Skip to content
Home - Responsibility - Our medicines - Pharmaceuticals in the environment    

Pharmaceuticals in the environment

We work continuously to improve our understanding of the way in which our pharmaceuticals interact with the environment. Our environmental scientists, located mainly at our Environmental Laboratory in Brixham, UK are committed to advancing research in this area.

Public interest in the Pharmaceuticals in the Environment (PIE) issue has grown in recent years, in part as a result of the linking of two independent scientific observations. Firstly, due to advancements in analytical capabilities, residues of a wide range of active pharmaceutical ingredients (APIs) began to be detected in surface waters in certain countries at concentrations of 0.01 to 0.1 µg/l (parts per billion). Secondly, some substances capable of interacting with the endocrine systems of aquatic animals, such as synthetic and natural œstrogens, were shown to be having some long-term sub-lethal effects on a few aquatic species in a small number of locations. Appropriately, questions about the potential long term environmental fate and effects of some pharmaceuticals are now being asked.

Our approach
The environmental profile of AstraZeneca’s new pharmaceuticals is assessed prior to applying for government approval in a manner that is, at a minimum, consistent with applicable regulatory regimes. The science in this area is continuously evolving, and AstraZeneca is committed to conducting its assessments based upon the best available science. In light of this changing science, there has been much activity in a number of areas over the last few years. For example, the United Kingdom and Sweden have carried out major reviews of the scientific data relevant to the potential impact caused by pharmaceutical residues in the environment. New Environmental Risk Assessment Guidelines have now been introduced in the European Union and are being revised in a number of other regions, particularly in Canada and Japan. AstraZeneca continues to work with the relevant pharmaceutical industry trade associations to provide expert input to the current public consultations. In anticipation of these new guidelines, and as an element of our internal PIE-related initiatives, we have reviewed the environmental risk assessments for our existing products and, where appropriate, have carried out further studies to replace previous default values with measured data.

We make this environmental risk data, together with available information on our existing products, publicly available via the Swedish Doctors Prescribing Guide  website using the voluntary disclosure system introduced by the Swedish Association of the Pharmaceutical Industry (LIF). The system was developed by LIF and a number of Swedish stakeholders, in conjunction with expert representatives from international pharmaceutical companies, convened and chaired by AstraZeneca. In association with the Association of British Pharmaceutical Industries we are also helping the Environment Agency for England and Wales to evaluate the risks of the existing medicines on their priority action list. We continue to investigate the potential application of green chemistry principles to our drug design process. In addition, we have introduced an Environmental Risk Management Plan that will accompany all new medicines through the development process and will enable all data relevant to the environmental risks associated with the use and disposal of medicines to be available at all key decision points.

Further data continues to be published on the presence of pharmaceutical residues in surface waters. This data is consistent with initial observations that, although variable, quantities present in the environment are likely to be several orders of magnitude below those that would pose any significant risk to human beings and are not high enough to cause immediate or short term (acute) harm to aquatic life. Nevertheless, a better understanding of the potential long term effects, if any, of pharmaceuticals in the environment continues to be a priority area of study for AstraZeneca’s environmental scientists, working both independently and in collaboration with other organisations to advance research in this area.

Although there is little evidence that the current concentrations of pharmaceuticals in the environment pose any significant risk the fact that they are present causes concern to some stakeholders. Complete elimination of such residues is unlikely to be possible. However, products in our development pipeline are likely to result in lower environmental residues than those in our current portfolio for two reasons. Firstly, the needs of the patient and the environment coincide, which means that changes in drug design aimed at improved treatment effectiveness will also improve the environmental performance. For example, the current treatment for tuberculosis requires the use of five different drugs over a period of 6-8 months, whereas the target for our TB research team in Bangalore is to produce a single drug that is effective within four months. If successful, this will lead to a significant reduction in drug released to the environment during the treatment of this widespread disease. Secondly, an increasing proportion of our pipeline consists of biopharmaceuticals and these types of molecule tend to be metabolised by the body or rapidly degraded in the environment.

Our research
AstraZeneca’s own scientists, located at our Brixham Environmental Laboratory, are at the forefront of research in this field, working both independently and in collaboration with other companies, leading academics and regulatory bodies to advance PIE-related research. We recently invested a further $24 million in new laboratories at the Brixham site to improve the facilities for the evaluation of environmental fate and persistence of pharmaceuticals.

Current work is concentrating on two areas of fundamental research. Firstly, improving our understanding of the processes leading to the breakdown of pharmaceutical residues by both biotic and abiotic processes, in the natural environment and in sewage treatment plants. This will improve our ability to model API concentrations in the environment, and promises to provide a better understanding of the fate of pharmaceuticals both in sewage treatment plants and in the wider environment. Secondly we are working to understand the potential for some APIs to exert atypical impacts on the biota in the receiving environment. In particular, we are investigating whether it is possible to predict ecological responses from the large amount of preclinical data that is already produced as part of the registration submission for all new drugs, thus reducing the need for additional animal testing. We expect the results to contribute positively to global efforts to continuously improve the overall state of scientific understanding in this area.

As the research moves forward, the understanding of some of the complexities of this issue improves. There was an initial concern that all pharmaceuticals might have long-term environmental effects that were not predictable, by extrapolation, from short-term studies. However, as evidence accumulates it appears that this may only be an issue for a small number of substances that demonstrate ‘atypical’ effects. For example, AstraZeneca has undertaken a fish full lifecycle study on tamoxifen that showed significantly less toxicity than might have been predicted for a hormonally acting compound. It also appears that even some closely related substances with the same mode of action can show very different environmental profiles. This has been observed with the beta-blockers, atenolol and propranolol, for example, where atenolol shows significantly lower toxicity to fish compared with propranolol. In addition, our research has demonstrated that natural photo-degradation, caused by sunlight, can be a powerful factor in the removal of pharmaceutical residues from the environment. For example, there is evidence that around 70% of propranolol can be destroyed this way. It seems, therefore, that all medicines should be evaluated on a case-by-case basis in these respects, rather than being grouped together as a single class or classes. We continue to publish our research in this area and a selection of our work is shown in the bibliography below.

Our performance
Consistent with our commitment to product stewardship and sustainable production, AstraZeneca works continually to better understand the way in which our drug substances interact with the environment. One of our stated objectives is to pursue site-specific opportunities to minimise the amount of product lost to wastewater during our manufacturing activities. As far as practicable, through our process design and operating procedures, we aim to avoid the loss of product to the environment during manufacturing and ensure that any losses that do occur are unlikely to cause harm. To this end, we continue to develop and refine assessment tools that enable us to screen our discharges through application of available data and current scientific knowledge. During 2006, we introduced a new expert system to help our engineers to select the most appropriate effluent treatment technology. This system was used to verify the design of our new manufacturing facility in Egypt, commissioned during that year.

Based upon work conducted to date, we have no scientific basis for believing that our manufacturing discharges pose a significant threat to the environment. For example, a recent study monitoring the effluent arising from the AstraZeneca manufacturing facilities in Södertälje, Sweden, showed concentrations of APIs well below any effect thresholds of concern. This study will be published in early 2008. However, we will continue to conduct internal evaluations for purposes of identifying future research needs and guiding internal risk management decisions. In the longer term, we will continue to work to ensure that the development and application of our evaluation techniques remains consistent with the evolving science, and that our manufacturing activities remain protective of human health and the environment. One example of our commitment is our commissioning in 2005 of a $36 million state of the art biological treatment facility at our Avlon Works in Bristol in the UK as well as improving effluent treatment at other facilities.

The above content was externally assured by Bureau Veritas, February 2008

BIBLIOGRAPHY
AstraZeneca publications related to Pharmaceuticals in the Environment

2003

Predicting the Effects of Endocrine Disrupting Chemicals on Fish Populations.
Brown A.R. ; Riddle A.M. ; Cunningham N.L. ; Kedwards T.J. ; Shillabeer N.S. ; Hutchinson T.H.
Human and Ecological Risk Assessment 2003 v9 n3 p761-788
Development of fish tests for endocrine disruptors.
Hutchinson T.H. ; Yokota H. ; Hagino S. ; Ozato K.
Pure and Applied Chemistry 2003 v75 n11-12 p2343-2353
Inhibition of gonadotropin-induced oviposition and ovarian steroidogenesis in the African clawed frog (Xenopus laevis) by the pesticide methoxychlor.
Pickford D.B. ; Morris I.D.
Aquat. Toxicol. 2003 v62 n3 p179-194
Dynamics of estrogen biomarker responses in rainbow trout exposed to 17beta-estradiol and 17alpha-ethinylestradiol.
Thomas-Jones E. ; Thorpe K.L. ; Harrison N. ; Thomas G. ; Morris C. ; Hutchinson T.H. ; Woodhead S. ; Tyler C.
Environmental Toxicology and Chemisry 2003 v22 n12 p3001-3008
Relative potencies and combination effects of steroidal estrogens in fish.
Thorpe K.L. ; Cummings R.I. ; Hutchinson T.H. ; Scholze M. ; Brighty G. ; Sumpter J.P. ; Tyler C.R.
Environ. Sci. Technol. 2003 v37 n6 p1142-1149

2004
Successful detection of (anti-) androgenic and aromatase inhibitors in pre-spawning adult fathead minnows (Pimephales promelas) using easily measured endpoints of sexual development.
Panter G.H. ; Hutchinson T.H. ; Hurd K.S. ; Stanley R.D. ; Sherren A. ; Tyler C.R.
Aquatic Toxicology 2004 v70 n1 p11-21
Application of a partition map and multimedia models to predict fate of pharmaceuticals in the environment.
Riddle A.M. ; Liu Q-T. ; Robinson P.F.
Environmental Science and Technology (In Press 2004)
Reproductive effects of exposure to oestrone in the fathead minnow
Thorpe K.L. ; Benstead R. ; Hutchinson T.H. ; Cummings R.I. ; Tyler C.R.
Fish Physiology and Biochemistry 2004 v28 p451-452
Qualitative and quantitative histomorphologic assessment of fathead minnow Pimephales promelas gonads as an endpoint for evaluating endocrine-active compounds: A pilot methodology study.
Wolf J.C. ; Dietrich D.R. ; Friedrich U. ; Caunter J.E. ; Brown A.R.
American Journal of Pathology (2004 - In Press)

2005
Evaluation of a lower tier exposure assessment model for veterinary medicines
.
Blackwell P.A. ; Boxall A.B.A. ; Kay P. ; Noble H .
Journal of Agriculture and Food Chemistry 2005 v53 p2192-2201
Predicting the effects of endocrine disrupting chemicals on healthy and disease impacted populations of perch (Perca fluviatilis).
Brown A.R.
Ecological Modelling (In press 2005)
Phototransformation and partitioning as removal processes of Propranolol from UK and US rivers.
Liu Q-T. ; Riddle A.M. ; Robinson P.F. ; Murray-Smith R.J. ; Gray N.
Environmental Science and Technology (In Press 2005)

2006
Pharmaceuticals in the environment: Implications for potential aquatic life impacts.
Cunningham ; Buzby ; Hutchinson T.H. ; Mastracio ; Parke N ; Roden N
Environmental Science and Technology 2006 v40 p3456 -3462
Effects of Human Pharmaceuticals on Aquatic Life: Next Steps.
Cunninghan V.L. ; Buzby M. ; Hutchinson T.H. ; Mastrocco F. ; Parke N. ; Roden N.
Environmental Science and Technology 2006 v40 n11 p3456 –3462
Development and validation of a direct homologous quantitative sandwich ELISA for fathead minnow (Pimephales promelas) vitellogenin.
Eidem J.K. ; Kleivedal H. ; Kroll K. ; Denslow N. ; van Aerle R. ; Tyler C.R. ; Panter G.H. ; Hutchinson
T.H. ; Goksoyr A.
Aquatic Toxicology 2006 v78 n2 p202 -206
Expression of target and reference genes in Daphnia magna exposed to ibuprofen.
Heckmann L.H. ; Connon R. ; Hutchinson T.H. ; Maund S.J. ; Sibly R.M. ; Callaghan A.
BMC Genomics 2006 v7 p175
Small is useful in endocrine disrupter assessment - four key recommendations for aquatic invertebrate research.
Hutchinson T.H.
Ecotoxicology 2006 v16 n1 p231 -238
Screening and testing of endocrine disrupters in fish - Biomarkers as signposts not traffic lights in risk assessment.
Hutchinson T.H. ; Ankley G.T. ; Segner H. ; Tyler C.
Environmental Health Perspectives 2006 (Suppl 1) v114 p106 –114
Availability of in vitro vitellogenin assay for screening of estrogenic and anti-estrogenic activities of environmental chemicals.
Iguchi T. ; Irie F. ; Urushitani H. ; Tooi O. ; Kawashima Y. ; Roberts M. ; Norrgren L ; Hutchinson T.H.
Environmental Sciences 2006 v13 p161 -183
Kinetics and degradation products for direct hydrolysis of beta-blockers in water.
Liu Q-T. ; Cumming R.I. ; Hetheridge M.J. ; Williams H.E.
Environmental Science and Technology 2006 v41 n3 p803 -810
QSAR approach for mixture toxicity prediction using independent latent descriptors and fuzzy membership functions.
Mwense M. ; Wang X.Z. ; Buontempo F.V. ; Horan N. ; Young A. ; Osborn D.
SAR and QSAR in Environmental Research 2006 v17 n1 p53 –73
Population growth rate and carrying capacity for Springtails Folsomia candida exposed to Ivermectin.
Noel H. ; Hopkin S. ; Hutchinson T.H. ; Williams T.D. ; Sibly R.
Ecological Applications 2006 v16 n2 p656 -665
Development of chronic tests for endocrine active chemicals. Part 1. An extended fish early-life stage test for oestrogenic active chemicals in the fathead minnow (Pimephales promelas).
Panter G.H. ; Hutchinson T.H. ; Bamforth J.E. ; Stanley R. ; Duffell S. ; Hargreaves A. ; Gimeno S.
Tyler C.R.
Aquatic Toxicology 2006 v77 p279 -290
Induction of decision trees using genetic programming for modelling ecotoxicity data: adaptive discretization of real-valued endpoints.
Wang X.Z. ; Buontempo F.V. ; Young A. ; Osborn D.
SAR QSAR Environ. Res. 2006 v17 n5 p451 –471

2007
Modelling the Impact of Direct Phototransformation on Predicted Environmental Concentrations (PECs) of Propranolol Hydrochloride in UK and US Rivers.
Chemosphere 2007 v66 p757 -766
Human health and environmental risk assessment of carmazepine in surface waters of North America and Europe.
Cunningham V. ; Hartmann A. ; D'Aco V. ; Perino C. ; Hutchinson T.H. ; Bechter R.
Environmental Science and Technology (In Press) 2007
Chronic toxicity of ibuprofen to Daphnia magna: effects on life history traits and population dynamics.
Heckmann L.H. ; Callaghan A. ; Hooper H.L. ; Connon R. ; Hutchinson T.H. ; Maund S.J. ; Sibly R.M.
Environmental Health Perspectives (in press) 2007
Summary of workshop on environmental assessment of human medicines: Development and use of aquatic toxicity data.
Montforts M.H.M.M. ; Brandt I. ; Hutchinson T.H.
Drug Information Journal 2007 v41 p2 -203
Guest Editorial: DIA/HESI/SAPS Conference on environmental risk assessment of human medicines (Stockholm, May 22-23, 2006).
Editor(s) :Montforts M., Spindler P., Taylor D. ,Williams R.
Drug Information Journal 2007 v41 p2 -129
Workshop on the use and modeling and monitoring in the environmental risk assessment of human medicines.
Murray-Smith R.J. ; Ramil M.
Drug Information Journal 2007 v41 p2 -195
Comparative physiology, pharmacology and toxicology of beta-blockers in fish: a critical review.
Owen S.F. ; Giltrow E. ; Huggett D.B. ; Hutchinson T.H. ; Saye J.A. ; Winter M.J. ; Sumpter J.P.
Aquatic Toxicology 2007 v82 n3 p145 -162
Uptake of Propranolol, a cardiovascular pharmaceutical, from water into fish plasma and its effects on growth and organ biometry.
Owen S.F. ; Huggett D.B. ; Hutchinson T.H. ; Hetheridge M.J. ; Kinter L.B. ; Ericson J.F. ; Sumpter J.P.
Toxicological Science (In Press) 2007
Acute and chronic effects of ibuprofen in the freshwater mollusc Planorbis carinatus (Gastropda: Planorbidae).
Pounds N.A. ; Hutchinson T.H. ; Maclean S.A. ; Webley M. ; Pascoe D.
Ecotoxicology and Environmental Safety (In Press) 2007
The EU project ERAPharm.
Snape J.R.
ERAPharm (In press) 2007
Deterministic and probabilistic acute-based environmental risk assessment for naproxen for western Europe.
Straub J.O. ; Stewart K.M.
Environmental Toxicology and Chemistry 2007 v26 n4 p795 -806
Evaluation of the reproductive effects of tamoxifen citrate in partial and full life-cycle studies using fathead minnows (Pimephales promelas).
Williams T.D. ; Caunter J.E. ; Lillicrap A.D. ; Hutchinson T.H. ; Gillings E. ; Duffell S.
Environmental Toxicology and Chemistry 2007 v26 n4 p695 -707
Defining the chronic impacts of Atenolol (Tenormin) on embryo-larval development and reproduction in the fathead minnow (Pimephales promelas).
Winter M.J. ; Lillicrap A.D. ; Caunter J.E. ; Hutchinson T.H. ; Alder A. ; Ramil M. ; Ternes T. ; Giltrow E. ; Sumpter J.P.
Aquatic Toxicology (In Press) 2007
 

AstraZeneca websites
Search
Quick links