Heavy metal (HM) contamination poses an escalating threat to human health and global terrestrial ecosystems. Inexpensive, eco-friendly technologies that reduce HM concentrations in soil are needed. Utilizing the synergy between hyperaccumulating plants and their rhizosphere microbes offers a promising approach to the bioremediation of HM-contaminated sites; however, the mechanisms underlying this plant-microbe relationship remain unclear. In the present study, high-resolution in situ imaging revealed that inoculation of the plant growth-promoting bacterium (PGPB) Bacillus megaterium altered the rhizosphere microenvironment of the Cd and Mn-hyperaccumulator Celosia argentea grown in HM-contaminated field soil. Decreased pH, increased O₂ fluxes, and stimulated microbial activity and enzyme-mediated C and P cycling were observed. Multi-omics analyses suggested that PGPB-modulated rhizosphere microbial succession selectively enriched beneficial taxa and functional genes associated with nutrient cycling and metal resistance. Transcriptomic and metabolomic profiling analysis revealed that the PGPB induced transcriptional reprogramming in C. argentea, leading to the activation of antioxidant defenses, metal transporter expression, and root exudate metabolism, with a focus on lipid- and sphingolipid-related pathways. These processes collectively enhanced the mobilization and uptake of Cd, Pb, and Zn at the root-soil interface, suggesting that the mutualistic plant-microbe system facilitated HM phytoextraction efficiency. Our findings offer novel insights into how microbial inoculants can rewire the rhizosphere microecology to regulate metal dynamics and enhance the remediation of multi-metal-contaminated soils.

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Photodegradation of microplastics (MPs) induced by sunlight plays a crucial role in determining their transport, fate, and impacts in aquatic environments. Dissolved black carbon (DBC), originating from pyrolyzed carbon, can potentially mediate the photodegradation of MPs owing to its potent photosensitization capacity. This study examined the impact of pyrolyzed wood derived DBC (5 mg C/L) on the photodegradation of polystyrene (PS) MPs in aquatic solutions under UV radiation. It revealed that the photodegradation of PS MPs primarily occurred at the benzene ring rather than the aliphatic segments due to the fast attack of hydroxyl radical (•OH) and singlet oxygen (¹O₂) on the benzene ring. The photosensitivity of DBC accelerated the degradation of PS MPs, primarily attributed to the increased production of •OH, ¹O₂, and triplet-excited state DBC (³DBC*). Notably, DBC-mediated photodegradation was related to its molecular weight (MW) and chemical properties. Low MW DBC (<3 kDa) containing more carbonyl groups generated more •OH and ¹O₂, accelerating the photodegradation of MPs. Nevertheless, higher aromatic phenols in high MW DBC (>30 kDa) scavenged •OH and generated more O₂•^-, inhibiting the photodegradation of MPs. Overall, this study offered valuable insights into UV-induced photodegradation of MPs and highlighted potential impacts of DBC on the transformation of MPs.

Drinking water distribution systems are increasingly vulnerable to sewage intrusion due to aging water infrastructure and intensifying water stress. While the health risks associated with sewage intrusion have been extensively studied, little is known about the impacts of intruded bacteria and dissolved organic matter (DOM) on microbiology in drinking water. In this dynamic study, we demonstrate that the intrusion of 1 % sewage into tap water resulted in immediate contamination, including an 8-fold increase in biomass (TCC), a 48.9 % increase in bacterial species (ASVs), a 12.5 % increase in organic carbon content (DOC), and a 13.5 % increase in unique DOM molecular formulae. Over time, sewage intrusion altered tap water microbiology by accelerating bacterial growth rates (5-fold faster), selectively promoting ASVs in community succession, and producing 998 more unique DOM formulae. More significantly, statistical analysis revealed that the intrusion of 1 % sewage shifted the driving force of bacterial and DOM composition covariance from a DOM-dependent process in tap water to a bacterial-governed process post-intrusion. Our results clearly demonstrate the disruptive effects of sewage intrusion into tap water, emphasizing the urgent need to consider the long-lasting impacts of sewage intrusion in drinking water distribution systems, in addition to its immediate health risks.