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PHARMACEUTICAL AND PERSONAL CARE PRODUCTS AS UBIQUITOUS POLLUTANTS FROM PERSONAL USE AND ACTIVITIES
Citation:
Daughton, C G. PHARMACEUTICAL AND PERSONAL CARE PRODUCTS AS UBIQUITOUS POLLUTANTS FROM PERSONAL USE AND ACTIVITIES. Presented at Environmental Science and Health Graduate Program, Reno, NV, October 16, 2002.
Impact/Purpose:
The research focused on in the subtasks is the development and application of state-of the-art technologies to meet the needs of the public, Office of Water, and ORD in the area of Water Quality. Located In the subtasks are the various research projects being performed in support of this Task and more in-depth coverage of each project. Briefly, each project's objective is stated below.
Subtask 1: To integrate state-of-the-art technologies (polar organic chemical integrative samplers, advanced solid-phase extraction methodologies with liquid chromatography/electrospray/mass spectrometry) and apply them to studying the sources and fate of a select list of PPCPs. Application and improvement of analytical methodologies that can detect non-volatile, polar, water-soluble pharmaceuticals in source waters at levels that could be environmentally significant (at concentrations less than parts per billion, ppb). IAG with USGS ends in FY05. APM 20 due in FY05.
Subtask 2: Coordination of interagency research and public outreach activities for PPCPs. Participate on NSTC Health and Environment subcommittee working group on PPCPs. Web site maintenance and expansion, invited technical presentations, invited articles for peer-reviewed journals, interviews for media, responding to public inquiries.
Subtask 3: To apply state-of-the-art environmental forensic techniques to the recognition and characterization of emerging pollutants in the aquatic environment. There is a need for high sensitivity and for a powerful method of structural characterization, advanced mass spectrometric and chromatographic techniques to be employed to meet the challenge of emerging pollutants, including pharmaceuticals and personal care products, agents of sabotage, and explosives. Ongoing efforts continue to identify previously unrecognized pollutants from a range of problematic samples having importance to regional and state contacts.
Subtask 4: To provide the Agency with a set of practical analytical methods for the selective and sensitive determination of selenium species (organic, inorganic, volatile and non volatile forms) in multiple media to accurately assess and if necessary control the risk of selenium exposure to organisms. This includes development of optimal extraction, digestion, separation and detection approaches.
Subtask 5: To develop and apply an analytical method that can extract and detect synthetic musks. The extent of exposure may be determined by measuring levels of synthetic musks from their potential source (communal sewage effluent). This subtask ends in FY05 with the deliverable of APM 21. Future applications to biosolids will be covered in subtask 6.
Subtask 6: Application, and improvement, of previously in-house developed sensitive, robust, and green, methodologies regarding the use of urobilin and sterols as a possible markers of sewage contamination.
Subtask 7: Adaptation and improvement of previously developed in-house methods, for PPCPs (e.g., antibiotics and musks) to solid materials (e.g. biosolids, sediments).
Subtask 8: Study of the presence of personal care products, incombustible organic compounds from the direct-piping of small engines exhaust in Lake Tahoe, and lake deposition of airborne pollutants from industrial activity
Description:
Perhaps more so than with any other class of pollutants, the occurrence of pharmaceuticals and personal care products (PPCPS) in the environment highlights the immediate, intimate, and inseparable connection between the individual activities of consumers and their environment. In contrast to other types of pollutants, PPCPs owe their origins in the environment directly to their worldwide, universal, frequent, highly dispersed, and individually small but aggregate/cumulative usage and disposal by multitudes of individuals. An overview of this multi-faceted issue can be found at a U.S. EPA web site (http://www.epa.gov/neriesdl/chemistry/phanna/index.htm), which also provides a reprint of a review article published in Environmental Health Perspectives as well as many other resources including several chapters from a new American Chemical Society book.
PPCPs can enter the environment following their ingestion or application by the user or administration to domestic animals. Disposal of unused/expired PPCPs in landfills and to domestic sewage are additional routes to the environment. Domestic sewage treatment plants are not specifically engineered to remove PPCPS; the efficiencies with which they are removed from sewage vary from nearly complete to ineffective. The aquatic environment serves as the major, ultimate receptacle for most PPCPS. Little is known with respect to actual or even potential adverse effects on non-target species; human exposure via drinking water is poorly defined. While PPCPs in the environment (or domestic drinking water) are not regulated, and even though their concentrations are extremely low (ng/L-ug/L), the consequences of exposure over multiple generations to multitudes of compounds having different as well as similar
modes of action prompts a plethora of questions. Although the environmental issues involved with two classes - antibiotics (e.g., selection for pathogen resistance) and sex steroids and certain other endocrine disruptors (e.g., aromatase disruption) - are the most widely recognized, numerous other therapeutic and consumer-use classes of PPCPs pose a wide range of additional and different environmental concerns.