Tag Archives: ecotoxicity

Safer aquatic systems with nano-encapsulated pesticides?

A May 19, 2025 news item on Nanowerk highlights research into making pesticides less toxic,

As global demand for food continues to rise, pesticide usage is intensifying—bringing unintended ecological consequences. Nanopesticides, which allow for controlled release and targeted action, are positioned as a more efficient and less environmentally disruptive solution. However, uncertainties persist, particularly regarding their fate in ecosystems post-application.

Traditional risk assessment methods often neglect early-stage emissions and fail to capture the complex behaviors of engineered nanomaterials in natural environments. The lack of robust ecotoxicity data and the absence of life-cycle-based regulatory guidelines further limit our understanding. These challenges underscore the urgent need to examine nanopesticide risks from synthesis to environmental degradation.

A May 19, 2025 Chinese Society for Environmental Sciences press release on EurekAlert (also on Newswise but credited to the Chinese Academy of Sciences), which originated the news item, provides more information, Note: Links have been removed,

Nanotechnology is transforming pesticide design with the promise of precision targeting and prolonged effectiveness. But how environmentally friendly are these innovations? A new study offers the first comprehensive life-cycle comparison between conventional imidacloprid (IMI) and its nano-encapsulated version (nano-IMI), tracking their environmental impacts from production through freshwater emissions. While nano-IMI incurs higher ecological costs during manufacturing, its environmental risks at the end-of-life stage are dramatically lower. Using an integrated assessment approach, researchers found that nano-IMI reduced freshwater ecotoxicity impact scores by up to five orders of magnitude compared to IMI. These findings highlight the importance of evaluating agrochemicals through a full lifecycle lens when developing safer alternatives.

To address these concerns, researchers from Jinan University and the University of Wisconsin–Madison published a study (DOI: 10.1016/j.ese.2025.100565) in Environmental Science and Ecotechnology on April 25, 2025. The team evaluated nano-encapsulated version (nano-IMI) and conventional imidacloprid (IMI) using a novel framework that integrates life cycle assessment (LCA), the USEtox ecotoxicity model, and the SimpleBox4Nano/SimpleBox fate model. This approach enabled the researchers to assess both production-stage environmental burdens and freshwater ecotoxicity, offering one of the most complete comparisons of nano- versus conventional pesticide formulations to date. The researchers chose imidacloprid, a widely used neonicotinoid insecticide, as a representative case. Their analysis showed that producing nano-IMI resulted in approximately four times greater ecotoxicity than conventional IMI, mainly due to the energy-intensive encapsulation process. However, once released into the environment, nano-IMI behaved differently. Modeling across various rainfall conditions revealed that nano-IMI had significantly lower freshwater emissions, thanks to its high soil retention and aggregation tendencies in water. Even when accounting for the eventual release of the active ingredient from nano-IMI, the overall ecological impact remained far below that of conventional IMI. These results suggest that although nano-formulations may increase production-related impacts, they can drastically reduce environmental harm during use and disposal.

“By combining traditional life cycle analysis with nano-specific fate modeling, we’ve introduced a robust tool for assessing the total environmental impact of nano-agrochemicals,” said Dr. Fan Wu, senior author of the study. “Our findings suggest that while nano-pesticides may require more resources to produce, their environmental behavior post-application can be far more favorable. This research lays the groundwork for smarter pesticide regulation and highlights the need to consider environmental risks across the entire product life cycle—not just at the point of use.”

This study marks an important step toward regulatory frameworks that reflect the unique behaviors of nanopesticides. The integrated modeling approach allows decision-makers to weigh the environmental trade-offs of production against long-term ecological risks. With the global nanopesticide market expected to grow from $735 million in 2024 to over $2 billion by 2032, such insights are both timely and essential. The research also highlights opportunities to improve manufacturing through green chemistry and sustainable nanocarrier design. Ultimately, full life-cycle assessments can help steer innovation toward agrochemical solutions that protect crops without compromising the health of aquatic ecosystems.

Here’s a link to and a citation for the paper,

A life cycle risk assessment of nanopesticides in freshwater by Mingyan Ke, Keshuo Zhang, Andrea L. Hicks, Fan Wu, Jing You. Environmental Science and Ecotechnology Volume 25, May 2025, 100565 DOI: https://doi.org/10.1016/j.ese.2025.100565 Creative Commons Licence: CC BY 4.0 (Attribution 4.0 International Deed)

This paper is open access.

NanoSustain published four case studies: zinc oxide, titanium dioxide, carbon nanotubes, and nanocellulose

A May 17, 2013 news item on Nanowerk highlight a European Commission-funded project, NanoSustain and its publication of a fact sheet and four case studies,,

NanoSustain, a €2.5 million NMP small collaborative project (2010-2013) funded by the European Union under FP7, has published a fact sheet and four case studies addressing these issues.

How do nanotechnology-based products impact human health and the environment?
Can they be recycled?
Can they be safely disposed of?
How can you find out?

The March 20, 2013 NanoSustain news release, which originated the news item, goes on to explain,

… the EC-funded NanoSustain project has been developing new sustainable solutions through an investigation of the life-cycle of nanotechnology-based products, in particular the physical and chemical characteristics of materials, hazard and exposure aspects, and end-of-life disposal or recycling to determine the fate and impact of nanomaterials.

A summary of the different materials and products tested within NanoSustain:

• Case Study #1: Titanium dioxide for paints
• Case Study #2: Zinc oxide for glazing products
• Case Study #3: Carbon nanotubes epoxy resins for plastics
– for structural or electrical/antistatic applications
• Case Study #4: Nanocellulose for advanced paper applications

Information about the individual experimental approaches

Descriptions of the different techniques developed

How these techniques have been successfully applied in physical-chemical characterisation; life-cycle analysis; final disposal; recycling.

Getting access to the case case studies and the fact sheet requires filling out a form but once you’ve done that you get instant access to the materials.

Here’s some information from EuroSustain’s fact sheet,

Factsheets

Analytical Techniques

Development of sustainable solutions for nanotechnology-based products based on hazard characterization and LCA1 The primary goal of the NanoSustain project is to develop new technical solutions for the sustainable design and use, recycling and final treatment of selected nanotechnology-based products.

To achieve this the project has the following objectives: 1) to assess the hazard of selected nanomaterials based on a comprehensive data survey and generation concerning their physicochemical (PC) and toxicological properties, exposure probabilities, etc., and the adaptation, evaluation, validation and use of existing analytical, testing and life-cycle assessment (LCA) methods; 2) to assess the impact of selected products during their life cycle in relation to material and energy flows (LCA); 3) to assess possible exposure routes and risks associated with the handling of these materials, their transformation and final fate; and 4) to explore the feasibility and sustainability of new technical solutions for end-of=life processes, such as reuse/recycling, final treatment or disposal.

Within NanoSustain an assessment has been made of the PC properties, exposure and toxicity, energy and material inputs and outputs at relevant stages of a material or product’s life-cycle. This means: material production, processing, manufacturing, use, transportation, and end-of-life (recycling/disposal). At each stage potential risks to human health and the environment have also been assessed, through a number of experimental models and test systems using materials that would be expected to be released from products containing nanomaterials.

Four nanomaterials were investigated that either already feature in commercial products or are expected to be commercialized on a large scale: titanium dioxide (TiO2) in paint, zinc oxide (ZnO) as a coating for glass, multi-walled carbon nanotubes (MWCNT) in epoxy resins, and nanocellulose in paper.

Detailed information on the nanomaterials have been summarized in internal project material datasheets (MDS), and will be made available as part of peer-reviewed publications on release studies and toxicological investigations. [emphases mine]

Having looked at the four case studies, each of which is two pages, I would describe them as teasers. There’s not a lot of information in them as to the results of the testing which makes sense when you see that they will be publishing in various publications.

I find the inclusion of titanium dioxide, zinc oxide and carbon nanotubes for life-cycle assessments easily understandable as they  have been integrated into many consumer products. However, it’s my understanding that nanocellulose has not reached that level of product integration. Still, given the number of times I’ve been told this is a ‘safe’ product, it’s interesting to see what NanoSustain has to say about its toxicity (from the NanoSustain’s nanocellulose case study),

Work in NanoSustain has provided new data and information on the physicochemical properties, potential human and environmental hazard and risk associated with relevant stages of the life-cycle of nanocellulose based products as well as on the overall energy and material input/output that may happen during manufacturing, use and disposal. Initial results indicate that the nanocellulose degrades efficiently under standard composting conditions, but does not in aquatic environments. Furthermore nanocellulose does not demonstrate any ecotoxicity. Unfortunately nanocellulose forms a gel when suspended in media for inhalation studies, and so no toxicology experiments could be performed (as for the other engineered nanomaterials studied in NanoSustain). Final results will be made available once published in peer-reviewed journals.

I have written many times about nanocellulose, a topic featuring some interesting and confusing nomenclature and taking this opportunity to highlight a couple of responses from folks who took the time to clarify things for me (from my Aug. 2, 2012 posting),

KarenS says:

Hi Maryse!

From my understanding, nanocrystaline cellulose (NCC), cellulose nanocrystals (CNC), cellulose whiskers (CW) and cellulose nanowhiskers (CNW) are all the same stuff: cylindrical rods of crystalline cellulose (diameter: 5-10 nm; length: 20-1000 nm). Cellulose nanofibers or nanofibrils (CNF), on the contrary, are less crystalline and are in the form of long fibers (diameter: 20-50 nm; length: up to several micrometers).

There is still a lot of confusion on the nomenclature of cellulose nanoparticles, but nice explanations (and pictures!) are given here (and also in other papers from the same conference):

http://www.tappi.org/Downloads/Conference-Papers/2012/12NANO/12NANO49.aspx

and there’s this from my Sept. 26, 2012 posting,

Gary Chinga Carrasco says:

The definition of cellulose nanofibrils as “diameter: 20-50 nm; length: up to several micrometers)” is somewhat simplified. For terminology on MFC terms you may want to take a look at: http://www.nanoscalereslett.com/content/6/1/417

Bringing this piece back to where I started, I look forward to seeing the NanoSustain case studies published with more details in the future.

Note: Since the folks at NanoSustain are likely using their form to collect data, I’m not linking back to the factsheet or nanocellulose case study as I would usually. So, if you want to look at the material, you do need to register via the form.