The data indicated that nitrogen and phosphorus pollution in Lugu Lake is progressively higher in the Caohai region than in Lianghai, and more intense during dry seasons than wet seasons. The core environmental culprits leading to nitrogen and phosphorus pollution were dissolved oxygen (DO) and chemical oxygen demand (CODMn). Lugu Lake's inherent production of nitrogen and phosphorus, at 6687 and 420 tonnes annually, respectively, stood in contrast to the 3727 and 308 tonnes per annum, respectively, of nitrogen and phosphorus added from external sources. Pollution sources, in descending order of contribution, show sediment as the most significant, followed by land-use categories, then resident and livestock breeding, and finally, plant decay. Sediment nitrogen and phosphorus loads contributed to a substantial 643% and 574% of the total load, respectively. Managing nitrogen and phosphorus pollution in Lugu Lake prioritizes controlling the natural release of sediment and blocking external inputs from shrubs and woodlands. Consequently, this investigation provides a theoretical framework and practical guidance for managing eutrophication in highland lakes.
Performic acid's (PFA) growing use in wastewater disinfection is a consequence of its strong oxidizing power and limited disinfection byproduct formation. Despite this, the disinfection methods and pathways for pathogenic bacteria are poorly understood. This investigation aimed to inactivate E. coli, S. aureus, and B. subtilis in simulated turbid water and municipal secondary effluent, utilizing sodium hypochlorite (NaClO), PFA, and peracetic acid (PAA). The plate count method, utilizing cell cultures, demonstrated the extreme sensitivity of E. coli and S. aureus to NaClO and PFA, resulting in a 4-log reduction in viability at a CT of 1 mg/L-min with an initial disinfectant concentration of 0.3 mg/L. A notably higher level of resistance was observed in B. subtilis. PFA's inactivation rate, with an initial disinfectant dose of 75 mg/L, needed a contact time of 3 to 13 mg/L-minute to achieve a 4-log reduction. The turbidity significantly impeded the disinfection process. For PFA to inactivate E. coli and Bacillus subtilis by four orders of magnitude, secondary effluent necessitated contact times six to twelve times longer than those in simulated, turbid water; Staphylococcus aureus could not be inactivated by four logs. The effectiveness of PAA as a disinfectant fell far short of the other two disinfectants' capabilities. E. coli inactivation by PFA mechanisms involved both direct and indirect reaction pathways, with PFA responsible for 73% of the reactions, and hydroxyl and peroxide radicals contributing 20% and 6%, respectively. PFA disinfection led to the complete breakdown of E. coli cells, in stark contrast to the largely intact exteriors of S. aureus cells. Regarding the experimental conditions, B. subtilis demonstrated the lowest level of harm. Cell culture-based analysis demonstrated a significantly higher inactivation rate than the flow cytometry-based detection. The source of this incongruity, post-disinfection, was determined to be viable, yet non-culturable bacteria. This research suggested PFA's efficacy in controlling ordinary wastewater bacteria, but its deployment against persistent pathogens should be approached with care.
Emerging poly- and perfluoroalkyl substances (PFASs) are gaining traction in China, as legacy PFASs are being progressively eliminated. The occurrence and environmental behaviors of emerging PFASs in Chinese freshwater environments remain poorly understood. Using 29 paired water and sediment samples from the Qiantang River-Hangzhou Bay, a vital drinking water resource for cities in the Yangtze River basin, this study assessed 31 perfluoroalkyl substances (PFASs), including 14 novel PFASs. Legacy PFAS, notably perfluorooctanoate, was the most prevalent compound found in water samples (ranging from 88 to 130 nanograms per liter) and sediment (with concentrations ranging from 37 to 49 nanograms per gram of dry weight). Emerging PFAS compounds were found in the water, with a noteworthy presence of 62 chlorinated polyfluoroalkyl ether sulfonates (62 Cl-PFAES; mean 11 ng/L, and a range of concentrations of 079 to 57 ng/L) and 62 fluorotelomer sulfonates (62 FTS; 56 ng/L, below the detection limit, below 29 ng/L). Eleven emerging PFAS compounds were identified in sediment samples, and prominently featured were 62 Cl-PFAES (mean concentration of 43 ng/g dw, varying from 0.19 to 16 ng/g dw), and 62 FTS (mean 26 ng/g dw, concentrations lower than the detection threshold of 94 ng/g dw). Spatially, the water samples collected near the neighboring cities indicated a greater presence of PFAS compared to samples taken further away. From the group of emerging PFAS compounds, 82 Cl-PFAES (30 034) displayed the largest mean field-based log-transformed organic carbon normalized sediment-water partition coefficient (log Koc), followed by 62 Cl-PFAES (29 035) and hexafluoropropylene oxide trimer acid (28 032). p-Perfluorous nonenoxybenzene sulfonate (23 060) and 62 FTS (19 054) displayed a comparatively reduced average log Koc value. Artenimol To our understanding, this investigation of emerging PFAS occurrences and partitioning in the Qiantang River is, to our knowledge, the most thorough to date.
For sustainable social and economic growth, and the health and vitality of its population, maintaining food safety standards is indispensable. The traditional risk assessment method for food safety, concentrated on the weighting of physical, chemical, and pollutant factors, lacks the holistic approach necessary to fully evaluate food safety risks. Accordingly, a novel food safety risk assessment model incorporating the coefficient of variation (CV) and the entropy weight method (EWM), is presented in this paper, designated as CV-EWM. The impact of physical-chemical and pollutant indexes on food safety is reflected in the objective weight of each index, determined using the CV and EWM methodologies, respectively. Weights derived from EWM and CV are coupled using the Lagrange multiplier approach. The combined weight is defined as the quotient of the square root of the product of the two weights and the weighted sum of the square roots of the respective products of the weights. Consequently, the CV-EWM risk assessment model is formulated to provide a thorough evaluation of food safety risks. To assess the compatibility of the risk assessment model, the Spearman rank correlation coefficient method is implemented. To conclude, the suggested risk assessment model is applied in order to ascertain the quality and safety risks related to sterilized milk. The model's output, generated by analyzing the attribute weights and comprehensive risk assessment of physical-chemical and pollutant indices affecting sterilized milk quality, scientifically determines the weight of these indices. This provides an objective method for evaluating overall food risk, which is particularly helpful in understanding the underlying causes of risk occurrence and subsequently controlling and preventing issues related to food quality and safety.
The naturally radioactive soil at the formerly operational South Terras uranium mine in Cornwall, UK, provided soil samples that contained arbuscular mycorrhizal fungi. Artenimol The species Rhizophagus, Claroideoglomus, Paraglomus, Septoglomus, and Ambispora were identified, and pot cultures were successfully cultivated for all, save for the Ambispora specimens. Species-level identification of cultures was achieved through a combination of morphological observations, rRNA gene sequencing, and phylogenetic analyses. These cultures, within a compartmentalized pot system, were instrumental in experiments designed to measure the contribution of fungal hyphae to the accumulation of essential elements, such as copper and zinc, and non-essential elements, including lead, arsenic, thorium, and uranium, in the tissues of Plantago lanceolata's roots and shoots. The treatments, without exception, produced no discernible impact, either positive or negative, on the biomass of the shoots and roots, according to the findings. Artenimol Rhizophagus irregularis applications exhibited a more considerable copper and zinc accumulation within the plant shoots, in contrast to the uptake and accumulation of arsenic in the roots when R. irregularis and Septoglomus constrictum were used together. In addition, R. irregularis caused an elevation in the uranium concentration within both the roots and the shoots of the P. lanceolata plant. This study explores fungal-plant interactions, which are vital for understanding the transfer of metals and radionuclides from soil to the biosphere at contaminated locations, for example, in mine workings.
The presence of excessive nano metal oxide particles (NMOPs) in municipal sewage treatment systems negatively impacts the activated sludge system's microbial community and metabolic activity, resulting in a compromised ability to remove pollutants. In this study, the influence of NMOPs on the denitrification phosphorus removal process was comprehensively examined, focusing on the efficiency of pollutant removal, key enzyme activities, microbial community diversity and abundance, and intracellular metabolic profiles. Considering ZnO, TiO2, CeO2, and CuO nanoparticles, ZnO nanoparticles showed the most notable impact on chemical oxygen demand, total phosphorus, and nitrate nitrogen removal, resulting in reductions of over 90% to 6650%, 4913%, and 5711%, respectively. Surfactants, combined with chelating agents, could potentially lessen the toxic impact of NMOPs on the denitrification-driven phosphorus removal process; chelating agents, in comparison, proved more effective for recovery. Under the influence of ZnO NPs, the removal percentages of chemical oxygen demand, total phosphorus, and nitrate nitrogen, respectively, recovered to 8731%, 8879%, and 9035% after the addition of ethylene diamine tetra acetic acid. By examining NMOPs' impacts and stress mechanisms on activated sludge systems, the study provides valuable knowledge and a solution to restore the performance of nutrient removal in denitrifying phosphorus removal systems under NMOP stress conditions.