EU TPO COSMETICS BAN

The September Purge: Europe’s War on Hidden Chemical Dangers

The European Union’s total ban on triphenylphosphine oxide (TPO) in cosmetic products, effective September 1, 2025, represents more than regulatory housekeeping—it embodies Europe’s increasingly aggressive stance against chemical ingredients that may pose long-term health risks even when present in trace amounts. This prohibition reflects a fundamental shift in consumer protection philosophy, where the precautionary principle trumps industry convenience and where European regulators are willing to disrupt global supply chains to eliminate substances that most consumers have never heard of but encounter daily.

The TPO Chemical Profile Triphenylphosphine oxide presents a complex regulatory challenge:

Industrial Applications: Widely used as catalyst and flame retardant in various manufacturing processes Cosmetic Function: Serving as stabilizer, antioxidant, and processing aid in beauty products Ubiquitous Presence: Found in everything from lipsticks and foundations to shampoos and moisturizers Trace Concentrations: Often present in minute quantities as manufacturing byproduct rather than intentional ingredient Detection Challenges: Requiring sophisticated analytical methods to identify and quantify

The Health Concerns Scientific research has identified multiple potential risks associated with TPO exposure:

Endocrine Disruption: Potential interference with hormonal systems affecting reproduction and development Skin Sensitization: Allergic reactions and contact dermatitis in sensitive individuals Bioaccumulation: Substance potentially building up in body tissues over time Environmental Persistence: Chemical stability leading to long-term environmental contamination Synergistic Effects: Unknown interactions with other cosmetic chemicals creating amplified risks

The Regulatory Evolution The TPO ban reflects Europe’s increasingly precautious approach to chemical safety:

REACH Regulation: Comprehensive chemical registration and evaluation system identifying problematic substances Cosmetics Regulation: Specific rules governing safety and composition of beauty products Scientific Committees: Expert panels evaluating emerging evidence about chemical risks Stakeholder Consultation: Industry and consumer group input informing regulatory decisions International Coordination: Cooperation with other regulatory agencies worldwide

The Industry Impact Cosmetic manufacturers face significant challenges adapting to the TPO prohibition:

Reformulation Costs: Expensive research and development to replace TPO in existing products Supply Chain Disruption: Need to verify TPO absence throughout complex ingredient networks Testing Requirements: Enhanced analytical testing to ensure compliance with ban Market Timing: Pressure to reformulate products before September 1 deadline Competitive Implications: Companies with TPO-free formulations gaining market advantages

The Consumer Perspective Most cosmetic users remain unaware of TPO presence and the reasons for its prohibition:

Ingredient Literacy: Limited consumer understanding of chemical names and functions Trust Assumptions: Belief that regulated products are inherently safe Price Sensitivity: Potential cost increases from reformulation affecting purchasing decisions Brand Loyalty: Consumer attachment to specific products potentially containing TPO Health Awareness: Growing concern about chemical exposure driving demand for “clean” cosmetics

The Global Implications Europe’s TPO ban influences international cosmetic regulation and trade:

Regulatory Leadership: EU standards often becoming global benchmarks for chemical safety Trade Barriers: Non-compliant products excluded from lucrative European market Harmonization Pressure: Other countries considering similar bans to maintain trade relationships Innovation Incentives: Global companies developing TPO-free alternatives for worldwide use Competitive Dynamics: European companies potentially gaining advantages in TPO-free product development

The Scientific Debate The evidence supporting TPO prohibition remains subject to ongoing scientific discussion:

Risk Assessment: Evaluation of exposure levels versus potential health effects Study Limitations: Challenges in conducting long-term human health studies Mechanistic Understanding: Incomplete knowledge of how TPO affects biological systems Dose-Response Relationships: Uncertainty about safe exposure levels and thresholds Alternative Assessments: Comparative safety evaluation of TPO replacement chemicals

The Precautionary Principle Europe’s approach reflects philosophical commitment to preventing potential harm:

Burden of Proof: Requiring industry to demonstrate safety rather than regulators proving harm Uncertainty Management: Acting on potential risks even without definitive scientific proof Long-term Thinking: Prioritizing future health outcomes over immediate economic considerations Democratic Values: Reflecting European public preferences for strict chemical regulation Risk Communication: Transparent discussion of scientific uncertainty and regulatory rationale

The Enforcement Challenge Implementing the TPO ban requires sophisticated monitoring and compliance systems:

Analytical Methods: Developing standardized testing procedures for TPO detection Market Surveillance: Regular testing of cosmetic products for banned substances Import Controls: Screening products from countries with different regulatory standards Penalty Frameworks: Establishing meaningful consequences for non-compliance Industry Cooperation: Working with manufacturers to ensure voluntary compliance

The Economic Calculations The TPO ban involves complex cost-benefit analysis:

Health Benefits: Potential reduction in allergic reactions and long-term health risks Economic Costs: Industry reformulation expenses and potential price increases Innovation Stimulus: Regulatory pressure driving development of safer alternatives Competitive Effects: Market advantages for companies already using TPO-free formulations Social Values: European willingness to pay for enhanced chemical safety

The Alternative Development Replacing TPO requires identifying safer chemical alternatives:

Functional Equivalents: Chemicals providing similar stabilizing and antioxidant effects Safety Profiles: Comprehensive evaluation of replacement chemical risks Performance Testing: Ensuring alternatives maintain product quality and effectiveness Cost Considerations: Economic viability of TPO replacements for widespread use Innovation Opportunities: Potential for breakthrough technologies eliminating need for chemical additives

The Consumer Education Need Successful implementation requires informed public understanding:

Chemical Literacy: Educating consumers about cosmetic ingredients and their functions Risk Communication: Explaining scientific rationale for TPO prohibition Product Labeling: Clear identification of TPO-free products for conscious consumers Media Coverage: Responsible reporting about chemical risks and regulatory responses Industry Transparency: Manufacturer communication about reformulation efforts and timeline

The International Harmonization Europe’s TPO ban may influence global cosmetic regulation:

Regulatory Convergence: Other countries potentially adopting similar prohibitions Trade Facilitation: Harmonized standards reducing barriers to international commerce Scientific Cooperation: Shared research and risk assessment across regulatory agencies Industry Standardization: Global companies adopting single formulations meeting strictest standards Consumer Protection: Worldwide improvement in cosmetic safety through European leadership

The Technology Innovation The TPO ban stimulates development of advanced cosmetic technologies:

Green Chemistry: Environmentally friendly alternatives to traditional chemical additives Nanotechnology: Novel approaches to product stabilization and preservation Biotechnology: Biological alternatives to synthetic chemical ingredients Smart Formulations: Products adapting to individual skin needs without problematic additives Analytical Advances: Improved methods for detecting and quantifying trace chemicals

The Long-term Vision The TPO prohibition represents broader transformation in cosmetic regulation:

Chemical Minimalism: Trend toward products with fewer synthetic additives Transparency Requirements: Enhanced disclosure of ingredient sources and functions Personalized Safety: Customized products based on individual chemical sensitivities Circular Economy: Sustainable cosmetic production and packaging systems Global Standards: Worldwide convergence on strict chemical safety requirements

The Industry Adaptation Cosmetic companies are developing various strategies for TPO compliance:

Reformulation Programs: Systematic replacement of TPO across product lines Supply Chain Audits: Comprehensive verification of ingredient sources and processing Alternative Research: Investment in developing safer chemical substitutes Consumer Communication: Marketing campaigns highlighting TPO-free formulations Regulatory Engagement: Active participation in policy development and implementation

The Broader Implications The TPO ban reflects changing relationships between regulation, industry, and consumers:

Regulatory Activism: Government willingness to intervene in markets for public health Consumer Empowerment: Informed consumers driving demand for safer products Industry Responsibility: Corporate accountability for long-term health and environmental effects Scientific Integration: Evidence-based policy making incorporating latest research findings Democratic Participation: Public involvement in regulatory decision-making processes

Conclusions:

1. The European Union’s total ban on triphenylphosphine oxide in cosmetic products, effective September 1, 2025, represents far more than the prohibition of an obscure chemical—it embodies Europe’s commitment to protecting consumers from potential health risks even when the science remains uncertain and the economic costs are substantial.

2. This regulatory action reflects a fundamental philosophical shift in how societies balance economic interests against public health concerns. Rather than waiting for definitive proof of harm, European regulators have chosen to act on emerging evidence suggesting that TPO may pose risks to human health and the environment. This precautionary approach prioritizes long-term safety over short-term convenience and industry profits.

3. For consumers, the TPO ban represents both protection and disruption. While most people have never heard of triphenylphosphine oxide, they encounter it daily in products they trust to enhance their appearance and well-being. The prohibition ensures that future cosmetic use won’t expose them to a potentially harmful substance, but it may also result in higher prices, reformulated products, and temporary market disruptions as manufacturers scramble to comply.

4. The cosmetic industry faces significant challenges in adapting to the new reality. Companies must invest heavily in reformulation, supply chain verification, and analytical testing to ensure compliance. Those that have already developed TPO-free alternatives may gain competitive advantages, while others may struggle to maintain product quality and affordability while meeting the September deadline.

5. Perhaps most significantly, Europe’s TPO ban demonstrates the continent’s growing influence over global cosmetic standards. When the world’s largest cosmetic market prohibits a substance, manufacturers worldwide often find it more economical to eliminate that ingredient entirely rather than maintain separate formulations for different markets. This “Brussels Effect” means that European regulatory decisions increasingly shape global product standards.

6. The ban also reflects changing consumer expectations about cosmetic safety. Modern consumers are increasingly sophisticated about ingredient lists, more concerned about long-term health effects, and more demanding of transparency from manufacturers. The TPO prohibition responds to these evolving preferences while potentially accelerating the trend toward “clean” cosmetics with minimal synthetic additives.

7. From a scientific perspective, the TPO ban represents both precaution and uncertainty. While evidence suggests potential risks from TPO exposure, definitive proof of harm remains elusive. This regulatory approach acknowledges that waiting for complete scientific certainty might mean accepting preventable health risks, especially when safer alternatives are available.

8. The September 1 implementation date creates urgency for all stakeholders. Manufacturers must complete reformulation and testing, regulators must prepare enforcement mechanisms, and consumers must prepare for potential changes in their favorite products. The success of this transition will influence future regulatory approaches to emerging chemical risks.

9. Ultimately, the TPO ban symbolizes Europe’s vision of consumer protection in the 21st century: proactive rather than reactive, precautionary rather than permissive, and willing to prioritize long-term health over short-term economic considerations. Whether this approach proves wise will depend on the balance between enhanced safety and economic costs, but it clearly establishes Europe as the global leader in cosmetic safety regulation.

10. The countdown to September 1 has begun, and with it, a new chapter in the relationship between chemistry, commerce, and consumer protection. The TPO ban may be just the beginning of a broader transformation in how societies regulate the chemicals that surround us daily, starting with the products we apply to our skin in pursuit of beauty and well-being.

11. For the companies, who coughed by surprise – we would like to offer help within LIFE FIT FOR REACH Project, where we are offering help in identifying substitutes to the chemicals, which are on the list of Substances of Very High Concern (SVHC). Please register to our contact form:

Shanghai Ranking 2023: Which Universities Rule the World of Science and Why?

Introduction: What is the Shanghai Ranking (ARWU)?

The Shanghai Ranking, officially known as the Academic Ranking of World Universities (ARWU), is one of the most prestigious global university rankings. It was established in 2003 by Shanghai Jiao Tong University and evaluates institutions primarily based on academic and research performance. Its criteria include the number of Nobel Prize winners among alumni and staff, the number of highly cited researchers, and the volume of articles published in top-tier journals like Nature and Science.

The 2023 ranking once again confirmed the dominance of American and British universities, but it also showed the advancement of institutions from Asia and continental Europe.


TOP 10 Universities in the World in 2023

  1. Harvard University (USA) – 1st place (consistently for years!)
  2. Stanford University (USA)
  3. Massachusetts Institute of Technology (MIT) (USA)
  4. University of Cambridge (United Kingdom)
  5. University of California, Berkeley (USA)
  6. Princeton University (USA)
  7. University of Oxford (United Kingdom)
  8. Columbia University (USA)
  9. California Institute of Technology (Caltech) (USA)
  10. University of Chicago (USA)

Key Observation:

  • 8 out of the top 10 universities are American, with two British institutions (Cambridge and Oxford) maintaining their elite status.
  • Why? These universities have enormous research budgets, employ the most distinguished scientists (including Nobel laureates), and attract the best students from around the world.

Which Universities Are Advancing the Fastest?

1. Chinese Universities – The Scientific Powerhouse of the East

  • Tsinghua University (22nd place) and Peking University (29th) – both in the TOP 30.
  • Fudan University and Shanghai Jiao Tong University are in the TOP 100.
  • Why? Massive government investment in science, collaboration with Western universities, and programs designed to attract international researchers.

2. Singapore – A Tiny Country with a Big Scientific Impact

  • National University of Singapore (NUS) – 71st place
  • Nanyang Technological University (NTU) – 88th place
  • Why? Strong funding for technology and engineering, and a high degree of openness to international collaboration.

3. Continental Europe – A Stable Presence

  • ETH Zurich (Switzerland) – 20th place (the highest-ranked in continental Europe)
  • Karolinska Institutet (Sweden) – 39th place (a leader in medicine)
  • University of Copenhagen (Denmark) – TOP 100
  • Why? High levels of research funding, strong academic traditions, and international cooperation.

Why Are Some Universities So Highly Ranked? Key Success Factors

  1. Money = Better Science
    • Harvard has an endowment of approximately $50 billion (larger than the GDP of some countries!).
    • American and British universities receive huge grants from the government and private companies.
  2. Nobel Laureates and World-Class Scientists
    • The ARWU ranking heavily rewards universities whose alumni or staff have won Nobel Prizes.
    • For example, Cambridge and MIT each have several dozen Nobel laureates associated with them.
  3. Prestigious Publications
    • Universities in the TOP 100 regularly publish in Nature and Science, which boosts their score.
  4. International Collaboration
    • The best universities attract students and scientists from all over the world, creating global research networks.

What Are the Implications?

  • Science is a financial race – Without significant funding, it is difficult to compete with Harvard or MIT.
  • Asia is rising in power – China and Singapore are investing heavily in science and are already catching up with the West.
  • Europe maintains its standard but lacks giants – ETH Zurich and Karolinska Institutet are excellent, but they don’t have the budgets of American universities.
  • Poland is far behind – The absence of a Polish university in the TOP 300 shows that without greater investment in science, advancement is difficult.

Summary

The Shanghai Ranking shows that science is a global game of prestige, money, and talent. American and British universities still rule, but Asia and continental Europe are gradually increasing their presence. Poland still has a lot of catching up to do, but the example of China shows that consistent investment can yield results.

Could Poland ever join the world’s elite? It’s possible, but it would require significantly greater funding for science, attracting international talent, and better collaboration with global research centers.

Integrating EMAS with Chemical Risk Management (CRM): Strengthening Sustainability and Compliance

In today’s industrial landscape, managing chemical risks is a critical component of environmental and occupational safety. Companies handling hazardous substances must comply with stringent regulations while minimizing their environmental footprint. The Eco-Management and Audit Scheme (EMAS), a robust EU environmental management framework, can play a pivotal role in enhancing Chemical Risk Management (CRM) by integrating systematic monitoring, compliance assurance, and continuous improvement.

This article explores how EMAS and CRM can be synergized to improve regulatory compliance, operational safety, and sustainability performance.


Understanding EMAS and Chemical Risk Management (CRM)

EMAS: A Framework for Environmental Excellence

EMAS is a voluntary EU certification that helps organizations establish an Environmental Management System (EMS), ensuring legal compliance, transparency, and continuous environmental improvement. Key elements include:

  • Environmental Policy & Legal Compliance – Ensuring adherence to regulations such as REACH, CLP, and Seveso III.
  • Risk Assessment & Mitigation – Identifying and reducing environmental impacts, including those from hazardous chemicals.
  • Performance Tracking & Reporting – Publicly disclosing environmental data, verified by third-party audits.

Chemical Risk Management (CRM): Safeguarding People and the Planet

CRM involves:

  • Hazard Identification – Assessing chemical risks to workers, communities, and ecosystems.
  • Exposure Control – Implementing safety measures (e.g., substitution, engineering controls, PPE).
  • Regulatory Compliance – Meeting requirements under REACH, CLP, OSHA, and other chemical safety laws.
  • Emergency Preparedness – Developing response plans for chemical spills or accidents.

The Synergy Between EMAS and CRM

Integrating EMAS with CRM enhances both environmental and occupational safety performance while ensuring compliance with evolving regulations. Key benefits include:

1. Enhanced Regulatory Compliance

  • EMAS requires organizations to monitor and comply with environmental laws, including chemical safety regulations.
  • CRM processes (e.g., safety data sheets, exposure limits) can be systematically tracked within the EMAS framework.

2. Improved Hazard Identification & Risk Reduction

  • EMAS promotes lifecycle thinking, encouraging substitution of hazardous chemicals with safer alternatives.
  • CRM data (e.g., toxicity levels, storage conditions) feeds into EMAS risk assessments, supporting preventive action.

3. Transparent Reporting & Stakeholder Trust

  • EMAS mandates public environmental statements, which can include chemical safety performance.
  • Verified CRM data (e.g., reduced chemical emissions, safer handling practices) strengthens corporate sustainability reporting under frameworks like CSRD.

4. Operational Efficiency & Cost Savings

  • Reducing chemical waste and optimizing usage aligns with EMAS-driven resource efficiency.
  • Lower risks of non-compliance fines and workplace incidents lead to long-term cost reductions.

Practical Steps for Integration

  1. Align EMAS EMS with CRM Processes
    • Incorporate chemical risk assessments into EMAS environmental reviews.
    • Track chemical usage, emissions, and incidents within the EMAS monitoring system.
  2. Leverage EMAS for Compliance & Best Practices
    • Use EMAS audits to verify compliance with REACH, Seveso III, and industrial emissions directives.
    • Adopt green chemistry principles (e.g., safer substitutes, closed-loop systems) as part of continuous improvement.
  3. Strengthen Emergency Preparedness
    • Integrate chemical spill response plans into EMAS emergency procedures.
    • Train employees on both environmental and chemical safety protocols.
  4. Enhance Reporting & ESG Alignment
    • Include CRM metrics (e.g., reduced hazardous substance use) in EMAS environmental statements and ESG reports.
    • Use EMAS verification to add credibility to sustainability disclosures.

Challenges & Opportunities

Challenges:

  • Data Complexity – Harmonizing CRM data with EMAS indicators requires structured systems.
  • Regulatory Evolution – Keeping up with changing chemical laws (e.g., EU Green Deal, PFAS restrictions).

Opportunities:

  • Competitive Advantage – Demonstrating leadership in safe and sustainable chemical management.
  • Innovation – Developing low-impact chemical processes that align with circular economy goals.

Conclusion

The integration of EMAS and Chemical Risk Management creates a powerful approach to sustainability, compliance, and workplace safety. By leveraging EMAS’s structured environmental management system, companies can systematically reduce chemical risks, improve transparency, and meet regulatory demands.

For organizations handling hazardous substances, this integration is not just a compliance exercise—it’s a strategic opportunity to build resilience, enhance reputation, and drive long-term sustainability.


Is your organization ready to strengthen its chemical risk management with EMAS? Stay ahead of regulatory demands and explore best practices at the upcoming “FUTURE WITH EMAS” conference on November 6-7, 2025, in Warsaw. Reserve your spot now by contacting us through the contact form!

#EMAS #EnvironmentalManagement #SustainableBusiness #CRM #Sustainability #Business #FitforREACH #POMInnO

Integrating EMAS and ESG: A Pathway to Sustainable Business Practices

In today’s business landscape, sustainability is no longer optional—it’s a necessity. Companies are increasingly expected to demonstrate their commitment to environmental and social responsibility. Two key frameworks that help organizations achieve this are EMAS (Eco-Management and Audit Scheme) and ESG (Environmental, Social, and Governance). While EMAS focuses on environmental management, ESG encompasses a broader range of sustainability criteria. Integrating these frameworks can provide a robust foundation for sustainable business practices and compliance with evolving regulations.


Understanding EMAS and ESG

EMAS: A Focus on Environmental Excellence

EMAS is a voluntary EU framework designed to help organizations evaluate, report, and improve their environmental performance. Key features include:

  • Environmental Management Systems (EMS): Aligned with ISO 14001, EMAS requires organizations to establish and maintain an EMS.
  • Legal Compliance: Organizations must demonstrate adherence to environmental regulations.
  • Transparency: Regular environmental reporting and third-party verification ensure credibility.
  • Continuous Improvement: EMAS encourages ongoing efforts to reduce environmental impacts.

ESG: A Holistic Approach to Sustainability

ESG criteria evaluate a company’s performance in three areas:

  1. Environmental: Climate change mitigation, resource efficiency, pollution control.
  2. Social: Labor practices, human rights, community engagement.
  3. Governance: Ethical business practices, transparency, anti-corruption measures.

ESG reporting is becoming mandatory for many companies under regulations like the EU’s Corporate Sustainability Reporting Directive (CSRD).


The Synergy Between EMAS and ESG

Integrating EMAS with ESG reporting offers several advantages:

1. Data Collection and Standardization

EMAS provides a structured framework for collecting environmental data, such as energy consumption, carbon footprint, and water usage. This data is directly applicable to the “E” (Environmental) pillar of ESG, streamlining the reporting process.

2. Credibility and Verification

EMAS requires third-party verification, ensuring the accuracy of environmental data. This enhances the reliability of ESG reports, which are increasingly scrutinized by investors and regulators.

3. Risk Management

Both frameworks emphasize identifying and mitigating risks—EMAS for environmental risks and ESG for broader sustainability risks. Combining these approaches helps organizations build resilience.

4. Regulatory Alignment

With the CSRD expanding sustainability reporting requirements, EMAS-certified organizations are better positioned to meet these demands, as they already have systems in place for environmental compliance and data tracking.

5. Operational Efficiency

EMAS promotes resource efficiency and waste reduction, which align with ESG goals. For example, reducing energy consumption (tracked under EMAS) directly supports ESG targets like lowering carbon emissions.


Practical Steps for Integration

  1. Leverage Existing Systems
    • Use EMAS-certified EMS to gather environmental data for ESG reports.
    • Align EMAS indicators (e.g., energy use, emissions) with ESG metrics.
  2. Expand Beyond Environmental
    • Complement EMAS with social and governance policies to cover all ESG pillars.
    • Implement frameworks like ISO 26000 (Social Responsibility) for the “S” and “G” aspects.
  3. Engage Stakeholders
    • Involve employees, suppliers, and customers in sustainability initiatives, as required by both EMAS and ESG.
  4. Third-Party Assurance
    • Ensure ESG reports are verified, similar to EMAS audits, to build trust with stakeholders.

Challenges and Opportunities

Challenges:

  • Data Complexity: Integrating data from EMAS into broader ESG reports can be resource-intensive.
  • Regulatory Uncertainty: Evolving ESG regulations (e.g., potential deregulation under the “Omnibus” proposal) may require adaptability.

Opportunities:

  • Competitive Advantage: Companies with EMAS and strong ESG performance can attract investors and customers.
  • Innovation: Sustainability-driven processes can lead to cost savings and new business models.

Conclusion

The integration of EMAS and ESG is not just about compliance—it’s a strategic opportunity to build a sustainable, resilient, and transparent business. By leveraging the strengths of EMAS for environmental management and expanding into social and governance areas, organizations can meet regulatory demands, enhance their reputation, and contribute to a more sustainable future.

For companies yet to adopt these frameworks, now is the time to start. The synergy between EMAS and ESG is clear: together, they provide a comprehensive pathway to sustainability excellence.


Is your organization ready to integrate EMAS and ESG? Contact sustainability experts today to begin your journey toward holistic sustainability reporting. This topic will be one of the important elements of the agenda for the upcoming “FUTURE WITH EMAS” conference, which is planned for November 6-7, 2025, in Warsaw. Reserve the date now and leave email through the contact form to receive further detailed information about the conference.

#EMAS #EnvironmentalManagement #SustainabilityLeadership #CSRD #ESGReporting #ESG #SustainabiltyReporting #Industry #SustainableDevelopment #FitforREACH #FuturrewithEMAS #POMInnO

EMAS and the Industrial Emissions Directive

During a special thematic session at the EUIndTech2025 conference in Cracow (June, 2025), Mr. Robert Pochyluk from the Polish Environmental Management Forum presented and discussed the consequences of upcoming legislative changes in environmental management systems, particularly in the context of integrating the EMAS system with the revised Industrial Emissions Directive (IED). These changes mean that previously voluntary environmental management systems will become mandatory for certain groups of enterprises, especially those required to hold integrated permits. We are at the threshold of a significant transformation of environmental practices in industry.

EMS as a Mandatory Tool

The EMAS system or ISO 14001, which for many years functioned as voluntary tools, are now being formally incorporated into legal obligations resulting from the revised IED directive. Article 14a of this directive imposes on operators of installations covered by the directive’s scope the obligation to implement an environmental management system – for each installation separately. This is a fundamental change, because until now organizations could apply one centralized system (for ISO 14001) covering the entire company structure. Currently, it may be necessary to adapt systems so that they individually cover each installation.

Required System Elements:

The environmental management system – according to the directive – must include, among others:

  • Environmental policy objectives oriented toward continuous improvement of efficiency, including actions related to waste reduction, water reuse, emission reduction, and energy consumption reduction.
  • Integration with energy management systems resulting from the energy efficiency directive.
  • An inventory of hazardous substances used and risk analysis of their use, along with assessment of possibilities for their substitution.
  • A transformation plan toward clean industrial technologies (here the European Commission still needs to specify details – deadline: end of 2025).

All this data will need to be publicly available – most likely in a form similar to the EMAS environmental statement. The European Commission has until the end of 2025 to specify this.

Deadlines:

The first compliance audits of environmental management systems must be conducted no later than July 1, 2027. This means that real preparations should begin no later than 2026, if not earlier. Delays may result not only in increased costs of certification services but also in the risk of failing to meet legal obligations.

Practical Effects of the Introduced Regulations for Companies:

  • They elevate the status of environmental management systems, making them not only a management tool but also a formal requirement,
  • They may lead to the need to reorganize ISO 14001 systems so that they cover each installation separately,
  • They may force certification bodies and EMAS verifiers to expand the scope of services and assessment methodology,
  • They may standardize the practice of administrative bodies, which have previously interpreted the significance of environmental systems differently when issuing permits.

Legal Context and National Implementation

The revision of the IED directive is to be implemented into Polish law by the end of 2026. It is expected that the changes will include amendments to the Environmental Protection Law (probably articles 204-214), determination of accreditation procedures for certification bodies, and principles for recognizing ISO 14001 systems and EMAS registration. Poland will have some degree of freedom in implementation, particularly regarding the recognition of certificates and verifiers.

This topic will be one of the important elements of the agenda for the upcoming “FUTURE WITH EMAS” conference, which is planned for November 6-7, 2025, in Warsaw. Reserve the date now and leave email through the contact form to receive further detailed information about the conference.

🌍 International Conference “FUTURE WITH EMAS” – Save the Date!

📅 November 6-7, 2025
📍 Warsaw, Poland

This autumn, POMInnO will coorganize a game-changing international conference where environmental management meets chemical safety and sustainability. “FUTURE WITH EMAS” will showcase how the trusted EMAS (Eco-Management and Audit Scheme) can drive meaningful integration with Chemical Risk Management (CRM) and Environmental & Social Governance (ESG).

💡 What to Expect:

  • Day 1: joint thematic sessions, case studies, practical tools and inspiring talks on the future of EMAS – concluded with the EMAS Gala and networking dinner.
  • Day 2: dedicated expert tracks for EMAS Article 49 representatives and LIFE Fit for REACH-2 project partners (closed sessions).

🎯 Who Should Attend?

  • environmental and sustainability managers,
  • EMAS and EMS practitioners,
  • chemical safety experts,
  • ESG professionals and regulatory compliance officers.

🔍 Why Attend?

  • Latest updates on EU regulations (EMAS, REACH, CSRD),
  • Real-world integration strategies for EMAS with ESG and CRM,
  • Inspiring speakers from across Europe,
  • Practical tools for SMEs and large enterprises,
  • Extensive networking opportunities with European environmental leaders.
  • 👥 Organized by: General Directorate for Environmental Protection, Polish Forum for Environmental Management, Łukasiewicz –  Industrial Chemistry Institute, and POMInnO.

🤝 Supported by: European Commission, Ministry of Climate and Environment

Cofinanced by: Life Fit for REACH 2 Project and National Fund for Environmental Protection and Water Management.

📩 Full agenda and registration details coming soon.
Save the date and leave your email to stay informed ➡️ Contact Form

The Impact of Batteries on the Environment

🔋 Do you know what happens to batteries after use? 🔋

📢 We use them daily in smartphones, laptops, and electric cars – but what comes next❓ If they end up in regular waste, they can cause soil, water, and air pollution 🌍😱

⚠️ What’s inside batteries?
Lead – neurotoxic, damages the nervous system 🧠
Mercury – accumulates in the food chain 🐟
Cadmium – carcinogenic and harmful to soil 🌱
Lithium – can lead to fires 🔥
Nickel –harmful to human health 🌱

♻️ What can you do?
✅ Dispose of used batteries at special collection points 🔄
✅ Choose devices with long-lasting batteries 📱
✅ Educate others – it makes a difference! 🎓

More details available here . 👉 Let’s protect our planet together! 🌱💚

👉 If you work for a company involved in battery collection, recycling, or disposal, or handle other hazardous materials, and want to explore how we can assist you within the LIFE Fit for REACH-2 project – fill out the questionnaire and we will contact you immediately. 🌱💚

#Batteries #Recycling #Environment #Ecology #WasteManagement #ZeroWaste #FitforREACH #LIFE

Understanding Hazardous Substances in Urban Environments: Key Insights from NonHazCity 3

Urban areas are constantly transforming, with construction and development shaping the cities of tomorrow. But amid this progress lies a hidden danger: the presence of hazardous substances in the very materials used to build our homes and cities.

The NonHazCity 3 project is tackling this issue head-on, aiming to reduce the risk of harmful substances infiltrating our urban spaces. Through targeted screening activities, the project sheds light on the areas that require deeper investigation, paving the way for a healthier, safer urban future.

The Scope of NonHazCity 3’s Screening Investigations

Focusing on five cities in the Baltic Sea region—Tallinn, Helsinki, Turku, Västerås, and Stockholm—NonHazCity 3 set out to understand how construction materials contribute to contamination in both indoor and outdoor environments. By examining five key matrices—construction materials, stormwater, indoor dust, indoor air, and residential wastewater—the project uncovered significant findings regarding hazardous substances in urban spaces.

While not every city screened all five matrices, the results revealed several harmful substances commonly found in construction materials, offering valuable insights for both policymakers and the construction industry.

Common Hazardous Substances Found in Urban Spaces

Here are some of the most problematic substances identified:

  • Phthalates: Often found in PVC flooring, cables, and roofing membranes, phthalates make plastics more flexible but disrupt hormones in living organisms.
  • PFAS: Known for their extreme persistence, PFAS are widely used in products like non-stick coatings and water-resistant fabrics but pose long-term health risks.
  • Bisphenols: These endocrine disruptors are commonly found in plastics.
  • Organophosphate Esters (OPEs): Used as flame retardants and plasticizers, OPEs are linked to adverse health effects.
  • Brominated Flame Retardants (BFRs): These substances can cause neurological and hormonal disruptions and linger in the environment.
  • Biocides: Widely used to prevent mold growth, biocides contribute to microbial resistance.
  • Chlorinated Paraffins (CPs): Persistent in the environment and potentially carcinogenic, CPs are often used in building materials.
  • Volatile Organic Compounds (VOCs): Found in paints and adhesives, VOCs can cause a range of health problems.
  • Metals: Toxic metals such as lead, cadmium, and mercury are present in construction materials and pose serious health risks even in small amounts.
  • Key Findings: The Reality of Hazardous Substances in Our Cities
  • Indoor Dust: The investigation showed that indoor dust closely reflects the hazardous substances found in the materials used within the building. In homes with PVC flooring and treated surfaces, higher concentrations of organic pollutants, like plasticizers, PFAS, and chlorinated paraffins, were detected.
  • Stormwater: Stormwater serves as a major conduit for pollutants, transporting contaminants like biocides, organophosphate esters, metals, and PFAS from buildings into natural environments. Cities with newer constructions, particularly those with wooden claddings, showed high levels of biocides like diuron, propiconazole, and mecoprop.
  • PFAS: The concentration of PFAS varied significantly between cities, underscoring the widespread use of these harmful substances in a range of products, despite their severe environmental and health impacts.
  • TCPP Contamination: This pervasive flame retardant was found in stormwater runoff, wastewater, and indoor dust, highlighting its widespread contamination in urban areas.
  • Emerging Substances: The research also found evidence of new hazardous substances replacing older ones in construction materials, pointing to the need for ongoing monitoring and research.

Recommendations for a Safer, Healthier Urban Future

  • For Regulators: Strengthen regulations on hazardous substances in construction materials and promote the use of safer alternatives.
  • For Public Authorities: Enforce compliance with current regulations and enhance monitoring for emerging contaminants. Public awareness campaigns can help citizens understand the risks, while improved waste management ensures recycled materials are hazard-free.
  • For Constructors: Avoid materials treated with harmful chemicals and demand transparency from suppliers regarding the substances used. Replace the most harmful chemicals with safer alternatives, and ensure robust waste management practices to prevent hazardous substances from re-entering the environment through recycling.

Conclusion: Collaboration for Safer Cities

The NonHazCity 3 project highlights the urgent need for continuous monitoring, stricter regulations, and the promotion of safer construction materials. By following these recommendations, cities in the Baltic Sea region—and around the world—can protect both the environment and public health.

Collaboration across cities and countries is crucial. By sharing knowledge and best practices, we can collectively tackle pollution caused by hazardous substances in construction materials and make our urban environments safer for everyone.

If you are interested in this article, if you would like to find out more about hazardous substances in your environment – you can find interesting information on our websites and social media, but you can also make your contact in the form and we will regularly inform you about our materials (articles, reports, training courses, meetings) in which we will deepen this topic and suggest safe and proven solutions. In this form you can also declare your willingness to actively participate in our project, which will be of benefit to us (feedback) but also to you (concrete support).

Let’s work together to build healthier, greener cities for future generations.

What are the End-of-Waste Criteria and why are they a significant element of waste management?

The End-of-Waste Criteria (EoW) represent a crucial regulatory element in the European Union’s (EU) waste management framework. Their purpose is to ensure that materials that cease to be considered waste meet certain quality and safety standards, essential for promoting the circular economy. A review of the literature in this area offers insights into the mechanisms behind the implementation of these criteria and the challenges associated with their practical application.

  1. Regulatory Framework and Implementation Principles
    Numerous publications address the regulatory frameworks related to EoW conditions. The main reference point is the Waste Framework Directive 2008/98/EC, which defines the core principles of waste management in the EU, including EoW criteria. Works such as the European Commission’s White Paper (2011) and commentary on this directive emphasize the importance of these regulations in promoting recycling and minimizing waste disposal. In Polish legislation, the issue of End-of-Waste is covered in Chapter 5 of Part I of the Waste Act.
    According to legal frameworks (Waste Framework Directive 2008/98/EC) and literature (Delgado Sancho et al, 2009), the core of the EoW system is four general conditions that must be met for a material to no longer be considered waste:
    1. Material Use – The material must be commonly used for specific purposes, similar to other market materials. This means that the material, which has lost its waste status, should have a real and practical use recognized in the economy (according to Art. 14 Sec. 1. 1) a) of the Waste Act: “the object or substance is to be used for specific purposes”).
    2. Existence of a Market or Demand for the Material – There must be a market or demand for the material, ensuring that it will not be treated as waste again. The material should have commercial value, and its recipients must be able to purchase or reuse it in compliance with regulations (according to Art. 14 Sec. 1. 1) b) of the Waste Act: “there is a market for such objects or substances or demand for them”).
    3. Meeting Technical and Legal Standards – The material, which ceases to be considered waste, must meet certain technical standards and legal requirements related to quality and safety, to be used without adverse effects on the environment or public health (according to Art. 14 Sec. 1. 1) c) of the Waste Act: “the object or substance meets the technical requirements for use for specific purposes and the requirements specified in the regulations, in particular concerning chemicals and products applicable to that object or substance, and in the applicable product standards”).
    4. No Harm to the Environment or Health – The material must undergo a recovery or recycling process, and its further use should not pose a threat to the environment or human health. This includes control over hazardous substances and potential contaminants that may be present in the waste (according to Art. 14 Sec. 1. 1) d) of the Waste Act: “the use of the object or substance does not lead to negative consequences for human life, health, or the environment”).
  • National Differences in Implementing EoW Criteria

The previous chapter addressed the general conditions that need to be met in order to achieve EoW status. The revised Waste Framework Directive (WFD) includes a provision by which certain specified waste shall cease to be waste when it has undergone a recovery operation and complies with specific criteria developed in accordance with a number of conditions. Those detailed criteria shall ensure a high level of protection of the environment and human health and facilitate the prudent and rational utilisation of natural resources. They shall include:

  • permissible waste input material for the recovery operation;
  • allowed treatment processes and techniques;
  • quality criteria for end-of-waste materials resulting from the recovery operation in line with the applicable product standards, including limit values for pollutants where necessary;
  • requirements for management systems to demonstrate compliance with the end-of-waste criteria, including for quality control and self-monitoring, and accreditation, where appropriate; and
  • a requirement for a statement of conformity.

At EU level we have several waste stream, for which the EoW criteria have been developed. These are: a) iron, steel and aluminium scrap (see Council Regulation (EU) N° 333/2011); b) glass cullet (see Commission Regulation (EU) N° 1179/2012), c) copper scrap (see Commission Regulation (EU) N° 715/2013). Recently, stakeholders and policymakers have been calling for identification of further possible material streams for which to develop end-of-waste criteria. JRC has started developing new scientific proposals for end-of-waste criteria for plastics and plans to do the same for textiles.

  • In addition, some publications, such as López-Portillo et al. (2021) and COM (2023), highlight national differences in the implementation of directives and the challenges of harmonizing these regulations across EU member states. Despite the common EU framework, the implementation of EoW criteria varies between member states. Harmonizing these regulations faces challenges, particularly due to differences in infrastructure, technological resources, the development level of waste management, and national regulations in individual countries.
    • Differences in Recycling Infrastructure: Some countries, especially those with more advanced waste management systems, have better-developed recycling infrastructure, allowing for more effective implementation of EoW criteria. For example, countries like Germany or the Netherlands have advanced sorting, separation, and processing systems that facilitate control over the quality of materials obtained from recycling. On the other hand, in countries with less developed infrastructure (e.g., some Central and Eastern European countries, including Poland), limited availability of technology and investment in the recycling sector may hinder the fulfillment of these criteria.
    • Different Regulatory Approaches: The introduction of EoW in some countries may be more restrictive than in others, depending on national regulations concerning environmental protection and public health. COM (2023) indicates that countries such as Denmark or Sweden apply stricter standards for recycling and waste processing, which increases the certainty that materials that cease to be considered waste are safe for the environment and health. Meanwhile, in other countries, where regulations may be less stringent, there is a risk that materials that formally meet EoW criteria may contain hazardous substances or not meet the appropriate quality standards.
    • Harmonizing Regulations: One of the key challenges authors highlight is the need for harmonizing regulations across the EU. López-Portillo et al. (2021) points out that differences in the approach to implementing EoW criteria may lead to problems in the EU’s internal market, where materials considered non-waste in one country may be treated differently in other member states. This, in turn, may lead to issues related to the trade of secondary materials and their cross-border flow.
  • Challenges of Harmonizing EoW
    The harmonization of EoW faces several challenges, which include:
    • Technological Issues: Differences in waste processing and recycling technology can make it difficult to ensure uniform quality standards for recovered materials in different countries. Countries with more advanced technologies may implement EoW regulations more quickly and effectively.
    • Regulations on Hazardous Substances: There could be differences at national level whether wastes are classified as hazardous or not. This can, in consequence impact how waste is treated and which materials can achieve non-waste status. COM (2023) notes that varying standards for chemicals may cause materials considered safe in one country not to meet the standards in another.
    • Management of Transboundary Waste: The flow of waste and secondary materials between EU member states presents an additional challenge. Problems may arise when materials considered non-waste in one country are transported to another, where regulations may be more restrictive. The need to adapt to different standards and regulations in individual countries complicates the creation of a single market for secondary materials.
  • The Importance of a Circular Economy
    Literature on EoW criteria often links them to the concept of the circular economy (CE). Studies such as Renfors (2024) and Geissdoerfer et al. (2017) analyze how EoW integrates into broader efforts to reduce the use of primary raw materials and promote recycling. Authors emphasize that effective implementation of EoW can contribute to reducing pressure on natural resources and cutting CO₂ emissions, which directly relates to the achievement of the EU’s climate goals.
  • Challenges with Hazardous Substances
    One of the main concerns raised in the literature on EoW criteria is the presence of hazardous substances in recycled materials. Articles such as Pivnenko & Astrup (2016) and Xu Pan (2022) highlight that chemical contaminants, including hazardous substances, can hinder the recycling and reuse process. Authors suggest that effective identification and elimination of these substances before the material is deemed “non-waste” is crucial for ensuring environmental and health safety.
  • Implementation in Poland
    Poland, as an EU member, implements EoW criteria according to EU regulations, though the literature on how these principles function in the Polish context is limited. Hryb and Ceglarz (2021) and IOŚ-PIB (2021) analyze the implementation of the Waste Framework Directive in Poland, pointing out issues related to recycling infrastructure, law enforcement, and low public awareness regarding the circular economy. The literature also emphasizes challenges related to the control and monitoring of materials deemed to meet EoW criteria, particularly in the context of hazardous waste. Several authors suggested that the EoW regulation in Poland will be an empty provision, without a significant impact on waste management practices (den Boer et al., 2017). Recently, additional EoW criteria have been developed in Poland for asphalt rubble waste (MCE, 2021) and waste generated in the process of energy combustion of fuels (MCE, 2022).
  • Future Challenges and Perspectives
    The literature on the future of EoW criteria and their role in the circular economy highlights the need for further harmonization of regulations within the EU and the improvement of recycling-related technologies. Hahladakis and Iacovidou (2018) suggest that modern technologies, such as automatic waste sorting and better material processing techniques, could contribute to more effective implementation of EoW criteria.

Summary/Conclusions
The End-of-Waste Criteria are an essential tool in promoting sustainable development and the circular economy. A key element of effective implementation of EoW criteria is the harmonization of regulations within the EU. The literature and experiences indicate key challenges, such as managing hazardous substances and differences in the implementation of regulations across various EU countries, including Poland. Despite these difficulties, further harmonization of regulations and the development of technology may contribute to the more efficient realization of these principles in the future.

This and other issues are being discussed in the Life Fit for Reach 2 project. Would You like to find out how our project can help You with REACH – fill in the form and we will contact You shortly.

Bibliografia:

  1. Geissdoerfer, Martin, Paulo Savaget, Nancy M.P. Bocken, i Erik Jan Hultink. 2017. “The Circular Economy – A New Sustainability Paradigm?” Journal of Cleaner Production 143: 757-768. https://doi.org/10.1016/j.jclepro.2016.12.048.
  2. Hahladakis, John N., i Eleni Iacovidou. 2018. “Closing the Loop on Plastic Packaging Materials: What is Quality and How Does it Affect Their Circularity?” Science of the Total Environment 630: 1394-1400. https://doi.org/10.1016/j.scitotenv.2018.02.330.
  3. Xu Pan, Christina W.Y. Wong, Chunsheng Li, 2022, Circular economy practices in the waste electrical and electronic equipment (WEEE) industry: A systematic review and future research agendas, Journal of Cleaner Production, 365, https://doi.org/10.1016/j.jclepro.2022.132671.
  4. IOŚ-PIB, 2021, GOSPODARKA ODPADAMI KOMUNALNYMI W POLSCE. Analiza możliwości i barier zagospodarowania odpadów z tworzyw sztucznych, pochodzących z selektywnego zbierania odpadów komunalnych, a kwestie GOZ, Warszawa,  https://www.teraz-srodowisko.pl/media/pdf/aktualnosci/11386-Raport-Gospodarka-odpadami-komunalnymi-w-Polsce.pdf
  5. López-Portillo, M.-P., Martínez-Jiménez, G., Ropero-Moriones, E. Saavedra-Serrano, M. C., 2021, “Waste treatments in the European Union: A comparative analysis across its member states” Heliyon, 7(12): 1-11, Elsevier, https://doi.org/10.1016/j.heliyon.2021.e08645.  
  6. Pivnenko, K. i Astrup T.  F.  2016. “The challenge of chemicals in material lifecycles”, Waste Management,  56:1-2, https://doi.org/10.1016/j.wasman.2016.08.016.
  7. Hryb, W. & Ceglarz, K., 2021, „Odpady komunalne w aspekcie gospodarki o obiegu zamkniętym.” Wydawnictwo Politechniki Śląskiej, Gliwice, https://repolis.bg.polsl.pl/dlibra/publication/81045/edition/72010/content
  8. COM(2023) 304 final; REPORT FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS identifying Member States at risk of not meeting the 2025 preparing for re-use and recycling target for municipal waste, the 2025 recycling target for packaging waste and the 2035 municipal waste landfilling reduction target, https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=COM%3A2023%3A304%3AFIN&qid=1686220362244 .
  9. Renfors, S.-M. (2024), “Education for the circular economy in higher education: an overview of the current state”, International Journal of Sustainability in Higher Education, Vol. 25 No. 9, pp. 111-127. https://doi.org/10.1108/IJSHE-07-2023-0270
  • E. den Boer, A. Gawłowski, K. Godlewska, M. Górski, R. Szpadt, B. Środa, H. Marliere, M. Kruś, A. Piotrowska, J. Bujny, T. Mądry., 2017, “Utrata statusu odpadu – rzeczywiste ułatwienie czy recyklingowa fikcja?” Logistyka Odzysku nr 2 (23), str. 23-33,
  • COM(2023) 304 final; REPORT FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS identifying Member States at risk of not meeting the 2025 preparing for re-use and recycling target for municipal waste, the 2025 recycling target for packaging waste and the 2035 municipal waste landfilling reduction target, https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=COM%3A2023%3A304%3AFIN&qid=1686220362244 .
  • Delgado Sancho L, Catarino A, Eder P, Litten D, Luo Z, Villanueva Krzyzaniak A., 2009, End-of-Waste Criteria. EUR 23990 EN. Luxembourg (Luxembourg): European Commission; . JRC53238, https://publications.jrc.ec.europa.eu/repository/handle/JRC53238
  • Geissdoerfer, Martin, Paulo Savaget, Nancy M.P. Bocken, i Erik Jan Hultink. 2017. “The Circular Economy – A New Sustainability Paradigm?” Journal of Cleaner Production 143: 757-768. https://doi.org/10.1016/j.jclepro.2016.12.048.
  • Hahladakis, John N., i Eleni Iacovidou. 2018. “Closing the Loop on Plastic Packaging Materials: What is Quality and How Does it Affect Their Circularity?” Science of the Total Environment 630: 1394-1400. https://doi.org/10.1016/j.scitotenv.2018.02.330.
  • Hryb, W. & Ceglarz, K., 2021, „Odpady komunalne w aspekcie gospodarki o obiegu zamkniętym.” Wydawnictwo Politechniki Śląskiej, Gliwice, https://repolis.bg.polsl.pl/dlibra/publication/81045/edition/72010/content
  • IOŚ-PIB, 2021, GOSPODARKA ODPADAMI KOMUNALNYMI W POLSCE. Analiza możliwości i barier zagospodarowania odpadów z tworzyw sztucznych, pochodzących z selektywnego zbierania odpadów komunalnych, a kwestie GOZ, Warszawa,  https://www.teraz-srodowisko.pl/media/pdf/aktualnosci/11386-Raport-Gospodarka-odpadami-komunalnymi-w-Polsce.pdf
  • López-Portillo, M.-P., Martínez-Jiménez, G., Ropero-Moriones, E. Saavedra-Serrano, M. C., 2021, “Waste treatments in the European Union: A comparative analysis across its member states” Heliyon, 7(12): 1-11, Elsevier, https://doi.org/10.1016/j.heliyon.2021.e08645
  • MCE, 2021, Regulation of the Minister of Climate and Environment of December 23, 2021, on specifying detailed criteria when certain types of asphalt rubble waste cease to be waste.
  • MCE, 2022, Regulation of the Minister of Climate and Environment of October 27, 2022, on specifying detailed criteria when certain types of waste generated in the process of energy combustion of fuels cease to be waste.
  • Pivnenko, K. i Astrup T.  F.  2016. “The challenge of chemicals in material lifecycles”, Waste Management,  56:1-2, https://doi.org/10.1016/j.wasman.2016.08.016.
  • Renfors, S.-M. (2024), “Education for the circular economy in higher education: an overview of the current state”, International Journal of Sustainability in Higher Education, Vol. 25 No. 9, pp. 111-127. https://doi.org/10.1108/IJSHE-07-2023-0270
  • Xu Pan, Christina W.Y. Wong, Chunsheng Li, 2022, Circular economy practices in the waste electrical and electronic equipment (WEEE) industry: A systematic review and future research agendas, Journal of Cleaner Production, 365, https://doi.org/10.1016/j.jclepro.2022.132671.

#CircularEconomy #WasteManagement #EoW #endofwaste #endofwastecriteria #Recycling #FitforREACH #Fit4RREACH

Health Effects of Chemical Exposure at Work

The health impacts of chemical exposure can be categorized into local and systemic effects. Local effects are typically immediate and involve irritation or damage to the point of contact, such as the skin, eyes, or respiratory tract. Systemic effects, on the other hand, may result from the absorption of chemicals into the bloodstream, affecting internal organs over time.

For instance, exposure to solvents like benzene can cause both acute effects, such as dizziness or headaches, and chronic effects, including bone marrow damage and leukemia (Smith, 2010). Some chemicals, like asbestos, are known to cause cancer after prolonged exposure, while others may have teratogenic or mutagenic effects, impacting reproductive health or causing genetic mutations in offspring.

Risk Assessment and Control Measures

The risk assessment process is a critical component of managing chemical hazards in the workplace. It involves identifying hazardous substances, evaluating the potential for exposure, and implementing control measures to reduce or eliminate the risk to workers. According to European Union directives and the United States Occupational Safety and Health Administration (OSHA) guidelines, employers are required to conduct regular risk assessments to ensure a safe working environment.

Employers must also ensure that employees are equipped with adequate personal protective equipment (PPE), such as gloves, respirators, and protective clothing, to minimize direct exposure to harmful chemicals. Additionally, engineering controls such as ventilation systems, chemical storage protocols, and spill containment measures are essential to maintain a safe workplace.

For over 500 chemical substances, permissible exposure limits (PELs) have been established to regulate workplace exposure and protect workers from long-term health consequences. Employers must monitor the air quality and ensure that these limits are not exceeded.

Regulatory Guidelines and Best Practices

Compliance with safety regulations and standards is essential for mitigating the risks associated with chemical exposure. Safety Data Sheets (SDS) provide critical information on the properties of chemicals, their hazards, and recommended protective measures. Employers must make these documents available to all employees who work with or around hazardous substances.

It is the responsibility of the employer to:

  • Ensure that employees are informed about the risks associated with chemical use.
  • Provide appropriate training on the handling and disposal of chemicals.
  • Establish emergency procedures in case of accidental spills, leaks, or exposure.

In addition to workplace safety regulations, international guidelines such as the Globally Harmonized System of Classification and Labelling of Chemicals (GHS) aim to standardize the communication of chemical hazards globally.

Conclusion

Ensuring the safe handling of chemical substances is a shared responsibility between employers and employees. Through comprehensive risk assessments, proper use of protective equipment, adherence to regulatory standards, and regular monitoring, it is possible to significantly reduce the dangers posed by chemicals in the workplace. By fostering a culture of safety and compliance, we can protect workers from the short- and long-term health risks associated with chemical exposure.

Would You like to find out how the Fit for REACH project can help You with safe handling of chemicals – please fill in this contact form shortly and we will contact You very soon.

References:

  1. European Agency for Safety and Health at Work. Dangerous substances in workplaces: OSHwiki. European Union, 2021. https://osha.europa.eu/en/themes/dangerous-substances.
  2. European Chemicals Agency. Guidance on the Application of the CLP Criteria. Application of the CLP criteria, Part4: Environmental Hazards v.6. 2024. https://echa.europa.eu/view-article/-/journal_content/title/part-4-of-the-guidance-on-the-application-of-the-clp-criteria.
  3. ILO, 2021, “Exposure to hazardous chemicals at work and resulting health impacts: A global review”, International Labour Office – Geneva, ISBN: 978-9-22-034219-0 (https://www.ilo.org/sites/default/files/wcmsp5/groups/public/@ed_dialogue/@lab_admin/documents/publication/wcms_811455.pdf)
  4. Occupational Safety and Health Administration (OSHA). Occupational Exposure to Hazardous Chemicals in Laboratories: 29 CFR 1910.1450. OSHA, 2023. https://www.osha.gov/laws-regs/regulations/standardnumber/1910/1910.1450.
  5. Smith, Martyn T. “Advances in understanding benzene health effects and susceptibility.” Annual Review of Public Health 31 (2010): 133-148. https://doi.org/10.1146/annurev.publhealth.012809.103646.