Abstract

The identification and characterization of lead-bearing and associated minerals in scales on lead pipes are essential to understanding and predicting the mobilization of lead into drinking water. Despite its long-recognized usefulness in the unambiguous identification of crystalline and amorphous solids, distinguishing between polymorphic phases, and rapid and non-destructive analysis on the micrometer spatial scale, the Raman spectroscopy (RS) technique has been applied only occasionally in the analysis of scales in lead service lines (LSLs). This article illustrates multiple applications of RS not just for the identification of phases, but also compositional and structural characterization of scale materials in harvested lead pipes and experimental pipe-loop/recirculation systems. RS is shown to be a sensitive monitor of these characteristics through analyses on cross-sections of lead pipes, raw interior pipe walls, particulates captured in filters, and scrapings from pipes. RS proves to be especially sensitive to the state of crystallinity of scale phases (important to their solubility) and to the specific chemistry of phases precipitated upon the introduction of orthophosphate to the water system. It can be used effectively alone as well as in conjunction with more standard analytical techniques. By means of fiber-optic probes, RS has potential for in situ, real-time analysis within water-filled pipes.

Highlights

  • Millions of lead service lines (LSLs) still deliver water to premises in the United States despite the long recognition of the health hazards of lead ingestion [1]

  • The results presented and discussed below are organized according to the Raman spectroscopic capability or the analytical concern they illustrate

  • Raman spectroscopy is an effective way to distinguish among the most common lead oxide phases encountered in many LSL systems, including our pipe-loop recirculation systems used to monitor the progress of the pipe-conditioning process [21,22]

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Summary

Introduction

Millions of lead service lines (LSLs) still deliver water to premises in the United States despite the long recognition of the health hazards of lead ingestion [1]. Recent tragic episodes of widespread elevated lead release into the water supplies of several U.S cities, remind us how sensitive the solubility of the solids that comprise the scale is to humancontrolled changes in the water source or treatment methods. Such sensitivity makes many municipal water supplies vulnerable to lead release, for instance, as has been experienced in Washington, DC [5], Flint, MI [3,6,7,8], and Newark, NJ [9], in the past 20 years. The fact that recognized elevations in lead concentration have persisted in some areas for months to years is a reflection of the challenge to passivating the inner surfaces of lead pipes from which the mineral scales have been totally or partially dissolved

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