Last data update: Mar 10, 2025. (Total: 48852 publications since 2009)
Records 1-5 (of 5 Records) |
Query Trace: Rane P[original query] |
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Notes from the Field: The National Wastewater Surveillance System's Centers of Excellence contributions to public health action during the respiratory virus season - four U.S. Jurisdictions, 2022-23
Valencia D , Yu AT , Wheeler A , Hopkins L , Pray I , Horter L , Vugia DJ , Matzinger S , Stadler L , Kloczko N , Welton M , Bertsch-Merbach S , Domakonda K , Antkiewicz D , Turner H , Crain C , Mulenga A , Shafer M , Owiti J , Schneider R , Janssen KH , Wolfe MK , McClellan SL , Boehm AB , Roguet A , White B , Schussman MK , Rane MS , Hemming J , Collins C , Abram A , Burnor E , Westergaard R , Ricaldi JN , Person J , Fehrenbach N . MMWR Morb Mortal Wkly Rep 2023 72 (48) 1309-1312 Wastewater surveillance (WWS), the systematic detection of infectious agents in wastewater, provided a valuable tool for monitoring SARS-CoV-2 circulation during the COVID-19 pandemic; surveillance has expanded from 20 to 53 jurisdictions across the United States, with increasing capacity to test for more respiratory pathogens (1,2). This report highlights the use of wastewater data by the four National Wastewater Surveillance System’s (NWSS) Centers of Excellence (California; Colorado; Houston, Texas; and Wisconsin) to guide public health action during the 2022–23 respiratory disease season. This activity was reviewed by CDC, deemed not research, and was conducted consistent with applicable federal law and CDC policy.* |
Wastewater Surveillance for Monkeypox Virus in Nine California Communities (preprint)
Wolfe MK , Yu AT , Duong D , Rane MS , Hughes B , Chan-Herur V , Donnelly M , Chai S , White BJ , Vugia DJ , Boehm AB . medRxiv 2022 09 Background: Wastewater represents a composite biological sample from the entire contributing population. People infected with monkeypox virus (MPXV)1 may excrete viral DNA into wastewater via multiple ways such as in feces, urine, skin lesions, and/or saliva. We describe results from rapid establishment of wastewater surveillance in selected regions in California within a month of the first reported case of monkeypox in the United States. Method(s): PCR assays targeting genomic DNA from MPXV were deployed in an ongoing wastewater surveillance program in California. MPXV DNA concentrations were measured daily in settled solids samples from nine wastewater plants. Results over a four-week period were validated across different MPXV assays, compared using influent and solids samples, and correlated using non-parametric methods (Kendall's tau) with the number of monkeypox cases reported from each sewershed. Result(s): MPXV DNA was detected at all nine sites between June 19 and August 1, 2022; 5 of 9 sites detected MPXV DNA prior to or within a day of the first case identified in the source sewershed. At the four sites with >10 positive detections, we observed a positive, statistically significant correlation (p <0.001) between MPXV DNA in wastewater solids and incidence rate of reported cases. Conclusion(s): Our findings suggest wastewater can be used to effectively detect the introduction of MPXV and monitor its circulation in the community to inform public health and clinical response. This flexible wastewater surveillance infrastructure may be rapidly leveraged to monitor other pathogens of public health importance that are shed into wastewater. Copyright The copyright holder for this preprint is the author/funder, who has granted medRxiv a license to display the preprint in perpetuity. It is made available under a CC-BY-ND 4.0 International license. |
Use of Wastewater for Mpox Outbreak Surveillance in California.
Wolfe MK , Yu AT , Duong D , Rane MS , Hughes B , Chan-Herur V , Donnelly M , Chai S , White BJ , Vugia DJ , Boehm AB . N Engl J Med 2023 388 (6) 570-572 ![]() ![]() In May 2022, cases of mpox (formerly known as monkeypox) virus (MPXV) infection were reported outside regions in Africa where it is endemic. The global spread of MPXV infection, coupled with evidence of human-to-human transmission of a typically zoonotic disease, triggered a rapid scale-up of public health response, including surveillance to identify cases and guide local response.1 However, access to and use of testing has been limited due in part to social stigma, difficulty recognizing a disease that is relatively new outside Africa, and potential for minimally symptomatic cases. A complementary surveillance approach that is independent of individual testing is through monitoring of wastewater, which represents a composite biologic sample from a community. The presence and concentration of pathogens that are shed into wastewater provide information about disease without the need for any involvement at the individual level, thereby offering an attractive means of attaining situational awareness for public health agencies and clinicians. |
A framework for integrating information resources for chemical emergency management and response
Seaton MG , Maier A , Sachdeva S , Barton C , Ngai E , Lentz TJ , Rane PD , McKernan LT . Am J Disaster Med 2019 14 (1) 33-49 Effective emergency management and response require appropriate utilization of various resources as an incident evolves. This manuscript describes the information resources used in chemical emergency management and operations and how their utility evolves from the initial response phase to recovery to event close out. The authors address chemical hazard guidance in the context of four different phases of emergency response: preparedness, emergency response (both initial and ongoing), recovery, and mitigation. Immediately following a chemical incident, during the initial response, responders often use readily available, broad-spectrum guidance to make rapid decisions in the face of uncertainties regarding potential exposure to physical and health hazards. Physical hazards are described as the hazards caused by chemicals that can cause harm with or without direct contact. Examples of physical hazards include explosives, flammables, and gases under pressure. This first line of resources may not be chemical-specific in nature, but it can provide guidance related to isolation distances, protective actions, and the most important physical and health threats. During the ongoing response phase, an array of resources can provide detailed information on physical and health hazards related to specific chemicals of concern. Consequently, risk management and mitigation actions evolve as well. When the incident stabilizes to a recovery phase, the types of information resources that facilitate safe and effective incident management evolve. Health and physical concerns transition from acute toxicity and immediate hazards to both immediate and latent health effects. Finally, the information inputs utilized during the preparedness phase include response evaluations of past events, emergency preparedness planning, and chemical-specific guidance about chemicals present. This manuscript details a framework for identifying the effective use of information resources at each phase and provides case study examples from chemical hazard emergencies. |
Application of the draft NIOSH Occupational Exposure Banding Process to Bisphenol A: A case study
Hines CJ , Lentz TJ , McKernan L , Rane P , Whittaker C . J Occup Environ Hyg 2018 16 (2) 1-20 Bisphenol A is a commercially important chemical used to make polycarbonate plastic, epoxy resins and other specialty products. Despite an extensive body of in vitro, animal and human observational studies on the effects of exposure to bisphenol A, no authoritative bodies in the U.S. have adopted or recommended occupational exposure limits for bisphenol A. In 2017, the National Institute for Occupational Safety and Health published a Draft process for assigning health-protective occupational exposure bands, i.e. an airborne concentration range, to chemicals lacking an occupational exposure limit. Occupational exposure banding is a systematic process that uses both quantitative and qualitative toxicity information on selected health effect endpoints to assign an occupational exposure band for a chemical. The Draft process proposes three methodological tiers of increasing complexity for assigning an occupational exposure band. We applied Tier 1 (based on the Globally Harmonized System of Classification and Labelling) and Tier 2 (based on authoritative sources/reviews) to assign an occupational exposure band to bisphenol A. Under both Tier 1 and 2, the occupational exposure band for bisphenol A was "E" (<0.01 mg/m(3)), an assignment based on eye damage. "E" is the lowest exposure concentration range, reserved for chemicals with high potential toxicity. If eye damage was excluded in assigning an air concentration exposure range, then bisphenol A would band as "D" (>0.01 to 0.1 mg/m(3)) under Tier 1 (based on reproductive toxicity and respiratory/skin sensitization) and under Tier 2 (based on specific target organ toxicity-repeated exposure). In summary, Tiers 1 and 2 gave the same occupational exposure band for bisphenol A when eye damage was included ("E") or excluded ("D") as an endpoint. |
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