Environmental risk caused by drug waste in the city of Rio de Janeiro, Brazil, during the SARS-Cov19 pandemic

Carla Patricia Figueiredo Antunes de Souza Débora Cynamon Kligerman Giselle Mendes Bezerra Jaime Lopes da Mota Oliveira About the authors

Abstract

The relationship between the distribution of medicines used in the Pandemic by SARS-COV-19 in the municipality of Rio de Janeiro and the estimated level of environmental risk caused by their residues was evaluated. The amount of medicines distributed by primary health care (PHC) units between 2019 and 2021 were collected. The risk quotient (RQ) corresponded to the ratio between the estimated predictive environmental concentration (PECest) obtained by the consumption and excretion of each drug and its non-effective predictive concentration (PNEC). Between 2019 and 2020, the PECest of azithromycin (AZI) and ivermectin (IVE) increased between 2019 and 2020, with a decrease in 2021 probably due to shortages. Dexchlorpheniramine (DEX) and fluoxetine (FLU) fell, returning to growth in 2021. While the PECest of diazepam (DIA) increased over these 3 years, ethinylestradiol (EE2) decreased possibly due to the prioritization of PHC in the treatment of COVID-19. The largest QR were from FLU, EE2 and AZI. The consumption pattern of these drugs did not reflect their environmental risk because the most consumed ones have low toxicity. It is worth noting that some data may be underestimated due to the incentive given during the pandemic to the consumption of certain groups of drugs.

Key words:
COVID-19; Environmental hazards; Pandemics; Pharmaceutical preparations; Toxicity

Introduction

Medication is extremely important when it comes to combating diseases and illnesses and provides a means for increasing the life expectancy of people. However, medication can also be the cause of health problems when used improperly or for purposes other than their therapeutic indication11 UEDA J. Impacto ambiental do descarte de fármacos e estudo da conscientização da população a respeito do problema. Rev Cienc Ambiente 2009; 5(1):1-6.. Inappropriate use of medication is the second largest cause of domestic poisoning in Brazil22 Sistema Nacional de Informações Tóxico-farmacológicas. Dados Nacionais. 2009. [acessado 2022 fev 15]. Disponível em: https://sinitox.icict.fiocruz.br/dados-nacionais
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, which is the seventh largest consumer of medication in the world33 The IQVIA Institute. Global Medicine Spending and Usage Trends: Outlook to 2025. 2021. [acessado 2022 mar 20]. Disponível em: https://www.iqvia.com/insights/the-iqvia-institute/reports/global-medicine-spending-and-usage-trends-outlook-to-2025#:~:text=Report%20Summary,projected%20to%20be%20%24157%20billion
https://www.iqvia.com/insights/the-iqvia...
. One of the reasons for these high consumption levels is the sale and marketing strategies used by manufacturers44 Barros JAC. A (des)informação sobre medicamentos: o duplo padrão de conduta das empresas farmacêuticas. Cad Saude Publica 2000; 16(2):421-427.. During the COVID-19 pandemic, the influence of the media, as well as government incentives, caused an increase in the consumption of various drug classes55 Silva RD, Rodrigues LHO, Souza ICS, Seixas KB, Lima AKBS, Maia RP. Dispensação de ansiolíticos e antidepressivos em farmácias privadas durante a pandemia de COVID-19. Temas Saude 2021; 21(6):314-333.. Poisoning by these substances may have increased during the pandemic owing to self-medication. However, there is little information on the possibility of residues from these drugs entering water systems and affecting the wild biota.

These residues reach the environment through incorrect disposal of surplus and/or expired medication and through their natural excretion after metabolization66 Zapparoli ID, Camara MRG, BECK C. Medidas mitigadoras para a indústria de fármacos Comarca de Londrina - PR, Brasil: impacto ambiental do despejo de resíduos em corpos hídricos. En: In 3º International Workshop Advanced in Cleaner Production. Cleaner Production Initiatives and Challenges for a Sustainable World. São Paulo; 2011.. As such, even when consumed in full, drug residue can enter the drainage and sanitary sewage systems of cities, contaminating water sources77 Escher M, Américo- Pinheiro J, Torres N, Ferreira L. A problemática ambiental da contaminação dos recursos hídricos por fármacos. Brazilian J Environ Sci 2019; 51:141-148.. Various authors have reported the presence of drug residues in water systems in almost all continents: Europe88 Maria Gavrilescu KDJASAFF. Emerging pollutants in the environment: present and future challenges in biomonitoring, ecological risks and bioremediation. New Biotechnol 2015; 32(1):147-156.

9 Bijlsma L, Serrano R, Ferrer C, Tormos I , Hernández F. Occurrence and behavior of illicit drugs andmetabolites in sewage water from the Spanish Mediterranean coast (Valencia region). Sci Total Environ 2014; 487:703-709.
-1010 Kummerer K. Pharmaceuticals in the Environment. The Annual Rev Environ Resour 2010; 35:57-75., North America1111 Kankaanpää A, Ariniemi K, Heinonen M, Kuoppasalmi K, Gunnar T. Use of illicit stimulant drugs in Finland: a wastewater study in ten major cities. Sci Total Environ 2014; 487:696-702., Asia 12,13, Oceania 14,15, and South America1616 Griffero L, Alcántara-Durán J, Alonso C, Rodríguez-Gallego L, Moreno-González D, García-Reyes JF, Molina-Díaz A, Pérez-Parada A. Basin-scale monitoring and risk assessment of emerging contaminants in South American Atlantic coastal lagoons. Sci Total Environ 2019; 697:134058..

These compounds are called emerging contaminants, and there are no regulations regarding their environmental threats1717 Gomes JP, Timo GO, Paula ML, Costa VL, Rocha Júnior PBS, Mello HH, Oliveira JLM. Occurrence of 17a-ethinylestradiol in Paranoá Lake watershed (Brasília, Brazil): sewage, freshwater and treated water. Rev Amb Agua 2021; 16(4):1-15.. The effects can be observed in very low concentrations (ng/L) and in various aquatic species1818 Montagnera C, Vidala C. Contaminantes emergentes em matrizes aquáticas do brasil: cenário atual e aspectos. Quim Nova 2017; 40(9):1094-1110.

19 Chimchirian RF, Suri RPS, Fu H. Free synthetic and natural estrogen hormones in influent and effluent of three municipal wastewater tretment plants. Water Environ Res 2007; 79(9):969-974.

20 Martín J, Camacho-Muñoz D, Santos JL, Aparaicio L, Alonso E. Occurrence of pharmaceutical compounds in wastewater and sludge from wastewaste treatment plants: removal and ecotoxicological impact os wastewater discharges and sludge disposal. J Hazard Mater 2021; 239-240:40-47.

21 Queiroz FB, Brandt EMF, Aquino SF, Chernicharo CAL, Afonso RJCF. Occurrence of pharmaceuticals and endocrine disruptors in raw sewage and their behavior in UASB reactors operated at different hydraulic retention times. Water Sci Technol 2012; 66(12):2562-2569.

22 Pessoa GP, Souza NC, Vidal CB, Alves JAC, Firmino PIM, Nascimento RF, Santos AB. Occurrence and removal of estrogens in Brazilian wastewater treatment plants. Sci Total Environ 2014; 490:288-295.
-2323 Froehner S, Piccioni W, Machado KS, Aisse MM. Removal capacity of caffeine, hormones, and bisphenol by aerobic and anaerobic sewage treatment. Water Air Soil Pollut 2011; 216:463-471.. Among these, antimicrobial resistance caused by antibiotic residue in the environment and the effects from estrogen observed in fish owing to the presence of hormones are the most cited in the literature2424 Melo JRR, Duarte EC, Moraes MV, Fleck K, Arrais PSD. Automedicação e uso indiscriminado de medicamentos durante a pandemia da COVID-19. Cad Saude Publica 2021; 37(4):e00053221..

Studies have used the risk quotient (RQ) in the assessment of ecological risk for emerging contaminants2525 Albuquerque AF, Ribeiro JS, Kummrow F, Nogueira AJ, Montagner CC, Umbuzeiro GA. Pesticides in Brazilian freshwaters: a critical review. Environ Sci Process Impacts 2016; 18(7):779-787.,2626 Sodré FF, Dutra PM, Santos VP. Pharmaceuticals and personal care products as emerging micropollutants in Brazilian surface waters: a preliminary snapshot on environmental contamination and risks. Ecletica Quimica 2018; 43: 22-34.. It can be calculated using the quotient between the concentration found in water systems (predicted environmental concentration, PEC) and maximum concentration at which no effect is observed on a given aquatic organism (predicted no-effect concentration, PNEC). PNEC values are constantly being updated/reassessed to enhance the effectiveness of risk assessment2727 Caldwell DJ, Mastrocco F, Anderson PD, Lange R, Sumpter JP. Predicted-no-effect concentrations for the steroid estrogens estrone, 17ß-estradiol, estriol, and 17a-ethinylestradiol. Environ Toxicol Chem 2012; 3(16):1396-1406.. Large RQ values show that the concentration of emerging contaminants in the environment exceed the ecological safety threshold (PNEC), thereby posing a threat to aquatic species2828 González S, López-Roldán R, Cortina JL. Presence and biological effects of emerging contaminants in Llobregat River basin: a review. Environ Pollut 2012; 161:83-92.. When the PEC value is lower than that of the PNEC, the risk can be considered as insignificant (Table 1).

Table 1
Risk exposure classification of aquatic biota with respect to pharmaceutical residue.

An indirect method of estimating the concentration values of a given drug in the water system (PECexc) is based on its consumption. This method requires data on the degree of metabolization and excretion of a given drug, as well as the possibility of it being removed/degraded by the sewage treatment systems2929 Gamarra JJS, Godoi AFL, Vasconcelos EC, Souza KMT, Oliveira CMR. Environmental Risk Assessment (ERA) of diclofenac and ibuprofen: a public health perspective. Chemosphere 2015; 120:462-469.. The city of Rio de Janeiro has an estimated population of over 6.5 million people3030 Instituto Brasileiro de Geografia e Estatística (IBGE). Rio de Janeiro [Internet]. 2021. Acessado 2022 mar 25]. Disponível em: https://cidades.ibge.gov.br/brasil/rj/rio-de-janeiro/panorama
https://cidades.ibge.gov.br/brasil/rj/ri...
, among whom 58% are served by primary health care (PHC) units3131 Santos PRd, Pereira , Graever , Guimarães M. e-SUS AB na cidade do Rio de Janeiro: projeto e implantação do sistema de informação em saúde. Cad Saude Colet 2021; 29(esp.):199-204.. Only 56% of the city’s sewage is collected and treated3232 Sistema Nacional de Informações sobre Saneamento (SNIS). Panorama de Saneamento no Brasil. Brasília: Secretaria Nacional de Saneamento. 2021. [acessado 2023 jan 26]. Disponível em: https://www.gov.br/mdr/pt-br/assuntos/saneamento/snis/produtos-do-snis/panorama-do-saneamento-basico-do-brasil
https://www.gov.br/mdr/pt-br/assuntos/sa...
, but most of the drug residue is not removed by conventional sewage treatment systems 18,33-35.

Our study assessed the estimated environmental risk from the residue of some drugs used during the COVID-19 pandemic, as a function of their distribution by PHC. For this purpose, we considered that all distributed drugs were properly used and that the pharmaceutical residue excreted through urine was placed in the sewage system without removal/degradation carried out by the sewage treatment systems.

Methodology

Study design

This exploratory study analyzed the medications distributed to the population of the city of Rio de Janeiro served by PHCs during the 2019-2021 period and the estimated risk of the residue from these drugs to the environment. This period is justified by the fact that a part of the drugs listed was used for managing the COVID-19 pandemic, declared in 2020.

Drug consumption

Data collection on medicines distributed to the population serviced by the public health system of the city of Rio de Janeiro between 2019 and 2021 using the SIGMA and SPPW/EXTRANET system, the use of which is restricted. For the purpose of this study, we assumed that all distributed drugs had been used properly. This collection was granted the consent of the agencies involved and the corresponding approvals from the relevant research ethics committees (ENSP 50881321.7.0000.5240 and SMSRJ 50881321.7.3001.5279). The drugs included in this study were azithromycin (antibiotic), ivermectin (antiparasitic), dexchlorpheniramine (antihistamine), diazepam (benzodiazepine), and fluoxetine (antidepressant), which have been widely used during the COVID-19 pandemic, as well as the 17α-Ethinylestradiol hormone, which is known as a drug with high potential risk and environmental hazard3636 Cunha DL, Paula LM, Silva SMC, Bila DM, Fonseca EM, Oliveira JLM. Ocorrência e remoção de estrogênios por processos de tratamento biológico de esgotos. Rev Ambiente Agua 2017; 12(2):249-262..

Estimation of drug excretion by the population

The excretion of each drug was determined of each drug using the pharmacokinetics of each product based on both the drug’s package insert and other sources3737 Cano A, Roura AC, Cortit LI. Farmacología de los anticonceptivos hormonales orales. In: Buil C, editores. Manual de anticoncepcíon hormonal oral. Zaragoza: Sociedad Española de Contracepción; 1997. p. 75-99.

38 Criado PR, Maruta CW, Criado RFJ, Machado Filho CD. Histamina, receptores de histamina e anti-histamínicos: novos conceitos. Ana Bras Dermatol 2010; 85(2):195-210.

39 González Canga A, Sahagún Prieto AM, Diez Liébana MJ, Fernández Martínez N, Sierra Vega M, García Vieitez JJ. The pharmacokinetics and interactions of ivermectin in humans - a mini-review. AAPS J 2008; 10(1):42-46.

40 West E, Rowland SJ. Aqueous Phototransformation of Diazepam and related human metabolites under simulated sunlight. Environ Sci Technol 2012; 46(9):4749-4756.

41 Andrés-Costa MJ, Proctor K, Sabatini MT, Gee AP, Lewis SE, Pico Y, Kasprzyk-Hordern B. Enantioselective transformation of fluoxetine in water and its ecotoxicological relevance. Sci Rep 2017; 7(1):15777.
-4242 Rodvold KA, Piscitelli SC. New oral macrolide and fluoroquinolone antibiotics: an overview of pharmacokinetics, interactions, and safety. Clin Infect Dis 1993; 17 (Suppl. 1):S192-S199.. Only their unchanged excretion in the urine was considered, given the lack of data on their fecal excretion. Based on these values, we calculated the amount of drug excreted every day (QFexc) using equation 1.

QFexc=(DosexdistributedQTDE)/365x%exc(1)

where Dose is the mass amount of the drug in each drug presentation; distributed QTDE is the amount of drug distributed to the serviced population per year; %exc is the percentage of drug that was eliminated exclusively in the urine after it was administered.

The volume of waste generated every day (Waste vol) by the population serviced by PHCs was calculated using equation 2.

WasteVol=Totalpopx0.58xWastepercapita(2)

where Total pop is the estimated total population of Rio de Janeiro3030 Instituto Brasileiro de Geografia e Estatística (IBGE). Rio de Janeiro [Internet]. 2021. Acessado 2022 mar 25]. Disponível em: https://cidades.ibge.gov.br/brasil/rj/rio-de-janeiro/panorama
https://cidades.ibge.gov.br/brasil/rj/ri...
; 0.58 corresponds to the population service by PHC3131 Santos PRd, Pereira , Graever , Guimarães M. e-SUS AB na cidade do Rio de Janeiro: projeto e implantação do sistema de informação em saúde. Cad Saude Colet 2021; 29(esp.):199-204.; Waste per capita is the amount of waste generated every day per person4343 Associação Brasileira de Normas Técnicas (ABNT). NBR 13969 - Tanques sépticos - Unidades de tratamento complementar e disposição final dos efluentes líquidos - Projeto, construção e operação. 1997..

The concentration of drug excreted, or its estimated predicted environmental concentration (PECest) in micrograms/liter (µg/L), by the population served by PHCs using equation 3.

PECest=QFexc/(Wastevol)x1,000(3)

Although 55% of the population of Rio de Janeiro has a collection and treatment system for generated waste, a decrease in the PECest by virtue of it passing through sewage treatment processes was not considered, given the limited available information on the removal/degradation potential of these compounds in these processes.

Risk quotient

We calculated the potential risk (RQ) based on the PECest and PNEC values of each drug, using Equation 4.

RQ=PECest/PNEC(4)

PNEC values for freshwater aquatic organisms are available in the NORMAL (2022) ecotoxicology database. The RQ classification was based on Environmentally Classified Pharmaceuticals (2014) (Table 1).

Results and discussion

Consumption of medication

Graph 1 shows the medication amount consumed by the population serviced by PHCs per year. Diazepam consumption slightly increased in 2020 and 2021 compared with 2019. Meanwhile, ethinylestradiol consumption decreased slightly. Azithromycin and ivermectin consumption increased in 2020 and decreased in 2021. Meanwhile, consumption of dexchlorpheniramine and fluoxetine decreased in 2020 and increased in 2021.

Graph 1
Comparison of medication amount per year.

Diazepam was already a widely used medication for relieving tension and other somatic or psychological complaints associated with anxiety disorders. Given these characteristics, many people used it during the COVID-19 pandemic; therefore, diazepam use increased between 2019 and 20214444 Alcantara A, Figel F, Campese M, Silva M. Prescrição de psicofármacos na atenção primária à saúde no contexto da pamdemia da COVID-19. Res Soci Develop 2022; 11(4):e19911420210.,4545 Centro de Estudos e Pesquisas em Emergências e Desastres em Saúde (Cepedes). Fundação Oswaldo Cruz. Psicofármacos na COVID-19 [Internet]. 2020. [acessado 2021 ago 3]. Disponível em: https://www.fiocruzbrasilia.fiocruz.br/wp-content/uploads/2020/06/cartilha_psicofarmacos.pdf
https://www.fiocruzbrasilia.fiocruz.br/w...
. Diazepam belongs to a class of drugs called benzodiazepines, which are indicated for the treatment of intense, disabling disorders or for extreme pain.

The drug levonorgestrel, which is associated with ethinylestradiol, is an oral contraceptive indicated for the prevention of pregnancy and control of menstrual irregularities. Its usage is tightly linked to public policies on birth control. A decrease in its consumption in 2020 and 2021 can be explained by the fact that health care units prioritized severe COVID-19 and severe-acute respiratory syndrome (SARS) cases4646 Rio de Janeiro. Resolução nº 4.330, de 17 de março de 2020. Dispõe sobre as orientações sobre a prevenção da transmissão e infecção pelo novo coronavirus (SAR-COV-2) e organização dos serviços de atenção primária à saúde do município do Rio de Janeiro. Diário Oficial do Rio de janeiro 2020; 17 mar.. Notably, there was no supply shortage during this period. Our study considered only the pharmacokinetics of 17α-ethinylestradiol, given that several studies have reported its harmful effects on wild aquatic biota 17,36,47,48, which would explain its low PNEC value (0.000035 μg/L). This drug was included in our study as a parameter for comparing its estimated environmental risk with respect to the other drugs4949 Bansal HK, Bala M, Gulshan. Reproductive drugs and environmental contamination: quantum, impact assessment and control strategies. Environ Sci Pollut Res 2018; 25(26):25822-25839..

Azithromycin was widely consumed during the COVID-19 pandemic owing to its properties. It has been recommended in the treatment of viral infections. Its anti-inflammatory effects could help decrease tissue damage caused by viruses, especially when administered at the beginning of the illness5050 Hinks TSC, Cureton L, Knight R, Wang A, Cane JL, Barber VS, Black J, Dutton SJ, Melhorn J, Jabeen M, Moss P, Garlapati R, Baron T, Johnson G, Cantle F, Clarke D, Elkhodair S, Underwood J, Lasserson D, Pavord ID, Morgan S, Richards D. Azithromycin versus standard care in patients with mild-tomoderate COVID-19 (ATOMIC2): an open-label, randomised. Lancet 2021; 9(10):1130-1140.. As such, this medication is part of the so-called COVID kit that was widely publicized by the Brazilian media, despite the fact that there is no scientific evidence regarding its effectiveness in the treatment of COVID-195151 Catherine E. Oldenburg SM, Benjamin A. Pinsky MP, Jessica Brogdon MT, Chen MC. Effect of oral azithromycin vs placebo on COVID-19 symptoms in outpatients with SARS-COV-2 Infection. JAMA 2021; 326(6):490-498..

Ivermectin is a drug used in the treatment of several kinds of parasite infestations, including intestinal strongyloidiasis, onchocerciasis, filariasis, scabies, and pediculosis3939 González Canga A, Sahagún Prieto AM, Diez Liébana MJ, Fernández Martínez N, Sierra Vega M, García Vieitez JJ. The pharmacokinetics and interactions of ivermectin in humans - a mini-review. AAPS J 2008; 10(1):42-46.. During the COVID-19 pandemic, ivermectin was widely recommended by some health professionals for the prevention and treatment of COVID-19. Despite the absence of scientific evidence of its effectiveness for this use, broad speculations resulted in great demand for this drug by the population, which may explain the 76% increase in its consumption from 2019 to 2020 via PHCs. The increased demand for this drug caused a shortage in the network the following year (2021). According to The Human Data Science Company™ (IQVIA), along with the Brazilian Federal Pharmacy Council (CFF)5252 Conselho Federal de Farmácia. Venda de remédios sem eficácia comprovada contra a Covid dispara [Internet]. 2021. [acessado 2022 mar 29]. Disponível em: https://www.cff.org.br/noticia.php?id=6197&titulo=Venda+de+rem%C3%A9dios+sem+efic%C3%A1cia+comprovada+contra+a+Covid+dispara
https://www.cff.org.br/noticia.php?id=61...
, between 2019 and 2020, the consumption of ivermectin showed an increase of over 500%, which resulted in a market shortage. One of the problems with its high consumption is poisoning - ivermectin can cause liver damage and even lead to death.

Dexchlorpheniramine is a first-generation antihistamine indicated for the treatment of allergies, urticaria, pruritus, allergic rhinitis, insect bites, allergic conjunctivitis, atopic dermatitis, and allergic eczemas. Therefore, it was included in some protocols for the treatment of COVID-195353 Silva J, Rego M, Santos L. Potenciais interações medicamentosas envolvendo fármacos reposicionados para COVID-19. Sci Elec Archi 2021; 14(11):1-24.. Another factor that can explain the increase in its consumption between 2020 and 2021 was produced by the influenza outbreak that affected Rio de Janeiro5454 Castro R. Agência Fiocruz de Notícias. Infogripe aponta aumento de 135% de casos de SRAG no Brasil [Internet]. 2022. [acessado 2022 set 9]. Disponível em: https://portal.fiocruz.br/noticia/infogripe-aponta-aumento-de-135-de-casos-de-srag-no-brasil
https://portal.fiocruz.br/noticia/infogr...
.

Fluoxetine is the active ingredient of numerous psychotropic drugs; it acts as a selective serotonin reuptake inhibitor. This medication is administered for the treatment of depression, obsessive-compulsive disorder, anxiety disorder, and bulimia nervosa. This became one of the most widely prescribed drugs worldwide5555 Zindler F, Tisler S, Loerracher AK, Zwiener C, Braunbeck T. Norfluoxetine is the only metabolite of fluoxetine in zebrafish (Danio rerio) embryos that accumulates at environmentally relevant exposure scenarios. Environ Sci Technol 2020; 54(7):4200-4209., including by public health systems. There was an increase in demand for this medication during the COVID-19 pandemic, which could explain its potential shortage in 2020. The use of psychotropic drugs is a concern for public health, since this medication is consumed by almost all age groups5656 Lobo L, Rieth C. Saúde mental e COVID-19: uma revisão integrativa da literatura. Saude Debate 2021; 45(130):885-901.,5757 Quemel G, Silva E, Conceição W, Gomes M, Rivera J, Quemel G. Revisão integrativa da literatura sobre o aumento no consumo de psicotrópicos em transtornos mentais como a depressão. BASR 2021; 5(3):1384-1403.. Health authorities should warn the population regarding the indiscriminate use of this drug class, making them aware of risks to health and quality of life, as well as of the adverse effects and impacts on the environment55 Silva RD, Rodrigues LHO, Souza ICS, Seixas KB, Lima AKBS, Maia RP. Dispensação de ansiolíticos e antidepressivos em farmácias privadas durante a pandemia de COVID-19. Temas Saude 2021; 21(6):314-333..

Excretion of medication and environmental risk

Considering the population served by PHCs (58%) in Rio de Janeiro, volume of generated wastewater per person (150 L/day), and pharmacokinetics of each drug, we calculated the concentration of each excreted drug (eqs. 1 and 2). For azithromycin, the main route of excretion is biliary excretion, but 6% of the drug is eliminated in the urine after its oral administration4242 Rodvold KA, Piscitelli SC. New oral macrolide and fluoroquinolone antibiotics: an overview of pharmacokinetics, interactions, and safety. Clin Infect Dis 1993; 17 (Suppl. 1):S192-S199.. Dexchlorpheniramine and its metabolites are mainly excreted in the urine, with 19% of the dose appearing within 24 hours and a total of 34% within 48 hours3838 Criado PR, Maruta CW, Criado RFJ, Machado Filho CD. Histamina, receptores de histamina e anti-histamínicos: novos conceitos. Ana Bras Dermatol 2010; 85(2):195-210.. Human metabolism of diazepam produces metabolites resulting from enzymatic biotransformation reactions that prolong the length of pharmaceutical activity. The main metabolites formed are nordiazepam, temazepam, and oxazepam; temazepam and oxazepam can also be used as anxiolytics in several countries5858 Wang C, Hou L, Li J, Xu Z, Gao T, Yang J. Occurrence of diazepam and its metabolites in wastewater and surface waters in Beijing. Environ Sci Pollut Res Int 2017; 24(18):15379-15389.. These substances are excreted by conjugation with glucuronic acid along with quantities ranging from 5% to 50% of diazepam, unchanged in the urine4040 West E, Rowland SJ. Aqueous Phototransformation of Diazepam and related human metabolites under simulated sunlight. Environ Sci Technol 2012; 46(9):4749-4756..

The main metabolite of fluoxetine is norfluoxetine; the two have the same potency and selectivity. Approximately 80% of it is eliminated in the urine and 15% is excreted in the feces4141 Andrés-Costa MJ, Proctor K, Sabatini MT, Gee AP, Lewis SE, Pico Y, Kasprzyk-Hordern B. Enantioselective transformation of fluoxetine in water and its ecotoxicological relevance. Sci Rep 2017; 7(1):15777.. Ivermectin is metabolized in human liver microsomes and mainly excreted in the feces, with only 1% of it exiting in the urine3939 González Canga A, Sahagún Prieto AM, Diez Liébana MJ, Fernández Martínez N, Sierra Vega M, García Vieitez JJ. The pharmacokinetics and interactions of ivermectin in humans - a mini-review. AAPS J 2008; 10(1):42-46.. Ethinylestradiol is primarily metabolized by aromatic hydroxylation, forming some metabolites and conjugates. Conjugated ethinylestradiol is excreted in the bile and subject to enterohepatic recirculation. About 40% of the drug is excreted in the urine, and 60%, through the feces3737 Cano A, Roura AC, Cortit LI. Farmacología de los anticonceptivos hormonales orales. In: Buil C, editores. Manual de anticoncepcíon hormonal oral. Zaragoza: Sociedad Española de Contracepción; 1997. p. 75-99.. Thus, we used the following excretion values: azithromycin, 6%; dexchlorpheniramine, 19%; diazepam, 50%; fluoxetine, 80%; ivermectin, 1%; and ethinylestradiol, 40%.

Table 2 shows the amount of each medication excreted daily in the urine (QFexc) and estimated concentration in the wastewater (PECest). For comparison, we carried out a literature review regarding the PEC values for these six drugs1717 Gomes JP, Timo GO, Paula ML, Costa VL, Rocha Júnior PBS, Mello HH, Oliveira JLM. Occurrence of 17a-ethinylestradiol in Paranoá Lake watershed (Brasília, Brazil): sewage, freshwater and treated water. Rev Amb Agua 2021; 16(4):1-15.,5959 Alcântara G. Estimativa do consumo e predição da concentração ambiental de diazepam via epidemiologia do esgoto. Brasília: Universidade de Brasília.

60 Danner MC, Robertson A, Behrends , Reiss J. Antibiotic pollution in surface fresh waters: Occurrence and effects. Sci Total Environ 2019; 664:793-804.

61 Brooks BW, Foran CM, Richards SM, Weston J, Turner PK, Stanley JK, Solomon KR, Slattery M, La Point TW. Aquatic ecotoxicology of fluoxetine. Toxicol Lett 2003; 142(3):169-183.
-6262 Fick J, Lindberg RH, Tysklind M, Larsson DG. Predicted critical environmental concentrations for 500 pharmaceuticals. Regul Toxicol Pharmacol 2010; 58(3):516-523..

Table 2
Amount excreted and concentration by medication from 2019 to 2021.

The mean PEC values found in the literature for azithromycin, dexchlorpheniramine, diazepam, fluoxetine, ivermectin, and ethinylestradiol were 0.563, 0.025, 2.4.10-5, 0.54, 0.2, and 0.07 µg/L, respectively. Among the PECest values obtained from the medication distribution/consumption data in Rio de Janeiro, only those for diazepam and fluoxetine exceeded the reference values. This result shows that mental health medications were the most consumed medication in Rio de Janeiro, probably owing to the social problems the city has faced over the years4444 Alcantara A, Figel F, Campese M, Silva M. Prescrição de psicofármacos na atenção primária à saúde no contexto da pamdemia da COVID-19. Res Soci Develop 2022; 11(4):e19911420210.,5757 Quemel G, Silva E, Conceição W, Gomes M, Rivera J, Quemel G. Revisão integrativa da literatura sobre o aumento no consumo de psicotrópicos em transtornos mentais como a depressão. BASR 2021; 5(3):1384-1403.,6363 Valécio M. Instituto de Ciência, Tecnologia e Qualidade (ICTQ). COVID-19 aumenta venda de ansiolíticos, medicamentos para insônia e vitaminas [Internet]. 2020. [acessado 2022 set 9]. Disponível em: https://ictq.com.br/varejo-farmaceutico/1552-covid -19-aumenta-venda-de-ansioliticos-medicamentos-para-insonia-e-vitaminas#:~:text=Covid%2D19%20aumenta%20venda%20de%20ansiol%C3%ADticos%2C%20medicamentos%20para%20ins%C3%B4nia%20e%20vitaminas,-Por%20Marcelo%
https://ictq.com.br/varejo-farmaceutico/...
that may have worsened during the pandemic. Although lower, the PEC for azithromycin in 2020 reached almost 50% of the PEC value found in the literature; this reflects its higher consumption as part of the treatment of the COVID-19 pandemic. Based on excretion (PECest) and PNEC data for each drug, we could calculate the RQ (Table 3).

Table 3
Comparison of risk quotient (RQ) estimated between 2019 and 2021.

Ivermectin, dexchlorpheniramine, and diazepam presented an insignificant estimated risk during the analyzed period. However, the assessed levels could have been underestimated. The reason for this is that our study was carried out using only distribution data from PHCs and, according to data from the CFF (2021), in the 2019-2020 period, there was a shortage of this drug owing to high demand from other networks (private and hospital). As for diazepam, although it had a very high PECest with respect to the values cited in the literature, its environmental risk was also negligible. Ivermectin could result in increased growth of animals receiving overdoses6464 Mancini L, Lacchetti I, Chiudioni F, Cristiano W, Di Domenico K, Marcheggiani S, Carere M, Bindi L, Borrello S. Need for a sustainable use of medicinal products: environmental impacts of ivermectin. Ann Ist Super Sanita 2020; 56(4):492-496., whereas diazepam could cause changes in the behavior of fish exposed to its residue5959 Alcântara G. Estimativa do consumo e predição da concentração ambiental de diazepam via epidemiologia do esgoto. Brasília: Universidade de Brasília..

Azithromycin presented low risk in 2019 and reached moderate risk in 2020. This result reflects its use as one of the medications recommended by the health system (“COVID kits”) for treatment during the COVID-19 pandemic. Despite decreased risk in 2021 (low risk), a potential shortage in the public network cannot be ruled out6565 Chaves LA, Osorio-de Castro C, Caetano M, Silva R, Luiza V. Nota técnica: Desabastecimento: uma questão de saúde pública global. Sobram problemas, faltam medicamentos [Internet]. 2020. [acessado 2021 set 9]. Disponível em: https://portal.fiocruz.br/documento/nota-tecnica-desabastecimento-uma-questao-de-saude-publica-global-sobram-problemas-faltam
https://portal.fiocruz.br/documento/nota...
. Meanwhile, this result can also be tied to the beginning of the vaccination campaign, especially for the most vulnerable age groups. A worrying fact about the risk associated with azithromycin is the potential for the development and proliferation of antibiotic-resistant bacteria6060 Danner MC, Robertson A, Behrends , Reiss J. Antibiotic pollution in surface fresh waters: Occurrence and effects. Sci Total Environ 2019; 664:793-804..

Fluoxetine showed a high environmental risk with similar values in 2019 and 2021. Even if the risk in 2020 was moderate, its value was close to the moderate-high limit, which might be related to shortages. Fluoxetine and its metabolites are toxic for the environment, scoring 6, on a scale from 0 to 9, in the PBT (persistent, bioaccumulative, and toxic) index5555 Zindler F, Tisler S, Loerracher AK, Zwiener C, Braunbeck T. Norfluoxetine is the only metabolite of fluoxetine in zebrafish (Danio rerio) embryos that accumulates at environmentally relevant exposure scenarios. Environ Sci Technol 2020; 54(7):4200-4209.,6666 Stockholm County Council. Environmentally Classified Pharmaceuticals. Stockholm: Stockholm County Council; 2014.. The presence of fluoxetine in the environment can interfere with the development and behavior of aquatic animals6767 Costa Junior IL, Pletsch AL, Torres YR. Ocorrência de fármacos antidepressivos no meio ambiente - revisão. Rev Virtual Quim 2014; 6(5):1408-1431..

Ethinylestradiol presented a high estimated risk only in 2019. In 2020 and 2021, the PHC units were dedicated to providing priority care to SARS patients4646 Rio de Janeiro. Resolução nº 4.330, de 17 de março de 2020. Dispõe sobre as orientações sobre a prevenção da transmissão e infecção pelo novo coronavirus (SAR-COV-2) e organização dos serviços de atenção primária à saúde do município do Rio de Janeiro. Diário Oficial do Rio de janeiro 2020; 17 mar., and the distribution of birth control medication, which includes ethinylestradiol, was reduced. This could be associated with the moderate environmental risk level observed in this period (Table 3). In addition to causing nuclear abnormalities in aquatic organisms, ethinylestradiol in the environment can interfere with the reproductive system and deviate the sex ratio in a species6868 Branco FOL, Cárdenas SMM, Serrão ICG, Cunha IRV, Amado LL, Kutter T. Contaminantes emergentes nas bacias hidrográficas brasileiras e seus potenciais efeitos a espécies ameaçadas de extinção. Rev Bras Meio Ambiente 2021; 9(2):140-174..

Even if drug distribution is directly related to increased exposure to the environment, the estimated environmental risk (RQ) will depend on the toxicity of the drug and its metabolites. Although some medications were consumed more, this was not reflected in the significance of their risk. Medications that have greater environmental toxicity increased or remained at the same estimated environmental risk. Given the importance of the subject, further research must be conducted on the environmental impact of drugs, especially those used for mental health, as they were consumed more during the period studied. Additionally, the residue from various drugs must be monitored in water sources to obtain PEC values within Brazilian local realities; this would allow for a better understanding of the relation between consumption and excretion/disposal of residues in the environment.

Conclusion

The environmental risk of azithromycin increased in 2020, which can be attributed to increased consumption linked with its use in the treatment of COVID-19. This trend regarding risk was not observed in the drug ivermectin, given that there was a shortage of it. The estimated environmental risk caused by fluoxetine was constant (high), with a slight decrease in 2020, probably owing to a shortage during the pandemic. ethinylestradiol was the only medication whose risk was significantly reduced in the 2020-2021 period, given the logistics of care provided by PHCs.

The primary research results that were used in the preparation of this article were inserted in the Scielo.Data repository: https://doi.org/10.48331/scielodata.QZOVID

Acknowledgement

This study was financially support by Fundação Carlos Chagas Filho de Amparo à Pesquisa do Estado do Rio de Janeiro (Faperj), project code number E-26/210.882/2021. The authors acknowledge yet Editage by English revision services.

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Publication Dates

  • Publication in this collection
    06 Mar 2023
  • Date of issue
    Mar 2023

History

  • Received
    07 Apr 2022
  • Accepted
    30 Sept 2022
  • Published
    02 Oct 2022
ABRASCO - Associação Brasileira de Saúde Coletiva Rio de Janeiro - RJ - Brazil
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