Occurrence of pharmaceuticals and cocaine in a Brazilian coastal zone

https://doi.org/10.1016/j.scitotenv.2016.01.051Get rights and content

Highlights

  • Pharmaceuticals and cocaine were assessed in a subtropical coastal zone

  • Acetaminophen, caffeine, diclofenac, ibuprofen, losartan and valsartan were quantified

  • Ibuprofen showed highest concentration in order of μg·L 1

  • Cocaine and benzoylecgonine were both quantified in all of the samples

Abstract

The present study determined environmental concentrations of pharmaceuticals, cocaine, and the main human metabolite of cocaine in seawater sampled from a subtropical coastal zone (Santos, Brazil). The Santos Bay is located in a metropolitan region and receives over 7367 m3 of wastewater per day. Five sample points under strong influence of the submarine sewage outfall were chosen. Through quantitative analysis by LC–MS/MS, 33 compounds were investigated. Seven pharmaceuticals (atenolol, acetaminophen, caffeine, losartan, valsartan, diclofenac, and ibuprofen), an illicit drug (cocaine), and its main human metabolite (benzoylecgonine) were detected at least once in seawater sampled from Santos Bay at concentrations that ranged from ng·L 1 to μg·L 1. In light of the possibility of bioaccumulation and harmful effects, the high concentrations of pharmaceuticals and cocaine found in this marine subtropical ecosystem are of environmental concern.

Introduction

As the world's population grows and becomes more concentrated in coastal zones, marine ecosystems become further exposed to both treated and untreated wastewater discharges composed of a mixture of emerging contaminants that includes bioactive compounds.

Drugs consumption is often associated with longevity and stressful lives, particularly in urban areas. Advances in medicine, the significant growth of chemistry and pharmaceutical companies, and changes in social conditions have all led to the more widespread use of pharmaceuticals and psychotropic substances (Borova et al., 2014).

In recent years, pharmaceuticals and personal care products (PPCPs) have been considered emerging contaminants of great concern to environmental protection agencies, such as the USEPA and Environment Canada (USEPA – United States Environmental Protection Agency, 2010, Environment Canada, 2011). As reported by Petrie et al. (2015), the presence of PPCPs in the environment is mainly attributed to the discharge of wastewater from WWTPs because conventional processes are not designed to remove such compounds, resulting in their discharge to receiving surface waters including rivers, lakes and coastal waters. There is accumulating evidence that domestic sewage carries PPCPs and illicit drugs into aquatic ecosystems, even after passing through wastewater processing facilities (Zuccato et al., 2008, Terzic et al., 2010, Gilbert, 2011, Baker et al., 2012, Baker and Kasprzyk-Hordern, 2013, Borova et al., 2014, Zenobio et al., 2015).

Most of the efforts to assess PPCPs occurrence and potential impacts on non-target organisms in aquatic environments have been focused in freshwater rivers and streams heavily impacted by wastewater effluent. However, because urban estuarine and marine environments typically receive inputs of complex mixtures of chemical contaminants from a variety of sources, including numerous municipal and industrial wastewater outfalls, characterization of PPCP concentrations in these environments is also important (Klosterhaus et al., 2013). A large number of analytical methodologies are available for their determination in surface waters, and recent trends are focused toward the development and application of generic methods that permit simultaneous analysis of multiclass compounds, including acidic, neutral, and basic pharmaceuticals (Gros et al., 2009).

Previous studies have observed PPCPs, as well as illicit drugs and their metabolites in marine environments (Maranho et al., 2015a, Klosterhaus et al., 2013, Fang et al., 2012, Weigel et al., 2002, Weigel et al., 2004). Such compounds have been found at low concentrations in surface waters (ng·L 1), but they are continually released into ecosystems. This steady flow contributes to their persistence and potential adverse effects (Andreu et al., 2016, Alygizakis et al., 2016). Concerning specifically illicit drugs and their breakdown products, occurrences in regions of production and use and areas with insufficient wastewater treatment are not well studied (Rosi-Marshall et al., 2015).

In light of the lack of data on the occurrence of pharmaceuticals and illicit drugs in tropical coastal zones, the main objective of this study was to measure the presence of 33 emerging contaminants, including pharmaceuticals, cocaine, and its main metabolite benzoylecgonine in water samples from the Santos Bay (São Paulo, Brazil).

Section snippets

Sampling sites

The sampling area selected in this study was Santos Bay (São Paulo, Brazil), which receives over 7367 m3 of sewage per day. The main pollution sources of this coastal zone include wastewater discharges without appropriate treatment (Abessa et al., 2005).

The local wastewater treatment plant (WWTP) receives discharges from the cities of Santos and São Vicente, a dense urban area with 766,421 inhabitants (IBGE, 2015). This population size increases by 18.8% in Santos and 15.8% in São Vicente during

Results and discussion

Nine compounds were detected in the seawater sampled at Santos Bay: two anti-inflammatories (ibuprofen and diclofenac); three antihypertensive (valsartan, losartan, and atenolol); one analgesic (acetaminophen); one illicit drug (cocaine) and its human metabolite (benzoylecgonine); and caffeine, which can be found in combination with pharmaceuticals and is considered as a wastewater tracer (Benotti and Brownawell, 2007). All the sampling stations were located in the adjacent area of the outfall

Conclusion

Our study demonstrated that the high concentrations of pharmaceuticals and cocaine found in this subtropical zone are of environmental concern and reported first data on these emerging contaminants in seawater from Brazilian coast. The main step to minimize this contamination by bioactive compounds should be the development of an effective treatment for wastewater discharges. In addition, new polices on environmental risk assessment, waste management, and public education must be enforced and

Acknowledgments

This study was funded by CNPq (Processes n° 481358/2012-9 and n° 481553/2012-6). Camilo Dias Seabra Pereira, Daniel Araki Ribeiro and Augusto Cesar also thank CNPq for the award of productivity fellowships. The authors would like to thank Daniel Temponi Lebre from Applied Mass Spectrometry Centre — Nuclear and Energy Research Institute (CEMSA, IPEN, São Paulo, Brazil) for technical support in LC–MS/MS analysis.

References (53)

  • S.L. Klosterhaus et al.

    Method validation and reconnaissance of pharmaceuticals, personal care products, and alkylphenols in surface water, sediments, and mussels in an urban estuary

    Environ. Int.

    (2013)
  • P.A. Lara-Martín et al.

    Occurrence, distribution and partitioning of nonionic surfactants and pharmaceuticals in the urbanized Long Island Sound Estuary (NY)

    Mar. Pollut. Bull.

    (2014)
  • A. Lolic et al.

    Assessment of non-steroidal anti-inflammatory and analgesic pharmaceuticals in seawaters of North of Portugal: occurrence and environmental risk

    Sci. Total Environ.

    (2015)
  • L.A. Maranho et al.

    Toxicological evaluation of sediment samples spiked with human pharmaceutical products: energy status and neuroendocrine effects in marine polychaetes Hediste diversicolor

    Ecotoxicol. Environ. Saf.

    (2015)
  • C.C. Martins et al.

    Spatial distribution of sedimentary linear alkylbenzenes and faecal steroids of Santos Bay and adjoining continental shelf, SW Atlantic, Brazil: origin and fate of sewage contamination in the shallow coastal environment

    Mar. Pollut. Bull.

    (2008)
  • C. Metcalfe et al.

    Illicit drugs in Canadian municipal wastewater and estimates of community drug use

    Environ. Pollut.

    (2010)
  • R. Moreno-González et al.

    Seasonal distribution of pharmaceuticals in marine water and sediment from a Mediterranean coastal lagoon (SE Spain)

    Environ. Res.

    (2015)
  • B. Petrie et al.

    A review on emerging contaminants in wastewaters and the environment: Current knowledge, understudied areas and recommendations for future monitoring

    Water Res.

    (2015)
  • E.J. Rosi-Marshall et al.

    A review of ecological effects and environmental fate of illicit drugs in aquatic ecosystems

    J. Hazard. Mater.

    (2015)
  • L.H. Santos et al.

    Ecotoxicological aspects related to the presence of pharmaceuticals in the aquatic environment

    J. Hazard. Mater.

    (2010)
  • S. Terzic et al.

    Illicit drugs in wastewater of the city of Zagreb (Croatia) — estimation of drug abuse in a transition country

    Environ. Pollut.

    (2010)
  • A. Togola et al.

    Multi-residue analysis of pharmaceutical compounds in aqueous samples

    J. Chromatogr. A

    (2008)
  • A.L.N. VanNuijs et al.

    Spatial and temporal variations in the occurrence of cocaine and benzoylecgonine in waste and surface water from Belgium and removal during wastewater treatment

    Water Res.

    (2009)
  • S. Weigel et al.

    Drugs and personal care products as ubiquitous pollutants: occurrence and distribution of clofibric acid, caffeine and DEET in the North Sea

    Sci. Total Environ.

    (2002)
  • S. Weigel et al.

    Determination of selected pharmaceuticals and caffeine in sewage and seawater from Tromsø/ Norway with emphasis on ibuprofen and its metabolites

    Chemosphere

    (2004)
  • J.E. Zenobio et al.

    Presence and effects of pharmaceutical and personal care products on the Baca National Wildlife Refuge, Colorado

    Chemosphere

    (2015)
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