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How influenza pandemic control can lead to unpreparedness: modelling the ecotoxicity of pharmaceutical usage. Andrew Singer acsi@ceh.ac.uk . Centre for Ecology & Hydrology Wallingford, UK. Summary of 2009 Pandemic in the UK.
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How influenza pandemic control can lead to unpreparedness: modelling the ecotoxicity of pharmaceutical usage Andrew Singer acsi@ceh.ac.uk Centre for Ecology & Hydrology Wallingford, UK
Summary of 2009 Pandemic in the UK • There were two ‘waves’ one immediately following the other. There were significant levels of background immunity among adults. This contributed to the first ‘wave’ peaking at the beginning of the school holidays in mid Summer when contact rates in children reduced. Once schools returned in September, infections grew again until mid October when there were not enough susceptible individuals left to sustain the pandemic. • The clinical effects of the influenza infection were similar to those of seasonal flu, but with an increase in the numbers of cases of viral pneumonitis in younger patients. Bacterial infections tended to be focussed in older patients and those with risk factors for severe flu. • Antibiotic prescribing in the second and third quarters of 2009 was not distinguishably different compared with the same period in the years preceding and following. This suggests that there was not great pressure on prescribing in primary care, as a result of the relatively mild pandemic.
“The Solution to Pollution is Dilution” Question: Will pandemic drug use ever yield enough drug to cause environmental problems? Answer: What drugs are being used? What problems are you looking for? How dilute do you need it to be? Is there enough water for dilution?
What is Pandemic Preparedness? … to slow the spread of influenza, through: • vaccines, 2) non-pharmaceutical measures 3) Antivirals and Antibiotics Virally-induced damage to the respiratory tract predisposes to bacterial invasion and infection.
O O O HN NH2 • H3PO4 O O O OH HN NH2 O 2 x 75 mg/d for 5 days ? Impact Assessment ? ?
1. epidemic model GLEaM – Global Epidemic and Mobility model • air mobility layer • 3400 airports in 220 countries • 20,000 connections • traffic data (IATA, OAG) • >99% commercial traffic • commuting mobility layer • daily commuting data • >30 countries in 5 continents • universal law of mobility • demographic layer • cells ¼° x ¼° • tessellation around • transportation hubs www.epiwork.eu Balcan et al. PNAS (2009) extended to the entire globe
R0 Secondary Infection Rate (pneumonia) 40% 2.3 15% 1.9 1.65 2% Pharmaceutical Use Model During an Influenza Pandemic Influenza Cases Viral Infectivity (R0) Secondary Infections AVP “GLeAM”: Global Epidemiology Model Antiviral Treatment (AVT) Antibiotic Use R0 = Basic Reproductive Number, the average number of secondary infections produced by a single infected individual while they are infectious, in an entirely susceptible population. This is a measure of the degree of transmissibility of an infection. AVT/AVP • No prophylaxis • Early stage Prophylaxis • - 2w • - 4w • Treatment 30% cases 54% reduction in pneumonia with antiviral treatment Kaiser (2003) Arch Intern Med; Nicholson (2000) Lancet; Treanor (2000) JAMA; Whitley (2000) Pediatr Infect Dis J
Estimated Global Tamiflu stockpile (2009) UK = 70-75% coverage (mostly Tamiflu)
β-lactam Cephalosporin Macrolide Tetracycline Quinolone Amoxicillin Clavulanic acid Cefotaxime Cefuroxime Erythromycin Clarithromycin Doxycycline Levofloxacin Moxifloxacin
LF2000-WQX works • Estimates water quality on a reach by reach basis – starting at the top • Makes a mass balance of the inputs to the reach • Sewage treatment plants, industrial discharges, tributaries • New concentrations calculated at the end of the reach allowing for degradation of the compound of interest • Output in GIS format
Available Dilution of Wastewater in WWTPs of Thames Catchment, UK
Interpandemic Antibiotic Use (excreted in England) Those highlighted in red to be used in a pandemic NHS BSA (2008) http://www.nhsbsa.nhs.uk/PrescriptionServices/Documents/NPC_Antibiotics_July_2008.ppt
results: antibiotics in WWTPs 300% 252% 200% relative increase to baseline 2007/2008 100% 13% 1% R0 = 1.65 R0 = 1.9 (AVT) R0 = 2.3 (AVT)
Mean Total Antibiotics In Thames S1 = AVP=0, rate of AVT = 30%, limited supply of Tamiflu S2 = 2wk AVP, AVP=1%, rate of AVT = 30%, limited supply of Tamiflu S3 = 4wk AVP, AVP=1%, rate of AVT = 30%, limited supply of Tamiflu S4 = 2wk AVP, AVP=10%, rate of AVT = 30%, limited supply of Tamiflu S5 = 4wk AVP, AVP=10%, rate of AVT = 30%, limited supply of Tamiflu S6 = AVP=0, rate of AVT = 30%, unlimited supply of Tamiflu
Mean Tamiflu In Thames S1 = AVP=0, rate of AVT = 30%, limited supply of Tamiflu S2 = 2wk AVP, AVP=1%, rate of AVT = 30%, limited supply of Tamiflu S3 = 4wk AVP, AVP=1%, rate of AVT = 30%, limited supply of Tamiflu S4 = 2wk AVP, AVP=10%, rate of AVT = 30%, limited supply of Tamiflu S5 = 4wk AVP, AVP=10%, rate of AVT = 30%, limited supply of Tamiflu S6 = AVP=0, rate of AVT = 30%, unlimited supply of Tamiflu
Determining Impact No acute toxicity Inhibition of microbial biofilms Tamiflu Microbial growth inhibition (WWTP & rivers) Antibiotics
Antiviral Affects on Biofilm Formation * * * * * * * * * * * * * Oseltamivir = 1 and 0.1 ug/ml Zanamivir = 0.1 and 0.01 ug/ml
Spatial distribution of toxicity in WWTPs & Rivers % of sewage plants >5% PAF ≤ 85 ≤100 % of Thames River length >5% PAF ≤ 10 ≤ 40
General Conclusions • A mild pandemic with a low rate of secondary infections is not projected to result in problems for sewage works or most UK rivers. • A pandemic with an R0 > ~2.0 is likely to pose operational challenges to sewage works which could result in the release of untreated sewage into receiving rivers.
Impact disruption of WWTPs widespread river pollution • contamination of rivers • degradation of drinking water • spread of antiviral and antibiotics resistance • eutrophication : • loss of acquatic ecosystem (fish kill) • temporary loss of ecosystem function
Solutions ? VACCINATION!!
Priority Research • Empirically determine vulnerability of sewage works. • Assess the short and long term risks to widespread antiviral and antibiotic release into the environment. • Empirically determine vulnerability of drinking water to contamination.
Additional Considerations • Compliance: • Vaccination rate including pre-pandemic and during pandemic. • Antivirals: 53% of those given oseltamivir were 100% compliant with taking their medication, 11% took less than 80% of that given and fewer than 1% did not comply at all. • Diagnostics for bacterial pneumonia • Between 3-6 million in the UK will have bacterial pneumonia but another 3-6 million will have viral pneumonia—untreatable by antibiotics, but as diagnosis is syndromic, they will all get antibiotics.
Additional Considerations: Investigational Anti-Influenza Agents NA inhibitors (NAIs) Peramivir, zanamivir (IV) A-315675 (oral) Long-acting NAIs (LANIs) Laninamivir (topical) ZNV dimers (topical) Conjugated sialidase DAS181 (topical) Protease inhibitors HA inhibitors Cyanovirin-N, FP Arbidol (oral) Polymerase inhibitors Ribavirin (oral, IV, inhaled) Favipiravir/T-705 (oral) Viramidine (oral) siRNA (IV, topical) NP inhibitors(nucleozin) Interferons IFN inducers RIG-I activator (5’PPP-RNA) Antibodies (anti-HA, NA, M2) Cationic airway lining modulators(iCALM- topical) http://ow.ly/3GJ4c
Combination Antiviral Therapy http://ow.ly/3GJ4c
Methodology: The water samples were pre-filtered (0.45 μm filters) and analyzed using an in-line SPE -tandem mass-spectrometry (MS/MS) system. Target compounds were Oseltamivir and 13 antibiotics, compounds included in the UK’s preparedness plans. • Results: Found 12 of 15 target chemical. Oseltamivir reached 480 ng/L in Oxford STW (exceeds Japan report of 293 ng/L). Antibiotic levels were consistent with previous studies.
Workshop 1: Tamiflu Focus Assess the potential human health impact and environmental hazards associated with use of Tamiflu during an influenza pandemic (risk ranking and identifying knoweldge gaps).
Workshop 2: WWTP Focus Antibiotic usage during a pandemic PECs Biodegradation Ecotoxicity of antibiotics to WWTPs. Diversity of WWTPs in UK
Future Workshops Post presentations of this workshop on PREPARE website. Literature output from workshop?
Thanks to Collaborators...and you! Vittoria Colizza Heike Schmitt Duygu BalcanAlessandro Vespignani Indiana University, Bloomington, USA Virginie D. J. Keller Richard J. Williams Centre Ecology & Hydrology vcolizza@isi.it ISI, Turin Italy h.schmitt@uu.nl Inst. Risk Assessment Sciences, Univ. Utrecht Johanna Andrews Wei E. Huang Dept Civil Structural Engineering, Univ Sheffield, UK