pH was adjusted to 6.5±0.2 in 0.01 M Ca(NO 3 ) 2 . Cd-salt added at rates 0, 2.5, 5.0, 7.5, 10 mg Cd kg -1  soil. Cd-nitrate was enriched in  111 Cd. Romaine lettuce was grown in the greenhouse for 35 days after transplanting. Four replications in randomized complete blocks.
New Test of Biosolids Cd Adsorption vs. Uptake (Kukier, Chaney, Ryan et al.) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Biosolids Application Sites, Rates, and Time Since Application Sampling  Biosolids  Cumulative   Years  Total Treatment  Application    since   last  Soil Cd Rate   application    Mg ha -1   mg kg -1 Hayden Farm  Control   0 - 0.20 Maryland Heat Treated 224 24 1.16 Composted 672 24 1.51 Nu-Earth 50 22 1.76 Nu-Earth 100 22 3.44 Minnesota Control   0 - 0.33 Low Rate 60 20 2.75 Medium Rate 120 20 5.30 High Rate 180 20 8.50 Fulton Co. Control 0 - 0.23 Chicago Biosolids 643 16 32.1
Composition of Biosolids In the Different Field Plots Biosolids  Cd  Zn  Fe mg/kg  mg/kg  % Heat-Treated 13.4 1329. 8.3 Composted 7.2 731. 4.1 Nu-Earth 212. 4140. 2.5 Twin Cities 140. 1890. 0.9 Chicago 263. 3660. 4.6 EPA-APL (mg/kg) 39. 2800. . EPA-CPLR (kg/ha) 39. 2800. .
Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils.
Romaine Lettuce grown on Hayden Farm Control and Long-Term Biosolids Compost-amended (672 t/ha) soils with 0-10 mg Cd/kg, at pH 6.5 in Ca(NO 3 ) 2 . Reduced uptake/toxicity of Cd to lettuce (control vs. biosolids-amended).
Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils pH=6.5
Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils.
Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils.
Phytoavailability of Biosolids Cd: ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Does increased consumption of fruits and vegetables increase risk from biosolids Cd? ,[object Object],[object Object],[object Object],[object Object],[object Object]
CONCLUSIONS ,[object Object],[object Object],[object Object],[object Object]

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Kukier chaney-2005-effect of biosolids on phytoavailability of cd

  • 1. Effect of Biosolids on Phytoavailability of Cd in Long-term Amended Soil. U. Kukier 1 , R.L. Chaney 2 , J.A. Ryan 3 , W.L. Daniels 1 , R.H. Dowdy 4 , and T. Granato 5 Virginia Tech, Blacksburg, VA; USDA-ARS Beltsville, MD; US EPA Cincinnati, OH
  • 2. Experimental Design Soil were collected from paired long-term biosolids-amended and unamended soils from controlled field tests in Maryland, Minnesota and Illinois. Soil pH was adjusted to 6.5±0.2 in 0.01 M Ca(NO 3 ) 2 . Cd-salt added at rates 0, 2.5, 5.0, 7.5, 10 mg Cd kg -1 soil. Cd-nitrate was enriched in 111 Cd. Romaine lettuce was grown in the greenhouse for 35 days after transplanting. Four replications in randomized complete blocks.
  • 3.
  • 4. Biosolids Application Sites, Rates, and Time Since Application Sampling Biosolids Cumulative Years Total Treatment Application since last Soil Cd Rate application Mg ha -1 mg kg -1 Hayden Farm Control 0 - 0.20 Maryland Heat Treated 224 24 1.16 Composted 672 24 1.51 Nu-Earth 50 22 1.76 Nu-Earth 100 22 3.44 Minnesota Control 0 - 0.33 Low Rate 60 20 2.75 Medium Rate 120 20 5.30 High Rate 180 20 8.50 Fulton Co. Control 0 - 0.23 Chicago Biosolids 643 16 32.1
  • 5. Composition of Biosolids In the Different Field Plots Biosolids Cd Zn Fe mg/kg mg/kg % Heat-Treated 13.4 1329. 8.3 Composted 7.2 731. 4.1 Nu-Earth 212. 4140. 2.5 Twin Cities 140. 1890. 0.9 Chicago 263. 3660. 4.6 EPA-APL (mg/kg) 39. 2800. . EPA-CPLR (kg/ha) 39. 2800. .
  • 6. Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils.
  • 7. Romaine Lettuce grown on Hayden Farm Control and Long-Term Biosolids Compost-amended (672 t/ha) soils with 0-10 mg Cd/kg, at pH 6.5 in Ca(NO 3 ) 2 . Reduced uptake/toxicity of Cd to lettuce (control vs. biosolids-amended).
  • 8. Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils pH=6.5
  • 9. Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils.
  • 10. Phytoavailability of Cd added to Long-Term Biosolids-Amended Soils.
  • 11.
  • 12.
  • 13.

Editor's Notes

  1. I recommend using this slide rather than the previous one which included the high Cd Chicago Nu-Earth. This shows the remarkable effect of high Fe biosolids on Cd phytoavailability. Comparison at equal soil pH.