Fibrous Structures: An Overview of Their Responsiveness to External Stimuli towards Intended Application.

In recent decades, the interest in responsive fibrous structures has surged, propelling them into diverse applications: from wearable textiles that adapt to their surroundings, to filtration membranes dynamically altering selectivity, these structures showcase remarkable versatility. Various stimuli, including temperature, light, pH, electricity, and chemical compounds, can serve as triggers to unleash physical or chemical changes in response. Processing methodologies such as weaving or knitting using responsive yarns, electrospinning, as well as coating procedures, enable the integration of responsive materials into fibrous structures. They can respond to these stimuli, and comprise shape memory materials, temperature-responsive polymers, chromic materials, phase change materials, photothermal materials, among others. The resulting effects can manifest in a variety of ways, from pore adjustments and altered permeability to shape changing, color changing, and thermal regulation. This review aims to explore the realm of fibrous structures, delving into their responsiveness to external stimuli, with a focus on temperature, light, and pH.

Oxidation of small aromatic compounds in rainwater by UV/H2O2: Optimization by response surface methodology.

The presence of aromatic compounds in rainwater is a matter of concern, mainly when the use of rainwater in buildings is intended. The present work aimed to assess the oxidation of a mixture of small aromatic compounds (benzoic, 3,5-dihydroxybenzoic and syringic acids) in rainwater by the UV/H2O2 process, and the possibility of its optimization by the response surface methodology. The extent of oxidation was assessed by ultraviolet-visible and molecular fluorescence spectroscopies. During the oxidation of the mixture new chromophoric compounds were formed at an initial stage, but they were then degraded at a later stage. The increase of the H2O2 concentration, resulted in a higher extent of oxidation, while the initial pH value showed no influence in the oxidation of the mixture. The optimization of the oxidation was performed using the uniform design with the factors: initial H2O2 concentration, initial pH, and reaction time. The response surface model found, through the best subsets regression, described the extent of oxidation as function of the following variables: initial H2O2 concentration and reaction time, interaction between them, and also their respective quadratic forms. The optimal conditions, the lowest H2O2 concentration (3.1 mM) for a selected maximum reaction time (4 h), were applied to rainwater samples spiked with the mixture of contaminants and resulted in an extent of oxidation higher than 99.5%, validating the application of the model to real samples. Therefore, the UV/H2O2 process coupled to its optimization via response surface methodology may be an alternative for rainwater treatment in buildings.

White bean (Phaseolus vulgaris L.) as a sorbent for the removal of zinc from rainwater.

The present work aimed to assess the sorption capacity of the common white bean (Phaseolus vulgaris L.) to remove Zn(II) from rainwater, rendering it suitable for use in buildings, and the efficiency of the process was evaluated for two initial Zn(II) concentrations, representing high (100 µg L-1) and very high (500 µg L-1) levels of Zn(II) in rainwater. The effects of the amount of beans (1, 5 and 10 beans per 50 mL), as well as the initial pH values of the zinc solution [acid (4), neutral (5.6) and basic (7) for atmospheric waters] were also assessed. The removal of Zn from water was affected by the change in pH values. When 5 and 10 beans were used, after 4 h and 2 h of contact time, respectively, the accumulated Zn(II) on the beans was released back into the solution, and this release occurred first for the highest tested pH value. The sorption rate of Zn(II) from the solution increased with the increasing amount of beans, but for 5 and 10 beans this only took place up to 4 h and 2 h, respectively. Furthermore, the removal percentages of Zn(II) increased with the increase of the initial concentrations of the metal in water. Kinetic studies revealed that a pseudo-first-order model provided the best fitting for the experimentally obtained values. Fourier transform infrared spectroscopy coupled with attenuated total reflectance (FTIR-ATR) analyses of the bean shells and cores indicated that contact with a Zn(II) solution did not cause notable alterations to the chemical structures of these bean components. Scanning electron microscopy (SEM) and energy dispersive X-ray spectroscopy (EDX) analyses suggested that the process of sorption occurred at the surface of the beans (shells). The results obtained in this study also suggest that the matrix of rainwater samples did not interfere with the removal of metal, and that the process of the removal of Zn(II) by the white beans can be applied to real samples. On the whole, results indicate that for the removal of Zn(II) from rainwater, 1 bean up to 6 h, or 5 and 10 beans up to 2 h can be used per 50 mL for the removal of up to 60% of Zn(II) present in water, thus constituting a viable solution for the effective reduction of this metal in rainwater.