Electrochemical Quantification of Lead Scale Particulates in Drinking Water
Lead contamination in drinking water can be caused by various types of lead: lead ions, soluble lead complexes, and lead particulates. Traditional detection methods such as inductively coupled plasma mass spectroscopy (ICP-MS) and atomic absorption spectroscopy (AAS) can detect all types of lead bec...
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Veröffentlicht in: | ACS ES&T water 2024-04, Vol.4 (4), p.1371-1380 |
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description | Lead contamination in drinking water can be caused by various types of lead: lead ions, soluble lead complexes, and lead particulates. Traditional detection methods such as inductively coupled plasma mass spectroscopy (ICP-MS) and atomic absorption spectroscopy (AAS) can detect all types of lead because of sample preparation. Nevertheless, these methods are expensive and require trained personnel. As electrochemical techniques are less expensive, portable, and easy to use, they are a promising alternative for lead detection in drinking water. However, electrochemistry is typically only able to detect lead ions. In this work, lead scales collected from a lead pipe are characterized to determine the types of lead compounds present within the lead corrosion scale. Subsequently, membrane electrolysis (ME) is used to acidify a drinking water solution containing lead corrosion scales, allowing for the dissociation of the particulate lead into lead ions. Square-wave anodic stripping voltammetry (SWASV) is then applied to determine the current associated with the lead ions being stripped off the working electrode, which originated from the particulates in the scales. Standard addition is used to determine the concentration of lead associated with the current response. This technique is compared to ICP-MS, and the relative errors between the two methods show that ME combined with SWASV is a viable approach for detecting lead contamination in drinking water due to lead corrosion scales. |
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Traditional detection methods such as inductively coupled plasma mass spectroscopy (ICP-MS) and atomic absorption spectroscopy (AAS) can detect all types of lead because of sample preparation. Nevertheless, these methods are expensive and require trained personnel. As electrochemical techniques are less expensive, portable, and easy to use, they are a promising alternative for lead detection in drinking water. However, electrochemistry is typically only able to detect lead ions. In this work, lead scales collected from a lead pipe are characterized to determine the types of lead compounds present within the lead corrosion scale. Subsequently, membrane electrolysis (ME) is used to acidify a drinking water solution containing lead corrosion scales, allowing for the dissociation of the particulate lead into lead ions. Square-wave anodic stripping voltammetry (SWASV) is then applied to determine the current associated with the lead ions being stripped off the working electrode, which originated from the particulates in the scales. Standard addition is used to determine the concentration of lead associated with the current response. 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Traditional detection methods such as inductively coupled plasma mass spectroscopy (ICP-MS) and atomic absorption spectroscopy (AAS) can detect all types of lead because of sample preparation. Nevertheless, these methods are expensive and require trained personnel. As electrochemical techniques are less expensive, portable, and easy to use, they are a promising alternative for lead detection in drinking water. However, electrochemistry is typically only able to detect lead ions. In this work, lead scales collected from a lead pipe are characterized to determine the types of lead compounds present within the lead corrosion scale. Subsequently, membrane electrolysis (ME) is used to acidify a drinking water solution containing lead corrosion scales, allowing for the dissociation of the particulate lead into lead ions. Square-wave anodic stripping voltammetry (SWASV) is then applied to determine the current associated with the lead ions being stripped off the working electrode, which originated from the particulates in the scales. Standard addition is used to determine the concentration of lead associated with the current response. 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Traditional detection methods such as inductively coupled plasma mass spectroscopy (ICP-MS) and atomic absorption spectroscopy (AAS) can detect all types of lead because of sample preparation. Nevertheless, these methods are expensive and require trained personnel. As electrochemical techniques are less expensive, portable, and easy to use, they are a promising alternative for lead detection in drinking water. However, electrochemistry is typically only able to detect lead ions. In this work, lead scales collected from a lead pipe are characterized to determine the types of lead compounds present within the lead corrosion scale. Subsequently, membrane electrolysis (ME) is used to acidify a drinking water solution containing lead corrosion scales, allowing for the dissociation of the particulate lead into lead ions. Square-wave anodic stripping voltammetry (SWASV) is then applied to determine the current associated with the lead ions being stripped off the working electrode, which originated from the particulates in the scales. Standard addition is used to determine the concentration of lead associated with the current response. This technique is compared to ICP-MS, and the relative errors between the two methods show that ME combined with SWASV is a viable approach for detecting lead contamination in drinking water due to lead corrosion scales.</abstract><pub>American Chemical Society</pub><doi>10.1021/acsestwater.3c00519</doi><tpages>10</tpages><orcidid>https://orcid.org/0000-0002-8392-1483</orcidid><orcidid>https://orcid.org/0000-0002-2508-6811</orcidid><orcidid>https://orcid.org/0000-0002-4379-7668</orcidid></addata></record> |
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title | Electrochemical Quantification of Lead Scale Particulates in Drinking Water |
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