Publication Cover
Journal of Environmental Science and Health, Part B
Pesticides, Food Contaminants, and Agricultural Wastes
Volume 40, 2005 - Issue 6
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Original Articles

Tylosin Sorption to Silty Clay Loam Soils, Swine Manure, and Sand

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Pages 841-850 | Received 21 Feb 2005, Published online: 20 Aug 2006
 

The objectives of this study were to assess sorption and desorption of tylosin, a macrolide antimicrobial chemical used in swine, cattle, and poultry production, in three silty clay loam soils of South Dakota and compare soil sorption to sand and manure sorption. The silty clay loam soils, from a toposequence in eastern South Dakota, standardized sand samples, and swine manure were used in 24-h batch sorption studies with tylosin concentrations ranging from 25 to 232 μ mole/L. Desorption from soil was conducted over a four-day period. Partition coefficients, based on the Freundlich isotherm (K f ) or K d values, were calculated. K f values for the silty clay loams were similar, not influenced by landscape position, and averaged 1350 with isotherm slopes ranging from 0.85 to 0.93. K f values for sand were dependent on solution/sand ratios and pH, ranging from 1.4 to 25.1. K d values of manure were dependent on the solution type and ranged from 840 L/kg with urine to about 175 L/kg when sorbed from water. Desorption of tylosin from each soil over the four-day period was < 0.2% of the amount added. The soils' high K f values and low desorption amounts suggest that once tylosin is in these soils, leaching to lower depths may not occur. However, this does not preclude runoff with soil eroded particles. If tylosin reaches a sand aquifer, through bypass flow or other mechanism(s), movement in the aquifer most likely would occur.

ACKNOWLEDGMENTS

Contribution from South Dakota Agricultural Experiment Station as journal series no. 3470. LC/MS was purchased with support from the National Science Foundation under grant no. 0091948. Funding was also provided by a grant from the South Dakota Agricultural Experiment Station.

Notes

*Matrix pH was determined in 1:1 soil/0.01M CaCl2 slurry.

*Units of K f are μ mol1 − 1/n L(1/n)/kg .

**Numbers in parentheses are the confidence interval (CI) for K f , antilog of log K f − CI log K f and log K f + CI log K f .

***Only K d values were calculated for these treatments, and numbers in parentheses are the 95% confidence intervals. Units for K d are L kg− 1.

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