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[Display omitted] • An enrichment method of glycoproteins using microfluidic paper-based analytical devices (μPADs) was developed. • The μPADs consist of two separate parts: the enrichment part (Chip I) and the detection part (Chip II). • The 3-aminophenylboronic acid immobilized on Chip I can capture glycoproteins at pH 8.0 and release them at pH 3.0. • The method can effectively enrich an ovalbumin solution with concentrations as low as 1.0 × 10−11 mol/L. • Glycoproteins was enriched from 1 × 106-fold diluted real egg white samples. We introduce a facile method for glycoprotein enrichment, separation, and detection using microfluidic paper-based analytical devices (μPADs). The μPADs comprise two distinct components: the enrichment region (Chip I) and the detection section (Chip II). The reusable Chip I is fabricated by immobilizing 3-aminophenylboronic acid (APBA) onto a circular paper substrate, demonstrating exceptional glycoprotein affinity. In disposable Chip II, glycoproteins react with periodic acid, generating carbonyl compounds that produce a purple-colored product upon reacting with the Schiff reagent. Alterations in color intensity are captured using an ordinary cell phone and are subsequently analyzed using Photoshop software. Observations note a linear increase in average color intensities from 1.0 × 10−3 to 5.0 × 10−3 mol/L, with an R2 value of 0.9927. The relative standard deviations (RSDs) of inter-day (n = 5) and intra-day (n = 5) assessments stand at 1.5 % and 1.4 %, respectively. Our proposed approach can effectively enrich an ovalbumin (OVA) solution with concentrations as low as 1.0 × 10−11 mol/L, resulting in enrichment rates of 107 to 108 times. The interference deviations of five substances relative to OVA lie within the range of − 2.0 % to + 2.0 %. The methodology successfully enriches glycoproteins from egg white samples diluted by a factor of 1 × 106, demonstrating that the proposed method is remarkably suitable for enriching glycoproteins from authentic samples. [ABSTRACT FROM AUTHOR]

Developing portable and sensitive biosensors for bacteria detection is highly demanded due to their association with environmental and food safety. Paper-based microfluidic chip is the suitable candidate for constructing pump-free biosensor since paper is hydrophilic, low-cost and easy to use. However, the contradiction between sensitivity and small sample volume seriously affects the application of paper-based chip for bacteria detection. Here, a new microfluidic biosensor, combining large PDMS reservoir for sample storage, hydrophilic paper substrate for pump-free water transport, coated microspheres for bacteria capture and super absorbent resin for water absorption, is designed for the detection of bacteria in aqueous samples. Once the sample solution is introduced in the reservoir, water will automatically flow through the gaps between microspheres and the target bacteria will be captured by the aptamer coated on the surface. To facilitate PDMS reservoir bonding and ensure water transport, the upper side of paper substrate is coated with Polyethylenimine modified PDMS and the bottom side is kept unchanged. After all the solution is filtrated, fluorescent dye strained bacteria are enriched on the microspheres. The fluorescent intensity representing the number of bacteria captured is then measured using a portable instrument. Through the designed microfluidic biosensor, the bacteria detection can be achieved with 2 mL sample solution in less than 15 min for water or 20 min for diluted milk. A linear range from 10 CFU/mL to 1000 CFU/mL is obtained. The paper-based 3D biosensor has the merits of low-cost, simple operation, pump-free and high sensitivity and it can be applied to the simultaneous detection of multiple bacteria via integrating different aptamers. [Display omitted] • A microfluidic chip is constructed for detecting bacteria with LOD of 10 CFU/mL. • A funnel-like PDMS reservoir is integrated for large sample solution storage. • Partially permeable paper and super absorbent resin are for self-pumping. • The target bacteria can be captured and enriched by coated microparticles. [ABSTRACT FROM AUTHOR]

Simple Summary: The B cell receptor (BCR) is a membrane-bound protein complex that is required for the normal development of B cells. BCR signalling is also involved in the pathogenesis of B cell cancers. While there is substantial literature on genomic analyses of the BCR, there are limited proteomic studies of receptor structure and its interactions with neighbouring proteins. This is partly due to the location of the BCR in the surface-membrane lipid environment that has limited the ability to enrich the complex for proteomic analysis. Here, we report an enrichment technique that can be used for mass spectrometry analyses of the BCR from live B cells. B cells are central to the adaptive immune response and provide long-lasting immunity after infection. B cell activation is mediated by the surface membrane-bound B cell receptor (BCR) following recognition of a specific antigen. The BCR has been challenging to analyse using mass spectrometry (MS) due to the difficulty of isolating and enriching this membrane-bound protein complex. There are approximately 120,000 BCRs on the B cell surface; however, depending on the B cell activation state, there may be hundreds-of-millions to billions of proteins in a B cell. Consequently, advanced proteomic techniques such as MS workflows that use purified proteins to yield structural and protein-interaction information have not been published for the BCR complex. This paper describes a method for enriching the BCR complex that is MS-compatible. The method involves a Protein G pull down on agarose beads using an intermediary antibody to each of the BCR complex subcomponents (CD79a, CD79b, and membrane immunoglobulin). The enrichment process is shown to pull down the entire BCR complex and has the advantage of being readily compatible with further proteomic study including MS analysis. Using intermediary antibodies has the potential to enrich all isotypes of the BCR, unlike previous methods described in the literature that use protein G-coated beads to directly pull down the membrane IgG (mIgG) but cannot be used for other mIg isotypes. [ABSTRACT FROM AUTHOR]

Simple Summary: Contemporary best practices for working with exhibit animals in zoological facilities incorporate behavioral research, theories on operant learning, animal welfare principles, and practical experience to provide animals with largely positive experiences when interacting with their caretakers and their environment. These best practices must be more fully implemented to increase ambassador animal welfare based on taxonomic and individual animal characteristics, experience with present and past caretakers, and ambassador program objectives. This implementation requires training staff to modify animal behavior using the most positive and least intrusive interactions possible. We rigorously consider how to apply best practices to meet ambassador program objectives and animal welfare needs by ensuring appropriate institutional support, the selection of the most suitable animals for the program's objectives, and the creation of an environment where animals recognize that they can choose whether to interact with humans and participate in programs, as well as exert control over their environment. Our synthesis provides a framework showing how staff can continually assess and address the behavioral response of ambassador animals to their environment—along with their interactions with humans during and outside of program usage—with the goal of meeting our most current and evolved criteria for ensuring high animal welfare. There is an ethical need to document and develop best practices for meeting ambassador animals' welfare needs within the context of meeting zoo and aquarium program objectives. This is because ambassador animals experience direct and frequent contact with humans. This paper rigorously synthesizes behavioral research and theory, contemporary practices, and personal experiences to offer key concepts that can be applied to meet ambassador animal welfare needs. These key concepts include addressing an animal's recognition of choice and control, the use of the most positive and least intrusive effective interventions when training animals to participate in programming, and an overall reduction in aversive strategy use. Our model for increasing ambassador animal welfare focuses on seven main areas of concern, including the following: choosing the most suitable animal for the program; choosing the human with the right skills and knowledge for the program; using the most positive, least intrusive, effective training methods; developing a strong trusting relationship between trainer and animal; developing a comprehensive enrichment program; the need for institutional support; and creating opportunities for animals to practice species-appropriate behaviors. Our model will provide guidelines for improved ambassador animal welfare that can be refined with future research. [ABSTRACT FROM AUTHOR]

Rare earth elements (REEs) have attracted much attention because of their unique physical and chemical properties. The root system is the plant organ most directly in contact with REEs, and it is critical to understand the mechanisms of interaction between the two. This paper investigates the effects of REEs on plant enrichment and fractionation, as well as on various developmental and toxicity indices of the root system. REEs are more likely to be deposited on the root surface under the influence of root secretion. The complexation between the two affects the uptake and fractionation of REEs and the altered pattern of root secretion. The toxicity mechanisms of REEs on plant root cells were lied in: (1) REEs generate reactive oxygen species after entering the plant, leading to oxidative stress and damage to plant cells; (2) REEs with higher charge-to-volume ratios compete for organic ligands with or displace Ca2+, further disrupting the normal function of plant root cells. It was shown that the sensitivity of inter-root microorganisms to REEs varied depending on the content and physicochemical properties of REEs. The paper also concluded with a meta-analysis of phytotoxicity induced by REEs, which showed that REEs affect plant physiological parameters. REEs, as a source of oxidative stress, triggered lipid peroxidation damage in plants and enhanced the activity of antioxidant enzymes, thus revealing the significant toxicity of REEs to plants. The phytotoxic effects of REEs increased with time and concentration. These results help to elucidate the ecotoxicology of rare earth-induced phytotoxicity. [Display omitted] • REEs mainly accumulate in roots with LREEs easily moving into above-ground plants. • Stimulated by REEs, the composition and exudation of root secretions can be altered. • REEs affect root cell function by displacing Ca2+ and inducing ROS. • Interactions between root secretions, microbes, and REEs influence plant growth. • Meta-Analysis reveals the diverse mechanisms of REEs-induced phytotoxicity. [ABSTRACT FROM AUTHOR]

Interactions of microplastics (MPs) biofilm with antibiotic resistance genes (ARGs) and antibiotics in aquatic environments have made microplastic biofilm an issue of keen scholarly interest. The process of biofilm formation and the degree of ARGs enrichment in the presence of antibiotic-selective pressure and the impact on the microbial community need to be further investigated. In this paper, the selective pressure of ciprofloxacin (CIP) and illumination conditions were investigated to affect the physicochemical properties, biomass, and extracellular polymer secretion of polyvinyl chloride (PVC) microplastic biofilm. In addition, relative copy numbers of nine ARGs were analyzed by real-time quantitative polymerase chain reaction (qPCR). In the presence of CIP, microorganisms in the water and microplastic biofilm were more inclined to carry associated ARGs (2–3 times higher), which had a contributing effect on ARGs enrichment. The process of pre-microplastic biofilm formation might have an inhibitory effect on ARGs (total relative abundance up to 0.151) transfer and proliferation compared to the surrounding water (total relative abundance up to 0.488). However, in the presence of CIP stress, microplastic biofilm maintained the abundance of ARGs (from 0.151 to 0.149) better compared to the surrounding water (from 0.488 to 0.386). Therefore, microplastic biofilm act as abundance buffer island of ARGs stabilizing the concentration of ARGs. In addition, high-throughput analyses showed the presence of antibiotic-resistant (Pseudomonas) and pathogenic (Vibrio) microorganisms in biofilm under different conditions. The above research deepens our understanding of ARGs enrichment in biofilm and provides important insights into the ecological risks of interactions between ARGs, antibiotics, and microplastic biofilm. [Display omitted] • Characteristics of PVC biofilm formation by different conditions were summarized. • Selective pressure of CIP had enrichment effect on ARGs in water and biofilm. • PVC biofilm created conditions for selective pressure to generate ARGs. • Biofilm maintained the abundance of ARGs better than the surrounding water. • Characterization of bacterial community composition in PVC biofilm was studied. [ABSTRACT FROM AUTHOR]

Generalized/extended finite element methods (GFEM/XFEM) for an interface problem are generally enriched by a distance function to the interface to handle discontinuities across the interface. Evaluations of the distance function and its gradients are needed for assembling stiffness matrices, which requires certain computational geometry algorithms. The computational complexity grows if the number of integration points is increased. Besides, the mathematical analysis on the effect of numerical integration has not been established in the field of GFEM/XFEM yet. This study designs an improved enriched function for a stable GFEM (SGFEM, a stable version of GFEM) based on the distance function, which only requires evaluating the distance function at nodes of elements that interact the interface (the gradients of distance function are not needed). The optimal convergence order (in the energy norm) of the SGFEM with such an improved enriched function is proven. In turn, we propose a perturbed variational formula, which can be integrated exactly by simple Gaussian rules designed in this paper. We prove that the SGFEM based on the improved enriched function and the perturbed variational formula (exactly integrated by the numerical integration) achieves the optimal convergence order for the interface problem. Namely, we develop a numerical integration rule for the SGFEM such that the optimal convergence order of SGFEM is maintained for the interface problem. The theoretical achievements are verified by numerical experiments. [ABSTRACT FROM AUTHOR]