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This article in JEQ

  1. Vol. 39 No. 3, p. 946-954
     
    Received: Dec 9, 2009


    * Corresponding author(s): bpeller@usgs.gov
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doi:10.2134/jeq2009.0487

Microbial Degradation of Plant Leachate Alters Lignin Phenols and Trihalomethane Precursors

  1. Brian A. Pellerin *a,
  2. Peter J. Hernesb,
  3. JohnFranco Saracenoa,
  4. Robert G. M. Spencerb and
  5. Brian A. Bergamaschia
  1. a U.S. Geological Survey, 6000 J Street, Placer Hall, Sacramento, CA 95819
    b Dep. Of Land, Air and Water Resources, Univ. of California, Davis, CA 95616. Assigned to Associate Editor Lakhwinder Hundal

Abstract

Although the importance of vascular plant–derived dissolved organic carbon (DOC) in freshwater systems has been studied, the role of leached DOC as precursors of disinfection byproducts (DBPs) during drinking water treatment is not well known. Here we measured the propensity of leachates from four crops and four aquatic macrophytes to form trihalomethanes (THMs)—a regulated class of DBPs—before and after 21 d of microbial degradation. We also measured lignin phenol content and specific UV absorbance (SUVA254) to test the assumption that aromatic compounds from vascular plants are resistant to microbial degradation and readily form DBPs. Leaching solubilized 9 to 26% of total plant carbon, which formed 1.93 to 6.72 mmol THM mol C−1 However, leachate DOC concentrations decreased by 85 to 92% over the 21-d incubation, with a concomitant decrease of 67 to 92% in total THM formation potential. Carbon-normalized THM yields in the residual DOC pool increased by 2.5 times on average, consistent with the preferential uptake of nonprecursor material. Lignin phenol concentrations decreased by 64 to 96% over 21 d, but a lack of correlation between lignin content and THM yields or SUVA254 suggested that lignin-derived compounds are not the source of increased THM precursor yields in the residual DOC pool. Our results indicate that microbial carbon utilization alters THM precursors in ecosystems with direct plant leaching, but more work is needed to identify the specific dissolved organic matter components with a greater propensity to form DBPs and affect watershed management, drinking water quality, and human health.

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