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Review

Assessing Sustainable Approaches in the Face of Industrial Chemical Pollution of Freshwater

Department of Chemistry, College of Science and Humanities in Al-Kharj, Prince Sattam bin Abdulaziz University, Al-Kharj 11942, Saudi Arabia
Sustainability 2026, 18(7), 3476; https://doi.org/10.3390/su18073476
Submission received: 11 February 2026 / Revised: 26 March 2026 / Accepted: 30 March 2026 / Published: 2 April 2026

Abstract

Freshwater ecosystems—including rivers, lakes, wetlands, and aquifers—are critical to global biodiversity, ecosystem functioning, and human well-being. However, these systems are increasingly threatened by industrial chemical pollution, stemming from the discharge of heavy metals, toxic organic compounds, pharmaceuticals, and untreated industrial waste. This pollution compromises water quality, disrupts ecological balance, and poses serious health, social, and economic risks, particularly to vulnerable communities. In response, a range of sustainable approaches have emerged to mitigate industrial pollution and restore freshwater integrity. This review critically assesses current strategies, including regulatory frameworks, green technologies, waste management innovations, and circular economy practices. Unlike previous reviews that often focus on specific pollutants or treatment technologies, this study integrates pollutant sources, environmental impacts, and sustainable mitigation approaches within a unified analytical framework. The analysis highlights that integrated strategies combining technological treatment, effective regulatory governance, and resource recovery practices are essential for reducing industrial pollution and improving long-term water sustainability. By synthesizing recent research and case studies, this review offers actionable insights into how sustainable approaches can be strengthened to address the growing challenge of industrial chemical pollution in freshwater systems.

1. Introduction

Freshwater systems, such as rivers, lakes, wetlands, and groundwater, are essential to ecological balance and the preservation of a rich and varied biodiversity [1]. These ecosystems are home to thousands of species—fish, amphibians, plants, and microorganisms—many of which are endemic, unable to survive elsewhere. Freshwater environments play a crucial role in nutrient cycling, soil quality, and maintaining habitat for wildlife. They also provide vital water resources for agriculture, industry, and human consumption. In addition to their ecological importance, freshwater systems are essential to human societies. They provide access to drinking water, agricultural irrigation, hydroelectric power, transportation routes, and spaces for recreation and cultural activities. Beyond their direct use by humans, they provide a variety of ecosystem services, such as climate regulation, flood control, and decomposition of organic matter, thereby supporting the health of the entire biosphere.
Despite their importance, freshwater systems are under growing threat by pollution [2,3], particularly by industrial chemical discharges [4,5]. According to the United Nations Environment Program, more than 80% of global wastewater is discharged into the environment without adequate treatment, particularly in developing countries where industrial treatment infrastructure is limited. The World Health Organization estimates that over 2 billion people rely on drinking water sources contaminated with pollutants, posing significant health risks. To better illustrate the magnitude of industrial chemical pollution and its implications for freshwater systems, key global indicators reported in recent international assessments are summarized in Table 1. These global indicators demonstrate the scale and urgency of industrial freshwater pollution and highlight the need for comprehensive assessments of sustainable mitigation strategies. Industrial pollutants, such as heavy metals [6], toxic chemicals [7], and pharmaceuticals [8] are often discharged directly into water bodies or end up in these environments through agricultural runoff, sewage, and inadequate waste management [9]. Environmental disasters associated with poorly managed waste sites, such as fires at illegal landfills, can further aggravate contamination, as rainfall can mobilize toxic residues and produce leachates that infiltrate soils and contaminate groundwater and nearby surface waters [10,11,12]. Heavy metals are a major concern due to their non-biodegradability, which leads to their accumulation in water, sediments and living organisms [13]. This phenomenon causes bioaccumulation and bio magnification processes within food chains, which can lead to serious health risks for aquatic ecosystems and humans, such as neurological damage, reproductive disorders and even cancers [14]. In addition, toxic chemicals such as pesticides [15], industrial solvents and persistent organic pollutants [16] alter the chemical composition of freshwater systems, causing lasting ecological damage. They disrupt the reproductive, developmental and immune systems of aquatic organisms, leading to a decline in biodiversity and impaired ecosystem functioning. Pharmaceuticals, including antibiotics, hormones and painkillers, are also a growing concern. Often introduced into freshwater through human waste and agricultural runoff, these substances persist in aquatic environments and can interfere with the endocrine systems of species, affecting their behavior, growth and reproductive success [17]. Polycyclic aromatic hydrocarbons are also a significant hazard in freshwater environments. These compounds are mainly produced during the incomplete combustion of fossil fuels and are released from industrial activities such as petroleum refining, coal processing, and vehicle emissions. They enter aquatic systems through atmospheric deposition, industrial effluents, and urban runoff [18]. As industrialization and urbanization continue, chemical pollution of freshwater ecosystems is likely to worsen, making it essential to develop strategies to mitigate this pollution and protect these vital ecosystems [19]. The cumulative effects of chemical contaminants threaten not only biodiversity, but also the ability of freshwater systems to provide services essential to human well-being and ecosystem health [20].
Industrial pollution of freshwater ecosystems has become an urgent global concern, with profound impacts on environmental health, social well-being and economic stability. By dumping harmful chemicals, heavy metals and untreated waste into rivers, lakes and streams, industries are seriously compromising the integrity of these essential resources. The uncontrolled release of pollutants leads to degradation of water quality, loss of biodiversity and disruption of aquatic ecosystems [21]. In the long term, this pollution reduces oxygen levels, kills aquatic life and destroys vital habitats for many species, threatening the ecological balance and risking the collapse of ecosystems on which millions of people depend for food, water and livelihoods [22]. On the social level, communities near polluted water sources face increased health risks, such as waterborne diseases, cancers and develop mental disorders due to exposure to contaminated water [23]. Vulnerable populations, often located near industrial areas, withstand the worst of these impacts, exacerbating social inequalities [24]. The scarcity of drinking water resources also fuels conflicts, causes migration and reduces the quality of life of those who depend on freshwater for their daily survival [25].
Table 1. Global indicators illustrate the scale and impact of industrial chemical pollution on freshwater systems.
Table 1. Global indicators illustrate the scale and impact of industrial chemical pollution on freshwater systems.
IndicatorEstimated ValueImplicationsReferences
Untreated wastewater discharged globally~80%Major contributor to freshwater pollution[26]
Population exposed to contaminated drinking water>2 billion peoplePublic health risks including waterborne diseases and toxic exposure[27]
Annual industrial wastewater generation~380 billion m3Increasing pressure on freshwater ecosystems[28]
Major pollutant categories in industrial effluentsHeavy metals, dyes, pesticides, pharmaceuticals, microplasticsPersistent contamination and ecological damage[29,30,31,32,33]
Industrial pollution of freshwater systems imposes a heavy economic burden. Costs related to water treatment, health care for exposed populations, diminished fisheries, and reduced agricultural productivity strain public and private resources. In regions already facing water scarcity, pollution compounds the crisis by threatening sectors such as agriculture, tourism, and energy production that depend on clean and accessible water [34]. Adopting sustainable approaches to reduce industrial pollution of freshwater is not only an environmental imperative, but also an economic and social necessity [35,36]. These initiatives must include strict regulations on industrial waste disposal, investments in green technologies, and the application of circular economy principles to limit waste generation and promote water reuse [37,38]. Without rapid action, the long-term effects of freshwater pollution risk becoming irreversible, with serious consequences for future generations. Sustainable practices are essential to preserve aquatic ecosystems, protect public health, and ensure economic resilience in the face of environmental challenges. Figure 1 provides a conceptual overview of the major industrial chemical pollutants affecting freshwater systems, their associated impacts on freshwater systems, and the sustainable approaches proposed to mitigate these pressures. Several review studies have addressed specific aspects of industrial chemical pollution in freshwater systems, including pollutant occurrence, treatment technologies, or risk assessment. However, most existing reviews focus on contaminant or mitigation approaches rather than providing an integrated perspective. Table 2 summarizes selected review articles and highlights the distinctive contribution of the present study. As shown in Table 2, previous reviews have generally focused on individual pollutant categories or specific treatment technologies. In contrast, the present review provides an integrated assessment that links major industrial pollutants, their ecological implications for freshwater systems, and the range of sustainable strategies—technological, regulatory, and circular economy-based—developed to mitigate their impacts.
This review aims to assess the sustainable approaches currently implemented to address industrial pollution in freshwater ecosystems, with particular attention to pollutants. It aims to analyze the effectiveness of these strategies in reducing pollution, restoring ecological balance, and ensuring long-term water quality. By identifying effective practices and areas requiring improvement, the study will also explore future directions to strengthen sustainable solutions. This includes a review of innovations in policies, technologies, and industrial practices that can help further mitigate industrial pollution, thereby ensuring the protection and preservation of freshwater resources for future generations. The review therefore addresses two central questions: (i) which industrial pollutants represent the most significant threats to freshwater systems, and (ii) which sustainable mitigation strategies are most effective for addressing these pollution challenges under different technological and economic conditions.

2. Overview of Industrial Pollution

Recent research on industrial chemicals polluting freshwater has identified a wide range of contaminants, including heavy metals, microplastics, persistent organic pollutants, pharmaceuticals and personal care products, pesticides, and textile dyes. These substances, originating from diverse sources, pose significant threats to aquatic ecosystems on a global scale. Understanding the characteristics and sources of industrial pollutants is essential for identifying which mitigation strategies are most suitable for different contamination scenarios. Below is a comprehensive overview of these pollutants, their sources, mechanisms of contamination, and the extent of their impact worldwide.

2.1. Heavy Metals

Heavy metals, such as lead, mercury, cadmium and arsenic, are among the most dangerous freshwater pollutants because of their high toxicity and persistence in the environment [46]. Mining and smelting of metals release these substances directly into water bodies, while industrial processes, such as electronics manufacturing and wastewater discharge, also contribute to the contamination of freshwater systems [37]. Improper disposal of batteries, electronic devices and other products containing metals can result in the release of contaminants into waterways. Direct discharges from industrial plants and smelters cause localized contamination of rivers and lakes, while atmospheric deposition from industrial emissions can transport these metals over long distances, contaminating distant freshwater systems. Environmental disasters can further intensify heavy-metal contamination. For example, fires at poorly managed landfills or industrial waste sites may mobilize metals such as Pb, Zn, and Cu from burned waste, while subsequent rainfall can generate contaminated leachates that infiltrate groundwater and nearby rivers [11]. Studies have shown that mining-impacted waters frequently contain elevated concentrations of cadmium and lead, while chromium and nickel are commonly associated with electroplating and tanning industries, demonstrating how heavy-metal pollution patterns vary according to industrial activities and environmental conditions [44,47]. Once introduced into aquatic environments, heavy metals can adsorb onto suspended particles and sediments, resulting in long-term contamination and potential remobilization under changing environmental conditions [48]. In response to these environmental risks, numerous sustainable technologies have been developed to remove heavy metal ions from industrial effluents as summarized in Table 3. Adsorption using low-cost and bio-based materials, such as biochar, agricultural residues, and natural clays, has attracted significant attention due to its simplicity and environmental compatibility. Biochar-based adsorbents have demonstrated high removal efficiencies for metals such as Pb2+ and Cd2+ in industrial wastewater treatment systems [49]. Membrane-based technologies, including nanofiltration and reverse osmosis, have also shown high effectiveness in separating dissolved heavy metal ions from wastewater [50]. In addition, polymer-enhanced ultrafiltration and hybrid membrane–adsorption systems have been proposed as environmentally friendly alternatives that improve heavy-metal removal efficiency while reducing chemical consumption [51]. These sustainable remediation approaches highlight the growing shift toward greener technologies capable of reducing heavy metal contamination while minimizing secondary environmental impacts. Key findings from the literature on heavy metal contamination and removal strategies are summarized in Table 3.

2.2. Microplastics

Microplastics, particles less than 5 mm, represent a growing influence on freshwater pollution [56]. They mainly come from larger plastic fragmentation as well as various industrial sources [16]. The degradation of plastic waste from landfills, poor disposal practices, and used products is one of the main sources of microplastics [57]. Industries, such as plastic production plants, can also release microplastics directly into waterways. Other sources include personal care products (which contain microbeads), textile washing (releasing fibers), and tire wear [58,59,60]. Microplastics enter freshwater systems through surface runoff, storm drains and wastewater discharges and are also transported by wind and rain from land sources. In freshwater ecosystems, these particles frequently accumulate in sediment or stay suspended in the water column leading to their ingestion by aquatic organisms [61]. Today, microplastics are present in almost every freshwater system, from rivers in densely populated areas to isolated mountain lakes. Their presence in drinking water, bottled water and aquatic wildlife raises concerns about human exposure and ecosystem health [62]. Recent research has focused on improving the removal of microplastics during wastewater treatment processes. Conventional treatment plants can remove a significant portion of microplastics through sedimentation and filtration; however, smaller particles often escape into receiving water bodies [63]. Advanced treatment technologies such as membrane bioreactors, rapid sand filtration, and dissolved air flotation have demonstrated enhanced removal efficiencies for microplastic particles as summarized in Table 4. Membrane filtration systems have been reported to remove the majority of microplastic particles in certain treatment configurations [64]. In addition, emerging green technologies based on bio-derived materials and biodegradable filtration media are being investigated as sustainable alternatives for microplastic capture [65]. Despite these advances, the widespread presence of microplastics in rivers, lakes, and even drinking water sources highlights the need for improved management strategies and more efficient removal technologies. Their persistence and potential ecological impacts make them a critical component of the broader challenge of industrial chemical pollution in freshwater systems. Key findings from the literature on microplastics contamination and removal strategies are summarized in Table 4.

2.3. Persistent Organic Pollutants

Persistent organic pollutants (POPs), including compounds such as polychlorinated biphenyls (PCBs), dioxins, polybrominated diphenyl ethers (PBDEs), and organochlorine pesticides such as DDT, are industrial chemicals that resist degradation in the environment and accumulate throughout the food chain [16,68]. These compounds are primarily released from industrial processes, waste incineration, electrical equipment containing PCB oils, and the historical use of agricultural pesticides, and have been widely associated with toxic, carcinogenic, and endocrine-disrupting effects in humans and wildlife [69,70]. POPs enter freshwater systems through direct industrial discharges, runoff from contaminated soils, and atmospheric deposition [71,72]. Once in water, their resistance to degradation makes them persistent in the long term. Found in freshwater systems around the world, even in regions far from industrial sources, POPs can travel long distances through the atmosphere [73]. They accumulate in sediments and aquatic organisms, causing serious effects on wildlife and risks to human health. To address these challenges, several sustainable remediation technologies have been developed to remove POPs from contaminated water as summarized in Table 5. Advanced oxidation processes (AOPs), including photocatalysis and ozone-based treatments, have demonstrated strong potential for degrading persistent organic contaminants by generating highly reactive radicals capable of breaking down stable chemical structures. Adsorption-based methods using activated carbon, biochar, and other bio-derived materials have also shown promising removal efficiencies for POPs due to their high surface area and strong sorption capacity [74]. In addition, emerging technologies such as constructed wetlands and bioremediation systems exploit natural biological processes to transform or immobilize persistent contaminants [75]. These approaches are increasingly recognized as environmentally sustainable solutions that can reduce POP concentrations in industrial effluents while minimizing chemical consumption and secondary pollution. Key findings from the literature on persistent organic pollutants contamination and removal strategies are summarized in Table 5.

2.4. Pharmaceuticals and Personal Care Products

Pharmaceuticals and personal care products (PPCPs), such as antibiotics, hormones and pain relievers, are gradually known as pollutants in freshwater ecosystems [79,80]. These substances enter aquatic environments primarily through wastewater treatment plants, many of which are not yet optimized for their complete elimination [81,82]. The inadequate disposal of unused drugs and runoff from agricultural land enriched with animal manure also contribute to their presence in surface waters [83,84]. PPCPs are often discharged into rivers and lakes via wastewater effluents, and in some cases pharmaceuticals can seep into groundwater from landfills and septic tanks [85]. Recent studies have explored several sustainable treatment strategies for removing PPCPs from wastewater as summarized in Table 6. Advanced oxidation processes, including ozonation and photocatalysis, have shown high efficiency in degrading pharmaceutical residues by generating reactive oxygen species that break down complex organic molecules [86]. Membrane filtration technologies, such as nanofiltration and reverse osmosis, have also been widely applied to remove pharmaceutical compounds from wastewater streams [87]. In addition, biologically based treatment methods, including membrane bioreactors and biofilm reactors, have demonstrated promising results for degrading certain pharmaceutical compounds through microbial activity [88]. These approaches highlight the importance of integrating advanced treatment technologies with conventional wastewater treatment systems to improve the removal of PPCPs and reduce their environmental impact. Key findings from the literature on pharmaceuticals and personal care products contamination and removal strategies are summarized in Table 6.

2.5. Pesticides

Pesticides, such as herbicides, insecticides and fungicides, are widely used in agriculture and various industrial applications. Their intensive use contributes significantly to the contamination of freshwater ecosystems [15]. They originate from various sources. Agricultural runoff serves as the main source of pesticide pollution, particularly from fields treated with herbicides and insecticides [93]. In addition, industrial activities, including the production of pesticides and improper waste disposal, can also discharge substantial quantities of these chemicals into adjacent water bodies [94]. Pesticides are broadly detected in freshwater around the world, with concentrations regularly exceeding regulatory limits. In addition, these pesticides can accumulate in sediments, resulting in durable ecological impacts, including bioaccumulation in aquatic organisms [95]. To mitigate pesticide contamination, several sustainable treatment technologies have been investigated as summarized in Table 7. Adsorption processes using activated carbon, biochar, and agricultural waste-derived materials have demonstrated strong potential for removing pesticide residues from contaminated water [96,97]. Photocatalytic degradation and other advanced oxidation processes have also been widely studied for their ability to break down pesticide molecules into less harmful compounds [98]. Additionally, nature-based solutions such as constructed wetlands and phytoremediation systems can reduce pesticide concentrations through plant uptake, microbial degradation, and sedimentation processes [99]. These environmentally friendly approaches provide promising alternatives for managing pesticide pollution in freshwater systems while minimizing the use of chemical reagents. Key findings from the literature on pesticides contamination and removal strategies are summarized in Table 7.

2.6. Textile Dyes and Auxiliaries

The textile industry relies heavily on dyes to impart color and functionality to fabrics, particularly during dyeing and finishing operations [104,105]. A wide range of synthetic dyes—such as reactive, direct, disperse, and vat dyes—are commonly used due to their colorfastness, versatility, and cost-effectiveness. These dyes are applied in aqueous media along with various auxiliaries, including salts, surfactants, and fixing agents, to promote dye uptake and uniform coloration [106,107]. However, dye fixation efficiencies vary depending on fiber type and process conditions, resulting in the presence of unfixed dyes in process waters. As a result, textile production generates dye-containing wastewater streams with diverse chemical compositions, reflecting the complexity and variability of textile dyeing operations [29]. In recent years, a variety of sustainable treatment technologies have been developed to address dye contamination in industrial effluents as summarized in Table 8. Biological treatment processes using specialized microorganisms have demonstrated the ability to degrade certain dye molecules through enzymatic reactions [108]. Adsorption methods employing activated carbon, biochar, and other natural materials have also shown high efficiency in removing dye molecules from wastewater [109]. In addition, advanced treatment technologies such as membrane filtration, electrochemical oxidation, and photocatalysis have been investigated for their ability to remove color and reduce organic load in textile effluents [110]. These sustainable treatment approaches are increasingly integrated into industrial wastewater management strategies to reduce environmental impacts and support cleaner textile production. Key findings from the literature on textile dyes and auxiliaries’ contamination and removal strategies are summarized in Table 8.

2.7. Polycyclic Aromatic Hydrocarbons (PAHs)

Polycyclic aromatic hydrocarbons (PAHs) are organic compounds composed of multiple fused aromatic rings that are primarily generated during incomplete combustion of fossil fuels, petroleum processing, industrial activities, and urban runoff [114]. Major anthropogenic sources include petroleum refining, coal combustion, vehicle emissions, and industrial discharges, which can introduce significant quantities of PAHs into rivers, lakes, and groundwater systems [115]. Due to their hydrophobic nature and chemical stability, PAHs tend to accumulate in sediments and aquatic organisms, resulting in long-term environmental persistence and potential bioaccumulation in food webs. Numerous studies have reported that several PAHs exhibit carcinogenic, mutagenic, and teratogenic properties, posing significant risks to both aquatic ecosystems and human health [45,116]. Consequently, PAHs have been widely recognized as priority pollutants and are frequently monitored in environmental assessment programs worldwide. Recent studies have increasingly examined sustainable remediation options for PAH-contaminated waters as summarized in Table 9. Biochar-based adsorption has been highlighted as a cost-effective and environmentally compatible strategy for removing PAHs from water, owing to the high surface area and sorption capacity of biochar materials [117]. Likewise, nature-based systems, including bioretention and constructed wetland-type systems, have shown strong potential for PAH removal through combined adsorption, sediment retention, plant-assisted uptake, and microbial degradation processes [118]. These findings indicate that sustainable PAH management should combine source control with green remediation technologies adapted to freshwater protection goals. Key findings from the literature on Polycyclic aromatic hydrocarbons contamination and removal strategies are summarized in Table 9.
To provide a structured overview of the diversity of industrial chemical pollutants and the range of sustainable mitigation strategies currently applied, Table 10 synthesizes key pollutant categories, sources, and management approaches reported in the literature.

3. Global Impact on Freshwater Systems

Industrial pollution is a major contributor to loss of biodiversity in freshwater systems. In some areas, species diversity has dramatically decreased due to exposure to toxic chemicals, even leading to the collapse of aquatic food webs. Pollution of freshwater systems by industry is a growing and alarming threat to ecosystems and human health. The diversity of pollutants calls for comprehensive solutions, including strengthened environmental regulations, advanced treatment technologies and improved waste management practices on a global scale. Meeting this challenge is essential to protect biodiversity and ensure access to safe drinking water. Assessing the impacts of industrial pollutants on biodiversity, ecosystem services, water quality, and human health helps determine the severity of contamination and supports the prioritization of appropriate mitigation strategies.
Industrial pollution represents one of the main factors of biodiversity loss in freshwater ecosystems [136]. Many contaminants, including heavy metals, pesticides, pharmaceuticals, and persistent organic pollutants, can alter the physicochemical conditions of water and disrupt the ecological processes that support aquatic communities [137]. Several studies have shown that exposure to toxic metals such as cadmium, mercury, and lead causes physiological stress, reproductive impairment, and increased mortality in fish and invertebrates [138,139,140]. Research has shown that metal contamination of freshwater environments can significantly reduce species richness and alter community composition, favoring pollution-tolerant organisms at the expense of sensitive taxa [141]. In addition to their direct toxicity, pollutants can indirectly affect biodiversity by altering trophic interactions and reducing primary productivity. Industrial discharges rich in nutrients can trigger eutrophication, leading to decreased oxygen levels and the collapse of fish and macroinvertebrate populations [142,143]. Comparative studies conducted on polluted and unpolluted rivers have consistently shown lower biodiversity indices and simplified trophic structures in contaminated ecosystems, thus highlighting the severe ecological consequences of industrial pollution.
Freshwater ecosystems provide essential ecosystem services that contribute to environmental stability and human well-being. These services include natural water purification, nutrient cycling, flood regulation, and the provision of habitats for aquatic organisms [145]. However, industrial chemical pollution can significantly alter these ecological functions. When toxic substances accumulate in sediments and the water column, the natural self-purification capacity of freshwater systems is compromised [146]. For example, heavy metals and organic pollutants can inhibit microbial communities responsible for nutrient cycling and the decomposition of organic matter [147]. Studies conducted in industrialized watersheds have shown that contamination reduces the ability of wetlands and riverbeds to filter pollutants and regulate nutrient flows [148]. Moreover, excessive nutrient inputs from industrial discharges can promote the proliferation of harmful algae that further degrade ecosystem functioning [149]. Such disturbances reduce the resilience of freshwater ecosystems and decrease their ability to provide vital ecosystem services in the long term.
Industrial activities are a major source of chemical contamination that significantly degrades the quality of freshwater [150]. Effluents from the mining, chemical, textile, and pharmaceutical industries introduce various pollutants, notably heavy metals, organic compounds, dyes, and microplastics, into aquatic environments [151,152]. These substances can alter fundamental parameters of water quality such as dissolved oxygen, pH, turbidity, and nutrient concentrations. Numerous studies have reported high concentrations of metals and organic pollutants in rivers impacted by industry, often exceeding regulatory thresholds for water potability and ecological safety [153]. For example, heavy metals from industrial processes tend to accumulate in sediments, where they can persist for decades and constitute sources of secondary pollution [154]. Similarly, industrial discharges rich in nitrogen, phosphorus, and organic compounds can promote eutrophication, leading to a decrease in oxygen and the formation of hypoxic dead zones [155,156]. Consequently, industrial pollution not only undermines ecological integrity but also reduces the quality of freshwater resources for drinking water supply and agriculture.
Contamination of freshwater systems by industrial chemicals also presents serious risks to human health. Communities that depend on rivers, lakes, or groundwater for drinking water, irrigation, and fishing are particularly vulnerable to this contamination [157]. Toxic metals such as arsenic, mercury, and lead are known to accumulate in aquatic organisms and can enter the human food chain through fish consumption. Prolonged exposure to these contaminants has been associated with neurological disorders, kidney damage, and various forms of cancer [151]. In addition to heavy metals, the presence of endocrine disruptors, pharmaceutical products, and persistent organic pollutants in freshwater systems is causing increasing public health concerns [158]. These substances can interfere with hormonal regulation and reproductive health, even at low concentrations [159,160]. Epidemiological studies conducted in industrialized regions have reported an increase in the incidence of chronic diseases among populations exposed to contaminated water sources [161]. Consequently, protecting freshwater resources from industrial pollution is essential not only for environmental preservation but also for safeguarding public health.

4. Relevance of Sustainability to Mitigating Industrial Pollution

Sustainable freshwater management is based on the judicious and efficient use of freshwater resources to meet the needs of the present without compromising those of future generations. It aims to preserve aquatic ecosystems, ensure their sustainability, and balance environmental, economic and social imperatives. This includes maintaining the quality and quantity of water resources, protecting aquatic environments, ensuring equitable access, and integrating conservation practices [162,163]. Addressing industrial chemical pollution requires sustainability-based approaches that integrate environmental protection, resource efficiency, and responsible industrial practices. Industrial pollution, through the discharge of toxic chemicals, heavy metals, and untreated wastewater, is a major source of freshwater contamination [164,165]. Sustainable water management seeks to limit the quantity and toxicity of industrial effluents through strict regulations [166], treatment technologies [167], and recycling practices [168], thereby helping to preserve water resources. By encouraging industries to adopt greener processes, such as reducing water consumption [169], reducing hazardous substances [170], and using closed-loop systems [171], wastewater discharges can be significantly reduced. These practices contribute to sustainability goals by minimizing industrial impact on freshwater resources [172]. Sustainability focuses on preserving freshwater ecosystems (rivers, lakes, wetlands) that are home to essential biodiversity and provide ecological services such as water filtration and flood prevention [173]. Industrial pollution threatens these ecosystems, leading to biodiversity loss and compromising natural purification systems. Sustainable practices aim to preserve these environments and their vital functions [174]. Climate change and increasing industrial activity are increasing pressures on the availability and quality of freshwater resources [175]. Sustainable water management promotes resilience by protecting resources from environmental risks such as pollution, droughts and increased demand [176]. By limiting industrial pollution, this approach strengthens the capacity of freshwater systems to cope with these challenges. The sustainable policies include regulations on pollutant discharges, incentives for water-efficient technologies and sanctions against industries that overuse or pollute water resources [177]. Economic instruments, such as pollution taxes, fines and water pricing, encourage industries to adopt environmentally friendly practices and reduce their ecological footprint [178].
Several countries have implemented sustainability-oriented policies and industrial practices to mitigate pollution from industrial activities. For example, the European Union Water Framework Directive has encouraged industries to adopt cleaner production technologies and stricter wastewater management practices to reduce pollutant discharges into freshwater systems [166]. In China, the development of eco-industrial parks has promoted industrial symbiosis and resource sharing between industries, significantly reducing waste generation and water consumption [179]. Similarly, Singapore’s water management strategy, including the reuse of treated wastewater through the NEWater program, has demonstrated how circular water management can enhance water security while reducing industrial discharges [180]. In India, stricter regulations and the promotion of Zero-Liquid-Discharge (ZLD) systems in the textile sector have helped limit wastewater pollution and improve industrial water reuse [181].
In conclusion, sustainable freshwater management is crucial to limiting the negative impacts of industrial pollution. By adopting cleaner production processes, protecting ecosystems and implementing long-term management strategies, it ensures that water resources remain available for future generations and the environment.

5. Sustainable Approaches to Prevent and to Reduce Pollution

To address these pollution challenges, a range of sustainable mitigation strategies have been developed. Evaluating their effectiveness and applicability under different environmental and economic conditions is essential for identifying the most appropriate solutions.

5.1. Cleaner Production Technologies

Cleaner production technologies aim to minimize environmental impacts by preventing pollution at the source, rather than treating it after the fact [182]. They rely on strategies such as eco-design, green chemistry and process optimization, which prioritize the reduction in waste, emissions and hazardous materials throughout the product life cycle [183]. These approaches allow industries to gain efficiency, conserve resources and reduce their environmental impact. Eco-design represents a key component of cleaner production by incorporating environmental considerations into product development and manufacturing processes. It aims to reduce the ecological footprint of products by taking into account each stage of their life cycle, from the extraction of raw materials to their end of life [184]. For example, life cycle-based eco-design approaches implemented in manufacturing industries have demonstrated reductions in material use by up to 30% while simultaneously lowering greenhouse gas emissions and waste generation. Compared with conventional product design approaches, eco-design integrates environmental performance indicators during the design stage, allowing industries to minimize environmental impacts before products enter large-scale production. Green chemistry is another important pillar of cleaner production, focusing on the development of safer chemical processes and products, generating less waste and limiting the use of hazardous substances [185]. In the pharmaceutical industry, green chemistry reduces the ecological footprint of drug production, aligning with sustainability goals by reducing the carbon footprint and the use of toxic substances [186,187]. Pfizer developed a green synthesis process for the manufacture of sertraline (Zoloft), applying the principles of green chemistry [188]. This process reduces solvent consumption by approximately 90% and significantly decreases the generation of hazardous waste. Similar green chemistry strategies have been adopted in several industrial sectors. For example, Merck developed a biocatalytic process to produce the antidiabetic drug sitagliptin, replacing a rhodium-catalyzed reaction with an enzymatic synthesis that significantly reduced hazardous waste generation [189]. Several chemical companies have introduced catalytic processes and solvent-reduction strategies to decrease volatile organic compound emissions and improve the sustainability of chemical production systems [190]. In addition, continuous-flow synthesis technologies are increasingly applied in pharmaceutical manufacturing to improve reaction efficiency while reducing solvent use and energy demand [191]. Process optimization also plays a critical role in reducing industrial pollution. It seeks to improve production efficiency, thereby reducing raw material and energy consumption while minimizing emissions and waste [192]. A novel painting process has been developed to optimize energy-intensive automotive paint shops as in Ford Motor Company (Dearborn, MI, USA). This technique involves applying three consecutive coats of paint without drying time between applications, resulting in a reduction in energy consumption and a decrease in volatile organic compound VOC emissions [193]. This process has significantly reduced energy consumption and emissions by nearly 20%, while increasing the efficiency of the production line. Such technological innovations demonstrate how operational improvements can contribute to both economic and environmental benefits. In water-intensive industries such as textile manufacturing, cleaner production strategies increasingly focus on water conservation and wastewater minimization. Zero-Liquid-Discharge (ZLD) systems have emerged as a promising solution for preventing wastewater discharge from industrial facilities [194]. These systems recycle all the water used in the dyeing process by removing contaminants through filtration and evaporation techniques. The water is reused, and the recovered chemicals are recycled or disposed of safely [195]. Studies report that ZLD systems can achieve water recovery rates exceeding 90%, significantly reducing freshwater consumption and preventing the release of contaminated effluents into natural water bodies by combining membrane concentration processes with thermal evaporation and crystallization stages [184]. However, the technology is associated with high capital and operational costs, largely due to the energy-intensive evaporation processes and specialized corrosion-resistant equipment required for handling highly concentrated brine. Consequently, ZLD is generally implemented in regions facing water scarcity or strict environmental regulations, where the economic benefits of water recovery and regulatory compliance outweigh the operational costs. Recent research therefore focuses on improving energy efficiency through hybrid membrane–thermal systems and optimized pretreatment strategies, enabling ZLD to be integrated into circular water management frameworks for industrial wastewater reuse [185]. By limiting the ecological footprint of production processes and products, cleaner production technologies support global sustainable development goals, which aim to mitigate climate change, conserve natural resources and protect ecosystems. They encourage a circular economy, where materials are continually reused and waste production is minimized.
Although cleaner production strategies provide clear environmental benefits, their effectiveness varies depending on industrial context, pollutant characteristics, and economic constraints. Compared with end-of-pipe treatment technologies such as advanced oxidation processes or membrane filtration, cleaner production approaches focus on preventing pollutant generation at the source, which often leads to lower long-term operational costs and reduced environmental burdens [192]. However, their implementation typically requires process redesign, technological upgrades, and organizational changes, which may involve significant initial investments. For example, eco-design and process optimization strategies are particularly effective for industries with high material consumption and complex supply chains, where reductions in raw material use and waste generation can generate substantial economic savings [196]. In contrast, technologies such as Zero-Liquid-Discharge systems are more suitable for water-intensive industries and regions facing water scarcity or strict regulatory constraints, where water recovery provides a clear economic incentive [181].
From a techno-economic perspective, the choice of treatment technology depends on pollutant concentration, treatment scale, and regulatory requirements. Highly contaminated industrial effluents often require advanced processes such as membrane filtration or advanced oxidation, whereas preventive approaches like green chemistry and process optimization reduce pollution at the source. Although nanotechnology-based treatments show very high removal efficiencies, their large-scale application remains limited by high material costs and potential environmental risks. As a result, nanotechnology is currently most viable where strict discharge standards or high-value water recovery justify higher investment costs. Effective mitigation strategies therefore often combine source-reduction measures with advanced treatment technologies to balance environmental performance and economic feasibility.
In conclusion, cleaner production technologies, through strategies like eco-design, green chemistry, and process optimization, are essential tools for industries looking to minimize their environmental impact. Compared with traditional end-of-pipe treatment technologies, these technologies not only help reduce pollution at the source but also align with economic and sustainability goals, leading to more efficient and responsible production practices across sectors. Nevertheless, the effectiveness of cleaner production strategies depends strongly on industry-specific conditions, economic feasibility, and regulatory incentives that encourage industries to adopt sustainable production practices. A synthesis of cleaner production approaches, including eco-design, green chemistry, process optimization, and zero-liquid-discharge systems, is presented in Table 11.

5.2. Regulatory Frameworks and Policies

5.2.1. Existing Regulations

Environmental regulations governing industrial pollutants exist at several levels (local, national and international). They aim to control and reduce industrial pollution. In 1972, Clean Water Act regulates the discharge of pollutants into the waters of the United States. It establishes quality standards for surface waters, requires industries to obtain permits for their discharges and imposes the use of best available technologies to minimize pollutants at source [198,199]. In 2000, European Water Framework Directive aims to protect and improve water quality throughout Europe. It requires member states to achieve a good ecological and chemical status of water bodies, limiting industrial discharges and enforcing compliance with environmental quality standards to avoid excessive contamination [166]. In 2004, Stockholm Convention on Persistent Organic Pollutants regulates the production, use and disposal of chemicals that persist in the environment, accumulate in living organisms and pose risks to human health and ecosystems. The convention covers industrial chemicals imposing global restrictions to minimize harmful emissions [200]. As part of the Clean Air Act, the National Emission Standards for Hazardous Air Pollutants in the United States sets limits on emissions of hazardous air pollutants, such as heavy metals, volatile organic compounds and other toxic substances [201]. It requires industries to adopt maximum achievable emission control technologies to limit their impact. The international treaty of Minamata Convention on Mercury aims to reduce mercury pollution worldwide. It regulates the use and emissions of mercury in industrial sectors such as mining, waste incineration, and chemical production, to protect the environment and public health [202].

5.2.2. Focus on Sustainability

Environmental regulations aim not only to reduce pollution, but also to promote sustainable practices by encouraging industries to adopt environmentally friendly methods. Regulations such as the US Clean Water Act and the EU Water Framework Directive focus on preventing pollution at source. They encourage the use of Best Available Techniques [203] and Cleaner Production Technologies [204], which limit pollutants before they are generated, in line with sustainability principles. Initiatives such as the European Circular Economy Action Plan, under the European Green Deal [205], encourage industries to reduce their use of resources, recycle waste and adopt green production processes. Similarly, the Stockholm Convention advocates for the sustainable management of chemicals by phasing out persistent organic pollutants. Many regulatory frameworks require industries to demonstrate compliance with sustainability objectives when applying for permits. For example, in the EU, companies must demonstrate how they intend to reduce pollution by adopting sustainable and resource-efficient production methods. Some regulations introduce financial incentives to reduce environmental impacts. The EU Emissions Trading System, for example, uses a market mechanism to lower greenhouse gas emissions, encouraging industries to innovate and adopt greener technologies to reduce their emissions costs [206].

5.2.3. Challenges

Despite significant progress, regulatory frameworks face various challenges in achieving sustainability goals and promoting green practices in industries. Effective enforcement of regulations remains a major challenge in many regions. Limited resources in developing countries, for example, often result in insufficient oversight of industrial activities. Even in countries with strong regulations such as the US or the EU, enforcement can be uneven, particularly in complex or smaller-scale industries. Some pollutants or practices still escape regulation. For example, while standards for water and air quality are often well defined, emerging substances such as microplastics and nanomaterials are less well regulated, despite their potential impacts on the environment and human health [207,208]. Regulatory frameworks differ widely across regions, with the EU enforcing strict water quality controls while other areas face weaker standards or limited enforcement, leading to environmental disparities. Regulatory frameworks often struggle to keep up with technological advances. As industries adopt new materials and production techniques, regulators may struggle to assess and regulate their environmental impacts in a timely manner. Artificial intelligence or nanotechnology, for example, raise environmental issues that current regulations struggle to address [209]. While schemes such as emissions trading provide financial incentives, some industries still perceive sustainable investments as having low short-term returns. Furthermore, subsidies and incentives for clean technologies sometimes remain insufficient to encourage the widespread adoption of sustainable practices, particularly in energy-intensive or fossil fuel-dependent sectors.

5.2.4. Areas for Improvement

To strengthen regulatory frameworks and better align them with sustainable development goals, several improvements can be considered. Allocating more resources to monitoring, enforcing regulations and imposing penalties for non-compliance could make frameworks more effective. Increased transparency, for example by requiring industries to disclose their pollution data publicly, could also encourage better compliance. Establishing uniform global standards for pollutants, emissions and sustainability criteria would reduce regional disparities and ensure high standards everywhere. The success of the Paris Agreement [210] for climate illustrates the potential for global cooperation in combating climate change. Furthermore, regulatory frameworks should evolve to include emerging pollutants, such as endocrine disruptors [211], microplastics and nanomaterials [212], ensuring that standards are aligned with scientific advances. Governments and international agencies could increase financial incentives, such as tax breaks, subsidies and specific grants, to encourage industries to adopt environmentally friendly technologies. Extending carbon-pricing mechanisms [213] to more sectors and regions could also help this transition. Moreover, many small and medium-sized enterprises face financial barriers to adopting cleaner technologies, and targeted support such as technical assistance, low-interest loans, or grants can help accelerate their transition to more sustainable practices.
In conclusion regulatory frameworks, at all levels, play a crucial role in managing industrial pollution and promoting sustainability. While current regulations have been successful in reducing some pollutants, they face challenges in terms of enforcement, gaps in standards, and adaptation to technological advances. By strengthening enforcement, harmonizing international standards, and increasing incentives for cleaner production practices, regulatory frameworks can better support sustainable industrial development.

5.3. Technological Solutions for Water Treatment

Technological solutions for water treatment play a critical role in mitigating industrial freshwater pollution by removing contaminants before discharge or reuse. These solutions include physical, chemical, and biological processes that enhance water quality and support sustainable water management. They can target a wide spectrum of pollutants such as heavy metals, organic contaminants, pharmaceuticals, and dyes. In recent decades, research has increasingly focused on combining different treatment processes to enhance removal efficiency while reducing energy consumption and operational costs. Bioremediation represents a sustainable strategy that relies on microorganisms, fungi or plants, to decontaminate water by breaking down or transforming contaminants into less harmful substances through enzymatic reactions [214,215]. Numerous studies have demonstrated that microbial communities can effectively degrade organic contaminants such as dyes, pesticides, and pharmaceutical residues through enzymatic biodegradation pathways [216]. For example, microbial consortia have achieved 80–99% decolorization of textile dyes in wastewater [217], while bacterial biofilms have been shown to degrade pesticide compounds and dye pollutants with efficiencies exceeding 70–86% [218]. Compared with physicochemical treatments, bioremediation offers lower operational costs and reduced chemical usage. However, its efficiency is strongly influenced by environmental conditions such as temperature, pH, oxygen availability, and contaminant concentration, which may limit its application in highly contaminated industrial effluents. Nature-based systems such as constructed wetlands provide another environmentally friendly treatment option by mimicking natural purification processes. These systems combine physical filtration, plant uptake, microbial degradation, and sedimentation to remove contaminants from wastewater [219,220]. Studies have shown that constructed wetlands can achieve removal efficiencies exceeding 70–90% for nutrients and organic pollutants under optimized conditions depending on wetland design, hydraulic loading rate, and plant species composition [99,221]. Compared with conventional treatment plants, wetlands require lower energy inputs and can provide additional ecosystem services such as habitat creation and carbon sequestration. Nevertheless, their application is constrained by land requirements and climatic conditions, which may limit their feasibility in densely populated industrial regions. Nanotechnology has emerged as a promising field in advanced water treatment due to the unique properties of nanomaterials, including high surface area, catalytic activity, and selective adsorption capacity. Nanomaterials such as metal oxide nanoparticles, carbon nanotubes, and nano-adsorbents have demonstrated strong potential for removing heavy metals and organic pollutants from contaminated water [222,223]. For example, several studies report removal efficiencies above 90% for metals such as lead and cadmium using nano-adsorbent materials [52]. Despite these advantages, concerns remain regarding the potential environmental risks associated with nanoparticle release, as well as the high production cost and challenges related to large-scale implementation. Membrane filtration technologies represent one of the most widely applied advanced treatment solutions for industrial wastewater purification. Processes such as reverse osmosis [224], ultrafiltration [225], and nanofiltration [226] rely on semi-permeable membranes to separate contaminants from water. These technologies have demonstrated high removal efficiencies for a wide range of pollutants, including heavy metals, pharmaceuticals, dyes, and microorganisms. For example, nanofiltration and reverse osmosis systems can achieve removal efficiencies greater than 90–99% for many dissolved contaminants [50,224]. Membrane systems are widely used in desalination and industrial water reuse applications due to their high reliability and treatment performance. However, their operation requires significant energy input and is often affected by membrane fouling, which increases maintenance requirements and operational costs.
Recent research trends increasingly focus on hybrid treatment systems, combining biological processes with advanced technologies such as membranes or adsorption. Such integrated systems aim to improve pollutant removal efficiency while reducing energy consumption and operational costs. For example, membrane bioreactors combine biological degradation with membrane separation, allowing simultaneous removal of organic contaminants and suspended solids [88,132]. These hybrid systems have shown promising results for treating complex industrial wastewater streams, particularly in sectors such as textile, pharmaceutical, and chemical manufacturing.
A comparative evaluation of these treatment technologies indicates that their applicability depends strongly on pollutant characteristics, treatment scale, and economic constraints, as summarized in Table 12. Biological approaches such as bioremediation are generally more suitable for moderate pollutant concentrations and biodegradable contaminants, where microbial activity can efficiently degrade organic compounds with relatively low operational costs [214]. In contrast, advanced physicochemical treatments such as membrane filtration or advanced oxidation processes are more effective for highly contaminated industrial effluents containing recalcitrant compounds, heavy metals, or pharmaceutical residues, where rapid and high removal efficiencies are required [87]. Nature-based systems such as constructed wetlands provide a cost-effective option for decentralized or low-strength wastewater treatment, but their implementation is often limited by land availability and hydraulic loading capacity [219].
From a techno-economic perspective, advanced technologies such as nanotechnology-based adsorption systems demonstrate excellent pollutant removal efficiencies; however, their large-scale implementation remains constrained by material production costs, nanoparticle stability, and environmental safety concerns. Nanotechnology becomes economically viable primarily in applications requiring selective removal of specific contaminants, high-value water recovery, or compliance with strict discharge regulations, where conventional treatments are insufficient. Consequently, recent research increasingly promotes hybrid treatment systems, combining biological, membrane, and adsorption processes to balance treatment efficiency, operational cost, and environmental sustainability [132].
Overall, technological solutions for water treatment represent essential tools for reducing industrial freshwater pollution. While advanced technologies such as membrane filtration and nanotechnology offer high removal efficiencies, nature-based and biological treatments provide more sustainable and energy-efficient alternatives. Consequently, the selection of appropriate treatment strategies should consider pollutant characteristics, economic feasibility, and environmental sustainability.

5.4. Circular Economy and Waste Management

5.4.1. Circular Economy Principles

The circular economy (CE) aims to design products without generating waste or pollution, to preserve materials and products for as long as possible, and to regenerate natural ecosystems [227]. In the context of water treatment and waste management, CE strategies focus on wastewater reuse, resource recovery, and process integration to reduce industrial discharges into freshwater ecosystems. Recent studies indicate that circular water management strategies can reduce industrial freshwater consumption by 30–70%, depending on the sector and treatment technologies employed. Compared with traditional linear production systems, circular approaches improve resource efficiency while simultaneously reducing pollutant loads entering aquatic environments. Water recycling and reuse represent key circular strategies for pollution prevention in industrial systems [228,229]. Several industries have successfully implemented closed-loop water management systems in which treated wastewater is reused within the same facility [197,230]. For example, industrial wastewater recycling in manufacturing facilities has been reported to reduce freshwater consumption by 40–60%, while significantly decreasing the discharge of contaminants into receiving water bodies [231,232,233]. In water-intensive sectors such as textiles and chemical manufacturing, advanced treatment technologies combined with internal water reuse can enable near-complete recycling of process water [127,234]. However, despite these benefits, wastewater recycling systems often require substantial investment in treatment infrastructure and operational monitoring to maintain water quality suitable for reuse. Another important element of the circular economy is resource recovery from waste streams. Industrial wastewater contains valuable resources such as nutrients, organic matter, and thermal energy that can be recovered and reused [235,236]. Nutrient recovery technologies, such as struvite precipitation, have been widely applied to recover phosphorus and nitrogen from wastewater streams, producing fertilizers that can be reused in agricultural systems [237,238]. In addition, heat recovery systems have been implemented in wastewater treatment plants to capture thermal energy for district heating or industrial processes, reducing reliance on external energy sources [239,240]. By designing more durable, repairable, and scalable products, industries reduce the amount of waste entering water systems [241]. This also reduces resource consumption and the energy required for production [242]. This principle is particularly applicable to water-using products and technologies, reducing their water footprint and impact on water quality in the long term. Compared with conventional wastewater treatment, resource recovery approaches transform waste streams into valuable resources, thereby improving both environmental and economic sustainability.

5.4.2. Industrial Symbiosis

Industrial symbiosis represents a complementary circular economy strategy in which industries exchange materials, energy, water, and by-products to improve overall resource efficiency. In such systems, the waste generated by one facility becomes a resource for another. Compared with conventional end-of-pipe treatment approaches, this model can significantly reduce freshwater consumption, energy demand, and waste generation by optimizing resource flows within industrial networks [243,244]. One of the most common examples is the Kalundborg Eco-Industrial Park in Denmark, where industries exchange resources and by-products, such as water, steam and waste [196,245]. For example, excess heat from a power plant heats local homes, while wastewater from one company is treated and reused by another. This closed-loop system significantly reduces freshwater usage and waste discharges. Similar industrial symbiosis initiatives have been implemented in the Ulsan Eco-Industrial Park in South Korea, where co-located industries—including petrochemical, automotive, and shipbuilding facilities—share water, energy, and by-products [196,246]. Treated wastewater is reused, waste heat is recovered, and materials are exchanged, reducing resource consumption and environmental impacts while improving industrial efficiency. In China, Tianjin Economic–Technological Development Area provides another example of large-scale industrial symbiosis. In this industrial cluster, the treated wastewater, waste heat, and by-products are shared among industries [179]. This reduces freshwater use, pollution, and energy consumption, demonstrating circular economic principles in practice. In the textile sector, industrial symbiosis involves the exchange and reuse of resources such as water, chemicals, and energy between processes or facilities [247]. For example, treated wastewater from rinsing or dyeing can be reused in other production stages, and sludge or fiber residues can be repurposed for energy or materials. These practices reduce freshwater consumption, minimize effluent discharge, and support circular and more sustainable textile manufacturing. The effectiveness of this approach depends strongly on several operating conditions, including geographical proximity between industries, compatible material and energy flows, and the availability of shared infrastructure for resource exchange. However, the implementation of industrial symbiosis also faces several economic, technical, and social challenges. Initial investment costs for shared treatment and distribution infrastructure can be substantial, and coordination between independent companies often requires strong governance structures and trust among stakeholders. Compared with nano-technologies industrial symbiosis generally offers lower operational costs but requires long-term planning and collaborative management. From an economic perspective, emerging technologies can complement industrial symbiosis by enabling more efficient pollutant removal prior to resource exchange. However, the widespread adoption of nanotechnology remains limited by high material costs and uncertainties regarding large-scale deployment. Consequently, environmental regulations play a critical role in promoting the adoption of advanced treatment technologies within circular industrial systems. Regulatory frameworks that encourage wastewater reuse, resource recovery, and stricter discharge standards can significantly accelerate the implementation of industrial symbiosis networks while facilitating the integration of advanced treatment technologies as alternatives to conventional wastewater treatment systems.
From a techno-economic perspective, circular economy strategies are most effective in industrial sectors characterized by high water consumption, recoverable resources, and stable production flows, such as textile, chemical, and food-processing industries [241]. Compared with conventional end-of-pipe treatment technologies, circular approaches focus on resource efficiency and pollution prevention, allowing industries to simultaneously reduce environmental impacts and operational costs. However, their implementation often requires significant initial investment in infrastructure, monitoring systems, and coordination between industrial actors. For example, wastewater reuse systems and resource recovery technologies are generally more viable in large industrial clusters or eco-industrial parks, where shared infrastructure reduces operational costs [196]. In contrast, advanced treatment technologies such as nanotechnology-based systems may offer higher pollutant removal efficiencies but remain economically viable primarily in cases requiring strict discharge compliance or high-value water recovery. Consequently, recent research increasingly emphasizes integrated industrial systems combining circular economy strategies with advanced treatment technologies, enabling industries to balance environmental performance, regulatory compliance, and economic feasibility.
Circular economy practices have proven effective in reducing pollution and limiting the industrial impact on freshwater resources. Companies that adopt these principles report significant reductions in their water consumption, pollutant discharges and overall environmental footprint. By integrating circular economy principles, industries contribute to more sustainable management of freshwater resources, reducing their pollution footprint and promoting long-term environmental and economic sustainability. Table 13 summarizes the circular economy and industrial symbiosis strategies for reducing industrial freshwater pollution.

5.5. Integrated Approaches for Sustainable Industrial Water Management

Although regulatory frameworks, technological solutions, and circular economy strategies are often discussed separately, their effectiveness increases when they are implemented in an integrated manner. Addressing complex industrial pollution challenges requires evaluating how different mitigation strategies interact and which combinations of technologies and policies provide the most effective solutions. Environmental regulations frequently drive the adoption of cleaner production technologies and advanced treatment systems by imposing stricter discharge limits. At the same time, circular economy approaches, such as wastewater reuse and industrial symbiosis, can improve the economic feasibility of advanced technologies by enabling resource recovery and shared infrastructure. However, these interactions may also create trade-offs, such as higher energy demand or investment costs associated with advanced treatment systems. In addition, selecting appropriate mitigation strategies requires consideration of the specific characteristics of industrial pollution. Biological treatments such as bioremediation and constructed wetlands are generally most suitable for biodegradable organic pollutants and moderate contaminant loads, offering relatively low operational costs and environmental compatibility. In contrast, advanced physicochemical technologies such as membrane filtration and advanced oxidation processes are more effective for highly contaminated industrial effluents containing persistent organic pollutants, heavy metals, or pharmaceutical residues that require rapid and high removal efficiency. Nanotechnology-based systems show promising performance for selective contaminant removal but remain economically viable mainly in applications requiring high-value water recovery or strict discharge standards. Consequently, integrated treatment strategies that combine preventive measures, advanced treatment technologies, and circular resource management approaches are often the most effective solution for addressing complex industrial pollution challenges.

6. Conclusions and Future Perspectives

The literature reviewed in this study demonstrates that industrial chemical pollution—including heavy metals, microplastics, persistent organic pollutants, pharmaceuticals, pesticides, textile dyes, and polycyclic aromatic hydrocarbons—poses significant risks to freshwater ecosystems, biodiversity, and human health. Addressing these challenges requires a combination of pollution prevention strategies, advanced treatment technologies, and circular resource management approaches. Cleaner production practices such as eco-design, green chemistry, and process optimization can reduce pollutant generation at the source, while treatment technologies including membrane filtration, advanced oxidation processes, bioremediation, and nature-based systems have shown strong potential for removing contaminants from industrial effluents. In parallel, circular economy strategies such as wastewater recycling, nutrient recovery, and industrial symbiosis can reduce freshwater consumption and minimize pollutant discharges through closed-loop resource use.
However, the reviewed studies also highlight that the performance and feasibility of these approaches vary depending on wastewater composition, industrial sector, and economic constraints. High-efficiency technologies such as reverse osmosis and zero-liquid-discharge systems provide excellent contaminant removal and water recovery but often involve high energy demand and operational costs. Conversely, biological and nature-based solutions are generally more cost-effective and environmentally compatible but may require larger land areas or longer treatment times. These findings suggest that integrated treatment strategies combining multiple technologies are often the most effective option for managing complex industrial wastewater streams.
Future research should focus on addressing several critical gaps identified in the literature. First, more comprehensive life cycle and techno-economic assessments of advanced treatment systems, particularly zero-liquid-discharge (ZLD) technologies, are needed to determine their economic feasibility for small and medium-sized industries. Second, further investigation is required to develop integrated treatment systems combining biological, membrane, and advanced oxidation processes capable of efficiently treating complex industrial wastewater containing mixed pollutants. Third, additional studies should evaluate the long-term environmental risks, operational stability, and cost thresholds of nanotechnology-based treatment systems under real industrial conditions. Finally, future work should examine policy instruments and regulatory frameworks that promote circular water management, including incentives for wastewater reuse, resource recovery, and industrial symbiosis within eco-industrial parks. Such targeted research efforts will help bridge the gap between laboratory-scale innovation and large-scale industrial implementation.

Funding

This research was funded by Prince Sattam bin Abdulaziz University, project number PSAU/2025/01/33524.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

No new data were created or analyzed in this study.

Acknowledgments

The author extends her appreciation to Prince Sattam bin Abdulaziz University for funding this research work through the project number (PSAU/2025/01/33524).

Conflicts of Interest

The author declares no conflicts of interest.

References

  1. Clarke, S.J. Conserving freshwater biodiversity: The value, status and management of high quality ditch systems. J. Nat. Conserv. 2015, 24, 93–100. [Google Scholar] [CrossRef]
  2. Cojoc, L.; de Castro-Català, N.; de Guzmán, I.; González, J.; Arroita, M.; Besolí-Mestres, N.; Cadena, I.; Freixa, A.; Gutiérrez, O.; Larrañaga, A.; et al. Pollutants in urban runoff: Scientific evidence on toxicity and impacts on freshwater ecosystems. Chemosphere 2024, 369, 143806. [Google Scholar] [CrossRef] [PubMed]
  3. du Plessis, A. Persistent degradation: Global water quality challenges and required actions. One Earth 2022, 5, 129–131. [Google Scholar] [CrossRef]
  4. Naidu, R.; Biswas, B.; Willett, I.R.; Cribb, J.; Kumar Singh, B.; Paul Nathanail, C.; Coulon, F.; Semple, K.T.; Jones, K.C.; Barclay, A.; et al. Chemical pollution: A growing peril and potential catastrophic risk to humanity. Environ. Int. 2021, 156, 106616. [Google Scholar] [CrossRef] [PubMed]
  5. Mu, L.; Tan, Z.; Luo, C.; Qiao, N. Exploring the contribution of the river chief system on controlling industrial water pollution under quasi-natural experimental conditions. Environ. Sci. Pollut. Res. 2023, 30, 89415–89429. [Google Scholar] [CrossRef]
  6. Botle, A.; Salgaonkar, S.; Tiwari, R.; Ambadekar, S.; Barabde, G.R. Brief status of contamination in surface water of rivers of India by heavy metals: A review with pollution indices and health risk assessment. Environ. Geochem. Health 2023, 45, 2779–2801. [Google Scholar] [CrossRef]
  7. Whelan, M.J.; Pemberton, E.; Hughes, C.B.; Swansborough, C.; Goslan, E.H.; Gouin, T.; Bell, V.A.; Bird, E.; Bull, S.; Segal, L.; et al. A tiered assessment of human health risks associated with exposure to persistent, mobile and toxic chemicals via drinking water. Sci. Total Environ. 2025, 958, 177868. [Google Scholar] [CrossRef]
  8. Arumugam, A.; Lee, K.E.; Ng, P.Y.; Shamsuddin, A.S.; Zulkifli, A.; Goh, T.L. Pharmaceuticals as Emerging Pollutants: Implications for Water Resource Management in Malaysia. Emerg. Contam. 2025, 11, 100470. [Google Scholar] [CrossRef]
  9. Dulsat-Masvidal, M.; Ciudad, C.; Infante, O.; Mateo, R.; Lacorte, S. Water pollution threats in important bird and biodiversity areas from Spain. J. Hazard. Mater. 2023, 448, 130938. [Google Scholar] [CrossRef]
  10. Alizamir, M.; Kazemi, Z.; Kazemi, Z.; Kermani, M.; Kim, S.; Heddam, S.; Kisi, O.; Chung, I.-M. Investigating Landfill Leachate and Groundwater Quality Prediction Using a Robust Integrated Artificial Intelligence Model: Grey Wolf Metaheuristic Optimization Algorithm and Extreme Learning Machine. Water 2023, 15, 2453. [Google Scholar] [CrossRef]
  11. Wang, F.; Song, K.; Lan, W.; Li, T.; Liu, J.; Liu, D. Identification and assessment of groundwater pollution from landfill leachate based on geophysical, spectroscopy, and hydrogeochemical methods. Sci. Rep. 2025, 15, 25558. [Google Scholar] [CrossRef] [PubMed]
  12. Huang, Z.; Liu, G.; Zhang, Y.; Yuan, Y.; Xi, B.; Tan, W. Assessing the impacts and contamination potentials of landfill leachate on adjacent groundwater systems. Sci. Total Environ. 2024, 930, 172664. [Google Scholar] [CrossRef] [PubMed]
  13. Khan, K.; Khan, M.S.; Younas, M.; Yaseen, M.; Al-Sehemi, A.G.; Kavil, Y.N.; Su, C.; Ali, N.; Maryam, A.; Liang, R. Pathways and risk analysis of arsenic and heavy metal pollution in riverine water: Application of multivariate statistics and USEPA-recommended risk assessment models. J. Contam. Hydrol. 2025, 269, 104483. [Google Scholar] [CrossRef]
  14. Cheng, W.; Yin, H.; Dong, F.; Li, X.; Zhang, D.; Lu, C. Analysis and probabilistic health risk assessment of vertical heavy metal pollution in the water environment of reservoir in the west coast new area of Qingdao, China. Environ. Pollut. 2024, 362, 125021. [Google Scholar] [CrossRef]
  15. Maggi, F.; Tang, F.H.M.; Tubiello, F.N. Agricultural pesticide land budget and river discharge to oceans. Nature 2023, 620, 1013–1017. [Google Scholar] [CrossRef]
  16. Okoye, C.O.; Addey, C.I.; Oderinde, O.; Okoro, J.O.; Uwamungu, J.Y.; Ikechukwu, C.K.; Okeke, E.S.; Ejeromedoghene, O.; Odii, E.C. Toxic Chemicals and Persistent Organic Pollutants Associated with Micro-and Nanoplastics Pollution. Chem. Eng. J. Adv. 2022, 11, 100310. [Google Scholar] [CrossRef]
  17. Arminini Neto, A.; Januário, E.F.D.; Vidovix, T.B.; Beluci, N.d.C.L.; Bergamasco, R.; Vieira, A.M.S. The role of membrane technology in addressing pharmaceutical pollution in water. Chem. Eng. Process.—Process Intensif. 2024, 202, 109837. [Google Scholar] [CrossRef]
  18. Jesus, F.; Pereira, J.L.; Campos, I.; Santos, M.; Ré, A.; Keizer, J.; Nogueira, A.; Gonçalves, F.J.M.; Abrantes, N.; Serpa, D. A review on polycyclic aromatic hydrocarbons distribution in freshwater ecosystems and their toxicity to benthic fauna. Sci. Total Environ. 2022, 820, 153282. [Google Scholar] [CrossRef]
  19. Zhou, L.; Appiah, R.; Boadi, E.B.; Ayamba, E.C.; Larnyo, E.; Antwi, H.A. The Impact of Human Activities on River Pollution and Health-Related Quality of Life: Evidence from Ghana. Sustainability 2022, 14, 13120. [Google Scholar] [CrossRef]
  20. Dippong, T.; Resz, M.-A.; Tănăselia, C.; Cadar, O. Assessing microbiological and heavy metal pollution in surface waters associated with potential human health risk assessment at fish ingestion exposure. J. Hazard. Mater. 2024, 476, 135187. [Google Scholar] [CrossRef] [PubMed]
  21. Franco, M.E.; Hollender, J.; Schirmer, K. Differential biotransformation ability may alter fish biodiversity in polluted waters. Environ. Int. 2025, 195, 109254. [Google Scholar] [CrossRef] [PubMed]
  22. Bashir, I.; Lone, F.A.; Bhat, R.A.; Mir, S.A.; Dar, Z.A.; Dar, S.A. Concerns and Threats of Contamination on Aquatic Ecosystems. In Bioremediation and Biotechnology: Sustainable Approaches to Pollution Degradation; Hakeem, K.R., Bhat, R.A., Qadri, H., Eds.; Springer International Publishing: Cham, Switzerland, 2020; pp. 1–26. [Google Scholar]
  23. Balasooriya, B.M.J.K.; Rajapakse, J.; Gallage, C. A review of drinking water quality issues in remote and indigenous communities in rich nations with special emphasis on Australia. Sci. Total Environ. 2023, 903, 166559. [Google Scholar] [CrossRef]
  24. Kelly, B.C.; Brewer, S.C.; Medina, R.M.; Bakian, A.V. Racial and ethnic disparities in health risk from industrial surface water pollution in the United States, 2011–2021. Health Place 2024, 89, 103343. [Google Scholar] [CrossRef] [PubMed]
  25. Nicolas-Artero, C.; Fuster-Farfán, X.; Huaico-Malhue, A. Interconnected water scarcities and environmental amenities migration in rural Chile. J. Rural Stud. 2025, 113, 103502. [Google Scholar] [CrossRef]
  26. UNESCO World Water Assessment Programme. The United Nations World Water Development Report 2021: Valuing Water; WWDR 2021; UNESCO: Landais, France, 2021. [Google Scholar]
  27. UN-Water. Summary Progress Update 2021: SDG 6—Water and Sanitation for All; UN-Water: New York, NY, USA, 2021. [Google Scholar]
  28. Qadir, M.; Drechsel, P.; Jiménez Cisneros, B.; Kim, Y.; Pramanik, A.; Mehta, P.; Olaniyan, O. Global and regional potential of wastewater as a water, nutrient and energy source. Nat. Resour. Forum 2020, 44, 40–51. [Google Scholar] [CrossRef]
  29. Kavitha, G.; Govindhan, M.; Premkumar, S. Dye pollution and its implications for human health, aquatic ecosystems, and sustainable wastewater treatment: A comprehensive review. J. Water Process Eng. 2025, 80, 109071. [Google Scholar] [CrossRef]
  30. Gupta, B.G.; Mukhopadhyay, R. Heavy metal contamination from textile wastewater and its health impacts: A case study from West Bengal with sustainable remediation approaches. Sci. Rep. 2025, 15, 29578. [Google Scholar] [CrossRef]
  31. Hoendervangers, P.; Goeteyn, L.; Rousseau, D.P.L.; Cirne, D.G.; Spanoghe, P. Monitoring of pesticides in the processing water and wastewater of vegetable processing companies: Sources and treatment challenges. J. Environ. Chem. Eng. 2025, 13, 119252. [Google Scholar] [CrossRef]
  32. Zhou, C.; Wang, G.; Han, D.; Diao, J.; Xie, Y.; Ren, P.; Su, C.; Liu, W.; Wang, T. Distribution and potential risk of pharmaceuticals and personal care products (PPCPs) subjected to land function: A case of coastal water source area, China. Mar. Pollut. Bull. 2025, 216, 117991. [Google Scholar] [CrossRef]
  33. Liu, Y.; Lyu, H.; Jin, T.; Guo, S.; Tang, J.; He, J. Microplastics hack the water supply system: What it means for water safety and human health? Water Res. 2026, 290, 125051. [Google Scholar] [CrossRef]
  34. Ingrao, C.; Strippoli, R.; Lagioia, G.; Huisingh, D. Water scarcity in agriculture: An overview of causes, impacts and approaches for reducing the risks. Heliyon 2023, 9, e18507. [Google Scholar] [CrossRef] [PubMed]
  35. Tavakoly Sany, S.B.; Hashim, R.; Rezayi, M.; Salleh, A.; Safari, O. A review of strategies to monitor water and sediment quality for a sustainability assessment of marine environment. Environ. Sci. Pollut. Res. 2014, 21, 813–833. [Google Scholar] [CrossRef] [PubMed]
  36. Tan, R.; Hu, R.; Vatn, A. What does sustainability demand? An institutionalist analysis with applications to China. J. Chin. Gov. 2021, 6, 486–514. [Google Scholar] [CrossRef]
  37. Moghimi Dehkordi, M.; Pournuroz Nodeh, Z.; Soleimani Dehkordi, K.; Salmanvandi, H.; Rasouli Khorjestan, R.; Ghaffarzadeh, M. Soil, air, and water pollution from mining and industrial activities: Sources of pollution, environmental impacts, and prevention and control methods. Results Eng. 2024, 23, 102729. [Google Scholar] [CrossRef]
  38. Velenturf, A.P.M.; Purnell, P. Principles for a sustainable circular economy. Sustain. Prod. Consum. 2021, 27, 1437–1457. [Google Scholar] [CrossRef]
  39. Pan, Y.; Gao, S.-H.; Ge, C.; Gao, Q.; Huang, S.; Kang, Y.; Luo, G.; Zhang, Z.; Fan, L.; Zhu, Y.; et al. Removing microplastics from aquatic environments: A critical review. Environ. Sci. Ecotechnol. 2023, 13, 100222. [Google Scholar] [CrossRef]
  40. Li, X.; Chen, Y.; Zhang, S.; Dong, Y.; Pang, Q.; Lynch, I.; Xie, C.; Guo, Z.; Zhang, P. From marine to freshwater environment: A review of the ecotoxicological effects of microplastics. Ecotoxicol. Environ. Saf. 2023, 251, 114564. [Google Scholar] [CrossRef]
  41. Meng, X.; Yuan, J.; Huang, Q.; Liu, R.; Yang, Y.; Yang, X.; Wang, K. A Review of Sources, Hazards, and Removal Methods of Microplastics in the Environment. Water 2025, 17, 102. [Google Scholar] [CrossRef]
  42. Ahammad, N.A.; Ahmad, M.A.; Hameed, B.H.; Mohd Din, A.T. A mini review of recent progress in the removal of emerging contaminants from pharmaceutical waste using various adsorbents. Environ. Sci. Pollut. Res. 2023, 30, 124459–124473. [Google Scholar] [CrossRef]
  43. Singh, A.; Pal, D.B.; Mohammad, A.; Alhazmi, A.; Haque, S.; Yoon, T.; Srivastava, N.; Gupta, V.K. Biological remediation technologies for dyes and heavy metals in wastewater treatment: New insight. Bioresour. Technol. 2022, 343, 126154. [Google Scholar] [CrossRef] [PubMed]
  44. Oladimeji, T.E.; Oyedemi, M.; Emetere, M.E.; Agboola, O.; Adeoye, J.B.; Odunlami, O.A. Review on the impact of heavy metals from industrial wastewater effluent and removal technologies. Heliyon 2024, 10, e40370. [Google Scholar] [CrossRef] [PubMed]
  45. Berríos-Rolón, P.J.; Cotto, M.C.; Márquez, F. Polycyclic Aromatic Hydrocarbons (PAHs) in Freshwater Systems: A Comprehensive Review of Sources, Distribution, and Ecotoxicological Impacts. Toxics 2025, 13, 321. [Google Scholar] [CrossRef] [PubMed]
  46. Jaishankar, M.; Tseten, T.; Anbalagan, N.; Mathew, B.B.; Beeregowda, K.N. Toxicity, mechanism and health effects of some heavy metals. Interdiscip. Toxicol. 2014, 7, 60–72. [Google Scholar] [CrossRef]
  47. Xu, W.; Jin, Y.; Zeng, G. Introduction of heavy metals contamination in the water and soil: A review on source, toxicity and remediation methods. Green Chem. Lett. Rev. 2024, 17, 2404235. [Google Scholar] [CrossRef]
  48. Hama Aziz, K.H.; Mustafa, F.S.; Omer, K.M.; Hama, S.; Hamarawf, R.F.; Rahman, K.O. Heavy metal pollution in the aquatic environment: Efficient and low-cost removal approaches to eliminate their toxicity: A review. RSC Adv. 2023, 13, 17595–17610. [Google Scholar] [CrossRef]
  49. Qiu, M.; Liu, L.; Ling, Q.; Cai, Y.; Yu, S.; Wang, S.; Fu, D.; Hu, B.; Wang, X. Biochar for the removal of contaminants from soil and water: A review. Biochar 2022, 4, 19. [Google Scholar] [CrossRef]
  50. Covaliu-Mierlă, C.I.; Păunescu, O.; Iovu, H. Recent Advances in Membranes Used for Nanofiltration to Remove Heavy Metals from Wastewater: A Review. Membranes 2023, 13, 643. [Google Scholar] [CrossRef] [PubMed]
  51. Huang, Y.; Feng, X. Polymer-enhanced ultrafiltration: Fundamentals, applications and recent developments. J. Membr. Sci. 2019, 586, 53–83. [Google Scholar] [CrossRef]
  52. Niazkhani, S.; Aminsharei, F.; Hassanzadeh-Tabrizi, S.A.; Malekzadeh, A.; Ameri, E. Synthesis and modification of nanofiltration membranes with dendrimer-modified graphene oxide to remove lead and cadmium ions from aqueous solutions. Clean. Eng. Technol. 2024, 23, 100843. [Google Scholar] [CrossRef]
  53. Cao, H.; Qi, J.; He, L.; Meng, F.; Zhao, J. Study on the adsorption performance of modified biochar for heavy metals lead and cadmium. J. Anal. Appl. Pyrolysis 2026, 195, 107684. [Google Scholar] [CrossRef]
  54. Mandal, R.R.; Raj, D. Sustainable removal of arsenic and mercury via integrated phytoremediation and biomass valorization of Eichhornia crassipes. Appl. Geochem. 2026, 198, 106699. [Google Scholar] [CrossRef]
  55. Lahnafi, A.; El-Kordy, A.; Elgamouz, A.; Tijani, N.; Kawde, A.-N. Enhanced removal of chromium (VI) via reduction to chromium (III) mediated by the iron(II)/iron(III) redox couple and filtration through a clay/zeolite Y composite membrane: Electrochemical mechanistic insights. J. Environ. Chem. Eng. 2025, 13, 118710. [Google Scholar] [CrossRef]
  56. Weis, J.S.; Alava, J.J. (Micro)Plastics Are Toxic Pollutants. Toxics 2023, 11, 935. [Google Scholar] [CrossRef]
  57. Wu, L.; Dong, J.; Shen, Z.; Zhou, Y. Microplastics as vectors for antibiotic resistance: Role of pathogens, heavy metals, and pharmaceuticals and personal care products. J. Water Process Eng. 2024, 67, 106124. [Google Scholar] [CrossRef]
  58. Khoironi, A.; Hadiyanto, H.; Hartini, E.; Dianratri, I.; Joelyna, F.A.; Pratiwi, W.Z. Impact of disposable mask microplastics pollution on the aquatic environment and microalgae growth. Environ. Sci. Pollut. Res. 2023, 30, 77453–77468. [Google Scholar] [CrossRef]
  59. Bashir, S.M.; Kimiko, S.; Mak, C.-W.; Fang, J.K.-H.; Gonçalves, D. Personal Care and Cosmetic Products as a Potential Source of Environmental Contamination by Microplastics in a Densely Populated Asian City. Front. Mar. Sci. 2021, 8, 683482. [Google Scholar] [CrossRef]
  60. Patil, P.M.; Mahamuni-Badiger, P.; Ingavale, R.R.; Patel, P.R.; Dhanavade, M.J. Usage of Microplastic Beads in Pharmaceuticals and Cosmetics Industry: A Review. In Microplastic Pollution; Shahnawaz, M., Adetunji, C.O., Dar, M.A., Zhu, D., Eds.; Springer Nature Singapore: Singapore, 2024; pp. 51–72. [Google Scholar]
  61. Arif, Y.; Mir, A.R.; Zieliński, P.; Hayat, S.; Bajguz, A. Microplastics and nanoplastics: Source, behavior, remediation, and multi-level environmental impact. J. Environ. Manag. 2024, 356, 120618. [Google Scholar] [CrossRef]
  62. Barceló, D. Microplastics in the environment: Analytical chemistry methods, sorption materials, risks and sustainable solutions. Anal. Bioanal. Chem. 2024, 416, 3479–3485. [Google Scholar] [CrossRef] [PubMed]
  63. Iyare, P.U.; Ouki, S.K.; Bond, T. Microplastics removal in wastewater treatment plants: A critical review. Environ. Sci. Water Res. Technol. 2020, 6, 2664–2675. [Google Scholar] [CrossRef]
  64. Hamidavi, F.; Gadkari, S.; Lee, J. Microplastic fiber filtration: Exploring operational parameters and their impact on ultrafiltration membrane performance. J. Water Process Eng. 2025, 77, 108436. [Google Scholar] [CrossRef]
  65. Zhuang, S.; Huang, S.; Dai, L.; Lu, X.; Long, Z.; He, Z. Recent advances in microplastics remediation via adsorption and photocatalytic degradation with bio-polymers and functionalized frameworks. Chem. Eng. J. 2025, 524, 169627. [Google Scholar] [CrossRef]
  66. Deng, H.; Wei, R.; Luo, W.; Hu, L.; Li, B.; Di, Y.n.; Shi, H. Microplastic pollution in water and sediment in a textile industrial area. Environ. Pollut. 2020, 258, 113658. [Google Scholar] [CrossRef]
  67. Zhou, Z.; Zhang, K.; Ren, Y.; Xiao, Y.; Hou, P.; Li, Y. Sustainable sand filtration strategies for microplastic removal in irrigation water. Environ. Res. 2026, 292, 123635. [Google Scholar] [CrossRef]
  68. La Guardia, M.J.; Mainor, T.M.; Luellen, D.R.; Harvey, E.; Hale, R.C. Twenty years later: PBDEs in fish from U.S. sites with historically extreme contamination. Chemosphere 2024, 351, 141126. [Google Scholar] [CrossRef]
  69. Li, L.; Chen, C.; Li, D.; Breivik, K.; Abbasi, G.; Li, Y.-F. What do we know about the production and release of persistent organic pollutants in the global environment? Environ. Sci. Adv. 2023, 2, 55–68. [Google Scholar] [CrossRef]
  70. Lesch, V.; Pieters, R.; Bouwman, H. Dioxins, PFOS, and 20 other Persistent Organic Pollutants in Eggs of Nine Wild Bird Species from the Vaal River, South Africa. Arch. Environ. Contam. Toxicol. 2024, 87, 287–310. [Google Scholar] [CrossRef]
  71. Zhang, K.; Wei, Y.-L.; Zeng, E.Y. A review of environmental and human exposure to persistent organic pollutants in the Pearl River Delta, South China. Sci. Total Environ. 2013, 463–464, 1093–1110. [Google Scholar] [CrossRef]
  72. Aravind kumar, J.; Krithiga, T.; Sathish, S.; Renita, A.A.; Prabu, D.; Lokesh, S.; Geetha, R.; Namasivayam, S.K.R.; Sillanpaa, M. Persistent organic pollutants in water resources: Fate, occurrence, characterization and risk analysis. Sci. Total Environ. 2022, 831, 154808. [Google Scholar] [CrossRef]
  73. Luarte, T.; Gómez Aburto, V.; Poblete-Castro, I.; Castro-Nallar, E.; Hunneus, N.; Molina-Montenegro, M.; Egas, C.; Azcune, G.; Pérez Parada, A.; Lohmann, R.; et al. Levels of persistent organic pollutants (POPs) in the Antarctic atmosphere over time (1980 to 2021) and estimation of their atmospheric half-lives. Atmos. Meas. Tech. 2023, 23, 8103–8118. [Google Scholar] [CrossRef]
  74. Ahmad, A.; Priyadarshini, M.; Yadav, S.; Ghangrekar, M.M.; Surampalli, R.Y. The potential of biochar-based catalysts in advanced treatment technologies for efficacious removal of persistent organic pollutants from wastewater: A review. Chem. Eng. Res. Des. 2022, 187, 470–496. [Google Scholar] [CrossRef]
  75. Li, M.; Zhao, X.; Yan, P.; Xie, H.; Zhang, J.; Wu, S.; Wu, H. A review of per- and polyfluoroalkyl substances (PFASs) removal in constructed wetlands: Mechanisms, enhancing strategies and environmental risks. Environ. Res. 2024, 262, 119967. [Google Scholar] [CrossRef]
  76. Vu, T.K.; Fauvelle, V.; Nguyen, T.T.; Bui, V.H.; Malleret, L. Occurrence and levels of industrial persistent organic pollutants under the Stockholm convention: A review of water resources in southeast Asian countries. J. Hazard. Mater. Adv. 2025, 20, 100872. [Google Scholar] [CrossRef]
  77. Devendrapandi, G.; Liu, X.; Balu, R.; Ayyamperumal, R.; Valan Arasu, M.; Lavanya, M.; Minnam Reddy, V.R.; Kim, W.K.; Karthika, P.C. Innovative remediation strategies for persistent organic pollutants in soil and water: A comprehensive review. Environ. Res. 2024, 249, 118404. [Google Scholar] [CrossRef]
  78. Wang, Q.; He, X.; Luo, Y.; Xu, J.; Li, Z. Simultaneous determination and removal assessment of organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs) in wastewater treatment plants, Zunyi, China. Water Resour. Ind. 2026, 35, 100345. [Google Scholar] [CrossRef]
  79. Verlicchi, P.; Al Aukidy, M.; Zambello, E. Occurrence of pharmaceutical compounds in urban wastewater: Removal, mass load and environmental risk after a secondary treatment—A review. Sci. Total Environ. 2012, 429, 123–155. [Google Scholar] [CrossRef]
  80. Yang, Y.; Ok, Y.S.; Kim, K.-H.; Kwon, E.E.; Tsang, Y.F. Occurrences and removal of pharmaceuticals and personal care products (PPCPs) in drinking water and water/sewage treatment plants: A review. Sci. Total Environ. 2017, 596–597, 303–320. [Google Scholar] [CrossRef]
  81. Joss, A.; Zabczynski, S.; Göbel, A.; Hoffmann, B.; Löffler, D.; McArdell, C.S.; Ternes, T.A.; Thomsen, A.; Siegrist, H. Biological degradation of pharmaceuticals in municipal wastewater treatment: Proposing a classification scheme. Water Res. 2006, 40, 1686–1696. [Google Scholar] [CrossRef]
  82. Deblonde, T.; Cossu-Leguille, C.; Hartemann, P. Emerging pollutants in wastewater: A review of the literature. Int. J. Hyg. Environ. Health 2011, 214, 442–448. [Google Scholar] [CrossRef]
  83. Kümmerer, K. Antibiotics in the aquatic environment—A review—Part I. Chemosphere 2009, 75, 417–434. [Google Scholar] [CrossRef]
  84. Gavrilescu, M.; Demnerová, K.; Aamand, J.; Agathos, S.; Fava, F. Emerging pollutants in the environment: Present and future challenges in biomonitoring, ecological risks and bioremediation. New Biotechnol. 2015, 32, 147–156. [Google Scholar] [CrossRef]
  85. Lapworth, D.J.; Baran, N.; Stuart, M.E.; Ward, R.S. Emerging organic contaminants in groundwater: A review of sources, fate and occurrence. Environ. Pollut. 2012, 163, 287–303. [Google Scholar] [CrossRef]
  86. Hama Aziz, K.H.; Mustafa, F.S.; Karim, M.A.H.; Hama, S. Pharmaceutical pollution in the aquatic environment: Advanced oxidation processes as efficient treatment approaches: A review. Mater. Adv. 2025, 6, 3433–3454. [Google Scholar] [CrossRef]
  87. Shin, Y.; Hwang, T.-M.; Nam, S.-H.; Kim, E.; Park, J.; Choi, Y.-J.; Kye, H.; Koo, J.-W. Evaluating Nanofiltration and Reverse Osmosis Membranes for Pharmaceutically Active Compounds Removal: A Solution Diffusion Model Approach. Membranes 2024, 14, 250. [Google Scholar] [CrossRef]
  88. Oberoi, A.S.; Surendra, K.C.; Wu, D.; Lu, H.; Wong, J.W.C.; Kumar Khanal, S. Anaerobic membrane bioreactors for pharmaceutical-laden wastewater treatment: A critical review. Bioresour. Technol. 2022, 361, 127667. [Google Scholar] [CrossRef]
  89. Ghazoui, M.; Boudouch, O.; Zahnoune, R.; Sylla, A.S.; Dabali, S.; Elkacmi, R. Multi-target adsorption of dyes and antibiotics on biomimetic carbon foams: Mechanisms, column design, and integrated treatment of mixed industrial effluents. Sep. Purif. Technol. 2026, 385, 136424. [Google Scholar] [CrossRef]
  90. Huang, Y.; Dong, X.; Ma, Z.-Y.; Tian, X.-Z.; Rao, Z. Characteristics and ecological risk assessment of antibiotics and hormones in landfill waters. China Geol. 2025, 8, 598–606. [Google Scholar] [CrossRef]
  91. Mota, S.; Sousa, E.; Cruz, M.T.; Martins de Almeida, I. Occurrence and ecotoxicity of cosmetic ingredients in aquatic ecosystems: A narrative review. Emerg. Contam. 2025, 11, 100512. [Google Scholar] [CrossRef]
  92. Coelho, F.D.A.; Campos, L.C.; Morgan, R. Prevalence of illicit drugs and pharmaceuticals in environmental waters—A global spatial review. J. Hazard. Mater. Adv. 2026, 21, 101088. [Google Scholar] [CrossRef]
  93. Singh, S.; Rawat, M.; Malyan, S.K.; Singh, R.; Tyagi, V.K.; Singh, K.; Kashyap, S.; Kumar, S.; Sharma, M.; Panday, B.K.; et al. Global distribution of pesticides in freshwater resources and their remediation approaches. Environ. Res. 2023, 225, 115605. [Google Scholar] [CrossRef]
  94. Rajmohan, K.S.; Chandrasekaran, R.; Varjani, S. A Review on Occurrence of Pesticides in Environment and Current Technologies for Their Remediation and Management. Indian J. Microbiol. 2020, 60, 125–138. [Google Scholar] [CrossRef]
  95. Pawan, K.; Kumar, R.; Thakur, K.; Mahajan, D.; Brar, B.; Sharma, D.; Kumar, S.; Sharma, A.K. Impact of Pesticides Application on Aquatic Ecosystem and Biodiversity: A Review. Biol. Bull. 2023, 50, 1362–1375. [Google Scholar] [CrossRef]
  96. Holanda, M.A.S.; Coelho Menezes, J.M.; Coutinho, H.D.M.; Teixeira, R.N.P. Effectiveness of biochar as an adsorbent for pesticides: Systematic review and meta-analysis. J. Environ. Manag. 2023, 345, 118719. [Google Scholar] [CrossRef]
  97. Eissa, F.; Alsherbeny, S.; El-Sawi, S.; Slaný, M.; Lee, S.S.; Shaheen, S.M.; Jamil, T.S. Remediation of pesticides contaminated water using biowastes-derived carbon rich biochar. Chemosphere 2023, 340, 139819. [Google Scholar] [CrossRef]
  98. Shanaah, H.H.; Alzaimoor, E.F.H.; Rashdan, S.; Abdalhafith, A.A.; Kamel, A.H. Photocatalytic Degradation and Adsorptive Removal of Emerging Organic Pesticides Using Metal Oxide and Their Composites: Recent Trends and Future Perspectives. Sustainability 2023, 15, 7336. [Google Scholar] [CrossRef]
  99. Tang, Z.; Wood, J.; Smith, D.; Thapa, A.; Aryal, N. A Review on Constructed Treatment Wetlands for Removal of Pollutants in the Agricultural Runoff. Sustainability 2021, 13, 13578. [Google Scholar] [CrossRef]
  100. Pilotto, F.; Golovko, O.; Hultberg, M. Water quality and pesticide contamination in agricultural streams: Assessing white-rot fungi and biochar treatments as remediation strategies. J. Environ. Manag. 2025, 394, 127282. [Google Scholar] [CrossRef] [PubMed]
  101. Sumantrao, S.K.; Kariyajjanavar, P.; C, V.C.; Shridhar, A.H.; Ghagane, S.C.; Chigari, S.S.; Bonageri, G.; Ansari, M.Z.; Alsubaie, A.S. Sunlight-driven GO/ZnO nanocomposite for photocatalytic degradation of Chlorpyrifos insecticide and its biological activities. J. Environ. Chem. Eng. 2025, 13, 115437. [Google Scholar] [CrossRef]
  102. Ignatowicz, K.; Łozowicki, J.; Łozowicka, B.; Piekarski, J. Degradation of selected triazole fungicides in constructed wetlands with application of biopreparation. Desalin. Water Treat. 2023, 301, 83–90. [Google Scholar] [CrossRef]
  103. Bhaskaralingam, A.; Sharma, G.; Wang, T.; Kumar, A.; Dhiman, P.; Kumar, D.; Shi, H. Bioremediation of pharmaceuticals waste and pesticides using various microorganisms: A review. Process Saf. Environ. Prot. 2025, 194, 1116–1132. [Google Scholar] [CrossRef]
  104. Parida, V.K.; Singh, N.; Priyadarshini, M.; Kumari, P.; Datta, D.; Tambi, A. Insights into the synthetic dye contamination in textile wastewater: Impacts on aquatic ecosystems and human health, and eco-friendly remediation strategies for environmental sustainability. J. Ind. Eng. Chem. 2025, 150, 247–264. [Google Scholar] [CrossRef]
  105. Mahjoubi, N.; Hamdi, R. Eco-Friendly Removal of Cationic and Anionic Textile Dyes Using a Low-Cost Natural Tunisian Chert: A Promising Solution for Wastewater Treatment. Water 2025, 17, 2806. [Google Scholar] [CrossRef]
  106. Acharya, T.R.; Lamichhane, P.; Negi, M.; Amsalu, K.; Dhakal, O.B.; Dahal, R.; Kaushik, N.; Kaushik, N.K.; Choi, E.H. Examining plasma-generated ozone and nitric oxide’s role in synthetic textile dye water remediation and ecotoxicological analysis. J. Environ. Manag. 2024, 370, 122554. [Google Scholar] [CrossRef]
  107. Burkinshaw, S.M.; Salihu, G. The role of auxiliaries in the immersion dyeing of textile fibres: Part 1 an overview. Dyes Pigments 2019, 161, 519–530. [Google Scholar] [CrossRef]
  108. Liu, S.; Li, H.; Wang, Y. Research on microbial community structure and treatment of dye wastewater with the enhancement of activated sludge by magnetic field at low temperature. RSC Adv. 2023, 13, 16471–16479. [Google Scholar] [CrossRef] [PubMed]
  109. Dutta, S.; Gupta, B.; Srivastava, S.K.; Gupta, A.K. Recent advances on the removal of dyes from wastewater using various adsorbents: A critical review. Mater. Adv. 2021, 2, 4497–4531. [Google Scholar] [CrossRef]
  110. Khan, S.; Noor, T.; Iqbal, N.; Yaqoob, L. Photocatalytic Dye Degradation from Textile Wastewater: A Review. ACS Omega 2024, 9, 21751–21767. [Google Scholar] [CrossRef] [PubMed]
  111. Balu, K.; Abisheik, T.; Niyitanga, T.; Kumaravel, S.; Ali, W.; Ehtisham Khan, M.; Kashif Ali, S.; Bashiri, A.H.; Zakri, W.; Pandiyan, V. Synthesis and characterization of X (X = Ni or Fe) modified BaTiO3 for effective degradation of Reactive Red 120 dye under UV-A light and its biological activity. Spectrochim. Acta Part A Mol. Biomol. Spectrosc. 2024, 320, 124556. [Google Scholar] [CrossRef]
  112. Jiang, R.; Li, X.; Li, C.; Fang, J.; Xing, Z.; Yu, G. An insight into the diazo dye Direct Red 23 adsorption on Ca-modified biochar in an aqueous solution: An investigation based on DFT and molecular dynamics. Sep. Purif. Technol. 2025, 354, 128655. [Google Scholar] [CrossRef]
  113. Muhtar, S.A.; Amanda, T.; Kurnia, N.R.; Putra, S.E.M.; Khairurrijal, K.; Arif, M.F.; Taher, T.; Rianjanu, A. Complex mixture dye removal using natural zeolite modified polyacrylonitrile/polyvinylidene fluoride (Ze-PAN/PVDF) composite nanofiber membrane via vacuum filtration technique. Mater. Today Commun. 2025, 42, 111357. [Google Scholar] [CrossRef]
  114. GeLe, T.; Wang, Z.; Li, H.; Bu, Z.; Wang, S.; Liu, S.; Liu, Z.; Xu, Z. Elevation-dependence distribution and dissolved organic matter (DOM)-mediated partitioning of polycyclic aromatic hydrocarbons (PAHs) in peatland waters from the Changbai Mountain area. Environ. Res. 2026, 292, 123685. [Google Scholar] [CrossRef]
  115. Czyz, E.; Štorková, M.; Erben, J.; Holec, P.; Švec, F.; Šatínský, D. Hydrophobic and aromatic polymer nanofibers for a spin-filter micro solid phase extraction of polycyclic aromatic hydrocarbons in river water. Adv. Sample Prep. 2026, 17, 100229. [Google Scholar] [CrossRef]
  116. Song, A.; Liu, R.; He, X.; Wei, L. Fabrication of robust polyimide-coated solid phase microextraction fibers for efficient extraction of fifteen polycyclic aromatic hydrocarbons from environmental water††Electronic supplementary information (ESI) available. RSC Adv. 2025, 15, 11826–11834. [Google Scholar] [CrossRef]
  117. Beljin, J.; Đukanović, N.; Anojčić, J.; Simetić, T.; Apostolović, T.; Mutić, S.; Maletić, S. Biochar in the Remediation of Organic Pollutants in Water: A Review of Polycyclic Aromatic Hydrocarbon and Pesticide Removal. Nanomaterials 2025, 15, 26. [Google Scholar] [CrossRef]
  118. Zhang, Y.; Xiong, J.; Zhou, J.; Liu, Y.; Zhang, Q. Polycyclic aromatic hydrocarbon removal from stormwater runoff by bioretention cells: A review. Environ. Sci. Process. Impacts 2026, 28, 11–26. [Google Scholar] [CrossRef]
  119. Zhu, Y.; Ji, S.; Liang, W.; Li, C.; Nie, Y.; Dong, J.; Shi, W.; Ai, S. A low-cost and eco-friendly powder catalyst: Iron and copper nanoparticles supported on biochar/geopolymer for activating potassium peroxymonosulfate to degrade naphthalene in water and soil. Chemosphere 2022, 303, 135185. [Google Scholar] [CrossRef] [PubMed]
  120. Arcelus-Arrillaga, P.; Daud, A.R.M.; Hellgardt, K.; Millan, M. Oxidative cracking of phenanthrene as polycyclic aromatic hydrocarbon model in supercritical water: Reaction pathways at low oxidant concentration. Next Energy 2026, 10, 100480. [Google Scholar] [CrossRef]
  121. Li, C.; Zhu, Y.; Zhang, T.; Nie, Y.; Shi, W.; Ai, S. Iron nanoparticles supported on N-doped carbon foam with honeycomb microstructure: An efficient potassium peroxymonosulfate activator for the degradation of fluoranthene in water and soil. Chemosphere 2022, 286, 131603. [Google Scholar] [CrossRef]
  122. Shi, Y.; Yun, H.; Xie, H.; Li, M.; Ye, J.; Zhang, M.; Yu, M. Risk assessment and capping control of sediment heavy metal pollution in the large drinking water reservoir. Process Saf. Environ. Prot. 2025, 207, 108369. [Google Scholar] [CrossRef]
  123. Wanjiya, M.; Huo, H.-Q.; Shen, Y.; Yin, M.-J.; An, Q.-F. Build water-channel in positively charged nanofiltration membranes for heavy metal ions removal. Sep. Purif. Technol. 2026, 386, 136593. [Google Scholar] [CrossRef]
  124. Jin, Y.-J.; Lin, X.-C.; Ma, L.-F.; Cao, X.-L.; Zhu, Q.-Y.; Xie, X.-Q.; Qiu, S.-Q.; Wu, Q.; Du, S.; Zhou, L.-H. Characteristics, water quality and health risk assessment of heavy metals in groundwater of rural areas in Nanchang, China. J. Food Compos. Anal. 2026, 149, 108793. [Google Scholar] [CrossRef]
  125. Choudhury, T.R.; Moniruzzaman, M.; Anonna, T.A.; Asad, H.A.; Samanta, P.; Islam, F. Evaluation of heavy metal contamination in soil, water, and fish in an industrial zone in Bangladesh: Ecological and potential health risk. Reg. Stud. Mar. Sci. 2025, 86, 104162. [Google Scholar] [CrossRef]
  126. Preonty, N.-E.J.; Hassan, M.N.; Reza, A.H.M.S.; Rasel, M.I.A.; Mahim, M.M.A.; Jannat, M.F.T. Pollution and health risk assessment of heavy metals in surface water of the industrial region in Gazipur, Bangladesh. Environ. Chem. Ecotoxicol. 2025, 7, 527–538. [Google Scholar] [CrossRef]
  127. Qi, W.; Yu, P.; Shi, Y.; Guo, H.; Ahmad, A.; Wei, T. Synergistic extraction-flocculation system enables closed-loop recovery of dyes, salts and thermal energy from textile wastewater. J. Clean. Prod. 2026, 538, 147312. [Google Scholar] [CrossRef]
  128. Yaseen, D.A.; Scholz, M. Textile dye wastewater characteristics and constituents of synthetic effluents: A critical review. Int. J. Environ. Sci. Technol. 2019, 16, 1193–1226. [Google Scholar] [CrossRef]
  129. Rasmussen, K.H.; Setiawati, M.D.; Gomes, K. Water Vulnerability in Dhaka, Narayanganj, and Gazipur Districts of Bangladesh: The Role of Textile Dye Production. Water 2025, 17, 2475. [Google Scholar] [CrossRef]
  130. Chowdhury, M.; Babu, M.S.; Hossain, S.; Mia, R.; Kabir, S.M.M. Optimizing textile dyeing and finishing for improved energy efficiency and sustainability in fleece knitted fabrics. Clean. Energy Syst. 2024, 9, 100154. [Google Scholar] [CrossRef]
  131. Fan, Q.; Hu, Y.; Huang, S.; Guo, Y.; Guo, J.; Liu, F.; Qi, W.; Liu, H.; Qu, J. Anti-epidemic pharmaceuticals predominantly contributed to PPCPs flux in the Yangtze River during 2020. Water Res. 2025, 286, 124228. [Google Scholar] [CrossRef]
  132. Buakaew, T.; Ratanatamskul, C. A review of in-situ technologies for enhancement of the removal of pharmaceuticals and personal care products (PPCPs) and mitigation of membrane fouling in membrane bioreactors. J. Hazard. Mater. Adv. 2026, 21, 100976. [Google Scholar] [CrossRef]
  133. Ravikumar, M.; Velmurugan, K.; John, A.J.; Selvarajan, E. Microalgae to remove pharmaceutical and personal care products (PPCPs) from wastewater. Biocatal. Agric. Biotechnol. 2024, 62, 103415. [Google Scholar] [CrossRef]
  134. Gao, Y.; Yuan, C.; Cheng, S.; Sun, J.; Ouyang, S.; Xue, W.; Zhang, W.; Zhou, L.; Wang, J.; Sun, S. Potential risks and hazards posed by the pressure of pharmaceuticals and personal care products on water treatment plants. Environ. Pollut. 2025, 378, 126344. [Google Scholar] [CrossRef]
  135. Guo, L.; Zhu, Y.; Chang, S.; Yu, W.; Mao, Y. Tracking microplastics in a drinking water supply system proximity to industrial facilities: Occurrence, source identification, and risk assessment. J. Hazard. Mater. 2026, 501, 140739. [Google Scholar] [CrossRef]
  136. Xiang, Q.; Xu, Y.; Hou, J.; Zhang, H.; Lu, Z.; Sun, M.; Wu, C.; Rao, H.; Su, G. Sustainable Gelatin–Sodium alginate aerogel adsorbent for efficient microplastic removal in water. Chem. Eng. Sci. 2025, 324, 123265. [Google Scholar] [CrossRef]
  137. Van Tri, D.; Barcelo, D.; Le Luu, T. The performances of persulfate activators to degrade the persistent organic pollutants in industrial wastewater. Case Stud. Chem. Environ. Eng. 2023, 8, 100539. [Google Scholar] [CrossRef]
  138. Ibrahim, I.A.; Rawindran, H.; Alam, M.M.; Leong, W.H.; Sahrin, N.T.; Ng, H.-S.; Chan, Y.J.; Abdelfattah, E.A.; Lim, J.W.; Aliyu, U.S.a.; et al. Mitigating persistent organic pollutants from marine plastics through enhanced recycling: A review. Environ. Res. 2024, 240, 117533. [Google Scholar] [CrossRef] [PubMed]
  139. Pavithran, R.K.; Reddy, S.G.; Kumar, B.S.; Mary, A.; Kugabalasooriar, S. Smart adsorbents: Innovations and advances in pesticide residue removal from water—A review. HydroResearch 2025. [Google Scholar] [CrossRef]
  140. Huang, Y.; Li, Z.; Fantke, P. Defining pesticide water quality standards for multi-use water resources to protect human health. Sci. Total Environ. 2025, 999, 180344. [Google Scholar] [CrossRef]
  141. Muniz-Junior, G.; Roque, F.d.O.; Pires, A.P.F.; Guariento, R.D. Are lower pesticide doses better? An evolutionary perspective on integrated pest management. Ecol. Model. 2023, 482, 110408. [Google Scholar] [CrossRef]
  142. Fallahi, A.; Taheriyoun, M.; Asghari, K. Water footprint assessment in an industrial symbiosis system based on environmental, economic, and social sustainability indices. J. Clean. Prod. 2024, 454, 142227. [Google Scholar] [CrossRef]
  143. Prajapati, V.; Shah, A.; Patel, R.; Trivedi, N.A.; Som, N.N.; Srivastava, D.N.; Pataniya, P.M.; Sumesh, C.K. Utilizing electrooxidation for textile effluent wastewater treatment and simultaneous electrocatalytic hydrogen production: Transforming waste into energy and promoting water reuse in a circular economy context. Renew. Energy 2024, 237, 121733. [Google Scholar] [CrossRef]
  144. Nidheesh, P.V.; Kumar, A.; Syam Babu, D.; Scaria, J.; Suresh Kumar, M. Treatment of mixed industrial wastewater by electrocoagulation and indirect electrochemical oxidation. Chemosphere 2020, 251, 126437. [Google Scholar] [CrossRef]
  145. Mushtaq, N.; Singh, D.V.; Bhat, R.A.; Dervash, M.A.; Hameed, O.b. Freshwater Contamination: Sources and Hazards to Aquatic Biota. In Fresh Water Pollution Dynamics and Remediation; Qadri, H., Bhat, R.A., Mehmood, M.A., Dar, G.H., Eds.; Springer: Singapore, 2020; pp. 27–50. [Google Scholar]
  146. Schwarzenbach, R.P.; Egli, T.; Hofstetter, T.B.; von Gunten, U.; Wehrli, B. Global Water Pollution and Human Health. Annu. Rev. Environ. Resour. 2010, 35, 109–136. [Google Scholar] [CrossRef]
  147. Ji, S.; Ma, S. The effects of industrial pollution on ecosystem service value: A case study in a heavy industrial area, China. Environ. Dev. Sustain. 2022, 24, 6804–6833. [Google Scholar] [CrossRef]
  148. Zedler, J.B.; Kercher, S. WETLAND RESOURCES: Status, Trends, Ecosystem Services, and Restorability. Annu. Rev. Environ. Resour. 2005, 30, 39–74. [Google Scholar] [CrossRef]
  149. Wurtsbaugh, W.A.; Paerl, H.W.; Dodds, W.K. Nutrients, eutrophication and harmful algal blooms along the freshwater to marine continuum. WIREs Water 2019, 6, e1373. [Google Scholar] [CrossRef]
  150. Lemessa, F.; Simane, B.; Seyoum, A.; Gebresenbet, G. Assessment of the Impact of Industrial Wastewater on the Water Quality of Rivers around the Bole Lemi Industrial Park (BLIP), Ethiopia. Sustainability 2023, 15, 4290. [Google Scholar] [CrossRef]
  151. Le, T.V.; Nguyen, B.T. Heavy metal pollution in surface water bodies in provincial Khanh Hoa, Vietnam: Pollution and human health risk assessment, source quantification, and implications for sustainable management and development. Environ. Pollut. 2024, 343, 123216. [Google Scholar] [CrossRef]
  152. Li, J.; Li, X.; Huang, Y.; Zhang, D.; Lv, F.; Huang, P. Dynamic leaching behaviors of heavy metals from recycled coal gangue aggregate under loading conditions during solid backfill mining. Environ. Pollut. 2024, 362, 125028. [Google Scholar] [CrossRef]
  153. Kljaković-Gašpić, Z.; Dvoršćak, M.; Orct, T.; Sekovanić, A.; Klinčić, D.; Jagić, K.; Šebešćen, D.; Klasiček, E.; Zanella, D. Metal(loid)s and persistent organic pollutants in yellow European eel from the Raša River, Croatia. Mar. Pollut. Bull. 2023, 187, 114527. [Google Scholar] [CrossRef] [PubMed]
  154. Barhoumi, B.; Beldean-Galea, M.S.; Al-Rawabdeh, A.M.; Roba, C.; Martonos, I.M.; Bălc, R.; Kahlaoui, M.; Touil, S.; Tedetti, M.; Driss, M.R.; et al. Occurrence, distribution and ecological risk of trace metals and organic pollutants in surface sediments from a Southeastern European river (Someşu Mic River, Romania). Sci. Total Environ. 2019, 660, 660–676. [Google Scholar] [CrossRef] [PubMed]
  155. Zheng, Y.; Wang, Q.; Zhang, X.; Yu, J.; Li, C.; Chen, L.; Liu, Y. Nitrogen and Phosphorus Retention Risk Assessment in a Drinking Water Source Area under Anthropogenic Activities. Remote Sens. 2022, 14, 2070. [Google Scholar] [CrossRef]
  156. Irimia, O.; Gaspar, E.; Stanciu, M.; Moșneguțu, E.; Bârsan, N. Optimizing Nitrogen and Phosphorus Removal from Wastewater in the Context of a Sustainable Economy. Water 2024, 16, 1585. [Google Scholar] [CrossRef]
  157. Jan, A.T.; Azam, M.; Siddiqui, K.; Ali, A.; Choi, I.; Haq, Q.M.R. Heavy Metals and Human Health: Mechanistic Insight into Toxicity and Counter Defense System of Antioxidants. Int. J. Mol. Sci. 2015, 16, 29592–29630. [Google Scholar] [CrossRef]
  158. Gonsioroski, A.; Mourikes, V.E.; Flaws, J.A. Endocrine Disruptors in Water and Their Effects on the Reproductive System. Int. J. Mol. Sci. 2020, 21, 1929. [Google Scholar] [CrossRef]
  159. Sonone, S.; Jadhav, S.; Singh Sankhla, M.; Kumar, R. Water Contamination by Heavy Metals and their Toxic Effect on Aquaculture and Human Health through Food Chain. Lett. Appl. NanoBioSci. 2020, 10, 2148–2166. [Google Scholar] [CrossRef]
  160. Bhat, A.A.; Ahmed, M.; Elboughdiri, N.; Singh, J.; Kriaa, K.; Maatki, C.; Hadrich, B.; Wani, A.K. Persistent organic pollutants (POP, s) in the 21st century: Emerging remediation technologies and future directions. Microchem. J. 2026, 221, 117041. [Google Scholar] [CrossRef]
  161. Singh, K.K.; Tewari, G.; Kumar, S.; Busa, R.; Chaturvedi, A.; Rathore, S.S.; Singh, R.K.; Gangwar, A. Understanding urban groundwater pollution in the Upper Gangetic Alluvial Plains of northern India with multiple industries and their impact on drinking water quality and associated health risks. Groundw. Sustain. Dev. 2023, 21, 100902. [Google Scholar] [CrossRef]
  162. Joseph, S.J.P.; K, J.; Boopathi, S.K.; P, A.P.R.; S, P.; Subramani, N. Ecological dynamics and biodegradation potential of freshwater epiplastic microalgae: A sustainable solution for plastic waste management. J. Water Process Eng. 2025, 77, 108521. [Google Scholar] [CrossRef]
  163. Yin, Z.; Zhao, Y. Microplastics pollution in freshwater sediments: The pollution status assessment and sustainable management measures. Chemosphere 2023, 314, 137727. [Google Scholar] [CrossRef]
  164. Roy, M.; Shamim, F. Research on the Impact of Industrial Pollution on River Ganga: A Review. Int. J. Prev. Control Ind. Pollut. 2020, 6, 43–51. [Google Scholar]
  165. Ochieng, G.; Seanego, E.; Nkwonta, O. Impacts of mining on water resources in South Africa: A review. Sci. Res. Essays 2010, 5, 3351–3357. [Google Scholar]
  166. Voulvoulis, N.; Arpon, K.D.; Giakoumis, T. The EU Water Framework Directive: From great expectations to problems with implementation. Sci. Total Environ. 2017, 575, 358–366. [Google Scholar] [CrossRef]
  167. Agrahari, S.; Kumar, S. Emerging and futuristic phyto-technologies for sustainable wastewater treatment with resource recovery and economical aspects. J. Water Process Eng. 2024, 65, 105753. [Google Scholar] [CrossRef]
  168. Zhuang, Y.; Zhang, L.; Chiu, Y.-h.; Guo, Z.; Chu, Y.; Du, X. Evaluating the recycling efficiency of industrial water use systems in China: Basin differences and factor analysis. J. Environ. Manag. 2022, 316, 115313. [Google Scholar] [CrossRef]
  169. Kumar, A.; Thakur, A. Chapter 7—Industrial water conservation by water footprint and Sustainable Development Goals. In Current Directions in Water Scarcity Research; Bandh, S.A., Malla, F.A., Eds.; Elsevier: Amsterdam, The Netherlands, 2024; Volume 8, pp. 87–117. [Google Scholar]
  170. Zhou, Z.; Liu, J.; Zhou, N.; Zhang, T.; Zeng, H. Does the “10-Point Water Plan” reduce the intensity of industrial water pollution? Quasi-experimental evidence from China. J. Environ. Manag. 2021, 295, 113048. [Google Scholar] [CrossRef] [PubMed]
  171. Karkou, E.; Teo, C.J.; Savvakis, N.; Poinapen, J.; Arampatzis, G. Industrial circular water use practices through the application of a conceptual water efficiency framework in the process industry. J. Environ. Manag. 2024, 370, 122596. [Google Scholar] [CrossRef]
  172. Singh, B.J.; Chakraborty, A.; Sehgal, R. A systematic review of industrial wastewater management: Evaluating challenges and enablers. J. Environ. Manag. 2023, 348, 119230. [Google Scholar] [CrossRef]
  173. Ahmed, S.F.; Kumar, P.S.; Kabir, M.; Zuhara, F.T.; Mehjabin, A.; Tasannum, N.; Hoang, A.T.; Kabir, Z.; Mofijur, M. Threats, challenges and sustainable conservation strategies for freshwater biodiversity. Environ. Res. 2022, 214, 113808. [Google Scholar] [CrossRef]
  174. Folke, C.; Carpenter, S.; Walker, B.; Scheffer, M.; Elmqvist, T.; Gunderson, L.; Holling, C.S. Regime Shifts, Resilience, and Biodiversity in Ecosystem Management. Annu. Rev. Ecol. Evol. Syst. 2004, 35, 557–581. [Google Scholar] [CrossRef]
  175. Vörösmarty, C.J.; McIntyre, P.B.; Gessner, M.O.; Dudgeon, D.; Prusevich, A.; Green, P.; Glidden, S.; Bunn, S.E.; Sullivan, C.A.; Liermann, C.R.; et al. Global threats to human water security and river biodiversity. Nature 2010, 467, 555–561. [Google Scholar] [CrossRef]
  176. Gleick, P.H. Water Use. Annu. Rev. Environ. Resour. 2003, 28, 275–314. [Google Scholar] [CrossRef]
  177. Helmer, R.; Hespanhol, I.; World Health Organization. Water Pollution Control: A Guide to the Use of Water Quality Management Principles; World Health Organization: Geneva, Switzerland, 1997. [Google Scholar]
  178. Molinos-Senante, M.; Donoso, G. Water scarcity and affordability in urban water pricing: A case study of Chile. Util. Policy 2016, 43, 107–116. [Google Scholar] [CrossRef]
  179. Shi, H.; Chertow, M.; Song, Y. Developing country experience with eco-industrial parks: A case study of the Tianjin Economic-Technological Development Area in China. J. Clean. Prod. 2010, 18, 191–199. [Google Scholar] [CrossRef]
  180. Lefebvre, O. Beyond NEWater: An insight into Singapore’s water reuse prospects. Curr. Opin. Environ. Sci. Health 2018, 2, 26–31. [Google Scholar] [CrossRef]
  181. Abdelfattah, I.; El-Shamy, A.M. Review on the escalating imperative of zero liquid discharge (ZLD) technology for sustainable water management and environmental resilience. J. Environ. Manag. 2024, 351, 119614. [Google Scholar] [CrossRef]
  182. de Oliveira Neto, G.C.; Correia, J.M.F.; Tucci, H.N.P.; Librantz, A.F.H.; Giannetti, B.F.; de Almeida, C.M.V.B. Sustainable Resilience Degree assessment of the textile industrial by size: Incremental change in cleaner production practices considering circular economy. J. Clean. Prod. 2022, 380, 134633. [Google Scholar] [CrossRef]
  183. Mora-Contreras, R.; Ormazabal, M.; Hernández-Salazar, G.; Torres-Guevara, L.E.; Mejia-Villa, A.; Prieto-Sandoval, V.; Carrillo-Hermosilla, J. Do environmental and cleaner production practices lead to circular and sustainability performance? Evidence from Colombian manufacturing firms. Sustain. Prod. Consum. 2023, 40, 77–88. [Google Scholar] [CrossRef]
  184. Wei Lun Lee, A.; Ying Chung, S.; Shee Tan, Y.; Mun Ho Koh, S.; Feng Lu, W.; Sze Choong Low, J. Enhancing the environmental sustainability of product through ecodesign: A systematic review. J. Eng. Des. 2023, 34, 814–843. [Google Scholar] [CrossRef]
  185. Idoko, F.; Ezeamii, G.; Ojochogwu, O. Green chemistry in manufacturing: Innovations in reducing environmental impact. World J. Adv. Res. Rev. 2024, 23, 2826–2841. [Google Scholar] [CrossRef]
  186. Sheldon, R.A. E factors, green chemistry and catalysis: An odyssey. Chem. Commun. 2008, 29, 3352–3365. [Google Scholar] [CrossRef]
  187. Mishra, M.; Sharma, M.; Dubey, R.; Kumari, P.; Ranjan, V.; Pandey, J. Green synthesis interventions of pharmaceutical industries for sustainable development. Curr. Res. Green Sustain. Chem. 2021, 4, 100174. [Google Scholar] [CrossRef]
  188. Quallich, G.J. Development of the commercial process for Zoloft®/sertraline. Chirality 2005, 17, S120–S126. [Google Scholar] [CrossRef]
  189. Savile, C.K.; Janey, J.M.; Mundorff, E.C.; Moore, J.C.; Tam, S.; Jarvis, W.R.; Colbeck, J.C.; Krebber, A.; Fleitz, F.J.; Brands, J.; et al. Biocatalytic Asymmetric Synthesis of Chiral Amines from Ketones Applied to Sitagliptin Manufacture. Science 2010, 329, 305–309. [Google Scholar] [CrossRef]
  190. Sheldon, R.A. Green and sustainable manufacture of chemicals from biomass: State of the art. Green Chem. 2014, 16, 950–963. [Google Scholar] [CrossRef]
  191. Plutschack, M.B.; Pieber, B.; Gilmore, K.; Seeberger, P.H. The Hitchhiker’s Guide to Flow Chemistry. Chem. Rev. 2017, 117, 11796–11893. [Google Scholar] [CrossRef]
  192. Satyro, W.C.; Contador, J.C.; Monken, S.F.d.P.; Lima, A.F.d.; Soares Junior, G.G.; Gomes, J.A.; Neves, J.V.S.; do Nascimento, J.R.; de Araújo, J.L.; Correa, E.d.S.; et al. Industry 4.0 Implementation Projects: The Cleaner Production Strategy—A Literature Review. Sustainability 2023, 15, 2161. [Google Scholar] [CrossRef]
  193. Pendar, M.-R.; Rodrigues, F.; Páscoa, J.C.; Lima, R. Review of coating and curing processes: Evaluation in automotive industry. Phys. Fluids 2022, 34, 101301. [Google Scholar] [CrossRef]
  194. Jahan, N.; Tahmid, M.; Shoronika, A.Z.; Fariha, A.; Roy, H.; Pervez, M.N.; Cai, Y.; Naddeo, V.; Islam, M.S. A Comprehensive Review on the Sustainable Treatment of Textile Wastewater: Zero Liquid Discharge and Resource Recovery Perspectives. Sustainability 2022, 14, 15398. [Google Scholar] [CrossRef]
  195. Moreira, V.R.; Lebron, Y.A.R.; Couto, C.F.; Maia, A.; Moravia, W.G.; Amaral, M.C.S. Process development for textile wastewater treatment towards zero liquid discharge: Integrating membrane separation process and advanced oxidation techniques. Process Saf. Environ. Prot. 2022, 157, 537–546. [Google Scholar] [CrossRef]
  196. Valenzuela-Venegas, G.; Vera-Hofmann, G.; Díaz-Alvarado, F.A. Design of sustainable and resilient eco-industrial parks: Planning the flows integration network through multi-objective optimization. J. Clean. Prod. 2020, 243, 118610. [Google Scholar] [CrossRef]
  197. Afzal, M.; Arslan, M.; Younus, S.; Müller, J.A.; Usman, M.; Yasin, M.; Mehmood, M.A.; Mehdi, T.; Islam, E.; Tauseef, M.; et al. A nature-based closed-loop wastewater treatment system at vehicle-washing facilities: From linear to circular economy. iScience 2024, 27, 109361. [Google Scholar] [CrossRef] [PubMed]
  198. Copeland, C. Clean Water Act: A Summary of the Law; U.S. Congressional Research Service: Washington, DC, USA, 2012; pp. 115–130. [Google Scholar]
  199. Charles, A.F.; Marty, D.M. History of the Clean Water Act. Water Resour. IMPACT 2001, 3, 26–30. [Google Scholar]
  200. Ritter, L.; Solomon, K.R.; Forget, J. Persistent Organic Pollutants: An Assessment Report on DDT, Aldrin, Dieldrin, Endrin, Chlordane, Heptachlor, Hexachlorobenzene, Mirex, Toxaphene, PCBs, Dioxins, and Furans. In Report for the International Programme on Chemical Safety (IPCS) Within the Framework of the Inter-Organization Programme for the Sound Management of Chemicals; International Programme on Chemical Safety (IPCS): Geneva, Switzerland, 2005. [Google Scholar]
  201. Rasmussen, S.L.; Alex, G.; Crockett, T.P. Waive goodbye to Aerospace NESHAP violations: A successful study in hazardous material management. Met. Finish. 2001, 99, 30–36. [Google Scholar] [CrossRef]
  202. Cheng, Y.; Nakajima, K.; Nansai, K.; Seccatore, J.; Veiga, M.M.; Takaoka, M. Examining the inconsistency of mercury flow in post-Minamata Convention global trade concerning artisanal and small-scale gold mining activity. Resour. Conserv. Recycl. 2022, 185, 106461. [Google Scholar] [CrossRef]
  203. Dijkmans, R. Methodology for selection of best available techniques (BAT) at the sector level. J. Clean. Prod. 2000, 8, 11–21. [Google Scholar] [CrossRef]
  204. Fijał, T. An environmental assessment method for cleaner production technologies. J. Clean. Prod. 2007, 15, 914–919. [Google Scholar] [CrossRef]
  205. Vela Almeida, D.; Kolinjivadi, V.; Ferrando, T.; Roy, B.; Herrera, H.; Vecchione Gonçalves, M.; Van Hecken, G. The “Greening” of Empire: The European Green Deal as the EU first agenda. Political Geogr. 2023, 105, 102925. [Google Scholar] [CrossRef]
  206. Biancalani, F.; Gnecco, G.; Metulini, R.; Riccaboni, M. The impact of the European Union emissions trading system on carbon dioxide emissions: A matrix completion analysis. Sci. Rep. 2024, 14, 19676. [Google Scholar] [CrossRef]
  207. Sharma, A.K.; Choudhary, H.; Chauhan, P.; Chaliha, J. Nanomaterials for the remediation of microplastics in wastewater. Nano Trends 2025, 12, 100152. [Google Scholar] [CrossRef]
  208. Bhagya, L.; Upeksha, S.T.; Kirthika, V.; Galpaya, C.; Koswattage, K.R.; Wijesekara, H.; Perera, V.; Ireshika, W.A.; Chamanee, G.; Rajapaksha, A.U. Nanomaterials for microplastics remediation in wastewater: A viable step towards cleaner water. J. Hazard. Mater. Adv. 2025, 19, 100773. [Google Scholar] [CrossRef]
  209. Krishnan, A.; Sundaram, T.; Nagappan, B.; Devarajan, Y.; Bhumika. Integrating artificial intelligence in nanomembrane systems for advanced water desalination. Results Eng. 2024, 24, 103321. [Google Scholar] [CrossRef]
  210. Stankovic, T.; Hovi, J.; Skodvin, T. The Paris Agreement’s inherent tension between ambition and compliance. Humanit. Soc. Sci. Commun. 2023, 10, 550. [Google Scholar] [CrossRef]
  211. Hassan, S.; Thacharodi, A.; Priya, A.; Meenatchi, R.; Hegde, T.A.; R, T.; Nguyen, H.T.; Pugazhendhi, A. Endocrine disruptors: Unravelling the link between chemical exposure and Women’s reproductive health. Environ. Res. 2024, 241, 117385. [Google Scholar] [CrossRef] [PubMed]
  212. Schirinzi, G.F.; Pérez-Pomeda, I.; Sanchís, J.; Rossini, C.; Farré, M.; Barceló, D. Cytotoxic effects of commonly used nanomaterials and microplastics on cerebral and epithelial human cells. Environ. Res. 2017, 159, 579–587. [Google Scholar] [CrossRef]
  213. Narassimhan, E.; Gallagher, K.S.; Koester, S.; Alejo, J.R. Carbon pricing in practice: A review of existing emissions trading systems. Clim. Policy 2018, 18, 967–991. [Google Scholar] [CrossRef]
  214. Kuppan, N.; Padman, M.; Mahadeva, M.; Srinivasan, S.; Devarajan, R. A comprehensive review of sustainable bioremediation techniques: Eco friendly solutions for waste and pollution management. Waste Manag. Bull. 2024, 2, 154–171. [Google Scholar] [CrossRef]
  215. Mazur, R.; Kowalewski, Z.; Głowienka, E.; Santos, L.; Jakubiak, M. Sustainability in Aquatic Ecosystem Restoration: Combining Classical and Remote Sensing Methods for Effective Water Quality Management. Sustainability 2024, 16, 3716. [Google Scholar] [CrossRef]
  216. Bharathi, D.; Nandagopal, J.G.T.; Ranjithkumar, R.; Gupta, P.K.; Djearamane, S. Microbial approaches for sustainable remediation of dye-contaminated wastewater: A review. Arch. Microbiol. 2022, 204, 169. [Google Scholar] [CrossRef]
  217. Mohanty, S.S.; Kumar, A. Enhanced degradation of anthraquinone dyes by microbial monoculture and developed consortium through the production of specific enzymes. Sci. Rep. 2021, 11, 7678. [Google Scholar] [CrossRef]
  218. Liaqat, I.; Khalid, A.; Rubab, S.; Rashid, F.; Latif, A.A.; Naseem, S.; Bibi, A.; Khan, B.N.; Ansar, W.; Javed, A.; et al. In Vitro Biofilm-Mediated Biodegradation of Pesticides and Dye-Contaminated Effluents Using Bacterial Biofilms. Microorganisms 2023, 11, 2163. [Google Scholar] [CrossRef] [PubMed]
  219. Wu, H.; Wang, R.; Yan, P.; Wu, S.; Chen, Z.; Zhao, Y.; Cheng, C.; Hu, Z.; Zhuang, L.; Guo, Z.; et al. Constructed wetlands for pollution control. Nat. Rev. Earth Environ. 2023, 4, 218–234. [Google Scholar] [CrossRef]
  220. Richardson, C.J.; Flanagan, N.E. Water quality and wetland vegetation responses to water level variations in a university stormwater reuse reservoir: Nature-based approaches to campus water sustainability. Sci. Total Environ. 2024, 948, 174616. [Google Scholar] [CrossRef] [PubMed]
  221. El Hanandeh, A.; Akrami, K. Assessment of Nutrient Removal in Surface Flow Constructed Wetland Treating Secondary Effluent with Low Organic, Nitrogen and Phosphorus Loads. Environments 2023, 10, 89. [Google Scholar] [CrossRef]
  222. Qu, X.; Alvarez, P.J.J.; Li, Q. Applications of nanotechnology in water and wastewater treatment. Water Res. 2013, 47, 3931–3946. [Google Scholar] [CrossRef]
  223. Liu, W.-J.; Qian, T.-T.; Jiang, H. Bimetallic Fe nanoparticles: Recent advances in synthesis and application in catalytic elimination of environmental pollutants. Chem. Eng. J. 2014, 236, 448–463. [Google Scholar] [CrossRef]
  224. Li, Z.; Zhao, Y.; Li, Y.; Lu, J.; Wang, M. Reverse osmosis process combining energy consumption analysis and mass transfer in the concentration of lithium-enriched brine. Desalination 2025, 594, 118309. [Google Scholar] [CrossRef]
  225. Shen, S.; Tian, L.; Jin, L.; Ma, J.; Chen, M.; Xiong, J. Arsenic(V) removal from water using polyelectrolyte enhanced ultrafiltration with poly(dimethyldiallylammonium chloride) (PDADMAC): Ion-selectivity based modeling and electric field influence. J. Environ. Chem. Eng. 2024, 12, 114686. [Google Scholar] [CrossRef]
  226. Sawadogo, B.; Nouhou Moussa, A.W.; Konaté, Y.; Tiendrebeogo, C.; Sossou, S.; Sidibé, S.D.S.; Karambiri, H. Integrated coagulation-flocculation with nanofiltration and reverse osmosis membrane for treating sugar cane industry effluent. Heliyon 2024, 10, e40805. [Google Scholar] [CrossRef] [PubMed]
  227. Jalali, S.; Nour-Mohammad, M.; Fakhroleslam, M. Toward circular water economy in mineral processing: Technological state of the art review and challenges analysis. Sustain. Mater. Technol. 2025, 46, e01733. [Google Scholar] [CrossRef]
  228. Castillo-Ospina, D.A.; Pinto, M.R.; Ometto, A.R. Waste picker organizations in recycling systems in latin american cases towards social inclusion in circular economy. Sustain. Futures 2025, 10, 101549. [Google Scholar] [CrossRef]
  229. Lalhmangaihzuala, S.; Rongpipi, M.; Vanlaldinpuia, K.; Rokhum, S.L. Chemo-catalytic recycling of PET waste: Progress and prospects for circular economy and valorization. Next Mater. 2025, 9, 101111. [Google Scholar] [CrossRef]
  230. Leng, Q.; Li, F.; Luo, Z.; Wang, L.; Zheng, K.; Wang, Z.; Wu, X. Simultaneous hydrogen generation and wastewater purification: An innovative closed-loop reverse electrodialysis system incorporating air–gap diffusion distillation. Energy Convers. Manag. 2024, 322, 119209. [Google Scholar] [CrossRef]
  231. López Zavala, M.Á. Implementation of circular economy of water in the automobile batteries recycling industry. Water Resour. Ind. 2025, 34, 100330. [Google Scholar] [CrossRef]
  232. Stankiewicz, K.; Boroń, P.; Prajsnar, J.; Żelazny, M.; Heliasz, M.; Hunter, W.; Lenart-Boroń, A. Second life of water and wastewater in the context of circular economy—Do the membrane bioreactor technology and storage reservoirs make the recycled water safe for further use? Sci. Total Environ. 2024, 921, 170995. [Google Scholar] [CrossRef]
  233. Robles, Á.; Aguado, D.; Barat, R.; Borrás, L.; Bouzas, A.; Giménez, J.B.; Martí, N.; Ribes, J.; Ruano, M.V.; Serralta, J.; et al. New frontiers from removal to recycling of nitrogen and phosphorus from wastewater in the Circular Economy. Bioresour. Technol. 2020, 300, 122673. [Google Scholar] [CrossRef] [PubMed]
  234. Guo, Y.; Yuan, D.; Ren, Y.; Wu, F.; Niu, Q.; Chen, D. Multi field coupled three-dimensional electrochemical system driven collaborative transformation of wastewater: Zero emission closed-loop and high-value resource recovery. Reg. Stud. Mar. Sci. 2025, 90, 104416. [Google Scholar] [CrossRef]
  235. Ranjan, V.P.; Sharma, H.B.; Goel, S. Urban mining for resource recovery from legacy waste: Advancing circular economy practices for sustainable waste management. J. Environ. Manag. 2026, 397, 128258. [Google Scholar] [CrossRef]
  236. Bosco, C.; Raspati, G.S.; Maurin, N.; Helness, H. A systematic literature review on resource recovery toward symbiotic circular economy solutions in the water sector. J. Environ. Manag. 2025, 393, 127298. [Google Scholar] [CrossRef]
  237. Kurniawan, T.A.; Bustos-Terrones, Y.A.; Loaiza, J.G.; Dissanayake, K.K.; Onn, C.W.; Abass, K.S.; Jumaniyozov, K.; Oktriono, K.; Wong, W.K.; Kusworo, T.D.; et al. Applying nutrient recovery from unused wastewater to overcome fertilizer shortage for global food security. J. Environ. Manag. 2025, 394, 127543. [Google Scholar] [CrossRef]
  238. Islam, M.; Saha, A.; Muenich, R.; Westerhoff, P. Closing the phosphorus loop: A spatial analysis of potential for wastewater-derived fertilizers to meet US agricultural demand. Sci. Total Environ. 2025, 1006, 180851. [Google Scholar] [CrossRef] [PubMed]
  239. Ordóñez, A.; Solís, I.; González, A.; Iglesias-Rodríguez, F.J.; Álvarez, R. Thermal use of urban wastewater: Some case studies. Energy Rep. 2025, 14, 5883–5892. [Google Scholar] [CrossRef]
  240. Alshamrani, A.; Abbas, H.A.; Alkhayer, A.G.; Mausam, K.; Abdullah, S.I.; Alsehli, M.; Rajab, H.; Ahmed, M.; El-Shafay, A.S.; Kassim, M. Application of an AI-based optimal control framework in smart buildings using borehole thermal energy storage combined with wastewater heat recovery. J. Energy Storage 2024, 101, 113824. [Google Scholar] [CrossRef]
  241. Das, A.K.; Hossain, M.F.; Khan, B.U.; Rahman, M.M.; Asad, M.A.Z.; Akter, M. Circular economy: A sustainable model for waste reduction and wealth creation in the textile supply chain. SPE Polym. 2025, 6, e10171. [Google Scholar] [CrossRef]
  242. Maldini, I.; Klepp, I.G.; Laitala, K. The environmental impact of product lifetime extension: A literature review and research agenda. Sustain. Prod. Consum. 2025, 56, 561–578. [Google Scholar] [CrossRef]
  243. Khan, Z.A.; Chowdhury, S.R.; Mitra, B.; Mozumder, M.S.; Elhaj, A.I.; Salami, B.A.; Rahman, M.M.; Rahman, S.M. Analysis of industrial symbiosis case studies and its potential in Saudi Arabia. J. Clean. Prod. 2023, 385, 135536. [Google Scholar] [CrossRef]
  244. Ramin, E.; Faria, L.; Gargalo, C.L.; Ramin, P.; Flores-Alsina, X.; Andersen, M.M.; Gernaey, K.V. Water innovation in industrial symbiosis—A global review. J. Environ. Manag. 2024, 349, 119578. [Google Scholar] [CrossRef]
  245. Gulipac, S. Industrial Symbiosis: Building on Kalundborg’s waste management experience. Renew. Energy Focus 2016, 17, 25–27. [Google Scholar] [CrossRef]
  246. Kim, H.-W.; Dong, L.; Choi, A.E.S.; Fujii, M.; Fujita, T.; Park, H.-S. Co-benefit potential of industrial and urban symbiosis using waste heat from industrial park in Ulsan, Korea. Resour. Conserv. Recycl. 2018, 135, 225–234. [Google Scholar] [CrossRef]
  247. Kuo, T.-C.; Chen, H.Y.; Rahmat, D.A.; Rumanti, A.A. Industrial Symbiosis Practice for Stakeholders: Insights from Textile Practices for Sectoral Transformation. Int. J. Precis. Eng. Manuf.-Green Technol. 2025, 12, 1939–1950. [Google Scholar] [CrossRef]
  248. Nahar, N.; Haque, M.S.; Haque, S.E. Groundwater conservation, and recycling and reuse of textile wastewater in a denim industry of Bangladesh. Water Resour. Ind. 2024, 31, 100249. [Google Scholar] [CrossRef]
Figure 1. Conceptual overview of industrial chemical pollutants, their impacts on freshwater systems, and sustainable mitigation solutions.
Figure 1. Conceptual overview of industrial chemical pollutants, their impacts on freshwater systems, and sustainable mitigation solutions.
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Table 2. Summary of previous review studies addressing industrial chemical pollution in freshwater systems.
Table 2. Summary of previous review studies addressing industrial chemical pollution in freshwater systems.
ReferenceFocus of the ReviewPollutants CoveredSustainable Approaches DiscussedKey Limitation
Pan et al., 2023 [39]Removal technologies for microplastics in aquatic environmentsMicroplasticsFiltration, coagulation, membrane processesFocus mainly on microplastic removal technologies
Li et al., 2023 [40]Ecotoxicological effects of microplastics in aquatic ecosystemsMicroplasticsEnvironmental monitoring and risk assessmentLimited discussion of treatment technologies
Meng et al., 2025 [41]Sources, hazards, and removal methods of microplasticsMicroplasticsAdsorption, filtration, biological removalFocus restricted to microplastics
Ahammad et al., 2023 [42]Removal of pharmaceutical emerging contaminants from wastewaterPharmaceuticals and emerging contaminantsAdsorption, nanomaterials, advanced treatmentFocus limited to pharmaceutical contaminants
Singh et al., 2022 [43]Biological remediation of dyes and heavy metals in wastewaterTextile dyes, heavy metalsBioremediation and biological treatment processesLimited discussion of regulatory frameworks
Oladimeji et al., 2024 [44]Industrial wastewater contamination by heavy metalsHeavy metalsAdsorption, coagulation, membrane filtrationFocus on heavy metals only
Berríos-Rolón et al., 2025 [45]Sources, environmental distribution, and ecotoxicological impacts of PAHs in freshwater systemsPolycyclic aromatic hydrocarbons (PAHs)Bioremediation, adsorption, advanced oxidation processes, and nature-based remediation strategiesFocus mainly on PAH occurrence and ecological impacts
This reviewIntegrated assessment of industrial freshwater pollution and sustainable mitigation strategiesHeavy metals, POPs, microplastics, PPCPs, pesticides, textile dyesRegulatory frameworks, green technologies, circular economy approachesProvides integrated synthesis across pollutants and mitigation strategies
Table 3. Key sources, environmental impacts, and removal strategies for heavy metal in freshwater systems.
Table 3. Key sources, environmental impacts, and removal strategies for heavy metal in freshwater systems.
Heavy MetalIndustrial SourceEnvironmental ImpactSustainable Treatment MethodsReferences
LeadBattery manufacturing, miningNeurotoxicity, bioaccumulation in aquatic organismsAdsorption using biochar/activated carbon; membrane filtration[52]
CadmiumElectroplating, fertilizers, miningToxicity to aquatic life, sediment accumulationBiosorption using agricultural residues; adsorption using biochar[53]
MercuryCoal combustion, chlor-alkali industryBiomagnification in aquatic food websAdsorption using natural sorbents; phytoremediation[54]
ChromiumLeather tanning, metal finishingCarcinogenic effects, aquatic toxicityMembrane filtration; electrochemical treatment[55]
Table 4. Key sources, environmental impacts, and removal strategies for microplastics in freshwater systems.
Table 4. Key sources, environmental impacts, and removal strategies for microplastics in freshwater systems.
Source of MicroplasticsEntry Pathway to FreshwaterEnvironmental ImpactSustainable Removal StrategiesReferences
Textile fibersWastewater discharge from washingIngestion by aquatic organismsMembrane filtration, membrane bioreactors[64,66]
Personal care products (microbeads)Domestic wastewaterBioaccumulation in aquatic food chainsCoagulation–flocculation, filtration[60]
Tire wear particlesRoad runoffToxic effects due to additivesSedimentation and flotation technologies[41]
Plastic waste fragmentationSurface runoffHabitat contaminationBio-based filtration materials[67]
Table 5. Key sources, environmental impacts, and removal strategies for persistent organic pollutants in freshwater systems.
Table 5. Key sources, environmental impacts, and removal strategies for persistent organic pollutants in freshwater systems.
POP TypeMain Industrial SourcesEnvironmental ImpactSustainable Treatment ApproachesReferences
PCBsElectrical equipment manufacturingBioaccumulation in aquatic organismsAdsorption using activated carbon/biochar[76]
DioxinsWaste incinerationLong-term ecosystem toxicityAdvanced oxidation processes[77]
Organochlorine pesticidesChemical industriesPersistent contamination of sedimentsBioremediation and phytoremediation[78]
Table 6. Key sources, environmental impacts, and removal strategies for pharmaceuticals and personal care products in freshwater systems.
Table 6. Key sources, environmental impacts, and removal strategies for pharmaceuticals and personal care products in freshwater systems.
PPCP CategoryMajor SourcesEnvironmental RisksSustainable Treatment TechnologiesReferences
AntibioticsHospitals, livestock productionAntibiotic resistanceMembrane bioreactors[89]
HormonesDomestic wastewaterEndocrine disruption in aquatic speciesAdvanced oxidation processes[90]
Cosmetic ingredientsPersonal care productsBioaccumulationHybrid biological–membrane treatment[91]
Painkillers/analgesicsPharmaceutical industriesChronic toxicityAdsorption using activated carbon[92]
Table 7. Key sources, environmental impacts, and removal strategies for pesticides in freshwater systems.
Table 7. Key sources, environmental impacts, and removal strategies for pesticides in freshwater systems.
Pesticide TypeMajor SourcesEnvironmental ImpactSustainable Treatment StrategiesReferences
HerbicidesAgricultural runoffToxicity to aquatic plantsBiochar adsorption[100]
InsecticidesCrop protection chemicalsToxicity to aquatic invertebratesPhotocatalytic degradation[101]
FungicidesAgricultural useBioaccumulation in sedimentsConstructed wetlands[102]
Industrial pesticide wasteChemical production facilitiesLong-term ecosystem contaminationBioremediation[103]
Table 8. Key sources, environmental impacts, and removal strategies for textile dyes and auxiliaries in freshwater systems.
Table 8. Key sources, environmental impacts, and removal strategies for textile dyes and auxiliaries in freshwater systems.
Dye TypeIndustrial SourceEnvironmental ImpactSustainable Treatment MethodsReferences
Reactive dyesCotton dyeing processesHigh COD and water colorationBiological degradation[111]
Direct dyesTextile finishingReduced light penetration in waterAdsorption using biochar[112]
Disperse dyesSynthetic fiber dyeingToxicity to aquatic organismsMembrane filtration[113]
Dye auxiliariesTextile processing chemicalsIncreased chemical load in wastewaterAdvanced oxidation processes[106]
Table 9. Key sources, environmental impacts, and removal strategies for polycyclic aromatic hydrocarbons in freshwater systems.
Table 9. Key sources, environmental impacts, and removal strategies for polycyclic aromatic hydrocarbons in freshwater systems.
PAH CompoundIndustrial SourceEnvironmental ImpactSustainable Treatment MethodsReferences
NaphthalenePetroleum refining, fossil fuel combustionToxicity to aquatic organismsBiochar adsorption; microbial degradation[119]
PhenanthreneCoal combustion, petroleum processingBioaccumulation in sedimentsBioremediation; advanced oxidation processes[120]
FluorantheneVehicle emissions, industrial combustionPersistent sediment contaminationActivated carbon adsorption; photocatalysis[121]
Table 10. Industrial Chemical Pollutants in Freshwater Systems: Sources, Sustainable approaches, and Environmental benefits.
Table 10. Industrial Chemical Pollutants in Freshwater Systems: Sources, Sustainable approaches, and Environmental benefits.
Pollutant CategoryIndustrial SourcesSustainable ApproachesEnvironmental BenefitsReferences
Heavy metalsMining, electroplating, metal finishing, textile processingAdsorption using biochar and natural materials, phytoremediation, membrane filtration, metal recoveryToxicity reduction, bioaccumulation prevention, resource recovery[122,123,124,125,126]
Textile dyes and auxiliariesTextile dyeing and finishing industriesCleaner dyeing processes, chemical substitutions, in-plant water reuse, advanced oxidationColor discharge reduction, chemical load decrease, freshwater conservation[29,127,128,129,130]
Pharmaceuticals and Personal Care ProductsPharmaceutical manufacturing, hospitalsSource control, hybrid biological–advanced treatment systemsChronic toxicity and antibiotic resistance risks reduction[32,131,132,133,134]
MicroplasticsTextile fibers (synthetic fabrics), plastic manufacturing, industrial effluentsSource reduction, filtration and membrane technologies, circular material managementParticulate pollution reduction, aquatic food webs protection[33,66,67,135,136]
Persistent Organic PollutantsChemical manufacturing, pesticide production, plastics and flame retardantsRegulatory control, substitution with safer chemicals, advanced treatmentLong-term reduction in bioaccumulative and toxic compounds[72,76,77,137,138]
PesticidesAgrochemical production, formulation industriesIntegrated pest management, cleaner production, controlled dischargeAquatic toxicity reduction, ecosystem resilience improvement[31,100,139,140,141]
Mixed industrial effluentsIndustrial parks, manufacturing clustersIndustrial symbiosis, circular water reuse, centralized treatmentFreshwater demand decrease, effluent discharge reduction[89,142,143,144]
Table 11. Comparative overview of cleaner production strategies applied to industrial pollution prevention.
Table 11. Comparative overview of cleaner production strategies applied to industrial pollution prevention.
ApproachPrincipleApplicationsEnvironmental BenefitsLimitationsReferences
Eco-designIntegrating environmental considerations during product designManufacturing industries, product life cycle optimization20–30% reduction in material use and waste generationRequires life cycle assessment and design modifications[197]
Green chemistryDesigning chemical processes that reduce hazardous substancesPharmaceutical and chemical manufacturingUp to 90% reduction in solvent consumption in some processesRequires process redesign and new catalysts[185]
Process optimizationImproving efficiency of industrial operationsAutomotive paint processes~20% reduction in energy use and VOC emissionsImplementation requires technological investment[193]
Zero-Liquid-DischargeRecycling wastewater through filtration and evaporationTextile and chemical industries>90–95% water recovery and reduced wastewater dischargeHigh capital and energy costs[181]
Table 12. Comparison of technological solutions for industrial wastewater treatment.
Table 12. Comparison of technological solutions for industrial wastewater treatment.
TechnologyMechanismPollutantsEnvironmental BenefitsLimitationsReferences
BioremediationMicrobial enzymatic degradationOrganic pollutants, dyes, pesticidesLow cost, environmentally friendlySensitive to environmental conditions[214]
Constructed wetlandsPlant uptake, microbial degradation, sedimentationNutrients, organic pollutants, metalsLow energy demand, ecosystem benefitsLarge land requirement[219]
NanotechnologyAdsorption and catalytic degradation using nanomaterialsHeavy metals, organic contaminantsHigh selectivity, high adsorption capacityCost and potential nanoparticle toxicity[207]
Membrane filtration Physical separation through semi-permeable membranesSalts, metals, organic compoundsHigh treatment efficiency, reliableHigh energy consumption, membrane fouling[87]
Hybrid systems Biological degradation + membrane separationComplex industrial wastewaterHigh efficiency for mixed pollutantsHigh capital and operational cost[132]
Table 13. Circular economy and industrial symbiosis strategies for reducing industrial freshwater pollution.
Table 13. Circular economy and industrial symbiosis strategies for reducing industrial freshwater pollution.
ApproachPrincipleApplicationsEnvironmental BenefitsLimitationsReferences
Water recycling and reuseReuse of treated industrial wastewater within production cyclesTextile dyeing plants, chemical manufacturing30–70% reduction in freshwater consumptionRequires advanced treatment and monitoring[248]
Resource recoveryRecovery of nutrients, energy, or materials from wastewaterStruvite precipitation, heat recoveryReduces waste and generates valuable resourcesTechnological complexity[237]
Industrial symbiosisExchange of resources between industriesKalundborg, Ulsan, Tianjin eco-industrial parksReduced water use, energy savings, lower emissionsRequires coordination and infrastructure[244]
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Hamdi, R. Assessing Sustainable Approaches in the Face of Industrial Chemical Pollution of Freshwater. Sustainability 2026, 18, 3476. https://doi.org/10.3390/su18073476

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Hamdi R. Assessing Sustainable Approaches in the Face of Industrial Chemical Pollution of Freshwater. Sustainability. 2026; 18(7):3476. https://doi.org/10.3390/su18073476

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Hamdi, Raghda. 2026. "Assessing Sustainable Approaches in the Face of Industrial Chemical Pollution of Freshwater" Sustainability 18, no. 7: 3476. https://doi.org/10.3390/su18073476

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Hamdi, R. (2026). Assessing Sustainable Approaches in the Face of Industrial Chemical Pollution of Freshwater. Sustainability, 18(7), 3476. https://doi.org/10.3390/su18073476

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