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28 September 2012 No. 32 ANAESTHESIA AND THE ENVIRONMENT Verushka Naidoo Commentator: S Jithoo Moderator: K de Vasconcellos Department of Anaesthetics CONTENTS OBJECTIVES ....................................................................................................... 3 INTRODUCTION ................................................................................................... 4 DRUG WASTAGE IN ANAESTHESIA ................................................................. 5 ANAESTHESIA AND THE ATMOSPHERE .......................................................... 7 THE IMPACT OF GENERAL ANAESTHETICS ON THE ENVIRONMENT .......... 8 Anaesthetics Gases and the Environment ........................................................ 8 Quantifying the Environmental Effect of Anaesthetic Drugs: Life Cycle Assessment ......................................................................................................... 9 STRATEGIES TO REDUCE OUR ENVIRONMENTAL FOOTPRINT ................. 11 Reducing Environmental Contamination by anaesthetic gases .................... 11 DISPOSABLE AND REUSABLE EQUIPMENT IN ANAESTHESIA ................... 14 CONCLUSION .................................................................................................... 18 REFERENCES.................................................................................................... 19 Page 2 of 19 OBJECTIVES To increase awareness on the impact of anaesthesia on the environment To suggest appropriate steps to prevent and limit drug wastage in theatre To provide an understanding of the impact that volatile agents and nitrous oxide has on the atmosphere To provide an understanding of life cycle assessments To discuss the impact that reusable and disposable items have on the environment Promote ways in which we can reduce, reuse and recycle Page 3 of 19 INTRODUCTION In our daily practice very little consideration has been given to the effects of anaesthesia on the environment. The aim of my talk is to increase awareness of the above mentioned topic and to highlight aspects of anaesthesia that contribute to environmental pollution and discuss ways in which we can reduce these impacts. The health care industry contributes to environmental pollution and global warming [19]. In the United States alone the health care sector contributes to more than 8% of the total carbon dioxide (CO2) emissions [17]. The negative impact of anaesthesia on the environment is an issue that requires much attention since environmental resources are limited. As population size and modern medicine continues to expand so does the number of anaesthetics we administer. From recent studies it has been shown that hospitals contribute significantly to CO2 emissions [15]. These findings are worrisome and as anaesthesiologists it is our responsibility to be aware of the potential harm that we present to the environment through our daily practices. It is through awareness that we can promote environmentally friendly policies and programs to reduce the negative impact of anaesthesia on climate change [15]. To address the environmental impact of anaesthesia this talk is going to focus on drug wastage in anaesthesia, the environmental effects of the anaesthetics agents themselves, and the environmental effect of the waste generated by the equipment necessary to practice anaesthesia. Page 4 of 19 DRUG WASTAGE IN ANAESTHESIA One of the factors contributing to environmental contamination is drug wastage. Drug wastage has significant adverse ecologic effects and the potential to increase health care costs [1]. In a study conducted by Mankes in New York, drug usage and wastage was investigated [1]. Fig 1 and Fig 2 below highlight the amount of drug wastage that occurs with common anaesthetic drugs. Dispensed (mL) 80000 70000 60000 50000 40000 30000 20000 10000 0 e in e Ep i Pr op At ro p ar ac ain ium At ra cu r r in e e ne ph in ed r Ep h Lid oc ain ea nd Ep i ne ph iv a ca i .. . ne e lin Bu p Su cc in Lid y lc ho oc Pr op of ain ol e Dispensed (mL) Figure 1: Volume of common anaesthetic agents dispensed [1] Wasted (percentage) 60 50 40 30 20 10 0 e in At ro p e ar ac ain ium Lid oc ain Pr op ne ph Ep i At ra cu r rin e e in ed r Ep h ea nd Ep i ne ph iva ca i rin e ne e Su cc in Bu p ylc ho lin ain oc Lid Pr op of ol e Wasted (percentage) Figure 2: Percentage of dispensed drug wasted [1] Page 5 of 19 Propofol was the most used and wasted drug in the facility, making up 45% of the total drug wastage by millilitre (mL). While propofols impact on the environment appears low, it does have the ability to accumulate in adipose tissue of aquatic organisms and under anaerobic conditions is not biodegradable. It is found to be toxic to aquatic life and may also contribute to adverse long term effects in the aquatic environment [1]. Since propofol is not biodegradable it has to be incinerated (>1000 degrees celcius) for no less than two seconds, which in itself is energy consuming [1]. Propofol is normally incinerated in our facility but it can find its way into the environment because of inadequate waste disposal by healthcare professionals. In the above study it was found that by decreasing the size of propofol vials, drug wastage was reduced from 29.2mL/day/bin to 2.8mL/day/bin, therefore reiterating the fact that reduction in waste occurs with feedback of information to healthcare professionals allowing them to change practice patterns that contribute negatively to the environment1. A reduction in wastage will in turn decrease hospital expenditure and the harmful effects of Propofol on the environment. A study by Chaudhary et al showed that in addition topropofol; rocuronium, vecuronium and neostigmine contribute significantly to total drug wastage [6]. The majority of propofol waste was due to the drug being left over in the vial. They also found that less propofol was wasted when smaller vials where used as in the study by Mankes et al [1]. In addition discussing the plan of anaesthesia beforehand prevented unnecessary wastage of drugs [6]. Although controversial from an infection control point of view, drug wastage can also be reduced by providing accessibility to multi-dose vials for certain drugs. For example wastage of rocuronium can be limited by loading only the calculated drug dose based on per kilogram body weight, therefore leaving behind sterile drug in the multi-dose vial that can be used for other cases. For drugs such as morphine an effective method to decrease wastage would be to load the drug in a 10ml syringe and then load into separate syringes for each case as per body weight. In this way one ampoule of morphine can be used for more than two cases6. Interventional education in the form of lectures, posters etc is also an important way to increase awareness and help reduce wastage and in turn the negative environmental impact it brings. Page 6 of 19 ANAESTHESIA AND THE ATMOSPHERE Figure 3: The Atmosphere [2] The atmosphere consists of five layers: the troposphere, stratosphere, mesosphere, thermosphere and exosphere. The composition of the atmosphere gradually changes due to diffusion of gas molecules: it consists of greater quantities of lighter gases at higher altitudes [2]. The stratosphere (which contains the ozone layer) and the troposphere are the two most important thermoregulatory layers of the earth [3, 18]. Life on earth is shielded from harmful ultraviolet radiation by the stratospheric ozone layer [18]. Shortwave ultraviolet radiation is absorbed by the ozone in the higher atmospheres [2]. Ozone depleting substances are directed to the stratosphere by air currents in the tropics. They are then broken down in the stratosphere by ultraviolet radiation and their by-products form radicals that contribute to ozone destruction. Half the solar energy is absorbed by the earth’s surface, while the rest is absorbed or reflected by clouds and atmosphere. Infrared radiation is also emitted from the earth’s surface [2]. This infrared radiation is absorbed by greenhouse gases in the troposphere and this energy is directed back to the earth. Studies bring to light that global warming potential and ozone depletion potential are significant for all the volatile agents, especially when used with nitrous oxide [3]. They therefore have the potential to impact negatively on the environment Page 7 of 19 THE IMPACT OF GENERAL ANAESTHETICS ON THE ENVIRONMENT Data suggest that in the United States alone fifty million patients have general anaesthetics administered to them each year [2]. General anaesthetics are not only administered in the hospital setting but also used extensively by veterinarians, dentists and in laboratories [1]. Recent studies show that anaesthetic gases have a significant impact on global warming and depletion of the ozone layer [2, 8]. In our operating theatres we have scavenging systems that decrease our exposure to general anaesthetics. These gases however are eliminated directly into the atmosphere unchanged because they undergo minimal metabolism when exhaled by patients. Sevoflurane, isoflurane, halothane, enflurane and desfluraneare are halogenated compounds and, since they are chemically similar to chloroflurocarbons, they contribute to depletion of the ozone layer [1,3]. Nitrous oxide is also an established greenhouse gas that can cause depletion of the ozone layer. Anaesthetics Gases and the Environment The impact that a gas has on the environment is determined by its atmospheric lifetime, global warming potential and ozone depleting potential. a) Atmospheric lifetime: Is the average time in years that a molecule resides in the atmosphere before it is removed by chemical reaction or deposition [4]. The more resistant a compound is to breakdown in the environment, the higher the atmospheric lifetime. Atmospheric lifetimes of more than two years contribute to ozone depletion for longer periods and tend to cause an imbalance of infrared radiation which, as discussed earlier, can contribute to global warming. b) Global Warming Potential: Is a measure of the total energy absorbed by a gas over a certain time (usually 100 years) in comparison to carbon dioxide [4]. i.e. the heat trapping potential of a greenhouse gas in the atmosphere [4]. c) Ozone Depletion Potential: The ozone depletion potential (ODP) is defined as the amount of degradation that a compound can cause to the ozone layer. Page 8 of 19 Compound Chlorofluorocarbons Carbon dioxide Nitrous oxide Halothane Isoflurane Sevoflurane Desflurane Atmospheric lifetime (years) 50-100 5-200 114 6.6-7.0 3.2-5.9 1.2-4.0 8.9-21.0 Global warming potential (GWP) 10900 1 298 510-571 141-218 1525-1746 Ozone Depletion potential (ODP) 1 0.017 1.56 0.03 0.00 0.00 Table 1: Atmospheric lifetimes, Global warming potential, and Ozone depletion potential of common anaesthetic gases [3] All of the volatile agents have atmospheric lifetimes of more than 2 years, with the exception of sevoflurane. Sevoflurane has a low GWP and atmospheric lifetime. Desflurane has the largest environmental impact, with the highest atmospheric lifetime and GWP of all the volatiles. Desflurane’s environmental impact is much higher than that of CO2. In comparison to the CFCs, halothane is shown to have a similar ODP. This is due to its bromine atom which is known to damage the ozone layer. Also of importance is the fact that halothane has a higher ODP than the CFCs (1.56x more). Nitrous Oxide and the Environment Nitrous oxide (N2O) has an atmospheric lifetime of 120 years [2]. Its global warming potential is about three hundred times that of carbon dioxide but its ozone depletion potential is lower than that of the chlorofluorocarbons [3]. Nitrous oxide reacts with oxygen atoms in the atmosphere to produce nitric oxide (NO), which can, in turn, contribute to ozone depletion. Nitrous oxide has been part of the atmosphere for millions of year as it is emitted by bacteria on earth. Agriculture is another source of nitrous oxide production, i.e. from nitrogen fertilizers, cultivation of soil, and animal waste. Livestock, burning of fossil fuels and industry also produces a large percentage of this gas. In 2006 in the USA, N2O use in anaesthesia was estimated to contribute to 3% of the total N2O emissions [2].According to recent studies nitrous oxide can contribute to greenhouse gas emissions and when administered with other volatile agents can increase emissions [2]. Quantifying the Environmental Effect of Anaesthetic Drugs: Life Cycle Assessment A tool known as a life cycle assessment is used to evaluate the impact that a product has on the environment during its life cycle and the resources used in the process. As medical personnel it is essential in our daily practice to take into consideration the life cycle of drugs. In doing so we can understand how our drug choices impact on the environment. Page 9 of 19 A study by Sherman et al looked at the environmental impact of sevoflurane, desflurane, isoflurane, nitrous oxide, and propofol by utilizing life cycle assessments of each drug. They looked at: resource extraction and manufacturing of the above drugs, transportation to hospitals, clinical use, and disposal or emission to the environment [8]. Figure 4: Life Cycle Assessment of Anaesthetic Agents [8] Manufacturing and production of agents Transport Use Disposal Isoflurane Production Extraction Of raw material Manufacturing of industrial gas Desflurane Production Sevoflurane Production Production of basic chemicals Emissions to Environment Health Care Facility Medical Waste Propofol Production Emissions to Environment Waste Anaesthetic gases Emissions to Environment Emissions were taken into consideration at each stage of the life cycle. Using SimaPro Life Cycle Assessment Software they were able to store data and assessment of impact was performed [8]. From the above study it was found that desflurane contributed more than the other agents towards life cycle Greenhouse gas emissions [8]. Furthermore the greenhouse gas emissions increased when administered with N2O/O2 for these agents. Propofol was found to have a small impact compared to the other agents. The impact of propofol was found to originate mainly from the energy required to function the syringe pump and not from the release of propofol to the environment itself [8]. There are several factors responsible for desflurane’s higher greenhouse gas emissions compared to the other agents: its rate of metabolism is low therefore a greater volume of gas is emitted unchanged to the environment, and it has a higher MAC value and global warming potential (GWP) than the other agents. Page 10 of 19 STRATEGIES TO REDUCE OUR ENVIRONMENTAL FOOTPRINT Reducing Environmental Contamination by anaesthetic gases a) Closed anaesthesia Studies have shown that closed circuit anaesthesia can decrease volatile anaesthetic use by 80% to 90% [2]. Using this technique one is able to limit environmental contamination. Closed circuit anaesthesia however is found to be unpopular among many anaesthesiologists due to the perceived difficulty in gaining reliable control over the concentration of inspired gases administered [9]. Previously, along with this came the added task of injecting anaesthetic liquid vapours, stringent management of fresh gas flow and estimation of circuit volume [10] . Recent developments of more advanced anaesthetic equipment however have made closed circuit anaesthesia simple and far more feasible for routine practice [9]. b) Control of Fresh Gas Flow Control of Fresh Gas Flow (FGF) in a more proficient manner can reduce environmental contamination intra-operatively. Fresh gas flow can be managed during all phases of anaesthesia i.e. induction, maintenance and emergence. Since we are directly responsible for the administration of anaesthetic gases and FGF, we are in fact directly accountable for the impact it may have on the environment. It is essential to understand the influence that FGF has on environmental contamination. In an article by Feldman et al, GASman simulations were used to approximate the anaesthetic gases utilized during a general anaesthetic [10]. GASman is a computer simulator used for estimating uptake and distribution of anaesthetic agents. This simulator is able to allow the user to display the time course of anaesthesia uptake and distribution in body compartments, the breathing circuit and the vaporizer. The user can enter information including patient profiles, FGF, gas delivery, and breathing circuit type. GASman can then calculate the distribution over time, and the amount of gas delivered and taken up by the patient. It can therefore estimate the amount of anaesthetic gases wasted [10, 11]. Page 11 of 19 Vapourizer setting FGF during Induction (15mins) FGFduring Maintenance (75mins) Amount Delivered Amount taken up Contamination Anaesthetic 1 2% Anaesthetic 2 2.5% 8L/min 8L/min 2L/min 1L/min 5.4L 1.3L 4.1L 4.28L 1.26L 3.02L Table 2: Gasman simulation of a 90 minute general anaesthetic al [10]. Modified from Feldman et Using GASman simulation Feldman was able to demonstrate that by using lower fresh gas flows, one can decrease the amount of contamination into the environment. He then went on further to examine the consequence of administering these fresh gas flows over a 35 year career (500 anaesthetics per year over a 35 year period). It was found that by reducing the FGF from 2L/min to 1L/min during the maintenance phase, 18,900L of isoflurane was prevented from being wasted into the atmosphere [10]. We can easily observe that by managing FGF effectively, we can reduce the amount of contamination into the environment. Reducing FGF during the maintenance phase is probably the ideal time to do so, but strategies to reduce contamination during emergence and induction can also be practised. Page 12 of 19 Figure 5- Recommendations for management of fresh gas flow [10] c) TIVA/Regional Anaesthesia Total intravenous or regional anaesthesia can eliminate the need for anaesthetic gases and therefore decrease the negative impact that they have on the environment. These techniques however utilize drugs, anaesthetic equipment, receptacles and energy. The impact that these techniques have on the environment has not been well investigated. Therefore in order to compare them with inhalational anaesthesia thorough life cycle assessments will have to be done [2,3] . The potential impact of the reusable/disposable components of intravenous anaesthesia will also be alluded to below. Strategies to reduce drug wastage also need to be addressed when employing TIVA as an environmentally friendly strategy. Page 13 of 19 d) Silica Zeolite (Deltazite) Standard anaesthetic gas scavenging systems collect and remove waste gases and transfer them to the atmosphere. To prevent environmental contamination new technologies have been developed. Silica Zeolite is a molecular sieve adsorbent. Trapping of halogenated hydrocarbons from the gas stream is achieved by passing it through a layer of hydrophobic and organophilic silica zeolite [12]. The cavities found in the crystal framework of the silica zeolite adsorb the halogenated hydrocarbons so removing them from the gas stream. By exposing the exhausted adsorbent to a purging gas stream the trapped agents can be regenerated [12]. The halogenated agents are extracted from the gas stream in liquid form and then purified by fractional distillation [12]. In a study by Doyle et al silica zeolite was effective in removing 1% isoflurane from exhaled humidified gas containing CO2 for 8 hours [12]. Zeolite filters (Deltasorb) are also used in scavenging lines to limit the amount of volatile released into the atmosphere [16]. Studies have shown that each canister can adsorb about two bottles of halogenated anaesthetics, therefore decreasing the amount released by 40-75% [2, 3]. e) Xenon [2, 3] Xenon occurs naturally in the atmosphere (0,08 parts per million). It has no toxic effect on the environment. It can be used in anaesthesia as a substitute to N2O for its analgesia properties. It also provides some degree of neuroprotection and haemodynamic stability. It can be used for rapid induction and emergence because of its low blood gas partition coefficient. It is manufactured through fractional distillation of liquid air and is very costly. The high cost therefore limits its use in clinical practice. Also it is not economical because it consumes large quantities of energy for production (220W/h per 1L xenon gas). This is more than the energy needed to produce N2O. f) Other ways to reduce Environmental Contamination Selection of gases that have a less negative impact on the environment for e.g. limiting use of N2O, or choosing to use sevoflurane or isoflurane over desflurane and halothane [3]. Developing newer anaesthetic gases with lower environmental impact Maintenance and testing of anaesthetic equipment to prevent leaks [5] DISPOSABLE AND REUSABLE EQUIPMENT IN ANAESTHESIA There has been a growing interest in the impact that reusable and disposable equipment and textiles has on the environment. A large proportion of CO 2 emissions are from the health care sector. Reusable equipment requires cleaning and disinfectants that may be toxic to the environment, whereas disposable items may add substantially to waste of landfills [15]. Page 14 of 19 In addition disposable items may require incineration that release toxins to the atmosphere. The environmental impact of manufacturing, disposal and waste management can be done by conducting life cycle assessments. Using life cycle assessments one can assess the financial and environmental impacts of such items therefore aiding decision making when selecting items for use in theatre. a) Disposable vs Reusable Laryngeal Mask Airways [13] The first Laryngeal Mask Airways (LMAs) that were used in the late 1980s were reusable, in the late 1990s disposable LMAsbecame available [13]. Previous studies conducted have shown no difference between reusable and disposable LMAs in terms of the way they function and their ability to be user friendly. Due to an increase in the number of general anaesthetics administered each year and financial constraints in the health sector, the types of LMAs purchased are normally dictated by costs. Eckelman et al conducted a comparative life cycle assessment of disposable and reusable Laryngeal Mask Airways. A cradle-to-grave study was done which looked at manufacturing, transportation and usage and wastage of the LMAs. The impact that the LMAs had on the environment was assessed using SimaPro life cycle assessment software and the Building for Environmental and Economic Sustainability impact assessment method [13] Used LMA + packaging Raw Materials LMA Materials Manufacturing Reusable LMA LMA Materials Use Solid Waste Management Transport/ Distribution Disposable LMA Raw Materials Packaging Used LMA + Packaging Transport/ Distribution Manufacturing Packaging Use Solid Waste Management Washing Autoclave Wastewater Treatment 40 Cycles Figure 6: Comparative Life Cycle Assessment of Disposable and Reusable Laryngeal Mask [13] The results of the above study have shown that the reusable LMA ClassicTM had fewer life cycle impacts than that of the disposable LMA UniqueTM. The reusable LMA contributes 7.4kg CO2e of GHGs over its life cycle, and the equivalent 40 disposable LMAs contribute 11.3kg CO2e, when looking at climate change Impacts [13]. Page 15 of 19 Figure 7: Comparison of environmental and human health (HH) impacts for disposable and reusable LMAs, Building for Environmental and Economic Sustainability (BEES) impact assessment method [13]. There are many factors that may contribute to these environmental impacts. These include the type of material used in the manufacturing of LMAs. Disposable LMAs consists of polyvinyl chloride (PVC) plastic whereas reusable LMAs are made of silicone. PVC has been linked with concerns regarding health[13] and burning of these plastics has obvious negative impacts on the environment. Disposable LMAs also require larger quantities of material in total for packaging. In addition Diethylhexyl phthalate (DEHP) is used in PVC products. DEHP has been identified as a likely carcinogen and could possibly be implicated in endocrine disruption [13]. Although the reusable LMAs have less of an impact on the environment than the disposables there is still some room for improvement. The process of autoclaving utilises large quantities of energy and water. These environmental impacts can be reduced by autoclaving more LMAs during a single cycle at once or with similar equipment [13]. Ordering LMAs in bulk can also reduce environmental impacts, as there will be less need for transport of LMAs by air which has negative effects on the atmosphere. b) Reusable and single-use Central Venous Catheter Insertion Kits [14]. In a study by McGain et al they looked at the impact that Reusable and SingleUse Central Venous Catheter Insertion Kits have on the environment and financially. The source of energy used for sterilization was examined and the effect that it has on CO2 emissions. Using SimaPro Software they were able to perform life cycle assessments on the reusable and single-use central venous catheter kits. Effects on the environment analysed included CO2 emissions, water and mineral use, ecotoxicity and solid waste [14]. Page 16 of 19 Sensitivity analyses on the source of electricity was also done on the reusable kits. These included brown coal, gas cogeneration and the standard electricity supply. CVC Kit Type Reusable kit (brown coal electricity), total weight=627g Single-use CVC kit, total weight=171g Total CO2 produced (grams) Total Water use (litres) 1211 27.7 407 2.4 Table 3:Comparison of CO2 produced and water used for Reusable and Single-use CVC kits [14] From the study it was demonstrated that the use of water and energy for the reusable kits were more than for the single use kits (this was based on the brown coal electricity). Majority of the CO2 emissions for the reusable kits came from sterilization (830g) whereas for the single use kits most of the CO2 emissions where from manufacture of plastics (170g). It was also demonstrated that the source of energy used in the sterilization process played an important role in the CO2 emissions produced. Type of CVC kit (and energy source) Single use (European energy mix) Reusable: brown coal Reusable: hospital cogeneration Reusable: United States electricity mix Reusable: European electricity mix CO2 emissions (grams) with 95% CIs Water use (liters) with 95% CIs 407 (379-442) 2.5 (2.1-2.9) 1211 (1099-1323) 27.7 (27.0-28.6) 436 (410-473) 26.0 (25.8-26.2) 764 (509-1174) 46.3 (36.6-62.6) 572 (470-713) 40.5 (36.4-45.8) Table 4: Modified from McGain F: CO2 Emissions and Water Use for the Single-Use and Reusable Central Venous Catheter(CVC) Kits Accounting for Different Energy Sources [14]. From the above table it can be seen that by using other sources of electricity instead of brown coal, CO2 emissions can be reduced. Types of energy sources with lower CO2 emissions include gas-fired boilers as a source of steam energy and nuclear powered electricity. In the above study for their hospital that used brown coal as an energy source and on average 500 CVC insertion kits yearly, reusable kits would have saved them $1000, however it would have produced 400kg more CO2 and used 12500 more litres of water than compared to the single-use CVC kits [14]. Page 17 of 19 Therefore when considering reusable kits one would have to examine the source of energy used for sterilization as it also contributes to increasing CO2 emissions. CONCLUSION Climate change has become an important issue for health care industries. The environmental impact of our actions should not be left unchecked. As anaesthesiologist we need to add environmental awareness to our list of responsibilities. The information provided in this booklet introduces some of the environmental implications of our clinical practice and offers suggestions on how to reduce these. As health care professionals we have the opportunity through education and research to promote environmentally friendly policies and reduce the negative impact of our actions. Page 18 of 19 REFERENCES 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. 13. 14. 15. 16. 17. 18. 19. Russell F.Mankes. Propofol Wastage in Anaesthesia. AnesthAnalg. 2012 May;114 (5):1091-2. Epub 2012 Mar 13 Ishizawa Y. General anesthetic gases and the global environment. AnesthAnalg 2011;112:213-7 Bosenberg M. Anaesthetic gases: environmental impact and alternatives. South Afr J AnaesthAnalg 2011;17(5):345-348 http://epa.gov/climatechange/glossary.html Goyal R, Kapoor MC. Anaesthesia: Contributing to pollution? J AnaesthClinPharmocol 2011;27:435-7 Chaudhary K, Garg R, Bhalotra AR, Anand R, Girdhar KK. Anesthetic drug wastage in the operating room: A cause for concern. J AnaesthClinPharmacol 2012;28:56-61 Sherman SJ, Cullen BF. Nitrous oxide and the greenhouse effect. Anaesthesiology 1988;68:816-7 Sherman J, Le C, Lamers V, Eckelman M. Life Cycle Greenhouse Gas Emissions of Anesthetic Drugs. AnesthAnalg 2012;114:1086-90 Schober P, Loer SA. Closed system anaesthesia- historical aspects and recent developments. Eur J Anaesthesiol 2006;23:914-20 Feldman JM. Managing Fresh Gas Flow to Reduce Environmental Contamination. AnesthAnalg 2012;114:1093-101 www.GASman.com Doyle DJ, Byrick R, Filipovic D, Cashin F. Silica zeolite scavenging of exhaled isoflurane: a preliminary report. Can J Anaesth 2002;49:799-804 Eckelman M, Mosher M, Gonzalez A, Sherman J. Comparative Life Cycle Assessment of Disposable and Reusable Laryngeal Mask Airways. AnesthAnalg 2012;114:1067-72 McGain F, McAlister S, MaGavin A, Story D. A Life Cycle Assessment of Reusable and Single-Use Central Venous Catheter Insertion Kits. AnesthAnalg 2012;114:1073-80 Huncke K, Ryan S, Paulsen W, Stanton C, Yost S, Striker AB. Greening the Operating Room: Reduce, Reuse, Recycle and Redesign. Thomasson R, Luttropp HH, Werner O. A reflection filter for isoflurane and other anaesthetic vapours. Eur J Anaesthesiol. 1989 Mar:6(2):89-94 U.K. Sustainable Development Commission. NHS Eng Carbon Footprinting Report 2008 Langbein T, Sonntag H, Trapp D, Hoffmann A, Malms W, Roth P, Mors V, Zellner R. Volatile Anaesthetics and the atmosphere: atmospheric lifetimes and atmospheric effects of halothane, enflurane, isoflurane, desflurane and sevoflurane. British Journ of Anaesth. 1999: 82(1): 66-73 Ryan S, Sherman J. Sustainable Anesthesia. AnesthAnalg 2012;114:921923 Page 19 of 19