<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd">
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article">
 <front>
  <journal-meta>
   <journal-id journal-id-type="publisher-id">
    anp
   </journal-id>
   <journal-title-group>
    <journal-title>
     Advances in Nanoparticles
    </journal-title>
   </journal-title-group>
   <issn pub-type="epub">
    2169-0510
   </issn>
   <issn publication-format="print">
    2169-0529
   </issn>
   <publisher>
    <publisher-name>
     Scientific Research Publishing
    </publisher-name>
   </publisher>
  </journal-meta>
  <article-meta>
   <article-id pub-id-type="doi">
    10.4236/anp.2025.141002
   </article-id>
   <article-id pub-id-type="publisher-id">
    anp-140802
   </article-id>
   <article-categories>
    <subj-group subj-group-type="heading">
     <subject>
      Articles
     </subject>
    </subj-group>
    <subj-group subj-group-type="Discipline-v2">
     <subject>
      Biomedical 
     </subject>
     <subject>
       Life Sciences, Chemistry 
     </subject>
     <subject>
       Materials Science, Engineering
     </subject>
    </subj-group>
   </article-categories>
   <title-group>
    Revolutionizing Hemodialysis Water Quality: Development and Evaluation of TiO₂ Nanoparticle-Enhanced Microporous Filters
   </title-group>
   <contrib-group>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Opeyemi Temilade
      </surname>
      <given-names>
       Enang
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Bakiyat Oluwagbemisola
      </surname>
      <given-names>
       Azeez
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Babatunde Temitope
      </surname>
      <given-names>
       Ogunyemi
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff2"> 
      <sup>2</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Aminah Abolore
      </surname>
      <given-names>
       Sulayman
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Dauda Olurotimi
      </surname>
      <given-names>
       Araromi
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff1"> 
      <sup>1</sup>
     </xref>
    </contrib>
    <contrib contrib-type="author" xlink:type="simple">
     <name name-style="western">
      <surname>
       Morufu Olalekan
      </surname>
      <given-names>
       Raimi
      </given-names>
     </name> 
     <xref ref-type="aff" rid="aff3"> 
      <sup>3</sup>
     </xref>
    </contrib>
   </contrib-group> 
   <aff id="aff1">
    <addr-line>
     aDepartment of Chemical Engineering, Ladoke Akintola University of Technology, Ogbomoso, Nigeria
    </addr-line> 
   </aff> 
   <aff id="aff2">
    <addr-line>
     aDepartment of Chemistry, Federal University Otuoke, Otuoke, Nigeria
    </addr-line> 
   </aff> 
   <aff id="aff3">
    <addr-line>
     aNiger-Delta Institute for Emerging and Re-Emerging Infectious Diseases (NDIERID), Federal University Otuoke, Otuoke, Nigeria
    </addr-line> 
   </aff> 
   <pub-date pub-type="epub">
    <day>
     06
    </day> 
    <month>
     02
    </month>
    <year>
     2025
    </year>
   </pub-date> 
   <volume>
    14
   </volume> 
   <issue>
    01
   </issue>
   <fpage>
    12
   </fpage>
   <lpage>
    36
   </lpage>
   <history>
    <date date-type="received">
     <day>
      28,
     </day>
     <month>
      January
     </month>
     <year>
      2025
     </year>
    </date>
    <date date-type="published">
     <day>
      22,
     </day>
     <month>
      January
     </month>
     <year>
      2025
     </year> 
    </date> 
    <date date-type="accepted">
     <day>
      22,
     </day>
     <month>
      February
     </month>
     <year>
      2025
     </year> 
    </date>
   </history>
   <permissions>
    <copyright-statement>
     © Copyright 2014 by authors and Scientific Research Publishing Inc. 
    </copyright-statement>
    <copyright-year>
     2014
    </copyright-year>
    <license>
     <license-p>
      This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/
     </license-p>
    </license>
   </permissions>
   <abstract>
    <b>Rationale: </b>Endotoxin contamination in conventionally purified water poses serious risks to hemodialysis patients, leading to complications such as inflammation and sepsis. Addressing these risks is essential for enhancing patient safety and meeting global dialysis water quality standards. Advanced filtration technologies, such as titanium dioxide (TiO₂)-based nanoparticle filters, offer a promising approach to improve water purification processes in renal care.
    <b> Objectives: </b>This study aimed to develop and evaluate the effectiveness of a TiO₂-based nanoparticle microporous filtration system for hemodialysis water purification. The objectives included analyzing the system’s performance in reducing chemical contaminants (calcium, magnesium, aluminum, and lead) and microbiological contaminants (total viable count [TVC] and endotoxin units [EU]) across multiple renal centers.
    <b> Methods: </b>Water samples from three renal centers (RC1, RC2, and RC3) were analyzed pre- and post-filtration. TiO₂ nanoparticles were synthesized using the sol-gel method and characterized via Fourier Transform Infrared (FTIR) spectroscopy and Scanning Electron Microscopy with Energy Dispersive X-ray analysis (SEM/EDX). The microporous filter, fabricated with TiO₂ nanoparticles, silicon dioxide, and polyethylene glycol (PEG), was tested for its ability to remove contaminants. Analytical techniques included spectroscopy for chemical analysis and microbiological assays for contaminant quantification.
    <b> Results: </b>Post-treatment analysis revealed significant reductions in chemical contaminants, with removal efficiencies averaging 78% for calcium, 80% for magnesium, 81% for aluminum, and 76.6% for lead across all centers. Microbiological contamination was also substantially reduced, with 78–80% removal of TVC and 76–84.6% reduction in EU levels. FTIR analysis confirmed the presence of hydroxyl groups critical for adsorption, while SEM/EDX characterization revealed a crystalline structure with a particle size of 1.45 nm, pore size of 4.11 μm, filter height of 2.56 mm, and bulk density of 0.58 g/cm³.
    <b> Conclusion: </b>The TiO₂-based nanoparticle filtration system demonstrated high efficacy in removing chemical and microbiological contaminants, significantly improving water quality for hemodialysis. These results highlight its potential as a practical solution for renal centers, especially in resource-constrained settings. Further studies are needed to evaluate its long-term performance and feasibility for widespread adoption.
    <b> Recommendation: </b>Renal centers should consider adopting TiO
    <sub>2</sub>-based nanoparticle filters to address persistent water quality challenges. Pilot implementations across diverse settings can provide insights into operational feasibility. Additional research should explore scalability, maintenance requirements, and cost-effectiveness to optimize integration into healthcare systems.
    <b> Significance Statement: </b>This study introduces a practical and innovative solution to improve hemodialysis water purification. By effectively reducing both chemical and microbiological contaminants, the TiO
    <sub>2</sub>-based filtration system has the potential to enhance patient safety and outcomes, particularly in settings where maintaining high water quality standards remains challenging.
   </abstract>
   <kwd-group> 
    <kwd>
     TiO
     <sub>2</sub> Nanoparticles
    </kwd> 
    <kwd>
      Hemodialysis
    </kwd> 
    <kwd>
      Water Purification
    </kwd> 
    <kwd>
      Endotoxin Contamination
    </kwd> 
    <kwd>
      Photocatalytic Filtration
    </kwd> 
    <kwd>
      Nanotechnology
    </kwd> 
    <kwd>
      Microporous Filter
    </kwd> 
    <kwd>
      Sol-Gel Synthesis
    </kwd> 
    <kwd>
      Microbiological Contaminants
    </kwd> 
    <kwd>
      Environmental Remediation
    </kwd>
   </kwd-group>
  </article-meta>
 </front>
 <body>
  <sec id="s1">
   <title>1. Introduction</title>
   <p>
    <xref ref-type="bibr" rid="scirp.140802-"></xref>Hemodialysis is a life-sustaining treatment for individuals with end-stage renal disease (ESRD). It removes waste products and excess fluids from your blood when your kidneys can no longer perform these functions. In Nigeria, the number of dialysis centers has increased significantly, from 10 centers two decades ago to more than 120 centers in 2015 <xref ref-type="bibr" rid="scirp.140802-1">
     [1]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-4">
     [4]
    </xref>. However, the quality of water used in hemodialysis remains a significant concern. Studies have shown that many centers in Nigeria do not meet the Association for the Advancement of Medical Instrumentation (AAMI) standards for chemical contaminants in dialysis water <xref ref-type="bibr" rid="scirp.140802-5">
     [5]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-8">
     [8]
    </xref>. For instance, a survey of six hemodialysis centers in Lagos revealed that none met the AAMI guidelines for most chemical contaminants. Only chlorine (0.48 ± 0.07 mg/L) and potassium (3.9 ± 0.95 mg/L) levels met the standards after treatment <xref ref-type="bibr" rid="scirp.140802-8">
     [8]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-16">
     [16]
    </xref>. Similarly, the same goes for other studies conducted in different parts of Nigeria <xref ref-type="bibr" rid="scirp.140802-17">
     [17]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-37">
     [37]
    </xref>. Globally, dialysis water quality is regulated by stringent standards to prevent patient exposure to harmful contaminants. The Association for the Advancement of Medical Instrumentation (AAMI) and the International Organization for Standardization (ISO) set benchmarks for permissible levels of chemical and microbial impurities in hemodialysis water. According to AAMI/ISO 23500 standards, dialysis water should contain less than 0.1 CFU/mL of bacteria and endotoxin levels below 0.25 EU/mL. Compliance with these standards is critical because any deviation can lead to severe complications, including endotoxemia, chronic inflammation, and cardiovascular issues in End-Stage Renal Disease (ESRD) patients <xref ref-type="bibr" rid="scirp.140802-5">
     [5]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-8">
     [8]
    </xref>. In high-income countries, adherence to these guidelines is strictly monitored, with regular water quality assessments and advanced treatment technologies ensuring safety. However, resource-limited settings, such as Nigeria, often struggle with regulatory enforcement and infrastructure challenges, leading to suboptimal dialysis water quality. Moreover, microbial contamination is a prevalent issue. A study evaluating the microbial quality of hemodialysis water in Lagos found that Escherichia coli was the most common organism isolated in both feed and treated water across all centers. The mean levels of E. coli in feed and treated water were 441.7 ± 87.90 and 168.5 ± 64.03, respectively <xref ref-type="bibr" rid="scirp.140802-19">
     [19]
    </xref>. These findings highlight the pressing need for improved water purification methods in hemodialysis centers, especially in resource-limited settings. Traditional water treatment systems, such as reverse osmosis and filtration, have limitations, including bacterial proliferation and challenging sanitization processes <xref ref-type="bibr" rid="scirp.140802-13">
     [13]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-16">
     [16]
    </xref>. Recent advancements in nanotechnology offer promising alternatives for dialysis water treatment. Titanium dioxide (TiO<sub>2</sub>) nanoparticles have garnered attention due to their exceptional photocatalytic activity, antimicrobial efficacy, and ability to degrade organic and inorganic pollutants. TiO<sub>2</sub>-based filtration systems can efficiently break down bacterial biofilms, minimize endotoxin formation, and reduce heavy metal contamination in water. Additionally, TiO<sub>2</sub> nanoparticles exhibit high stability, chemical resistance, and self-cleaning properties, making them a superior alternative to conventional water treatment methods. Notably, their ability to generate reactive oxygen species under ultraviolet (UV) or visible light enhances microbial disinfection, which is crucial for maintaining dialysis water purity <xref ref-type="bibr" rid="scirp.140802-17">
     [17]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-37">
     [37]
    </xref>. Despite these advantages, the application of TiO<sub>2</sub> nanoparticle-based filtration systems in hemodialysis water purification remains underexplored, necessitating further research into their efficacy and safety. Addressing this gap is crucial for improving the safety and quality of hemodialysis treatment, particularly in regions like Nigeria, where water contamination poses significant health risks to patients <xref ref-type="bibr" rid="scirp.140802-17">
     [17]
    </xref>-<xref ref-type="bibr" rid="scirp.140802-37">
     [37]
    </xref>. This study aims to develop and evaluate a TiO<sub>2</sub> nanoparticle-based microporous filter system for hemodialysis water purification. By focusing on the efficiency of this novel filtration system in removing chemical and microbiological contaminants from water samples collected from multiple renal centers, the research seeks to enhance the safety and quality of hemodialysis treatment. Thus, the findings could have significant implications for reducing water-related complications in patients with ESRD, thereby contributing to the overall objectives of the Sustainable Development Goals (SDGs), particularly those related to health and well-being.</p>
  </sec><sec id="s2">
   <title>2. Methodology</title>
   <p>The materials utilized in this study were sourced from reliable suppliers to maintain consistency and accuracy. Titanium isopropoxide (TTIP), ethanol, deionized water, hydrochloric acid, and methyl orange were procured from Sigma-Aldrich Ltd, as outlined in prior studies on nanoparticle synthesis for water purification <xref ref-type="bibr" rid="scirp.140802-7">
     [7]
    </xref>. Water samples for analysis were collected from the final reverse osmosis (RO) purification stage at three tertiary healthcare institutions, coded as BT, LT, and UT. Sampling ports were disinfected with 70% ethanol and flushed for two minutes before collecting the water samples to ensure the removal of any residual contaminants <xref ref-type="bibr" rid="scirp.140802-9">
     [9]
    </xref>.</p>
   <sec id="s2_1">
    <title>2.1. Synthesis of TiO<sub>2</sub> Nanoparticles</title>
    <p>TiO<sub>2</sub> nanoparticles were synthesized via the sol-gel method, which is widely recognized for producing high-purity nanoparticles with tailored properties <xref ref-type="bibr" rid="scirp.140802-11">
      [11]
     </xref>. A solution containing 100 mL of TTIP and 500 mL of ethanol was prepared and stirred continuously for 30 minutes at room temperature. Subsequently, deionized water and hydrochloric acid were added dropwise in a 1.2:1 molar ratio under constant stirring at 200 rpm. This process was maintained for 2 hours at 21˚C, ensuring the solution’s pH was adjusted to 3 <xref ref-type="bibr" rid="scirp.140802-9">
      [9]
     </xref>. To facilitate hydrolysis and condensation reactions, the solution was continuously stirred under controlled temperature conditions, allowing for the gradual formation of TiO<sub>2</sub> nanoparticles. The resulting sol was then aged for 24 hours at room temperature, enabling particle growth and structural stabilization. The formed gel was dried at 120˚C for 2 hours to remove residual solvents and promote crystallization. Finally, the dried gel was calcined at 450˚C for 4 hours to enhance its crystallinity and optimize its surface area for effective water purification applications.</p>
   </sec>
   <sec id="s2_2">
    <title>2.2. Characterization of TiO<sub>2</sub> Nanoparticles</title>
    <p>The synthesized nanoparticles were characterized using advanced analytical techniques to confirm their structural, morphological, and chemical properties. Fourier-transform infrared (FTIR) spectroscopy was employed to identify functional groups in the range of 4000 - 400 cm<sup>−1</sup>, a method previously validated in similar studies <xref ref-type="bibr" rid="scirp.140802-13">
      [13]
     </xref>. Scanning electron microscopy (SEM) (Hitachi SU 3500) was used to examine the surface morphology and particle size distribution, while X-ray diffraction (XRD) analysis (X’Pert PRO, PANalytical) provided insights into the crystalline structure and phase composition <xref ref-type="bibr" rid="scirp.140802-14">
      [14]
     </xref>. These techniques ensured that the nanoparticles met the required specifications for their intended application.</p>
   </sec>
   <sec id="s2_3">
    <title>2.3. Filter Fabrication</title>
    <p>The TiO<sub>2</sub>-based filter was fabricated by combining synthesized TiO<sub>2</sub> nanoparticles with polyethylene glycol (PEG) in a 7:3 weight ratio. To improve dispersion, the TiO<sub>2</sub>-PEG mixture was ultrasonicated for 1 hour before further processing. To enhance the structural stability, 0.1 g of silica particles was added to the mixture, as reported in prior nanoparticle-based filter designs <xref ref-type="bibr" rid="scirp.140802-15">
      [15]
     </xref>. The resulting mixture was thoroughly homogenized, compressed into disc form using a hydraulic press, and heated at 100˚C for 2 hours. Following this step, the discs were subjected to gradual heating at 200˚C for 1 hour before reaching the final sintering temperature of 305˚C. This incremental heating process was employed to prevent microcrack formation and to ensure uniform porosity and mechanical strength in the final filter.</p>
   </sec>
   <sec id="s2_4">
    <title>2.4. Water Sample Analysis</title>
    <p>The collected water samples were subjected to comprehensive physicochemical and microbiological analyses to evaluate the performance of the TiO<sub>2</sub>-based filter. Parameters such as pH, conductivity, and hardness were measured using standard protocols, with a DR5000 spectrophotometer providing accurate quantification of chemical properties <xref ref-type="bibr" rid="scirp.140802-4">
      [4]
     </xref>. Metal concentrations, including essential and toxic elements, were determined using Flame Atomic Absorption Spectrophotometry (Perkin-Elmer 2380) <xref ref-type="bibr" rid="scirp.140802-6">
      [6]
     </xref>. The filtration efficiency was compared with conventional reverse osmosis (RO) and activated carbon filtration techniques to assess the superiority of the TiO<sub>2</sub>-based filter in removing heavy metals and organic contaminants.</p>
   </sec>
   <sec id="s2_5">
    <title>2.5. Bacteriological and Endotoxin Testing</title>
    <p>The bacteriological quality of the water samples was assessed using heterotrophic plate counts on R2A agar medium, which is optimal for detecting heterotrophic bacteria in low-nutrient environments <xref ref-type="bibr" rid="scirp.140802-3">
      [3]
     </xref>. Endotoxin levels, which are critical for evaluating water quality in hemodialysis, were quantified using the Limulus Amebocyte Lysate (LAL) gel-clot method <xref ref-type="bibr" rid="scirp.140802-8">
      [8]
     </xref>. Additionally, the operational costs, energy requirements, and long-term maintenance needs of the TiO<sub>2</sub>-based filter were analyzed and compared with existing advanced purification methods. This evaluation provided insights into the cost-effectiveness and practical applicability of the developed filtration system in real-world dialysis settings.</p>
   </sec>
   <sec id="s2_6">
    <title>2.6. Study Limitation</title>
    <p>While the performance of the filtration system based on TiO<sub>2</sub> was quite good in chemical and microbiological contaminant removal, some limitations still occurred. First, there is no study on long-term durability or whether this filter would easily get clogged. Further research concerning operational longevity, maintenance, and long-term usage affecting filtration performance should be conducted. Second, TiO<sub>2</sub> nanoparticles have been widely regarded as antimicrobial agents; however, toxicity has not been deeply assessed in this work. Further studies are needed regarding health risks, nanoparticle leaching, and environmental implications with thorough in vitro and in vivo toxicity testing. Finally, a full cost-benefit analysis was not performed, nor was the scalability of the implementation of this filtration system in various dialysis centers. Production, installation, and maintenance costs should be compared against conventional dialysis water treatment methods in future studies to establish the economic feasibility of widespread adoption. The effort put into addressing these gaps will enhance the understanding of how to practically apply TiO<sub>2</sub>-based filtration systems in hemodialysis water purification.</p>
   </sec>
  </sec><sec id="s3">
   <title>3. Results and Discussion</title>
   <sec id="s3_1">
    <title>3.1. Assessment of Water Quality in Dialysis: Microbial, Endotoxin, and Chemical Analysis</title>
    <p>
     <xref ref-type="table" rid="table1">
      Table 1
     </xref> and <xref ref-type="fig" rid="fig1">
      Figure 1
     </xref> assessed the microbial, endotoxin, and chemical quality of water samples from reverse osmosis (RO) systems used in dialysis across three tertiary healthcare institutions (RC1, RC2, RC3) and tap water (TP). In terms of microbial contamination, the total viable count (TVC) for RC1, RC2, RC3, and TP ranged from 40.18 CFU/ml to 60.20 CFU/ml, meeting the dialysis water limit (&lt;100 CFU/ml) but exceeding the action limit (AL) of 50 CFU/ml in RC2 and TP. Endotoxin levels were significantly higher than the maximum allowable level (MAL) of 0.25 EU/ml for dialysis water and 0.5 EU/ml for dialysis fluid, with RC1, RC2, RC3, and TP reporting values of 1.07, 1.97, 2.5, and 3.95 EU/ml, respectively. pH values ranged from 7.0 to 8.2, staying within the acceptable range for dialysis processes. While, <xref ref-type="table" rid="table1">
      Table 1
     </xref> and <xref ref-type="fig" rid="fig1">
      Figure 1
     </xref> reveal critical insights into water quality challenges. The high endotoxin levels, particularly in RC3 and TP, raise concerns about patient safety during dialysis, as endotoxin exposure is associated with inflammatory responses. These findings align with those of Pathak, Elan, and Devi <xref ref-type="bibr" rid="scirp.140802-38">
      [38]
     </xref>, who identified endotoxin contamination as a recurrent issue in dialysis water systems. Additionally, the microbial counts exceeding AL in some samples underscore the need for stringent monitoring, consistent with the recommendations of the CDC <xref ref-type="bibr" rid="scirp.140802-39">
      [39]
     </xref>. The higher microbial and endotoxin levels in TP compared to RO-treated samples highlight the importance of reverse osmosis in achieving improved water quality, as supported by the Renal Fellow Network <xref ref-type="bibr" rid="scirp.140802-40">
      [40]
     </xref>. This study’s findings underscore the importance of robust water treatment protocols in healthcare settings. Elevated endotoxin levels are consistent with the findings of Zhuang and Chen <xref ref-type="bibr" rid="scirp.140802-41">
      [41]
     </xref>, who highlighted the limitations of conventional water treatment systems in effectively reducing endotoxin levels. The integration of titanium dioxide (TiO<sub>2</sub>) nanoparticles for water purification, as demonstrated in this study, offers a promising solution to these challenges. Wang and Wu <xref ref-type="bibr" rid="scirp.140802-42">
      [42]
     </xref> emphasize the efficacy of TiO<sub>2</sub> in removing microbial and endotoxin contaminants, supporting its application in dialysis water treatment. Moreover, Tiwari and Sharma <xref ref-type="bibr" rid="scirp.140802-43">
      [43]
     </xref> documented the photocatalytic properties of TiO<sub>2</sub> nanoparticles, enhancing their suitability for healthcare applications. However, the slight deviations in microbial quality from action limits align with González-Esquivel et al.</p>
    <table-wrap id="table1">
     <label>
      <xref ref-type="table" rid="table1">
       Table 1
      </xref></label>
     <caption>
      <title>
       <xref ref-type="bibr" rid="scirp.140802-"></xref>Table 1. TVC, endotoxin, and pH values of universally acceptable standard dialysis fluid and water samples.</title>
     </caption>
     <table class="MsoTableGrid custom-table" border="0" cellspacing="0" cellpadding="0"> 
      <tr> 
       <td rowspan="2" class="acenter" width="23.29%"><p style="text-align:center">Contaminant</p></td> 
       <td class="custom-bottom-td acenter" width="20.24%" colspan="2"><p style="text-align:center">Dialysis water</p></td> 
       <td class="custom-bottom-td acenter" width="20.26%" colspan="2"><p style="text-align:center">Standard dialysis fluid</p></td> 
       <td class="custom-bottom-td acenter" width="36.21%" colspan="4"><p style="text-align:center">Water sample</p></td> 
      </tr> 
      <tr> 
       <td class="custom-bottom-td custom-top-td acenter" width="10.11%"><p style="text-align:center">MAL</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="10.13%"><p style="text-align:center">AL</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="10.13%"><p style="text-align:center">MAL</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="10.13%"><p style="text-align:center">AL</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="9.04%"><p style="text-align:center">RC1</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="9.06%"><p style="text-align:center">RC2</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="9.04%"><p style="text-align:center">RC3</p></td> 
       <td class="custom-bottom-td custom-top-td acenter" width="9.06%"><p style="text-align:center">TP</p></td> 
      </tr> 
      <tr> 
       <td class="custom-top-td acenter" width="23.29%"><p style="text-align:center">TVC (CFU/ml)</p></td> 
       <td class="custom-top-td acenter" width="10.11%"><p style="text-align:center">&lt;100</p></td> 
       <td class="custom-top-td acenter" width="10.13%"><p style="text-align:center">50</p></td> 
       <td class="custom-top-td acenter" width="10.13%"><p style="text-align:center">&lt;100</p></td> 
       <td class="custom-top-td acenter" width="10.13%"><p style="text-align:center">50</p></td> 
       <td class="custom-top-td acenter" width="9.04%"><p style="text-align:center">45.63</p></td> 
       <td class="custom-top-td acenter" width="9.06%"><p style="text-align:center">54.12</p></td> 
       <td class="custom-top-td acenter" width="9.04%"><p style="text-align:center">40.18</p></td> 
       <td class="custom-top-td acenter" width="9.06%"><p style="text-align:center">60.20</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="23.29%"><p style="text-align:center">Endotoxin (EU/ml)</p></td> 
       <td class="acenter" width="10.11%"><p style="text-align:center">&lt;0.25</p></td> 
       <td class="acenter" width="10.13%"><p style="text-align:center">0.125</p></td> 
       <td class="acenter" width="10.13%"><p style="text-align:center">&lt;0.5</p></td> 
       <td class="acenter" width="10.13%"><p style="text-align:center">0.25</p></td> 
       <td class="acenter" width="9.04%"><p style="text-align:center">1.07</p></td> 
       <td class="acenter" width="9.06%"><p style="text-align:center">1.97</p></td> 
       <td class="acenter" width="9.04%"><p style="text-align:center">2.5</p></td> 
       <td class="acenter" width="9.06%"><p style="text-align:center">3.95</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="23.29%"><p style="text-align:center">pH</p></td> 
       <td class="acenter" width="10.11%"><p style="text-align:center"></p></td> 
       <td class="acenter" width="10.13%"><p style="text-align:center"></p></td> 
       <td class="acenter" width="10.13%"><p style="text-align:center"></p></td> 
       <td class="acenter" width="10.13%"><p style="text-align:center"></p></td> 
       <td class="acenter" width="9.04%"><p style="text-align:center">7.0</p></td> 
       <td class="acenter" width="9.06%"><p style="text-align:center">7.3</p></td> 
       <td class="acenter" width="9.04%"><p style="text-align:center">7.6</p></td> 
       <td class="acenter" width="9.06%"><p style="text-align:center">8.2</p></td> 
      </tr> 
     </table>
    </table-wrap>
    <p>
     <xref ref-type="bibr" rid="scirp.140802-"></xref>MAL = Maximum Allowable Level, AL = Action level (typically 50% of maximum level).</p>
    <fig id="fig1" position="float">
     <label>Figure 1</label>
     <caption>
      <title>Figure 1. Shows the contaminant levels in dialysis water samples. It includes: TVC (CFU/ml) and Endotoxin (EU/ml) as bar charts and pH levels as a line plot.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId18.jpeg?20250226091013" />
    </fig>
    <p>
     <xref ref-type="bibr" rid="scirp.140802-44">
      [44]
     </xref>, who noted potential challenges in ensuring complete microbial elimination in dialysis water systems. Similarly, Shirdareh and Nasiri <xref ref-type="bibr" rid="scirp.140802-45">
      [45]
     </xref> observed variations in microbial contamination control, emphasizing the need for innovative technologies like nanoparticle-enhanced filtration. On the other hand, studies like Amara, Boulahdour, and Benhamouda <xref ref-type="bibr" rid="scirp.140802-46">
      [46]
     </xref> caution against the potential toxicological effects of TiO<sub>2</sub> nanoparticles, suggesting further evaluations for clinical safety and efficacy. The study highlights the necessity of advanced water purification technologies in healthcare settings, particularly in dialysis units. The findings reinforce the significance of integrating TiO<sub>2</sub> nanoparticle-based filters to enhance microbial and endotoxin removal, contributing to safer dialysis water. As supported by Kaur and Singh <xref ref-type="bibr" rid="scirp.140802-47">
      [47]
     </xref>, adopting emerging nanomaterials can bridge gaps in current water treatment practices. However, ensuring consistent adherence to international standards, as outlined by ANSI/AAMI/ISO <xref ref-type="bibr" rid="scirp.140802-8">
      [8]
     </xref>, remains critical for patient safety. Future implementations should consider long-term monitoring and toxicity assessments to optimize the efficacy and safety of nanoparticle-based filtration systems.</p>
   </sec>
   <sec id="s3_2">
    <title>3.2. Electrolyte Concentrations in Dialysis Water: Implications for Patient Safety and Treatment Efficacy</title>
    <p>
     <xref ref-type="table" rid="table2">
      Table 2
     </xref> and <xref ref-type="fig" rid="fig2">
      Figure 2
     </xref> present the concentrations (in ppm) of critical electrolytes (calcium, magnesium, aluminum, and lead) in dialysis water across three sample collection points (RC1, RC2, and RC3) and a total pooled sample (TP). Calcium levels ranged from 0.537 ppm in RC3 to 1.479 ppm in TP, while magnesium showed the highest concentration in TP (2.836 ppm) and the lowest in RC1 (1.624 ppm). Aluminum concentrations were fairly consistent, ranging from 0.802 ppm in RC2 to 1.038 ppm in TP. Lead concentrations, a key toxic contaminant, peaked at 0.538 ppm in RC2 and showed the lowest value of 0.120 ppm in RC1. These variations highlight the importance of monitoring dialysis water for both essential and potentially toxic electrolytes. While <xref ref-type="table" rid="table2">
      Table 2
     </xref> and <xref ref-type="fig" rid="fig2">
      Figure 2
     </xref> underscore the variability in water quality across sampling points, revealing that certain contaminants,</p>
    <table-wrap id="table2">
     <label>
      <xref ref-type="table" rid="table2">
       Table 2
      </xref></label>
     <caption>
      <title>
       <xref ref-type="bibr" rid="scirp.140802-"></xref>Table 2. Spectrometry analysis of chemical contaminant before treatment</title>
     </caption>
     <table class="MsoTableGrid custom-table" border="0" cellspacing="0" cellpadding="0"> 
      <tr> 
       <td class="custom-bottom-td acenter" width="18.69%"><p style="text-align:center">Electrolytes</p></td> 
       <td class="custom-bottom-td acenter" width="20.09%"><p style="text-align:center">Ca</p><p style="text-align:center">Conc. (ppm)</p></td> 
       <td class="custom-bottom-td acenter" width="20.02%"><p style="text-align:center">Mg</p><p style="text-align:center">Conc. (ppm)</p></td> 
       <td class="custom-bottom-td acenter" width="21.18%"><p style="text-align:center">Al</p><p style="text-align:center">Conc. (ppm)</p></td> 
       <td class="custom-bottom-td acenter" width="20.02%"><p style="text-align:center">Pb</p><p style="text-align:center">Conc. (ppm)</p></td> 
      </tr> 
      <tr> 
       <td class="custom-top-td acenter" width="18.69%"><p style="text-align:center">RC1</p></td> 
       <td class="custom-top-td acenter" width="20.09%"><p style="text-align:center">0.612</p></td> 
       <td class="custom-top-td acenter" width="20.02%"><p style="text-align:center">1.624</p></td> 
       <td class="custom-top-td acenter" width="21.18%"><p style="text-align:center">1.021</p></td> 
       <td class="custom-top-td acenter" width="20.02%"><p style="text-align:center">0.120</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="18.69%"><p style="text-align:center">RC2</p></td> 
       <td class="acenter" width="20.09%"><p style="text-align:center">1.299</p></td> 
       <td class="acenter" width="20.02%"><p style="text-align:center">2.735</p></td> 
       <td class="acenter" width="21.18%"><p style="text-align:center">0.802</p></td> 
       <td class="acenter" width="20.02%"><p style="text-align:center">0.538</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="18.69%"><p style="text-align:center">RC3</p></td> 
       <td class="acenter" width="20.09%"><p style="text-align:center">0.537</p></td> 
       <td class="acenter" width="20.02%"><p style="text-align:center">1.826</p></td> 
       <td class="acenter" width="21.18%"><p style="text-align:center">1.024</p></td> 
       <td class="acenter" width="20.02%"><p style="text-align:center">0.336</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="18.69%"><p style="text-align:center">TP</p></td> 
       <td class="acenter" width="20.09%"><p style="text-align:center">1.479</p></td> 
       <td class="acenter" width="20.02%"><p style="text-align:center">2.836</p></td> 
       <td class="acenter" width="21.18%"><p style="text-align:center">1.038</p></td> 
       <td class="acenter" width="20.02%"><p style="text-align:center">0.361</p></td> 
      </tr> 
     </table>
    </table-wrap>
    <fig id="fig2" position="float">
     <label>Figure 2</label>
     <caption>
      <title>Figure 2. Shows the electrolyte concentrations (Calcium, Magnesium, Aluminum, and Lead) across the different sampling points (RC1, RC2, RC3, TP).</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId19.jpeg?20250226091015" />
    </fig>
    <p>particularly lead and aluminum, exceeded acceptable thresholds for dialysis water safety as outlined by the Centers for Disease Control and Prevention <xref ref-type="bibr" rid="scirp.140802-39">
      [39]
     </xref>. The elevated levels of magnesium and calcium, while not toxic, could influence the ionic balance critical for patients undergoing dialysis, aligning with findings from Pathak et al. <xref ref-type="bibr" rid="scirp.140802-38">
      [38]
     </xref>. Such deviations underscore the importance of rigorous water purification systems, especially in healthcare settings. The data is significant to the overall study as it emphasizes the need for effective filtration technologies in dialysis water treatment, particularly the role of advanced materials like titanium dioxide nanoparticles <xref ref-type="bibr" rid="scirp.140802-43">
      [43]
     </xref>. The concentrations of aluminum and lead suggest potential contamination sources that could compromise patient safety, highlighting the critical role of nanomaterials in enhancing filtration efficiency <xref ref-type="bibr" rid="scirp.140802-41">
      [41]
     </xref> <xref ref-type="bibr" rid="scirp.140802-48">
      [48]
     </xref>. This aligns with studies advocating for stricter regulations and innovations in dialysis water treatment <xref ref-type="bibr" rid="scirp.140802-40">
      [40]
     </xref>. <xref ref-type="table" rid="table2">
      Table 2
     </xref> and <xref ref-type="fig" rid="fig2">
      Figure 2
     </xref> bear significant real-world implications. High lead concentrations, as seen in RC2, can exacerbate renal complications in dialysis patients, a concern previously highlighted by Shirdareh and Nasiri <xref ref-type="bibr" rid="scirp.140802-45">
      [45]
     </xref>. The slightly elevated aluminum levels align with González-Esquivel et al. <xref ref-type="bibr" rid="scirp.140802-44">
      [44]
     </xref>, who reported similar findings in dialysis water, attributing them to inadequate filtration protocols. Furthermore, the increased magnesium and calcium levels may contribute to mineral imbalance, reinforcing recommendations by Kaur and Singh <xref ref-type="bibr" rid="scirp.140802-47">
      [47]
     </xref> for incorporating nanotechnology to achieve precise contaminant removal. Advanced purification methods, such as titanium dioxide nanoparticle-based systems, have demonstrated efficacy in reducing aluminum and lead levels in dialysis water, as supported by studies like Wang and Wu <xref ref-type="bibr" rid="scirp.140802-42">
      [42]
     </xref>. However, disparities in contaminant levels across collection points (e.g., RC1’s low lead but higher magnesium) suggest that systemic inefficiencies or inconsistencies in water treatment could undermine patient safety. This necessitates routine monitoring and potential deployment of hybrid nanomaterial systems, as emphasized by Zhang and Li <xref ref-type="bibr" rid="scirp.140802-49">
      [49]
     </xref>. Ultimately, these findings advocate for a multidisciplinary approach integrating robust filtration technologies and strict compliance with safety standards to mitigate risks in dialysis care.</p>
   </sec>
   <sec id="s3_3">
    <title>3.3. Characterization of Titanium dioxide Nanoparticles for Water Treatment</title>
    <p>The SEM analysis results (<xref ref-type="fig" rid="fig3">
      Figure 3
     </xref>) reveal critical characteristics of sol-gel-synthesized TiO<sub>2</sub> nanoparticles, including a lump-like crystalline morphology, small particle size (1.45 nm), and an interconnected porous network with an average pore size of 4.11 µm. These structural features enhance their catalytic activity and filtration efficiency. The findings align with the work of Liu &amp; Zhang <xref ref-type="bibr" rid="scirp.140802-48">
      [48]
     </xref>, who emphasized that the small particle size and anatase phase of TiO<sub>2</sub> nanoparticles improve their photocatalytic properties, essential for water purification applications. Similarly, Kaur &amp; Singh <xref ref-type="bibr" rid="scirp.140802-47">
      [47]
     </xref> highlighted that advanced nanomaterials, such as TiO<sub>2</sub>, exhibit superior performance due to their high surface area and hierarchical pore structures, supporting the observed synthesis outcomes. The bulk</p>
    <fig id="fig3" position="float">
     <label>Figure 3</label>
     <caption>
      <title>Figure 3. SEM analysis of TiO<sub>2</sub> nanoparticles</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId20.jpeg?20250226091015" />
    </fig>
    <p>density of 0.58 g/cm<sup>3</sup> and uniform morphology distribution were also consistent with Shukla &amp; Kumar <xref ref-type="bibr" rid="scirp.140802-50">
      [50]
     </xref>, who noted that TiO<sub>2</sub> materials with optimized structural parameters balance effective contaminant removal and fluid throughput, particularly for applications like dialysis water treatment. Moreover, Zhuang &amp; Chen <xref ref-type="bibr" rid="scirp.140802-41">
      [41]
     </xref> demonstrated that TiO<sub>2</sub> nanoparticles significantly reduce contaminants in hemodialysis water, correlating with the observed potential of the synthesized materials for physical filtration and photocatalytic degradation. Contrary to conventional mesoporous TiO<sub>2</sub> materials (2 - 50 nm), the larger pore size observed in this study may raise concerns about reduced filtration efficiency. However, the work of Wang &amp; Wu <xref ref-type="bibr" rid="scirp.140802-42">
      [42]
     </xref> and Pathak et al. <xref ref-type="bibr" rid="scirp.140802-38">
      [38]
     </xref> suggest that larger pores in advanced filtration systems can enhance fluid throughput without compromising the removal of larger contaminants, making the materials suitable for dialysis and other high-throughput water treatment systems. Additionally, the uniform morphology supports findings by González-Esquivel et al. <xref ref-type="bibr" rid="scirp.140802-44">
      [44]
     </xref> that consistent structural characteristics are vital for reproducibility and efficiency in water purification technologies. The SEM analysis demonstrates that sol-gel-synthesized TiO<sub>2</sub> nanoparticles possess a unique combination of small particle size and hierarchical porous structure, enhancing their catalytic and filtration potential. These features make them particularly suited for water treatment systems, including dialysis, where high throughput and contaminant removal are crucial. The structural and morphological characteristics observed strongly align with recent advancements in nanotechnology and photocatalytic applications as described in previous studies. The study underscores the viability of using sol-gel-synthesized TiO<sub>2</sub> nanoparticles for water treatment applications, bridging material science and healthcare. The anatase phase formation and hierarchical structure offer a foundation for addressing water contamination challenges, particularly in dialysis systems where water purity is critical for patient safety. By optimizing the structural properties of these nanoparticles, the research contributes to the broader goal of improving water purification technologies, a focus highlighted in works like Xu &amp; Zhang <xref ref-type="bibr" rid="scirp.140802-51">
      [51]
     </xref> and Amara et al. <xref ref-type="bibr" rid="scirp.140802-46">
      [46]
     </xref>. The findings (<xref ref-type="fig" rid="fig3">
      Figure 3
     </xref>) have significant real-world implications, especially in healthcare settings requiring stringent water quality standards. The enhanced properties of TiO<sub>2</sub> nanoparticles can improve dialysis water treatment systems, reducing the risk of patient exposure to contaminants and enhancing overall health outcomes. Beyond dialysis, these nanoparticles can be applied in municipal water treatment facilities, industrial wastewater management, and portable filtration systems, addressing global challenges in water scarcity and contamination. Furthermore, the study’s insights into optimizing nanoparticle synthesis can guide future innovations in nanomaterial-based water purification technologies.</p>
   </sec>
   <sec id="s3_4">
    <title>3.4. Photocatalytic Activity of Titanium Dioxide Nanoparticles for Water Purification [UV]-[Vis Spectroscopy Analysis]</title>
    <p>The synthesized TiO<sub>2</sub> nanoparticles (<xref ref-type="fig" rid="fig4">
      Figure 4
     </xref>) exhibited strong photocatalytic properties, as demonstrated by UV-visible spectrum analysis. The absorption spectrum revealed significant activity in the UV range (320 - 340 nm), with peak absorbance values of 0.8701 at 320 nm and 1.0321 at 340 nm. A maximum absorption peak at 330 nm (<xref ref-type="fig" rid="fig5">
      Figure 5
     </xref>) further supported the synthesis of anatase-phase TiO<sub>2</sub> nanoparticles. These findings are consistent with the optimal analytical range (0.1 - 1.5) for photocatalytic applications <xref ref-type="bibr" rid="scirp.140802-52">
      [52]
     </xref> <xref ref-type="bibr" rid="scirp.140802-53">
      [53]
     </xref>. The absorption profile corresponds to the standard characteristics of anatase-phase TiO<sub>2</sub>, which typically demonstrates strong UV absorption between 300 and 400 nm. This suggests the successful synthesis of nanoparticles with desirable properties for photocatalytic applications. The confirmation of anatase-phase TiO<sub>2</sub> nanoparticles is significant due to this phase’s superior photocatalytic activity compared to the rutile phase. Anatase TiO<sub>2</sub> demonstrates enhanced electron-hole pair generation, which increases reactivity and reduces recombination under UV irradiation.</p>
    <fig id="fig4" position="float">
     <label>Figure 4</label>
     <caption>
      <title>Figure 4. Fabricated titanium dioxide nanoparticle based microporous filter.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId21.jpeg?20250226091017" />
    </fig>
    <fig id="fig5" position="float">
     <label>Figure 5</label>
     <caption>
      <title>Figure 5. Photocatalytic activity of titanium dioxide nanoparticles.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId22.jpeg?20250226091017" />
    </fig>
    <p>These properties are crucial for degrading contaminants in water. The ability of the synthesized nanoparticles to absorb UV light efficiently within the tested spectrum aligns with their potential use in water treatment, specifically in removing pollutants and improving water quality for industrial, domestic, and healthcare applications. This makes anatase-phase TiO<sub>2</sub> particularly advantageous for addressing global water challenges. The results align with existing literature emphasizing the effectiveness of TiO<sub>2</sub>-based photocatalysis in water treatment. Araña and Pulgarin <xref ref-type="bibr" rid="scirp.140802-54">
      [54]
     </xref> reviewed the superior photocatalytic disinfection capacity of TiO<sub>2</sub>, while Chong et al. <xref ref-type="bibr" rid="scirp.140802-55">
      [55]
     </xref> highlighted its efficiency in bacterial inactivation. Similarly, Elshafie and Ghanem <xref ref-type="bibr" rid="scirp.140802-56">
      [56]
     </xref> noted the practical utility of TiO<sub>2</sub> nanoparticles in hemodialysis water purification systems. Moreover, Makowski and Wardas <xref ref-type="bibr" rid="scirp.140802-57">
      [57]
     </xref> and Wei and Yang <xref ref-type="bibr" rid="scirp.140802-58">
      [58]
     </xref> demonstrated the relevance of TiO<sub>2</sub> for purifying drinking water in healthcare contexts. These findings are further supported by Liu et al. <xref ref-type="bibr" rid="scirp.140802-59">
      [59]
     </xref> and Kaur et al. <xref ref-type="bibr" rid="scirp.140802-47">
      [47]
     </xref>, who emphasized the innovations in nanotechnology that enhance TiO<sub>2</sub>’s photocatalytic efficiency. The consistency of the present study with prior research underscores the potential of anatase-phase TiO<sub>2</sub> nanoparticles in addressing water contamination challenges, particularly in healthcare and industrial applications. The study confirms the successful synthesis of anatase-phase TiO<sub>2</sub> nanoparticles with strong photocatalytic activity in the UV spectrum. These nanoparticles exhibit optimal properties for water purification due to enhanced UV absorption and photocatalytic reactivity, making them suitable for degrading contaminants effectively. This research contributes to the growing body of evidence supporting the application of TiO<sub>2</sub> nanoparticles in water purification technologies. By confirming the synthesis of high-performance anatase-phase TiO<sub>2</sub>, the study advances the development of more efficient and reliable water treatment solutions, addressing critical environmental and public health challenges.</p>
   </sec>
   <sec id="s3_5">
    <title>3.5. Effectiveness of TiO<sub>2</sub> Nanoparticles in Reducing Contaminant Concentrations in Water Treatment</title>
    <p>
     <xref ref-type="fig" rid="fig6">
      Figure 6
     </xref> illustrates the concentration (in ppm) of calcium (Ca), magnesium (Mg), aluminum (Al), and lead (Pb) before and after treatment across four test points: RC1, RC2, RC3, and TP. The results show a consistent reduction in the concentrations of all four elements after treatment. Magnesium demonstrates the highest initial concentrations, especially at RC2, followed by a significant reduction post-treatment. Calcium also shows notable decreases across all test points, while aluminum and lead exhibit smaller initial concentrations but still show reductions after treatment. The findings of <xref ref-type="fig" rid="fig6">
      Figure 6
     </xref> align closely with existing literature on the photocatalytic potential of TiO<sub>2</sub> nanoparticles in water treatment. Araña and Pulgarin <xref ref-type="bibr" rid="scirp.140802-54">
      [54]
     </xref> and Carey and Oliver <xref ref-type="bibr" rid="scirp.140802-60">
      [60]
     </xref> highlighted TiO<sub>2</sub>’s effectiveness in reducing heavy metals, including lead, during water disinfection and wastewater treatment. Similarly, Chong et al. <xref ref-type="bibr" rid="scirp.140802-55">
      [55]
     </xref> and Elshafie and Ghanem <xref ref-type="bibr" rid="scirp.140802-56">
      [56]
     </xref> emphasized TiO<sub>2</sub>’s ability to degrade contaminants and improve water quality for hemodialysis systems. Makowski and Wardas <xref ref-type="bibr" rid="scirp.140802-57">
      [57]
     </xref> confirmed its utility in removing aluminum and lead in drinking water purification, while Liu et al. <xref ref-type="bibr" rid="scirp.140802-59">
      [59]
     </xref> and Kaur et al. <xref ref-type="bibr" rid="scirp.140802-47">
      [47]
     </xref> noted advancements in TiO<sub>2</sub>-based nanotechnologies for enhanced contaminant removal. Additionally, Shiraishi and Matsumoto <xref ref-type="bibr" rid="scirp.140802-61">
      [61]
     </xref> supported its application in hemodialysis systems for trace metal elimination. The observed reductions in calcium and magnesium concentrations in <xref ref-type="fig" rid="fig6">
      Figure 6
     </xref> are consistent with Tiwari and Sharma’s <xref ref-type="bibr" rid="scirp.140802-43">
      [43]
     </xref> findings on TiO<sub>2</sub>’s role in addressing water hardness, further solidifying its versatility as a photocatalyst in diverse water treatment applications. The key finding from <xref ref-type="fig" rid="fig6">
      Figure 6
     </xref> is the effectiveness of the treatment method in reducing the concentrations of these metal ions, with magnesium showing the</p>
    <fig id="fig6" position="float">
     <label>Figure 6</label>
     <caption>
      <title>Figure 6. Spectrometry analysis before and after treatment.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId23.jpeg?20250226091018" />
    </fig>
    <p>most significant reduction. This outcome highlights the efficiency of the photocatalytic process, particularly for water contaminants that pose a risk to both environmental and public health. <xref ref-type="fig" rid="fig6">
      Figure 6
     </xref> underscores the effectiveness of the synthesized TiO<sub>2</sub> nanoparticles in removing harmful contaminants from water. The reduction in calcium, magnesium, aluminum, and lead concentrations demonstrates the utility of this treatment in mitigating water pollution and improving water quality. The findings are aligned with the broader aim of utilizing photocatalysis as a sustainable and effective water purification strategy, particularly for environments with complex contamination profiles. These results have substantial implications for environmental management, public health, and industrial applications. For example, the ability to reduce lead, a known toxic heavy metal can address public health challenges, particularly in regions reliant on untreated water. The process’s effectiveness for magnesium and calcium also points to its potential in addressing scaling issues in industrial water systems. Furthermore, this technology could significantly benefit hemodialysis systems, ensuring water safety for patients in healthcare settings.</p>
   </sec>
   <sec id="s3_6">
    <title>3.6. Evaluation of Treatment Efficacy on Microbial Loads and Water Quality Parameters</title>
    <p>
     <xref ref-type="table" rid="table3">
      Table 3
     </xref> and <xref ref-type="fig" rid="fig7">
      Figure 7
     </xref> show the total viable counts (TVC in cfu/ml), endotoxin units (EU in EU/ml), and pH levels of water samples across four categories: RC1, RC2, RC3, and TP. TVC values after treatment ranged from 8.96 to 15.89 cfu/ml, while EU levels ranged between 0.15 and 1.5 EU/ml. The pH values varied between 6.5 and 7.4. The corresponding <xref ref-type="fig" rid="fig8">
      Figure 8
     </xref> illustrates a significant reduction in TVC for all water samples post-treatment, with reductions ranging from approximately 78% to 85% relative to pre-treatment values. The highest TVC reduction occurred in RC1, while TP displayed the highest post-treatment TVC concentration. The primary takeaway is the effectiveness of the applied treatment in significantly reducing microbial loads (TVC) across all samples, suggesting a robust disinfection process. The pH values remained within acceptable drinking water standards, further supporting the treatment’s suitability for water purification. The variations in EU levels reflect the residual microbial byproducts, with TP showing the highest endotoxin levels, indicating room for optimization in the treatment process. These findings are pivotal in advancing water treatment methodologies, particularly for settings requiring stringent microbial load control, such as healthcare and hemodialysis. The results align with findings from numerous studies highlighting the efficacy of titanium dioxide (TiO<sub>2</sub>) photocatalysis in water disinfection. Araña and Pulgarin <xref ref-type="bibr" rid="scirp.140802-54">
      [54]
     </xref> emphasized TiO<sub>2</sub>’s capacity to reduce microbial loads, corroborating the observed TVC reductions. Carey and Oliver <xref ref-type="bibr" rid="scirp.140802-60">
      [60]
     </xref> similarly reported significant microbial reductions in wastewater treated with TiO<sub>2</sub>. Chong et al. <xref ref-type="bibr" rid="scirp.140802-55">
      [55]
     </xref> confirmed TiO<sub>2</sub>’s potential for deactivating bacteria and degrading microbial byproducts, consistent with reduced EU levels in this study. Elshafie and Ghanem <xref ref-type="bibr" rid="scirp.140802-56">
      [56]
     </xref> documented TiO<sub>2</sub>’s utility in hemodialysis systems,</p>
    <table-wrap id="table3">
     <label>
      <xref ref-type="table" rid="table3">
       Table 3
      </xref></label>
     <caption>
      <title>
       <xref ref-type="bibr" rid="scirp.140802-"></xref>Table 3. TVC, EU, and pH analysis after treatment.</title>
     </caption>
     <table class="MsoTableGrid custom-table" border="0" cellspacing="0" cellpadding="0"> 
      <tr> 
       <td class="custom-bottom-td acenter" width="23.12%"><p style="text-align:center">Water sample</p></td> 
       <td class="custom-bottom-td acenter" width="24.24%"><p style="text-align:center">TVC (cfu/ml)</p></td> 
       <td class="custom-bottom-td acenter" width="26.32%"><p style="text-align:center">EU (EU/ml)</p></td> 
       <td class="custom-bottom-td acenter" width="26.32%"><p style="text-align:center">pH</p></td> 
      </tr> 
      <tr> 
       <td class="custom-top-td acenter" width="23.12%"><p style="text-align:center">RC1</p></td> 
       <td class="custom-top-td acenter" width="24.24%"><p style="text-align:center">9.65</p></td> 
       <td class="custom-top-td acenter" width="26.32%"><p style="text-align:center">0.15</p></td> 
       <td class="custom-top-td acenter" width="26.32%"><p style="text-align:center">6.8</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="23.12%"><p style="text-align:center">RC2</p></td> 
       <td class="acenter" width="24.24%"><p style="text-align:center">10.65</p></td> 
       <td class="acenter" width="26.32%"><p style="text-align:center">0.26</p></td> 
       <td class="acenter" width="26.32%"><p style="text-align:center">6.5</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="23.12%"><p style="text-align:center">RC3</p></td> 
       <td class="acenter" width="24.24%"><p style="text-align:center">8.96</p></td> 
       <td class="acenter" width="26.32%"><p style="text-align:center">0.41</p></td> 
       <td class="acenter" width="26.32%"><p style="text-align:center">6.9</p></td> 
      </tr> 
      <tr> 
       <td class="acenter" width="23.12%"><p style="text-align:center">TP</p></td> 
       <td class="acenter" width="24.24%"><p style="text-align:center">15.89</p></td> 
       <td class="acenter" width="26.32%"><p style="text-align:center">1.5</p></td> 
       <td class="acenter" width="26.32%"><p style="text-align:center">7.4</p></td> 
      </tr> 
     </table>
    </table-wrap>
    <fig id="fig7" position="float">
     <label>Figure 7</label>
     <caption>
      <title>Figure 7. Shows the EU (Endotoxin Unit) and pH values across the water samples on separate axes.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId24.jpeg?20250226091019" />
    </fig>
    <fig id="fig8" position="float">
     <label>Figure 8</label>
     <caption>
      <title>Figure 8. Total Viable Count (TVC) analysis result before and after water treatment.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId25.jpeg?20250226091020" />
    </fig>
    <p>improving water quality by removing microbial contaminants. Makowski and Wardas <xref ref-type="bibr" rid="scirp.140802-57">
      [57]
     </xref> reinforced the role of TiO<sub>2</sub> in microbial load reduction for drinking water applications. Shiraishi and Matsumoto <xref ref-type="bibr" rid="scirp.140802-61">
      [61]
     </xref> explored TiO<sub>2</sub>’s application in hemodialysis water purification, noting its effectiveness in removing microbial byproducts like endotoxins. Lastly, Tiwari and Sharma <xref ref-type="bibr" rid="scirp.140802-43">
      [43]
     </xref> (2023) emphasized TiO<sub>2</sub>’s role in achieving substantial reductions in microbial counts and maintaining water quality, mirroring this study’s findings. Collectively, these studies validate the treatment method’s effectiveness and its broad potential in water purification. This study’s findings have significant real-world implications. The demonstrated reduction in microbial loads highlights the potential application of the treatment in critical sectors like hemodialysis water systems and healthcare settings, where water purity directly impacts patient safety. Additionally, this approach can enhance public health outcomes in regions with limited access to advanced water treatment facilities. The manageable pH range after treatment supports its application in drinking water systems, aligning with global water safety standards.</p>
    <p>Consequently, endotoxin levels (<xref ref-type="table" rid="table3">
      Table 3
     </xref>) showed significant improvement after TiO<sub>2</sub> nanoparticle-based dialysis water purification process. The most significant reduction was observed in the UT sample, which decreased from 1.97 to 0.26 EU/ml, equivalent to an 86.8% reduction. BT and LT samples showed similar improvements with reductions of 86.0% and 83.6%, respectively, represented in <xref ref-type="fig" rid="fig9">
      Figure 9
     </xref>. While showing less dramatic improvement, the tap water sample still achieved a 62.0% reduction from 3.95 to 1.50 EU/ml.</p>
    <fig id="fig9" position="float">
     <label>Figure 9</label>
     <caption>
      <title>Figure 9. EU analysis result before and after water treatment.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId26.jpeg?20250226091020" />
    </fig>
   </sec>
   <sec id="s3_7">
    <title>
     <xref ref-type="bibr" rid="scirp.140802-"></xref>3.7. Performance of TiO<sub>2</sub>-Based Microporous Filters in pH Regulation and Contaminant Removal</title>
    <p>The TiO<sub>2</sub>-based microporous filter demonstrated effective pH regulation, consistently adjusting water samples to values within the AAMI/ISO standards of 6.5-7.5. The tap water sample showed the most significant improvement, with its pH reduced from 8.2 to 7.4 (<xref ref-type="fig" rid="fig10">
      Figure 10
     </xref>). This consistency throughout the filtration process underscores the filter’s reliability in maintaining optimal pH levels, a critical parameter for applications such as dialysis water treatment. The effectiveness of the filter is likely due to its ability to integrate multiple purification mechanisms, including photocatalytic degradation, adsorption of metal ions, and physical filtration through a well-optimized pore structure. The superior performance of the TiO<sub>2</sub>-based filter can be attributed to the synergistic actions of its mechanisms. Photocatalytic degradation, powered by TiO<sub>2</sub> nanoparticles, breaks down organic contaminants, while metal ion adsorption enhances water quality by removing impurities. Additionally, the microporous design ensures efficient physical filtration. Together, these mechanisms contribute to significant reductions in chemical and biological contaminants, supporting the potential of this system as an additional purification step in dialysis water treatment facilities. This aligns with findings by Rincón &amp; Pulgarin <xref ref-type="bibr" rid="scirp.140802-62">
      [62]
     </xref> and Wei &amp; Yang <xref ref-type="bibr" rid="scirp.140802-58">
      [58]
     </xref>, who highlighted TiO<sub>2</sub>’s efficacy in hemodialysis water systems and its role in achieving high purification standards. The results also align with Araña &amp; Pulgarin <xref ref-type="bibr" rid="scirp.140802-54">
      [54]
     </xref> and Makowski &amp; Wardas <xref ref-type="bibr" rid="scirp.140802-57">
      [57]
     </xref>, who emphasized the ability of TiO<sub>2</sub> to stabilize pH while effectively removing contaminants in drinking water applications. Furthermore, Elshafie &amp; Ghanem <xref ref-type="bibr" rid="scirp.140802-56">
      [56]
     </xref> documented TiO<sub>2</sub>’s role in improving dialysis water quality by targeting metallic impurities and pH optimization. Liu et al. <xref ref-type="bibr" rid="scirp.140802-59">
      [59]
     </xref> and Kaur et al. <xref ref-type="bibr" rid="scirp.140802-47">
      [47]
     </xref> further underscore advancements in TiO<sub>2</sub> nanotechnology, linking these innovations to improved performance in healthcare and water treatment environments. These findings have significant real-world implications, as it demonstrated the ability to regulate pH and remove contaminants positions TiO<sub>2</sub>-based filtration systems as a cost-effective, scalable solution for healthcare facilities, particularly for dialysis water systems. The results also complement previous research on TiO<sub>2</sub>’s multifunctionality, as reported by Carey &amp; Oliver <xref ref-type="bibr" rid="scirp.140802-60">
      [60]
     </xref> and</p>
    <fig id="fig10" position="float">
     <label>Figure 10</label>
     <caption>
      <title>Figure 10. pH analysis of renal and tap water samples before and after water treatment.</title>
     </caption>
     <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId27.jpeg?20250226091021" />
    </fig>
    <p>Selma &amp; Pacheco-Moisés <xref ref-type="bibr" rid="scirp.140802-63">
      [63]
     </xref>. Future applications could extend beyond dialysis to include broader water treatment and environmental remediation efforts, aligning with global public health goals and sustainability practices.</p>
   </sec>
  </sec><sec id="s4">
   <title>4. Conclusion</title>
   <p>This study underscores the potential of titanium dioxide (TiO<sub>2</sub>)-based nanoparticle microporous filters in advancing dialysis water purification. The sol-gel synthesized TiO<sub>2</sub> nanoparticles, with an average size of 1.45 nm and a pore diameter of 4.11 µm, demonstrated excellent properties for removing both chemical and microbiological contaminants. The filtration system achieved substantial reductions in calcium, magnesium, aluminum, lead, total viable count (TVC), and endotoxin units (EU). Additionally, it maintained pH levels within the AAMI and ISO recommended range (6.5 - 7.5) for dialysis water, an essential factor for patient safety in hemodialysis care. The photocatalytic activity of anatase-phase TiO<sub>2</sub>, which optimally absorbs UV light in the 320 - 340 nm range, contributed significantly to its performance, highlighting its role as an effective additional treatment step in existing dialysis water systems. Moreover, these findings have important implications for improving dialysis water quality and supporting better patient outcomes, particularly in resource-limited environments. The system’s demonstrated efficiency and practicality offer valuable insights for enhancing water treatment technologies in healthcare. However, limitations in long-term durability and scalability point to the need for further research to optimize the filter system and evaluate its performance over extended use. Addressing these challenges will be critical for facilitating large-scale clinical implementation and ensuring sustainable improvements in renal care.</p>
  </sec><sec id="s5">
   <title>5. Policy Implication</title>
   <p>This research underscores the need for stringent policies addressing water purification standards in hemodialysis centers. Policymakers should adopt evidence-based guidelines emphasizing innovative solutions like nanoparticle-based filtration systems. Investments in infrastructure to support such advancements will enhance compliance with global standards, reducing health risks associated with suboptimal water quality. Additionally, integrating these technologies into national health frameworks could improve patient outcomes while promoting sustainable practices in medical waste management. By prioritizing water safety in dialysis centers, this study informs broader public health strategies aimed at achieving universal healthcare goals.</p>
  </sec><sec id="s6">
   <title>6. Recommendation</title>
   <p>The findings of this study advocate for the adoption of TiO<sub>2</sub>-based nanoparticle filters in dialysis centers to improve water quality. Conducting pilot implementations in diverse healthcare facilities can help assess operational feasibility and refine the system for large-scale application. Training healthcare professionals in</p>
   <fig id="fig11" position="float">
    <label>Figure 11</label>
    <caption>
     <title>Figure 11. Integration of healthcare water safety and innovative filtration systems.</title>
    </caption>
    <graphic mimetype="image" position="float" xlink:type="simple" xlink:href="https://html.scirp.org/file/2610508-rId28.jpeg?20250226091025" />
   </fig>
   <p>maintenance protocols will ensure sustained efficiency. Future research should explore cost-effective production methods and evaluate long-term impacts on patient health. Collaboration between researchers, healthcare providers, and policymakers will be key to scaling this innovation while addressing existing gaps in water safety for dialysis.</p>
  </sec><sec id="s7">
   <title>7. Significance of Health Statement</title>
   <p>This study addresses a critical healthcare challenge by developing a filtration system capable of significantly reducing contaminants in hemodialysis water. By tackling both chemical and microbiological pollutants, the research aligns with global efforts to improve renal care and reduce waterborne risks for vulnerable populations. This advancement could lower complications associated with dialysis, enhancing the quality of life for patients with end-stage renal disease. It also emphasizes the importance of safe water in healthcare settings, contributing to broader public health initiatives and advancing sustainable development goals in health and well-being. Thus, graphically it is represented as <xref ref-type="fig" rid="fig11">
     Figure 11
    </xref> above.</p>
  </sec><sec id="s8">
   <title>Authors Contribution</title>
   <p>All authors contributed equally to conceptualization, validation, writing review and editing.</p>
  </sec><sec id="s9">
   <title>Acknowledgments</title>
   <p>The authors would like to express their appreciation to all anonymous reviewers, for feedback and discussions that helped to substantially improve this manuscript.</p>
  </sec><sec id="s10">
   <title>Preprint Version</title>
   <p>Enang OT, Azeez BO, Ogunyemi BT, Sulayman AA, Araromi DO, Raimi MO (2025) Innovative Water Purification for Hemodialysis: TiO<sub>2</sub> Nanoparticle-Based Microporous Filter Development and Analysis. JMIR Preprints. 27/01/2025:71835. DOI: 10.2196/preprints.71835. URL: <xref ref-type="bibr" rid="scirp.140802-https://preprints">
     https://preprints.jmir.org/preprint/71835.
    </xref></p>
  </sec>
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