Environmental fate of monosodium methanearsonate (MSMA)—Part 2: Modeling sequestration and transformation

Author:

Williams W. Martin1ORCID,Cheplick J. Mark1,Cohen Stuart Z.2ORCID,Eldan Michal3,Hoogeweg Cornelis G.1,Masue‐Slowey Yoko4,Vamshi Raghu1ORCID

Affiliation:

1. Waterborne Environmental, Inc. Leesburg Virginia USA

2. Environmental & Turf Services, Inc. Wheaton Maryland USA

3. Luxembourg Industries Ltd., The Organic Arsenical Products Task Force Washington District of Columbia USA

4. DeSimone Consulting Engineers New York New York USA

Abstract

AbstractMonosodium methanearsonate (MSMA), a sodium salt of monomethylarsonic acid (MMA), is a selective contact herbicide used for the control of a broad spectrum of weeds. In water, MSMA dissociates to ions of sodium (Na+) and monomethylarsonate (MMA) that is stable and does not transform abiotically. In soils characteristic of MSMA use, several simultaneous processes can occur: (1) microbial methylation of MMA to dimethylarsinic acid (DMA), (2) microbial demethylation of MMA to inorganic arsenic (iAs), (3) methylation of iAs to MMA, and (4) sorption and sequestration of MMA and its metabolites to soil minerals. Sequestered residues are residues that cannot be desorbed from soil in environmental conditions. Sequestration is rapid in the initial several days after MSMA application and continues at a progressively slower rate over time. Once sequestered, MMA and its metabolites are inaccessible to soil microorganisms and cannot be transformed. The rate and extent of the sorption and sequestration as well as the mobility of MMA and its metabolites depend on the local edaphic conditions. In typical MSMA use areas, the variability of the edaphic conditions is constrained. The goal of this research was to estimate the amount of iAs potentially added to drinking water as a result of the use of MSMA, with models and scenarios developed by the US Environmental Protection Agency for pesticide risk assessment. In this project, the estimated drinking water concentrations (EDWCs) for iAs were assessed as the average concentration in the reservoir over a 30‐year simulation with annual applications of MSMA at maximum label rates. When the total area of suitable land was assumed to be treated, EDWCs ranged from <0.001 to 0.12 µg/L. When high estimates of actually treated acreage are considered, the EDWCs are below 0.06 µg/L across all scenarios. Integr Environ Assess Manag 2024;00:1–12. © 2024 The Author(s). Integrated Environmental Assessment and Management published by Wiley Periodicals LLC on behalf of Society of Environmental Toxicology & Chemistry (SETAC).

Publisher

Wiley

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1. Environmental fate of monosodium methanearsonate (MSMA)—Part 1: Conceptual model;Integrated Environmental Assessment and Management;2024-06-25

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