1. Introduction
Pharmaceuticals are a group of emergent organic compounds that have contributed to enhance our quality of life. The pharmaceutical industry is responsible for the development, production, and marketing of branded and generic pharmaceuticals. In 2014, total pharmaceutical revenues worldwide exceeded 1 trillion United States dollars (USD) for the first time. The market has been growing at an annual rate of 5.8% since 2017. In 2017, worldwide pharmaceutical market revenue was USD 1143 billion and will reach 1462 billion USD in 2021 [
1]. The largest fraction of these revenues corresponds to North America due to the leading role of the US pharmaceutical industry. However, during recent years, the Chinese pharmaceutical industry has shown the highest growth rates amongst countries worldwide [
1]. Several factors such as reduced taxes and lowered drug prices in the US, a gross domestic product growth greater than 6% in China and India, widespread population ageing and sedentary lifestyles leading to increase chronic disease, industrialized data services in research and development (R&D) enabling the use of clinical trial data in trial simulations, lowered regulatory barriers for new drugs in the US, and high urban pollution levels increasing the incidence of conditions such as asthma are driving healthcare market growth [
2].
Musculoskeletal drugs were the largest pharmaceutical market worldwide with 14% of the total in 2017. The second-, third- and fourth-largest markets were those of cardiovascular, oncological, and anti-infective drugs. The fifth-largest market was that of pharmaceuticals for treating metabolic disorders such as diabetes; diseases of the thyroid and pituitary glands will be the fastest-growing segment of the global pharma market by 2021. This segment will grow at 9% per year in the future, following recent growth of 11.6%. The DrugBank database 2019 (version 5.1.3, released on 2 April 2019) contained 13,336 drugs; 10,256 were small-molecule drugs and 1670 were biotech drugs, while 3732 were approved, 2593 were approved small-molecule, 130 were nutraceutical, 6304 were experimental, 205 were illicit and 256 were withdrawn drugs.
In addition to the pharmaceutical market, pharmaceutical consumption worldwide was also growing, partly driven by a growing need for drugs to treat ageing-related and chronic diseases and changes in clinical practice [
3]. Consumption of cholesterol-lowering drugs had nearly quadrupled, use of antidepressant drugs doubled and consumption of antihypertensive and antidiabetic drugs nearly doubled in Organization for Economic Cooperation and Development (OECD) countries between 2000 and 2015 [
3,
4]. Demand for local and imported pharmaceutical products increased as economies grew, and healthcare provision and insurance mechanisms expanded. Not only was demand increasing, but also the diversity of pharmaceutical needs as emerging markets increasingly address noncommunicable diseases (NCDs) already prevalent in stronger economies, including diabetes and hypertension, while communicable diseases that afflict many emerging markets such as acquired immunodeficiency syndrome, malaria and tuberculosis persist [
5]. The increase in the global population is also contributing to pharmaceutical consumption.
It is clear that in 2020 the COVID-19 pandemic has modified and will continue modifying the pharmaceutical market and in the coming years in terms of revenues and investment in new chemical and biological entities due to the efforts to generate a greater amount and more effective vaccines again the SARS-CoV-2 virus. Similarly, the consumption trends in the world will present important changes driven by the urgent need of vaccinating world population to decrease the number of infected people and deaths. In this work, COVID-19 pandemic effects on the drugs market and pharmaceutical consumption trends are not discussed because such data are still not totally available.
As the pharmaceutical market grows and consumption increases, the discharge of pharmaceuticals and their metabolites into the environment, including water, also increases due to their inappropriate management, treatment, and disposal. The occurrence and fate of pharmaceuticals in the environment and the water cycle at trace levels (in the range of nanograms per liter to micrograms per liter) has been widely discussed and reported in the literature during the last two decades; pharmaceuticals are now recognized worldwide as an environmental concern and human health risk [
6,
7,
8,
9,
10,
11,
12,
13,
14,
15,
16,
17,
18,
19,
20,
21,
22,
23,
24,
25,
26,
27,
28,
29,
30,
31,
32,
33,
34,
35]. Adverse effects such as endocrine disruption, changes in behavior, chronic toxicity and impacts to nutrient cycling have been caused by pharmaceuticals in aquatic and terrestrial organisms [
8,
13,
17,
19,
21,
36,
37,
38,
39,
40]. Synergistic effects of antibiotics and antimicrobials in aquatic ecosystems have also been reported [
9,
23].
Pharmaceuticals and their metabolites/oxidation products have been detected in wastewater, surface water, sediments, groundwater and drinking water and have numerous routes by which they enter into the water cycle. They can originate from several sources such as domestic and industrial raw wastewater, treated wastewater and sludge from wastewater treatment plants, septic tanks, latrines, hospitals and pharmaceutical manufacturing facilities, aquaculture, livestock farming and landfills [
22,
25,
27,
28,
29,
30,
34,
41,
42,
43,
44,
45,
46,
47,
48,
49,
50,
51,
52].
During the last two decades, a great number of studies have been completed with the aim of determining effective and viable methods to remove or degrade pharmaceuticals and their metabolites and oxidation products from wastewater, surface water, groundwater and drinking water. Several reviews can be found in the literature related to the removal of pharmaceuticals in municipal wastewater treatment plants using different treatment methods [
20,
53,
54,
55,
56,
57,
58,
59,
60,
61]. Due to the COVID-19 pandemic and the massive vaccination that is occurring and will occur in the coming months worldwide, the number of studies to detect the SARS-CoV-2 virus, the vaccine constituents and pharmaceuticals used to treat the disease will increase importantly. Additionally, different methods to degrade such substances will also be a common issue on research reports. In this work, such issues are not discussed because such studies are currently ongoing.
Advanced oxidation processes have also been applied for degrading pharmaceuticals. Amongst several approaches, one can mention ozonation [
62]; chlorination [
63]; chemical [
64]; reverse osmosis [
65]; activated carbon [
66]; sonolysis [
67]; electrocatalysis [
68]; photo-Fenton [
69]; photocatalysis [
70] and nonthermal plasma [
71]. However, only partial degradation of pharmaceuticals (between 14% and 88%), instead of total mineralization, has been reported in previous studies [
69,
72]. Additionally, in most cases, the reaction times were not sufficiently short [
73], the intermediates/oxidation products were not degraded [
74,
75] and a continuous injection of oxygen to generate H
2O
2 was required; thus, these can be considered expensive and ineffective methods.
Recently, technologies such as electrochemical oxidation have shown promising progress due to their versatility, energy efficiency, automation, environmental compatibility, and cost-effectiveness and are currently being used for pharmaceutical removal [
76]. However, when electrochemical oxidation is used to degrade pharmaceuticals, potential generation of intermediate/oxidation products has been reported [
63,
77,
78,
79,
80]. These by-products can have high levels of toxicity and/or can be even more difficult to degrade using typical methods than the initial compound [
76]. Fortunately, research worldwide has been addressing this challenge; for instance, it has been successfully oxidized pharmaceuticals and their transformation products using an electrochemical oxidation cell with stainless-steel electrodes [
81,
82], in which these results are promising for practical applications because short reaction times and low current densities are needed; such current densities can be potentially supplied by photovoltaic cells.
Despite the intensive research work done worldwide in different pharmaceutical research activities such as disposal and fate, environmental impacts and concerns, human health risks, removal, degradation and development of treatment technologies, there has never been an attempt to analyze the relationships among the pharmaceuticals market, the consumption trends, the fatal disease incidence rate and disease burden in the population with respect to the different pharmaceuticals research fronts. Therefore, this paper addresses and discusses the current pharmaceuticals market, the pharmaceuticals consumption trends, the diseases of incidence, and their relationship with the different pharmaceutical research fronts with the aim of finding the drivers and interests that motivate and promote the research on pharmaceuticals.
Additionally, a review of the legislation and regulations available worldwide related to the treatment and disposal of pharmaceuticals into the environment was conducted. The study reveals a growing global pharmaceutical market, a continuous increase of pharmaceutical consumption and an intensive research work on different pharmaceuticals fronts; however, such research is not totally aligned with the market trends and consumption patterns. Furthermore, the legislation and regulations available do not address the treatment and disposal of emergent contaminants, such as the pharmaceuticals; neither these legislations nor regulations promote incentives in favor of the pharmaceutical industry to generate new drugs that can provide adequate treatment for the patient, but also that the drugs have to be friendly to the environment under a philosophy of green chemistry.
As a result, this review study considers in
Section 2 the pharmaceutical market, in which the global market, the distribution and revenue are discussed, as well as the profits of the companies with their products of pharmaceutical consumption.
Section 3 addresses the causes of death and the burden of disease by relating the gross national income per capita versus the disability-adjusted life years lost due to diseases. In
Section 4, information is presented on the studies that have been carried out on the removal of different pharmaceutical groups in wastewater; the activity carried out for these studies is presented by continent and countries most active in research.
Section 5 shows the current five research fronts, these are society and public policies (legislation for the removal of drugs in wastewater), wastewater treatment, health risk, detection of drugs in wastewater, and development of environmentally friendly drugs. In
Section 6, trends in drug removal studies in wastewater based on methods and technologies are presented. Finally, in
Section 7 of conclusions, this review study makes a recapitulation of the topics addressed in order to analyze the coincidences and disagreements of the efforts made by society to achieve sustainability in the treatment of drugs in wastewater. As mentioned above, the information presented and the analysis carried out in this study does not include the high impacts in the short, medium and long term of the COVID-19 pandemic on the pharmaceutical market, consumption trends, disease incidence and research activities in water and wastewater.
3. Causes of Death and Burden of Disease
According to the 2017 world census, 57 million people died [
86]. Thus, the census shows that the causes of death have a correlation with income levels and that they change from country to country.
Figure 17 shows the number of deaths by cause throughout the world for 2017 [
85]. From the information presented in this figure, it is possible to distinguish that cardiovascular disease, anticancer, respiratory system and psychiatry-neurological pharmaceutical drugs are more related to the most typical causes of death. As a result, the world requires production of more of these medications related to the diseases presented in
Figure 17.
According to the census presented by H. Ritchie and M. Roser [
86], the Global Burden of Disease assessment assigns each death to one specific cause; here, the risk health outcomes and the disease burden are closely related to the variation in risk factors. For example, it can be linked to four broad risk categories: behavioral, environmental, occupational, and metabolic risks.
Figure 18 shows the number of deaths by risk factors throughout the world during 2017 [
86].
Figure 18 shows that the leading causes of risk are high blood pressure, smoking, high blood sugar, air pollution and obesity. These factors are related to the pharmaceutical drugs addressing cardiovascular diseases, the respiratory system, and metabolic disorders. As a result, this ranking of risk factors associated with deaths does not correspond with the research efforts of the studies published by country. For example, there is information of the publication by country in the
Section 4.2. “Research Trends by Country” in this review article, in which one can note that the number of publications related to the removal of anti-infectives and anti-inflammatories pharmaceutical drugs is predominant against that of the other pharmaceutical groups. Thus,
Figure 18 shows that, from the perspective of the number of deaths by risk factor, academia and industry have different agendas or priorities according to the number of scientific reports found in Scopus related to the removal of pharmaceuticals from wastewater. Additionally, there are not sufficient statistics regarding the number of deaths by risk factor throughout the world. Moreover, in the world census report by M. Roser and H. Ritchie [
86], data are presented by correlating economic factors with diseases. As a result, the data were classified into three groups of diseases as described in
Table 1.
From
Table 1,
Figure 19 shows the total disease burden throughout the world in 2017 as measured using the disability-adjusted life years (DALYs) value in millions. In this context, one DALY equals one lost year of healthy life. In this figure, the diseases in blue are NCDs; the diseases in red are communicable, maternal, neonatal, and nutritional diseases; injuries are shown in grey.
Figure 19 almost follows the ranking position of diseases described in
Figure 17 (number of deaths by cause). Therefore, the predominant group according to the census is the NCDs; specifically, cardiovascular, cancer and musculoskeletal disorders are the leading groups of the diseases that require more medication throughout the world. Inherently, the Scopus search on musculoskeletal diseases and the removal from wastewater of the pharmaceuticals used to attend such disease did not show results. From the same order of logic, one of the pharmaceutical groups less studied is the anticancer drugs in water treatment; however, according to
Figure 19, cancer is one of the most relevant groups of diseases in which more people require medication as well as for cardiovascular system-related diseases.
Figure 20 shows the DALYs lost due to two major groups: communicable and NCDs. It can be observed that communicable diseases are correlated with average income levels.
In
Figure 20, it is very revealing to observe the trend in the correlation of the DALYs lost against gross national income for both groups of diseases (noncommunicable and communicable) as reported by the world census [
87].
The main observation shown in
Figure 20 is that the countries with a robust economy suffer less impact from diseases. In addition, the group of NCDs is less inhibited by the economic factor.
Figure 21 shows that countries with an extremely low health expenditure have the highest DALY rates. Thus, it is clearly perceived that spending on public policies related to citizens’ welfare results in the wellness of the nation; there is a payoff. Furthermore, the data shown in
Figure 21 demonstrate that, for instance, countries such as South Korea, Chile, China, Colombia, Peru, Thailand, the Czech Republic, Poland, and Cuba, to name but a few, are investing less than USD 2000 per capita; however, given this, they have the lowest DALY rates. Consequently, they are demonstrably more efficient in their resource management to obtain the same results of those countries that are spending four times or more of this amount such as Switzerland, the US and Norway for their health system.
Figure 21 shows the number of DALYs per 100,000 individuals vs. the health expenditure per capita in USD.
5. Current Pharmaceutical Research Fronts
In addition to describing the pharmaceutical market, the consumption of drugs worldwide, the causes of death and burden of disease, we mentioned that it is important to describe the research efforts done by the world in the removal of the pharmaceutical groups in water or wastewater. Therefore, in this subject it is relevant to separate the different topics in the research activity of the removal of drugs groups; as a result, the methodology used is shown in
Table 5, in which there are five different research fronts to be involved; this engagement research corresponds to the environmental problem of removal of these emerging pharmaceutical pollutants. In this way, for instance, if one wants to find scientific articles in Scopus related with the research from the society and public policies the research chain used was (Public policies) or (legislation) + pharmaceuticals + (water) or (wastewater) or (disposal), as the second column in
Table 5 remarks. In the similar way, in
Table 5 it is shown the keywords used in the research to find the five research fronts.
From the methodology described in
Table 5, it is shown in
Figure 23 the research fronts. The results obtained from the Scopus in regards of the research front it is possible to observe that most of the research activity correspond to the pharmaceutical detection, followed by environmental treatment. The R&D of environmentally friendly drugs, the drugs health risk on water and society and public policies (legislation for drug removal in water) are the fronts with less attention. The previous result is expected, because when a drug is created the laboratories first are focus on the fact that the new drug can be effective for the cure of a specific disease to be treated in a patient. Therefore, degradability in an environmentally friendly manner is not a priority. As a result, the efficacy of the drug in the patient dominates the world agenda, leaving in a second term the priority for their health risk due to exposure of the drug in water or to enact laws that prohibit its presence in wastewater. In other words, the free market economic system provides rules so that the mass production of drugs and their sale in the market is favorable without having any restriction on their environmental impact. Likewise, part of the enormous problem in the growth of drug consumption lies in the fact that many countries in the world citizens can buy drugs for their consumption without the need to go to a doctor for their prescription. Equally, in some countries with greater regulation for restricting patient prescriptions, a black market is observed that allows people to access to drugs. Specifically, it is relevant to also take a look of the waste public policy treaties or agreements of water waste regulations as it is shown in
Table 6 below.
Table 6 describes various waste regulations and their pharmaceutical approaches. Here one can observe that the laws/regulations are generally focused in wastes generated through production processes instead of the wastes that are produced through drug consumption. As a result, by not incorporating into public policy treaties, protocols and conventions the need to decrease the presence of drugs in water as a society, there is therefore no work agenda for researchers, the economic sector and the government to begin to remove the most consumed medications. Likewise, the lack of this demand for the removal of medicines in water means that the international organizations and the government do not pressure the companies in the pharmaceutical industry to generate environmentally friendly medicines.
Regarding the health risk of drugs specifically in drinking water, studies in the U.K., Australia and the U.S. indicate that appreciable adverse effects are highly unlikely. This due to the concentrations of drugs in drinking water being generally more than 1000 times below the Minimum Therapeutic Dose (MTD), which represents the lowest clinically active dose [
102]. However, this is not a reason to rejoice since as mentioned in different market studies, per capita consumption of drugs has been increasing globally and not enough attention is paid to the long-term effects of drug residues on both the population and the environment. In fact, it is estimated that the active ingredients are secreted unchanged through urine and feces after consumption of 30% to 90% of the time, directly entering the environment through wastewater [
89]. During water treatment, in most cases, contaminants can be partially removed nonetheless the remaining traces persist in the water effluents [
103]. As a result, there is indeed a biological accumulation of these emergent pollutants in the ecosystem.
Although the drugs turn out to be beneficial, this does not exempt them from the potential damage they represent to the flora and fauna through the alteration of ecosystems and the possible long-term adverse effect on human health. Therefore, even more attention must be paid to the production of environmentally friendly drugs and to achieve this it is essential to know the 12 principles of green chemistry and apply them in each developmental process described below by Jordan et al. [
104].
- (a)
Prevention. Before to generate a treating process in waste, it is much better to prevent the generation of it.
- (b)
Atom economy. To maximize the incorporation of the regents used on a final product it is convenient to use methods for synthetic the process to avoid not wanted intermediates or produce final products with unnecessary steps.
- (c)
Chemical syntheses with less dangerous precursors and products. Where it is possible, it is convenient to use less toxic and reactive methods that affect the environment or people.
- (d)
Chemical-safe design. For proper use of chemicals, they must be designed with the aim of being less toxic to the environment and people.
- (e)
Safe auxiliaries and solvents. Solvents used as auxiliaries, or drying agents among others, should as far as possible be used in a reduced form.
- (f)
Search for design in energy efficiency. The use of energy required for chemical processes should be kept to a minimum. The above is possible referring to concepts of thermodynamics where the variables of temperature, pressure, volumes, among others, play important roles for the energy required in the process.
- (g)
Use of renewable inputs. As far as possible, raw materials can be used for the purposes of renewable sources.
- (h)
Derivatives reduction. The use of protective groups such as structural modifications to reduce the production of waste and energy consumption should be avoided.
- (i)
Catalysis. As far as possible, the use of catalysts can reduce waste and the appropriate energy requirements such as selectivity among others.
- (j)
Design for degradation. Synthetic molecules must be designed for adequate decomposition in the environment once used. The foregoing anticipates accumulation as a chronic effect.
- (k)
Real time analysis in preventing contamination. In real time, the supervision of the chemical process must be monitored. The above prevents the production of potential hazardous materials due to a control.
- (l)
Intrinsically safer chemistry in preventing accidents. The reagents, and the stages of the whole process must be safer to reduce accidents and/or reduce the exposure of chemical substances in people and the environment.
After considering the 12 principles, it is evident that from 2001 to 2020 the general revenue in pharmaceutical industries has tripled due to excessive consumption of drugs in people. We observe such examples in the years 2000 to 2015 with the quadruple consumption of drugs associated with cholesterol by people, or double the consumption of drugs to treat depression, hypertension, or diabetes, among others. This upward consumption trend is present in all OECD countries in the world, which is why there is an urgent need to incorporate mechanisms to regulate the production of drugs under a green chemistry guideline in laws and treaties worldwide. Likewise, it is important not to omit that the current consumption of medicines with synthetic processes that are not friendly to the environment can cause side effects in people, causing a chronic affectation that triggers in other diseases or even can cause and increment in deaths or quality of life. As a result, it is necessary to evaluate the green drug production strategy and its impact on the environment [
104]. This can be determined with the help of the following factors:
The selected synthetic route and its effect on the environment.
Consider studies on life cycle assessment and the environmental impact of the drug during the development process. It is essential to select compounds that have the least possible adverse effect on the environment.
Jointly assess the possible persistence of the drug in the environment and its toxicity and biodegradability.
While there is no full certainty about the adverse effect of drug residues in the environment, it is proposed in these analyzed exercises to push the social commitment to dedicate an effort devoted to a precautionary approach in which the objective is embrace and increase the acceptance of green chemistry as an essential parameter in the production of future drugs.
6. Methods and Technologies for the Removal of Pharmaceuticals
Figure 24,
Figure 25,
Figure 26,
Figure 27,
Figure 28,
Figure 29 and
Figure 30 show the percentage distributions of the research efforts in producing a scientific study according to different wastewater treatments for each pharmaceutical group. Therefore, the information presented in this section corresponds to the collected data of the Scopus database. Consequently, the information method consisted of finding a research chain by using the following keywords in the Boolean operators: wastewater OR water; remotion OR removal and finally, any of the terms of the pharmaceutical groups described in
Table 2. As a result,
Table 7 it is shown the keywords associated with the removal methods. Moreover, in the Scopus research, we used as filters results only for scientific articles for the period from 1998 to 202 in English.
In
Figure 24, the most explored methods to remove anti-infective drugs are the biotreatment processes or flocculation with 29% and activated carbon with 30%. This tendency can be expected due to this method is the most economical to treat general pollutants in wastewater but certainly it is not the most effective. Likewise, the activated carbon has been commonly used in pesticides and other volatile organic pollutants, as well as to eliminating the chlorine added in the first stage treatment, through a reducing chemical reaction. However, this method not always is effective to the removal of drugs in wastewater. the oxidation process has been more effective in removing drugs due to be a method that involves the formation of free hydroxyl radicals at very large overpotentials, which is why the radicals present by drugs are oxidized. In fact, to be more effective the process is common to see the coupling of the oxidation process with ozone processes, ultraviolet radiation, etc. However, it is a method that involves a lot of energy and high costs compared to the other methods.
In
Figure 25, the methods more commonly used to remove anti-inflammatory drugs are the biotreatment processes or flocculation with 23%, activated carbon and oxidation processes each with 24% and photo methods with 24%. Here the costliest methods such as oxidation process and photo methods have been shown to be effective with respect to others. However, if other methods are present in scientific studies can be notable due to are less expensive to remove the drug pollutants. In addition, activated carbon has been shown to be widely used for being a well know treatment process for organic compounds.
In
Figure 26, the most explored methods to remove anticancer drugs is activated carbon with 28%, followed by oxidation processes with 21%, and photo methods with 21%. Similar to
Figure 25, the costliest methods of oxidation process and photo methods are become useful for removal medication related with cancer.
In
Figure 27, the methods more commonly used to remove cardiovascular system drugs are the oxidation processes with 19%, biotreatment processes or flocculation with 23%, activated carbon with 20% and photo methods with 23%. Likewise,
Figure 27 shows roughly a similar distribution in most of the methods, for which the investigation to remove drugs related to the cardiovascular system is presented as a subject not very widely explored to outline a main methodology as the most effective.
In
Figure 28, the methods more commonly used to remove psychiatric-neurological drugs are the biotreatment processes or flocculation with 25%, oxidation processes with 19%, activated carbon with 21%, and photo methods with 22%. Similar to the effect found in
Figure 27,
Figure 28 also reveals an approximate distribution of the various drug removal methods. Therefore, it is possible that the research to eliminate drugs related to the nervous system has not been widely studied; Thus, a predominant methodology has not been presented as the most effective.
In
Figure 29, the methods more commonly used to remove metabolic disorder drugs are the biotreatment processes or flocculation with 28%, membrane processes with 12%, oxidation processes 15%, activated carbon each with 23% and photo methods with 18%. Thus, the percentage distribution of different methodologies is well distributed, which it can be an indicative that the removal of this pharmaceutical group has been explored though all methods almost in the same frequency.
In
Figure 30, the methods more commonly used to remove hematological drugs are nonthermal plasma with 29%, membrane processes with 21%, and activated carbon with 19%. For the association of metal ions such as iron in blood as part of the subject to deal with hematological drugs it is possible to see a dominant treatment method such as it is in this case the non-thermal plasma process in
Figure 30.
In
Figure 31, the methods more commonly used to remove respiratory system drugs are activated carbon with 35% and biotreatment processes or flocculation with 29%. Once more time, the activated carbon has been shown to be widely used to remove drugs related to metabolic disorder for being a well know treatment process for organic compounds. However, an economical method such as it is the biotreatment process or flocculation has been shown to be effective and popular.
In the case of the removal of the pharmaceutical group of alimentary tract and metabolism, there are just three studies in which the removal method used was activated carbon, as it is shown in
Figure 32.
7. Conclusions
In this work, an attempt was done to analyze the pharmaceutical market, drugs consumption trends and the pharmaceutical research interests worldwide. Notably, this work was a big challenge, first because classification and conventions for naming various pharmaceutical groups are not the same throughout communities; for business people and economists, it is not the same as that for the communities of health professionals or scientists who address chemistry or the environment.
Intensive research work has been conducted worldwide in different pharmaceutical research fronts such as pharmaceutical detection in water and wastewater, disposal, fate, environmental impacts and concerns and environmental treatment, human health risks, and degradation and development of treatment technologies for green chemistry in the production of drugs; however, such research is not totally aligned with the market trends and consumption patterns. There are other drivers and interests that encourage and promote the pharmaceutical removal research in wastewater and water. Thus, this paper is an important contribution to those that are interested not only on the pharmaceutical market, drugs consumption, or disease burden rate; consequently, it is also critical to associate the above-mentioned subjects to the different pharmaceutical research fronts for the drug removal in water and wastewater currently under attention and concern of the scientific community.
It was evidenced in this work that public policy treaties, protocols and agreements have not incorporated a demand or need to decrease the presence of medicines in water, therefore, there is no work agenda for researchers, the economic sector and the government to begin to eliminate most of the most consumed medications. Likewise, the lack of this demand for the elimination of medicines in water means that international organizations and the government do not pressure at least legally to companies in the pharmaceutical industry to generate environmentally friendly medicines. In addition, the ecosystem will soon accumulate a saturation threshold of the concentration of the active components of the drugs due to it is estimated that the active ingredients are secreted unchanged through urine and feces after consumption in 30% to 90% of the cases, directly entering the environment through wastewater. During water treatment, in most cases, contaminants can be partially removed nonetheless the remaining traces persist in the water effluents. Thus, the work agenda must consider conducting research on the health risk link to the drug exposure present in water.
In terms of the pharmaceutical market, the study shown that the most active continents are North America and Europe. This relation is also the same in terms of the research efforts to study the removal of pharmaceuticals in wastewater. However, the study of the treatment of drugs in water has recently become very active in Asian countries such as China that is now leading as a country in conducting such studies. Over the last two decades, the production of scientific articles addressing the study of drug removal in water of the pharmaceutical group of anti-infective drugs has been increasing. Specifically, it has been observed that the most studied pharmaceutical groups for the removal in wastewater and water are anti-infectives, and anti-inflammatories; in contrast, the alimentary tract and metabolism is the less studied pharmaceutical group. In the case of the alimentary tract and metabolism pharmaceutical group, there is a possibility that the research studies are not using ‘alimentary tract’ and/or ‘metabolism’ as a keyword to classify these studies, or this pharmaceutical group can be highly omitted since medication related to the alimentary tract and metabolism is highly present in businesspeople and economist studies, which show intense activity in the production, sales and consumption of world reports.
On the other hand, according to the world census, the priority for removal of drugs should be focused on the study of the removal of cardiovascular system-related drugs because they address the sector with the highest number of deaths. In addition, cardiovascular diseases are the main risk factor for health worldwide. Research fronts are increasingly more focused on the detection of drugs as an emerging pollutant in water, followed by environmental treatments. The more studied water treatment methods, according to this research are biotreatment processes or flocculation, followed by activated carbon, oxidation processes and photo methods.
As a general overview, this work presents that the indicators in the pharmaceutical industry are revenues from drug sales and this has caused an exorbitant consumption by people. As a result, there is a rise in the consumption and sales where there are no effective restrictions to avoid self-prescription, or medical doctors themselves are not having a concern that their patients should consume fewer drugs to treat the same diseases. Therefore, the economic system has governed the priority in profits and not the concern about developing policies to have an economy respecting the sustainability of producing green chemistry drugs, or reducing the risk of exposure of drugs in water by studying more the toxicity of them or by adding more regulations on wastewater discharges by the governments.
Finally, this review study, presented as its main objective, the worrying need to make known to the different sectors of society, government, economic sector and health systems the unpostponable need to act to generate more effective public policies to mitigate the contamination of water by drugs, where currently there is no coincidence, or in any case only partial, between the drugs most studied in their removal by researchers and the most consumed and/or sold drugs. It is important to note that the information presented together with its analysis in this study does not include the high impacts in the short, medium and long term of the COVID-19 pandemic on the pharmaceutical market, consumption trends, disease incidence and research activities in water and wastewater. Nonetheless, when the information would be available it will be interesting to conduct a research to evaluate and address such effects.