Species sensitivity distributions for ethylparaben to derive protective concentrations for soil ecosystems.

Ethylparaben is used as an antifungal preservative. Although some countries have implemented regulations for human exposure to parabens, environmental regulations for ethylparaben have not been established. This study provides new toxicological data for ethylparaben, for which data regarding soil organisms were previously lacking. Although ethylparaben toxicity has been reported in other species, we present herein the first comprehensive study of its toxicity in soil organisms. We used 12 test species (Lycopersicon esculentum, Vigna radiata, Hordeum vulgare, Oryza sativa, Eisenia andrei, Folsomia candida, Lobella sokamensis, Caenorhabiditis elegans, Chlamydomonas reinhardtii, Chlorococcum infusionum, Chlorella sorokiniana, Chlorella vulgaris) from eight taxonomic groups for acute bioassays and nine test species (L. esculentum, V. radiata, H. vulgare, O. sativa, C. reinhardtii, C. infusionum, C. sorokiniana, and C. vulgaris) from five taxonomic groups for chronic bioassays. A suite of acute and chronic toxicity tests, using 21 soil species, was conducted to estimate EC50 values, which facilitated the construction of species sensitivity distributions (SSDs) and the calculation of protective concentrations (PCs). Acute and chronic PC95 values (protective concentration for 95% of species) for ethylparaben were estimated to be 14 and 5 mg/kg dry soil, respectively. To the best of our knowledge, this is the first study to evaluate the toxicity of ethylparaben to soil species and derive PCs for soil ecosystems based on SSDs. Therefore, the data presented in this study can be used as a basis for further investigations of paraben toxicity to the soil environment.

Multigenerational effects of polyethylene terephthalate microfibers in Caenorhabditis elegans.

Microfibers (MFs) have recently become an increasingly prevalent pollutant in ecosystems and pose a direct threat to organisms and an indirect threat via adsorption of other pollutants. Here, we used Caenorhabditis elegans to study multigenerational effects of polyethylene terephthalate (PET) MFs (diameter 17.4 µm) by observing the maternal generation (P0) to the seventh offspring generation (F7) with continuous MF exposure. Exposure to 250-µm PET MFs decreased locomotion behavior and induced intestinal reactive oxygen species (ROS) in the P0 generation compared with other PET MF sizes. Moreover, no notably negative effects on survival were observed in any generation during continuous exposure to 250-µm PET MFs. However, the reproduction rate clearly decreased in the F2 and F3 generations but gradually recovered in the F4-F7 generations. Developmental abnormalities showed a close relationship with body length. Although some recovery was confirmed, there were significant decreases in body length in the F2-F5 generations. Interestingly, growth inhibition was also observed in the F6 generation without MF exposure. ROS production and dermal damage in the P0-F5 generations might have resulted in the toxicological responses. To the best of our knowledge, this is the first study to provide evidence of multigenerational toxicity of MFs in C. elegans.

Comparative study of feminine hygiene product regulations in Korea, the European Union, and the United States.

Recently, Korean consumers have experienced public health issues as a result of problematic feminine hygiene products. Consumers and local civic groups have urged manufacturers and the Korean government to provide clear information based on comprehensive studies and strengthen related policies. In this study, we collected and compiled information on the relevant regulations and organizations in Korea, the European Union, and the United States to compare the management systems and legal status of feminine hygiene products around the world. We confirmed that the definition of feminine hygiene products is similar for Korea, the EU, and the US; however, they are categorized as quasi-drugs in Korea, general products in the EU, and medical devices in US according to various regulations. Although we cannot completely prevent human exposure to chemicals in modern society, it is vital to establish a management system for the safe use and production of feminine hygiene products in a scientifically and legally sound manner. This research can contribute to the regulatory toxicology and risk assessment fields of feminine hygiene product research.

Changes in soil properties after remediation influence the performance and survival of soil algae and earthworm.

Previous research on soil remediation focused on soil properties and not on its effects on soil ecosystems. The present study investigated the adverse effects of soil physicochemical changes due to remediation on the biological indicators Chlorococcum infusionum and Chlamydomonas reinhardtii (algae) and Eisenia andrei (earthworm). Soil physicochemical properties, concentrations of total, bioavailable, and water-soluble heavy metals in soil were measured before and after remediation. Changes in soil pH, electrical conductivity, total nitrogen, and total phosphorous immediately after soil remediation were the primary causes of the biomass and photosynthetic activity inhibition observed in C. infusionum and C. reinhardtii, and the survival, normality, and burrowing behavior decrease observed in E. andrei in remediated soils showing dramatic changes in those properties. These findings suggest that remediated soils need some time to recover before restoring their functions, although heavy metals are no longer contaminating the soil.

Comparative study of the sensitivity of Daphnia galeata and Daphnia magna to heavy metals.

Daphnia galeata and Daphnia magna belong to the family Daphniidae. Daphnia galeata has a smaller body size and longer helmet than D. magna. Although D. galeata is widely distributed in the northern hemisphere, it is not as commonly used in aquatic ecotoxicity tests as D. magna. There have been only few ecotoxicological studies on the toxicity of heavy metals, organic matter, and nanomaterials in D. galeata. Thus, there is a need to discover new test species and expand the number of currently known test species to elucidate species sensitivity to aquatic pollutants. We carried out a comparative study on the sensitivity of D. magna (which represents the test water flea species) and D. galeata to heavy metal toxicity. The acute toxicity values (EC50 and LC50) of 11 heavy metal species, including silver (Ag+), arsenite (As3+), cadmium (Cd2+), chromate (Cr6+), cupric (Cu2+), ferrous (Fe2+), mercury (Hg2+), manganese (Mn2+), nickel (Ni2+), lead (Pb2+), and zinc (Zn2+), in D. galeata and D. magna were compared by conducting acute toxicity assays and comparing the data with the available data. The age of the tested Daphnia individuals and the type of exposure medium were considered for more reliable comparison of species sensitivity. We observed that D. galeata was more sensitive to Ag+, As3+, Cr6+, Fe2+, Ni2+, and Pb2+ than D. magna. The sensitivity to Cu2+, Cd2+, and Zn2+ was similar for D. magna and D. galeata. This study presents important aquatic toxicity and sensitivity data on D. galeata, which is not a widely used species in aquatic ecotoxicology studies. Our results recommend D. galeata as a suitable species for aquatic ecotoxicity tests because of its higher sensitivity.

Species Sensitivity Distributions for Nonylphenol to Estimate Soil Hazardous Concentration.

Nonylphenol is an endocrine-disrupting chemical that mimics estrogenic activity. Few studies have investigated the soil ecotoxicity of nonylphenol in the environment, based on probabilistic approaches. The present study generated soil toxicity data for nonylphenol through bioassays that determined the acute and chronic species sensitivity distributions and estimated the hazardous concentrations of nonylphenol in soil in order to protect soil ecosystems. We used eight soil-based organisms from six taxonomic groups for acute assays and five soil-based organisms from four taxonomic groups for chronic assays. The hazardous concentration values of nonylphenol in soil, based on acute and chronic species sensitivity distributions, were estimated using compiled data from the present study, as well as previous studies. This is the first study that generated sufficient data to develop species sensitivity distributions for nonylphenol in soil, and to determine hazardous concentrations of nonylphenol for soil environments.

The current state of the art in research on engineered nanomaterials and terrestrial environments: Different-scale approaches.

Recent studies regarding the environmental fate of engineered nanomaterials (ENMs) reported that most ENMs were eventually deposited in landfills. Therefore, it is important to evaluate the environmental effects of ENMs on soils through long-term and environmentally relevant studies. Our review of 65 studies published since 2007 revealed that ENMs had adverse effects on terrestrial species, including soil microorganisms, plants, and earthworms. The papers reported the results of soil toxicity tests for ENMs at the microcosm and mesocosm levels, in the field, and through food chains, as well as their effects on species sensitivity distributions. Little research has been conducted on the interaction between ENMs and actual environmental conditions, such as their effects on a community of multiple species or species sensitivity distributions. Few studies have used mesocosms, and only a single study has been conducted in the field. The present review provides a broad perspective on the impact of ENMs on soil organisms as reported in the literature and highlights directions for future work.

A new and sensitive method for measuring in vivo and in vitro cytotoxicity in earthworm coelomocytes by flow cytometry.

This study describes a new and sensitive method for measuring the in vivo and in vitro cytotoxicity of 2 earthworm species, Eisenia andrei and Perionyx excavatus, exposed to copper. Specifically, we measured the number of coelomocyte cells that were affected by copper following in vivo and in vitro exposure by flow cytometry, after calcein acetoxymethyl ester (calcein-AM) staining. We found that the coelomocyte viability of both earthworm species was noticeably reduced in the in vivo cytotoxicity test at concentrations of 100mg/kg copper in dry soil. However, pathological symptoms, such as mucous secretion and bleeding, swelling, thinning, and fragmentation, and burrowing symptoms were not evident following exposure to copper levels of <400mg/kg dry soil. In conclusion, the present study demonstrates that calcein-AM is a more sensitive test of earthworm coelomocyte cytotoxicity compared to the traditional individual level toxicity test. Therefore, this test could be used to detect low levels of metal contamination in soils.

Interaction of citrate-coated silver nanoparticles with earthworm coelomic fluid and related cytotoxicity in Eisenia andrei.

Understanding the interaction of nanoparticles with biological fluid is important for predicting the behavior and toxicity of nanoparticles in living systems. The earthworm Eisenia andrei was exposed to citrate-coated silver nanoparticles (cAgNPs), and the interaction of cAgNPs with earthworm coelomic fluid (ECF), the cytotoxicity of cAgNPs in earthworm coelomocytes was assessed. The neutral red retention assay showed a reduction in lysosomal stability after exposure. The toxicity of silver ions dissolved from cAgNPs in the soil medium was not significant. The aggregation and dissolution of cAgNPs increased in ECF, which contains various electrolytes that alter the properties of nanoparticles, and their subsequent toxicity. Microscopic and dissolution studies demonstrated that the aggregation of cAgNPs rapidly increased, and readily dissolved in ECF. The bioavailability of cAgNPs to earthworms induced lysosomal cytotoxicity. This is the first report to test the interaction and lysosomal cytotoxicity of nanoparticles in earthworm biofluids.

Zinc oxide nanoparticles delay soybean development: a standard soil microcosm study.

Soybean is an important crop and a source of food for humans and livestock. In this study, for the first time, the long-term effects of zinc oxide (ZnO) nanoparticles on the growth, development, and reproduction of soybean [Glycine max (L.) Merrill] were evaluated in a standard soil microcosm study. The soil was treated with 0, 50, or 500 mg/kg (dry weight) of ZnO nanoparticles. The growth and development of soybean plants were tracked during a cultivation period of 8-9 weeks under greenhouse conditions. Soybean development was damaged in both treatment groups, particularly in the group that received 500 mg/kg ZnO nanoparticles. In comparison with the control group, the roots and shoots of soybeans in treatment groups were shorter and had smaller surface area and volume. Furthermore, the plants in the 500 mg/kg treatment group did not form seeds. ZnO nanoparticles negatively affected the developmental stages and reproduction of soybean plants in a soil microcosm.

Evidence of soil particle-induced ecotoxicity in old abandoned mining area.

Ecotoxicity of heavy metals in soil is primarily associated with their bioaccessibility and bioavailability in the soil media. However, in some exceptional cases, soil ecotoxicity has been observed despite high total metal concentrations and low extractable metal concentrations in contaminated field sites; therefore, other exposure pathways must be considered. Therefore, the aim of this study was to evaluate the soil-particle induced ecotoxicity in an old mining area. We hypothesized that heavy metals, strongly adsorbed onto soil particles of consumable size for soil organisms, exhibit ecotoxicity, especially on soil particles ∼1 µm to 300 µm in size. A plant seedling assay, in vivo cytotoxicity assay using earthworm immune cells, and a metal bioconcentration assessment were performed. The results of soil particle toxicity revealed that the soil from the study area (A1-A4) had a low contribution to the soil ecotoxicity of extractable metals. For instance, the concentration of extractable arsenic was only 1.9 mg/kg soil, despite the total arsenic concentration reaching 36,982 mg/kg soil at the A1 site. The qualitative and quantitative analyses using SEM-EDX and ICP-OES, as well as principal component analyses, supported the hypothesis of the present study. Overall, the study results emphasize the importance of soil particle-induced ecotoxicity in long-term contaminated field soils. Our study results can inform on effective site-specific soil ecological risk assessment as they suggest the inclusion of soil particle-induced ecotoxicity as an important criterion in old, contaminated field sites, even when the extractable metal fraction in the field soil is low. ENVIRONMENTAL IMPLICATION: Bioaccessibility and bioavailability are primary factors contributing to the soil ecotoxicity of heavy metals. However, in some cases, such as long-term contaminated field sites, soil ecotoxicity has been confirmed even when low extractable metal concentrations were detected alongside high total metal concentrations. The findings of this study reveal that soil particles of edible size could be sources of soil ecotoxicity in the case of long-term contaminated fields with low extractable metal concentrations. The results of this study would contribute to the area of site-specific soil ecological risk assessment.

Microplastics promote the accumulation of negative fungal groups and cause multigenerational effects in springtails.

The environmental persistence of microplastics (MPs) is ubiquitous and problematic. Despite an increase in research on the soil ecotoxicity of MPs, the response of springtails to MP pollution remains unexplored. We hypothesized that MPs promote the accumulation of negative soil fungal groups and cause multigenerational effects in springtails. We performed a multigenerational study of high-density polyethylene MPs using springtail Folsomia candida and analyzed the soil fungal community. We found that soil entomopathogenic fungi and negative soil fungal groups accumulated in springtail F. candida due to soil MP pollution; subsequently, MPs negatively affected F. candida in the F2 generation. To the best of our knowledge, this is the first study to investigate the correlations between MP pollution, soil fungi, and fungi-feeding springtails. The study provides evidence of the accumulation of soil entomopathogenic fungi and negative soil fungal groups in F. candida caused by soil MP pollution.

Understanding boron toxicity in aquatic plants (Salvinia natans and Lemna minor) in the presence and absence of EDTA.

Even though boron is a widely used element in various industries and a contributor to water pollution worldwide, few studies have examined the toxicity of boron in aquatic plants. EDTA is used to maintain aquatic plants cultures, however it is possible to modify the toxicity of metals. The objective of this study is to assess the toxicity of boron in aquatic plants and explore the impact of EDTA presence on the resulting toxic responses. Floating watermoss Salvinia natans and duckweed Lemna minor were exposed to concentrations ranging from 5 to 100 mg/L for 7 days and 1 to 60 mg/L for 3 days, respectively. Growth and photosynthetic activity parameters were investigated in the presence and absence of EDTA. Growth inhibitions in both aquatic plants were observed in a concentration-dependent manner, irrespective of the presence or absence of EDTA. For instance, based on the specific growth rate (leaves coverage), EC10 values for S. natans were calculated as 12.7 (9.9-15.3) mg/L and 8.0 (5.8-10.3) mg/L with and without EDTA, respectively. In the case of L. minor, EC10 values were calculated as 1.3 (0.8-1.89) mg/L and 2.0 (0.4-4.3) mg/L with EDTA without EDTA, respectively. Significant effects were also observed on the photosynthetic capacity, however there was no change in the increase of boron concentration. Generally, negligible effects of EDTA to the toxicity of boron were observed in the present study. By comparing toxicity results based on the presence and absence of EDTA, which is an essential element in the test medium, the results of this study are expected to be utilized for the ecological risk assessment of boron in aquatic ecosystems.

Microplastic ingestion in aquatic and soil biota: A comprehensive review of laboratory studies on edible size and intake pattern.

Microplastic contamination is ubiquitous and can be transferred through the food chain to humans. However, studies on microplastic size have mainly focused on large animals with a body length >20 mm. To address this gap, we conducted a comprehensive review of 169 laboratory studies to determine the edible size of microplastics for macrofauna and flora in aquatic and soil biota. Our findings indicate that microplastics with a size of <300 µm and 1 µm, respectively, are edible for these organisms, which are positioned at the base of the food chain. We also analyzed intake and depuration patterns and identified factors affecting microplastic ingestion. Our study fills an important knowledge gap by identifying the range of microplastic sizes that can enter the food chain and be transferred to humans. The study findings have strong implications for the ecological risk assessment of microplastics and suggest a starting point for mitigating this threat.

Multigenerational study of gold nanoparticles in Caenorhabditis elegans: transgenerational effect of maternal exposure.

In this study, the generational transfer and multigenerational effect of gold nanoparticles (AuNPs) on Caenorhabditis elegans were investigated by observing the parental generation (F0) to the fourth offspring generation (F4) using food-exposure approaches. There were no significant changes on survival rate under all generations by AuNP maternal exposure to the F0 generation. However, reproduction rate was clearly affected in the F2 generation but then gradually recovered in the F3 and F4 generations. The abnormalities of the reproductive system showed a close relationship with reproduction rates. These phenomenons may be due to the germ-line transfer. The germ line of F0 generation such as gonad and embryo germ cell may be affected during their development by maternal exposure of AuNPs, and this generation caused transgeneration effect on future generations. To the best of our knowledge, this is the first study to provide the evidence of transgenerational effects by maternal exposure of nanoparticles to the next generations.

Multigenerational effects of microplastic fragments derived from polyethylene terephthalate bottles on duckweed Lemna minor: Size-dependent effects of microplastics on photosynthesis.

The 2019 global coronavirus disease pandemic has led to an increase in the demand for polyethylene terephthalate (PET) packaging. Although PET is one of the most recycled plastics, it is likely to enter the aquatic ecosystem. To date, the chronic effects of PET microplastics (MPs) on aquatic plants have not been fully understood. Therefore, this study aimed to investigate the adverse effects of PET MP fragments derived from PET bottles on the aquatic duckweed plant Lemna minor through a multigenerational study. We conducted acute (3-day exposure) and multigenerational (10 generations from P0 to F9) tests using different-sized PET fragments (PET0-200, < 200 µm; PET200-300, 200-300 µm; and PET300-500, 300-500 µm). Different parameters, including frond number, growth rate based on the frond area, total root length, longest root length, and photosynthesis, were evaluated. The acute test revealed that photosynthesis in L. minor was negatively affected by exposure to small-sized PET fragments (PET0-200). In contrast, the results of the multigenerational test revealed that large-sized PET fragments (PET300-500) showed substantial negative effects on both the growth and photosynthetic activity of L. minor. Continuous exposure to PET MPs for 10 generations caused disturbances in chloroplast distribution and inhibition of plant photosynthetic activity and growth. The findings of this study may serve as a basis for future research on the generational effects of MPs from various PET products.

Assessing the risks of silver nanoparticle-concentrated matrix application in agricultural soil: Implications for plant and soil enzymes.

The practice of reusing biosolids may be an effective strategy for addressing nutrient reuse and soil shortages. However, the accumulation of silver nanoparticles (AgNPs) in biosolids poses a major ecological hazard to organisms. In this study, we evaluated the effects of AgNPs on plant and soil enzymes in terrestrial ecosystems by exposing soybean Glycine max, as well as soil, to varying concentrations of AgNPs embedded either on the surface soil layer or throughout the soil matrix. We found that exposing the plants to 20 mg AgNPs/kg soil that was embedded throughout the soil matrix had a significant impact. Conversely, soil enzymes (dehydrogenase, urease, and fluorescein diacetate hydrolase) were affected by exposure to 20 and 80 mg AgNPs/kg of soil embedded on the surface soil layer or throughout the soil matrix at 20 mg AgNPs/kg soil. The toxic effects of AgNPs were induced by different receptor habitats. The presence of AgNPs in soil led to developmental retardation, inhibited root growth, reduced photosynthetic activity, and decreased transpiration rates in leaves. These plants also produced fewer fruits compared to soybean plants grown in regular soil without AgNPs. Moreover, most of the AgNPs soil groups demonstrated a decrease in soil enzyme activity in the surface soil; therefore, soil-capping patterns involving embedded stressors should be considered. These findings provide valuable insights that will contribute substantially to advancements in the field of biosolids for land applications.

Salvinia natans microplate assay: A simple and efficient method for evaluating aquatic toxicity.

This study proposes a microplate assay for chemical toxicity evaluation using S. natans; this assay is a miniaturization of a culture dish assay from previous studies. The optimal initial frond number of S. natans in the microplate assay was established and the feasibility of the microplate assay was evaluated. To evaluate the applicability of the developed method, S. natans was exposed to six model chemicals (one metalloid and five heavy metals) and the specific growth rate and photosynthetic activity were compared. We determined that the optimal initial frond number was four fronds for the microplate assay. Additionally, toxicity sensitivity to six model chemicals revealed similar results to the culture dish assay. Therefore, we propose that the S. natans microplate assay is a simple and effective method to assess ecotoxicity as it requires less test solution and area than the culture dish assay. This methodology can be expandable to ecotoxicological research.

Acute and multigenerational effects of petroleum- and cellulose-based microfibers on growth and photosynthetic capacity of Lemna minor.

Comparative toxicological assessment studies on the effects of petroleum- and cellulose-based microfibers on aquatic plants are limited. Therefore, we evaluated the acute and 10-generational toxicological effects of two types of petroleum- and cellulose-based microfibers on the duckweed Lemna minor. Plant growth and photosynthesis parameters were monitored as bioindicators. The multigenerational test revealed the following ranking of the microfibers according to the severity of their effects on L. minor: polypropylene > lyocell > viscose > polyethylene terephthalate. The acute tests revealed a significant increase in the energy required to initiate photosynthesis, although the growth of L. minor was not adversely affected by any microfiber. Both petroleum- and cellulose-based microfibers induced adverse effects on the growth and photosynthesis of L. minor in multigenerational tests. The results of the generational tests contribute to the understanding of the long-term adverse effects of microfibers on aquatic plants.

Length- and polymer-dependent ecotoxicities of microfibers to the earthworm Eisenia andrei.

Microfibers are widespread environmental pollutants introduced to the soil environment because of the increasing use of plastic polymers. However, research on the soil ecotoxicity of microfibers is limited, especially when compared to research on their aquatic toxicity. This study investigated the effects of sub-chronic microfiber exposure on the earthworm Eisenia andrei. We compared the effects of three types of microfibers: short lyocell microfibers (231 ± 126 µm long), short polypropylene microfibers (191 ± 107 µm long), and long polypropylene microfibers (891 ± 141 µm long). After exposure for 21 days, earthworm survival, coelomocyte viability, cast microbial viability, and gut microbial viability were assessed, and a histopathological examination of the digestive tract and reproductive tissues was conducted. In addition, long polypropylene microfibers egested by the earthworms were collected to explore the possibility of earthworm-driven biofragmentation. Results indicated that high exposure concentration (1000 mg/kg dry soil) negatively affected earthworm coelomocytes and intestinal tissue, gut, and cast microbiomes. Although all three microfiber types reduced earthworm survival, the short polypropylene microfibers were more toxic to the earthworms than the long polypropylene microfibers or short lyocell microfibers, which indicated that size-dependent soil ecotoxicity was induced. PP microfibers were found to more negatively affect cast microbial activity and intestinal tissue than lyocell microfibers, indicating polymer-dependent soil ecotoxicity potential against earthworm species. This study provides evidence that synthesized microfibers cause cytotoxicity and decrease gut microbiome viability in earthworms, and that they can be biofragmented by earthworms.