Contamination Status of Novel Organophosphate Esters Derived from Organophosphite Antioxidants in Soil and the Effects on Soil Bacterial Communities

Risks of biodegradable films: The time-lagged release of phthalic acid esters and organophosphates esters under realistic agricultural environments

Agricultural plastic films, while boosting crop productivity, may pose significant environmental risks due to additive release during crack degradation. Phthalic acid esters (PAEs) and organophosphate esters (OPEs), widely used as plasticizers and flame retardants respectively, represent two additive categories of the greatest environmental concern due to their persistence and endocrine-disrupting properties. This study systematically investigated the dynamic release of PAEs and OPEs from polyethylene (PE) and biodegradable poly (butylene adipate-co-terephthalate)/polylactic acid (PBAT/PLA)-based films under four simulated agricultural conditions: Natural conditions (NC), UV irradiation (UV), high temperature (HT), and flooding (FC). Uncultivated soil exhibited Σ8PAEs and Σ7OPEs approximately of 1317.5 ng/g and 1931.1 ng/g, respectively. During a 360 d incubation period, the contents of PAEs in soil surged during a short-term period, which may link to the desorption of adsorbed contaminant. Biodegradable films released higher PAEs concentrations than PE films, with secondary contamination peaks emerging 180-360 d post-incubation. Scanning electron microscopy (SEM) observations revealed that structural degradation (e.g., cracks/holes) during early degradation (0-180 d) unexpectedly amplified additive leaching in later stages, contrasting with assumptions of reduced contamination risks over time. UV irradiation had a photo-degradation effect on PAEs further accelerated the release of pollutants by 25-40 %, while high temperature and flooding conditions showed limited promoting effects along with NC conditions. These findings highlight the need for additive-free formulations and environment-specific mulch management policies to mitigate soil contamination risks.

Traditional and novel organophosphate esters in atmosphere of greenhouse covered with mulch films: Seasonal variations, partitioning and exposure risks

Mulch films play a critical role in the accumulation of organophosphate esters (OPEs) in greenhouse soils. However, their impact on the occurrence, partitioning and health risks of atmospheric OPEs is unclear. This study fully investigated multi-media distributions of eleven traditional OPEs and four novel OPEs in greenhouses covered with degradable mulch films. The atmospheric concentrations exhibited substantial variability, ranging from 539 to 14821 pg/m³ in the gas phase and from 242 to 8320 pg/m³ in the particle phase, with summer levels higher than winter levels. Significant correlations (p < 0.05) were detected between OPE concentrations in mulch films and in air, indicating mulch films as a major source. First-order kinetic model effectively characterized the release patterns of dominant congeners including triphenyl phosphate and tris(2,4-ditert-butylphenyl) phosphate from degradable films. The Li-Ma-Yang model showed superior predictive capability for gas-particle partitioning than the Harner-Bidleman model. Total concentrations of OPEs in uncoated soils were at a range of 274-955 μg/kg. Soil-air exchange behaviors of OPEs governed by inherent volatility exhibited a seasonal dependence. While non-carcinogenic risks of OPEs for greenhouse farmers via air inhalation and dermal contact were negligible, holistic health assessments should integrate other uptake pathways and consider transformation products of OPEs.

Microbial metabolism in wormcast affected the perturbation on soil organic matter by microplastics under decabromodiphenyl ethane stress

Large-scale plastic wastes annually inevitably induce co-pollution of microplastics (MPs) and novel brominated flame retardants (NBFRs), while gaps remain concerning their effect on terrestrial function. We investigated the impact of polylactic acid (PLA) or polyethylene (PE) MPs after aging in soil-earthworm microcosms under decabromodiphenyl ethane (DBDPE) contamination. MPs altered the food (i.e. soil) of earthworms and affected cast composition, which in turn further affected soil function. After 28 days of exposure, MPs, especially UV-aged MPs, caused the significant enrichment of plastics-degrading bacteria and C/N cycling functions in wormcast, with increased dissolved organic matter consumption after co-exposure (1 % MPs accompanied by 10 mg kg-1 DBDPE). Aging significantly affected soil carbon sequestration, while its effects varied depending on the types of MPs. Notably, soil organic matter was the most impactor affecting wormcast bacteria, highlighting the importance of earthworm's activity on soil carbon. In comparison, PLA-MPs induced stronger responses to the C/N cycling process based on its biodegradable property than PE-MPs, however, aging had a greater effect on PE-MPs due to the formation of oxygen molecules from nothing in the structure. This study expands our current understanding of the interactions of aged MPs and DBDPE in the terrestrial ecosystem. SYNOPSIS: This study highlighted that both MPs before and aging altered the bacterial communities in wormcast and further affected soil ecology during earthworm feeding and excretion.

Synthetic phenolic antioxidant contamination in farmland soils induced by mulching films: Distribution and transformation pathways

The occurrence and distribution of synthetic phenolic antioxidants (SPAs) originating from mulch film in farmland soils, along with their transformation characteristics and pathways, remain largely unknown. This study is the first to investigate nineteen SPAs and four transformation products (TPs) in farmland soils across China. In film-mulching soils, concentrations of SPAs (median, range: 83.6 ng/g, 20.6-863 ng/g) and TPs (46.4 ng/g, 8.36-489 ng/g) were found significantly higher than in nonfilm-mulching soils, suggesting that mulch film is an important SPA source in farmlands. The ecological risk posed by SPAs was considerable, with estimated risk quotients (RQs) reaching up to 14.7. Furthermore, a laboratory soil incubation experiment was conducted on pentaerythritol tetrakis(3-(3,5-di-tert-butyl-4-hydroxyphenyl)-propionate) (Ir1010), a typical SPA with high estimated ecological risk (RQs up to 3.01). The half-life of Ir1010 in unsterilized soil was 6.73 days, much shorter than in sterilized soils, suggesting that soil microbes effectively promoted its transformation rate. Importantly, ten TPs of Ir1010 were identified in soil through nontargeted screening using high-resolution mass spectrometry, indicating aromatic epoxidation, hydroxylation, and hydrolysis as transformation pathways. This study firstly reveals the occurrence SPAs and TPs in farmland soils and suggests their transformation mechanism, highlighting the complex risks posed by these emerging agricultural contaminants.

Degradation mechanisms of isodecyl diphenyl phosphate (IDDP) and bis-(2-ethylhexyl)-phenyl phosphate (BEHPP) using a novel microbially-enriched culture

Organophosphate esters (OPEs) pose significant environmental concerns due to their widespread presence, potential toxicity, and persistence. This study investigated the degradation of the isodecyl diphenyl phosphate (IDDP) and bis-(2-ethylhexyl)-phenyl phosphate (BEHPP) using a novel enrichment culture, which could degrade 85.4 % and 78.2 % of 1 mg/L IDDP and BEHPP after 192 h and 172 h, respectively, under extremely low bacterial dosage (the initial OD600 nm= 0.0075, biomass was approximately 1 mg/L). The identification of intermediate products suggested that the degradation reactions likely included hydrolysis, hydroxylation, methylation, carboxylation, and glycosylation. Metagenomic analysis highlighted the crucial role of enzymes in degrading IDDP and BEHPP, including phosphatase, phosphodiesterase, cytochrome P450, and hydroxylase. Pure strains Burkholderia cepacia ZY1, Sphingopyxis terrae ZY2, and Amycolatopsis ZY3 were isolated, and their efficient individual degradation abilities were confirmed. These efficiencies were lower compared to the enrichment culture, emphasizing the importance of microbial interactions for effective degradation. The pathways identified for these strains illustrated their involvement in different degradation steps, reinforcing the synergy between different degraders. Molecular dynamics simulations provided insights into the interactions between alkaline phosphatase (ALP), cytochrome P450 (CYP450), and hydroxylase with OPEs. These enzymes demonstrated a strong binding capacity with both BEHPP and IDDP, exhibiting distinct binding site preferences that may contribute to varied metabolic pathways. These findings comprehensively reveal the transformation mechanisms of OPEs.

Emerging and legacy organophosphate flame retardants in the tropical estuarine food web: Do they exhibit similar bioaccumulation patterns, trophic partitioning and dietary exposure?

Emerging organophosphate flame retardants (E-OPFRs) are a new class of pollutants that have attracted increasing attention, but their bioaccumulation patterns and trophodynamic behaviors in aquatic food webs still need to be validated by comparison with legacy OPFRs (L-OPFRs). In this study, we simultaneously investigated the bioaccumulation, trophic transfer, and dietary exposure of 8 E-OPFRs and 10 L-OPFRs in a tropical estuarine food web from Hainan Island, China. Notably, the Σ10L-OPFRs concentration (16.1-1.18 × 105 lipid weight (lw)) was significantly greater than that of Σ8E-OPFRs (nondetectable (nd) - 2.82 × 103 ng/g lw) among the investigated organisms, and they both exhibited similar trends: fish Collapse

Key Words

• Bioaccumulation
• Biotransformation
• Legacy and emerging organophosphate flame retardants
• Organism partitioning
• Trophic transfer

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Affiliation(s)

Qianyi Huang Key Laboratory of Tropical Marine Bio-resources and Ecology, Guangdong Provincial Key Laboratory of Applied Marine Biology, South China Sea Institute of Oceanology, Chinese Academy of Sciences, Guangzhou 510301, China University of Chinese Academy of Sciences, Beijing 100049, China
Rui Hou Guangdong Provincial Key Laboratory of Water Quality Improvement and Ecological Restoration for Watersheds, School of Ecology, Environment and Resources, Guangdong University of Technology, Guangzhou 510006, China
Yuchen Wang College of Life Sciences and Engineering, Jinan University, Guangzhou 510632, China
Lang Lin South China Sea Bureau of Ministry of Natural Resources, Guangzhou 510310, China
Hengxiang Li Key Laboratory of Tropical Marine Bio-resources and Ecology, Guangdong Provincial Key Laboratory of Applied Marine Biology, South China Sea Institute of Oceanology, Chinese Academy of Sciences, Guangzhou 510301, China
Shan Liu Key Laboratory of Tropical Marine Bio-resources and Ecology, Guangdong Provincial Key Laboratory of Applied Marine Biology, South China Sea Institute of Oceanology, Chinese Academy of Sciences, Guangzhou 510301, China
Xiangrong Xu Guangxi Laboratory on the Study of Coral Reefs in the South China Sea, Coral Reef Research Center of China, School of Marine Sciences, Guangxi University, Nanning 530004, China
Kefu Yu Guangxi Laboratory on the Study of Coral Reefs in the South China Sea, Coral Reef Research Center of China, School of Marine Sciences, Guangxi University, Nanning 530004, China Southern Marine Science and Engineering Guangdong Laboratory (Guangzhou), Guangzhou 511458, China
Xiaoping Huang Key Laboratory of Tropical Marine Bio-resources and Ecology, Guangdong Provincial Key Laboratory of Applied Marine Biology, South China Sea Institute of Oceanology, Chinese Academy of Sciences, Guangzhou 510301, China

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Novel Organophosphate Ester Tris(2,4-di-tert-butylphenyl)phosphate Alters Lipid Metabolism: Insights from Lipidomic Analysis and mRNA Expression

Tris(2,4-di-tert-butylphenyl)phosphate (TDTBPP), a novel organophosphate ester (OPE), has been extensively detected in various environmental and biological samples; however, its potential biological effects remain unexplored. In this study, we investigated biotransformation characteristics, alteration of lipid metabolism, and mRNA expression in primary mouse hepatocytes (PMHs) following exposure to TDTBPP. After 36-h exposure in PMHs, TDTBPP exhibited a high stability potential with no statistically significant degradation trend. Subsequently, we analyzed the disruption of lipid homeostasis in PMHs following exposure to 0-4.5 μM TDTBPP. Lipidomic analysis indicated that TDTBPP disrupted lipid homeostasis in PMHs, and several lipid classes were dysregulated, in particular, glycerolipids and glycerophospholipids. Additionally, three lipids were proposed as potential lipid biomarkers of TDTBPP exposure, including triglycerides (TGs) and phosphatidylcholines (PCs). These observations were further supported by transcriptional changes, with significant alteration observed in genes associated with lipid uptake, de novo lipogenesis, β-oxidation of fatty acids, glycerolipid metabolism, and lipid export. Overall, these findings highlight the detrimental effects of TDTBPP on lipid homeostasis, providing important insights for health risk assessments of this abundant OPE in the environment.

Different wetting states in riparian sediment ecosystems: Response to microplastics exposure

Climate change alters the wetting state of riparian sediments, impacting microbial community response and biogeochemical processes. Microplastics (MPs) invade nearly all ecosystems on earth, posing a significant environmental risk. However, little is known about the response mechanism of MP exposure in sediment ecosystems with different wetting states under alternating seasonal rain and drought conditions. In this study, sediments with three different wetting states were selected to explore the differential response of ecosystems to PLA MP exposure. We observed that PLA MP exposure directly affected biogeochemical processes in sediment ecosystems and induced significant changes in microbial communities. PLA MP exposure was found to alter the composition of key species and microbial functional groups in the ecosystem, resulting in a more complex, interconnected, but less stable microbial network. Our findings showed that PLA MP exposure enhances the contribution of stochastic processes, for example the dispersal limitation increasing from 7.41 % to 54.32 %, indicating that sediment ecosystems strive to buffer disturbances from PLA MP exposure. In addition, 87 pathogenic species were detected in our samples, with PLA MPs acting as vectors for their transmission, potentially amplifying ecosystem disturbance. Importantly, we revealed that submerged sediments may present a greater environmental risk, while alternating wet and dry sediments demonstrate greater resistance and resilience to PLA MPs pollution. Overall, this study sheds light on how sediment ecosystems respond to MP exposure, and highlights differences in sediment response mechanisms across wetting states.

Target and Nontarget Analysis of Organophosphorus Flame Retardants and Plasticizers in a River Impacted by Industrial Activity in Eastern China

Industrial activities are a major source of organophosphorus flame retardants (OPFRs) and plasticizers in aquatic environments. This study investigated the distribution of 40 OPFRs in a river impacted by major industrial manufacturing plants in Eastern China by target analysis. Nontarget analysis using high-resolution mass spectrometry was further employed to identify novel organophosphorus compounds (NOPs). Thirty-four OPFRs were detected in river water samples, with total concentrations of 62.9-1.06 × 103 ng/L (median: 455 ng/L). Triphenylphosphine oxide and diphenyl phosphoric acid were ubiquitously detected up to 620 and 127 ng/L, respectively. Among 26 identified NOPs, 17 were reported for the first time in the environment, including 14 novel organophosphate esters (especially 4 heterocycles and 3 oligomers), 2 organophosphites, and an organophosphonate. Bis(2,4-di-tert-butylphenyl) hydrogen phosphate and 2,2-dimethylpropoxy(propyl)phosphinic acid with high predicted persistence or toxicity were widely detected, with semiquantified concentrations up to 990 and 1.0 × 103 ng/L, respectively. Structurally similar organophosphorus heterocycles exhibited consistent variation trends, suggesting a common emission source. Estimated annual river discharges to the sea were 20.6-37.0 kg/yr for OPFRs and 30.8-161 kg/yr for NOPs. These findings indicate that industrial activities contribute OPFRs and NOPs to the river catchment and its estuary, posing ecological risks to both terrestrial and marine environments.

Novel organophosphate esters and their transformation products in offshore sediment from Eastern China: Occurrence, temporal trend, and risk assessment

Offshore sediment serves as an important sink for traditional organophosphate esters (TOPEs) originating from terrestrial sources. However, the contamination characteristics of novel OPEs (NOPEs) and their hydrolyzed and hydroxylated transformation products (Di- and OH-OPEs) in marine sediment are still unknown. In this study, 34 OPE-associated contaminants were measured in six offshore sediment cores (71 samples) collected from Eastern China. The total concentrations of Σ15TOPEs, Σ3NOPEs, Σ9Di-OPEs, and Σ7OH-OPEs in surface sediments were 3.16-73.4, n.d.-16.3, 4.48-21.4, and 0.14-0.42 ng g-1, respectively. NOPE compounds, such as tris(2,4-di-tert-butylphenyl) phosphate and its diester product, exhibited high contamination levels, primarily due to their high hydrophobicity and extensive industrial applications. Additionally, atmospheric transportation, along with wet and dry deposition and ocean currents, plays a crucial role in their distribution in offshore sediment. The location conditions and historical usage also influenced the vertical distributions of OPE-associated contaminants in sediment cores. Notably, a concentration peak of bis(2,4-di-tert-butylphenyl) phosphate (B2,4DtBPP) was dating back to 1940s, indicating the early usage of antioxidant tris(2,4-di-tert-butylphenyl) phosphite. Furthermore, a risk quotient (RQ) model was employed to assess the ecological risks posed by OPEs. Generally, the acute toxicity-based predicted no-effect concentrations for studied compounds were 1 to 2 orders of magnitude lower than those based on chronic toxicity. NOPEs and B2,4DtBPP exhibited high ecological risks, with maximum RQ values of 1570-4877 based on acute toxicity and 93.4-197 based on chronic toxicity. Notably, ΣRQ values for NOPEs were significantly higher than those of TOPEs (Mann-Whitney U test, p < 0.001), indicating their severe ecological risks in offshore sediment. Therefore, given the continuous input and considerable persistence of NOPEs in offshore sediment, their toxic effects and mechanisms warrant thorough investigation. This study provides the first evidence for the occurrence, temporal trends, and potential risks of NOPEs in marine sediment environment.

Electrochemical degradation of aromatic organophosphate esters: Mechanisms, toxicity changes, and ecological risk assessment

Aromatic organophosphate esters (AOPEs), including triphenyl phosphate (TPHP), tricresyl phosphate (TCP), and 2-ethylhexyl diphenyl phosphate (EHDPP), pose significant health and ecological risks. Electrochemical advanced oxidation process (EAOP) is effective in removing refractory pollutants. In this study, the degradation performance and detoxication ability of AOPEs by EAOP were investigated. Hydroxylation, oxidation, and bond cleavage products were identified as major degradation products (DPs) due to the reaction with ·OH and O₂·-. Toxicity assessments using ecological structure activity relationship (ECOSAR) model and flow cytometry (FCM) revealed the cytotoxicity and aquatic toxicity for DPs were significantly decreased. 16S rRNA gene sequencing of sediment exposure to AOPEs and DPs were applied to assess ecological toxicity, and results showed reduced bacterial richness and diversity with EHDPP and TCP, while TPHP slightly enhanced richness. AOPEs and DPs altered bacterial genera involved in carbon, nitrogen, sulfur cycling and organic compound degradation. Bacterial community assembly suggested elevated stochastic processes and reduced ecotoxicity, confirming AOPEs can be effectively detoxified by 10-min EAOP treatment. Molecular ecological network analysis indicated increased complexity and stability of bacterial communities with DPs. These findings comprehensively revealed the toxicity of AOPEs and their DPs and provided the first evidence of effective degradation and detoxification by EAOP from ecotoxicological perspective.