This work investigated efficacies of commonly used healthcare and personal care disinfectants, including glutaraldehyde, chlorhexidine, ethanol, povidone-iodine, benzalkonium chloride, phenol, free chlorine, hydrogen peroxide (H2O2), and 254 nm UV light, in degrading (as measured by qPCR analyses of ∼1000 bp amplicon loss) and deactivating (as measured by transforming activity loss) bacterial antibiotic resistance genes (ARGs) during inactivation of antibiotic-resistant bacteria (ARB) on inanimate surfaces or in aqueous suspension. Intracellular ARGs (iARGs) blt, mecA, and ampC, within vegetative cells of Bacillus subtilis, Staphylococcus aureus, and Pseudomonas aeruginosa, respectively, were treated on PTFE and/or stainless-steel surfaces or in aqueous phosphate buffer (PB; H2O2 only), to simulate potential healthcare and personal care cleaning applications under representative disinfectant exposure conditions. No chemical disinfectant yielded more than limited (≤1.9log10) iARG degradation/deactivation under the conditions investigated, even when ARB cells were extensively inactivated (at levels from 3.1log10 to ≥6log10). In contrast, UV irradiation yielded up to ∼2.8-3.2log10 iARG degradation/deactivation at corresponding ARB inactivation levels up to ∼4log10 in the case of the blt gene within B. subtilis cells on PTFE surfaces, though levels of iARG degradation/deactivation and ARB inactivation were generally lower than expected based on prior aqueous-phase results, likely due to light-shielding effects at the typical ∼108-109 CFU/mL cell inoculum densities used for surface disinfection tests. During exposure to H2O2 in PB, iARG deactivation and ARB inactivation reached up to 1.7log10 and >3.5log10, respectively, while iARG degradation was minimal (≤0.2log10); this appears to be driven by DNA-strand fragmentation (as observed by pulsed-field gel electrophoresis analysis) likely resulting from reaction with endogenous HO• (or Fe(IV)) generated via intracellular iron-catalyzed H2O2 decomposition. While all investigated disinfectants were able to effectively inactivate ARB cells themselves, these results demonstrate that most are ineffective in simultaneously degrading and deactivating iARGs, highlighting the potential benefits of employing disinfectants such as 254 nm UV light, that selectively target bacterial DNA, to improve mitigation of antibiotic resistance dissemination.

Combinations of UV with oxidants can initiate advanced oxidation processes (AOPs) and enhance bacterial inactivation. However, the effectiveness and mechanisms of UV-AOPs in damaging nucleic acids (e.g., antibiotic resistance genes (ARGs)) and cell integrity represent a knowledge gap. This study comprehensively compared ARG degradation and cell membrane damage under three different UV-AOPs. The extracellular ARG (eARG) removal efficiency followed the order of UV/chlorine > UV/H2O2 > UV/peracetic acid (PAA). Hydroxyl radical (•OH) and reactive chlorine species (RCS) largely contributed to eARG removal, while organic radicals made a minor contribution. For intracellular ARGs (iARGs), UV/H2O2 did not remove better than UV alone due to the scavenging of •OH by cell components, whereas UV/PAA provided a modest synergism, likely due to diffusion of PAA into cells and intracellular •OH generation. Comparatively, UV/chlorine achieved significant synergistic iARG removal, suggesting the critical role of the RCS in resisting cellular scavenging and inactivating ARGs. Additionally, flow cytometry analysis demonstrated that membrane damage was mainly attributed to chlorine oxidation, while the impacts of radicals, H2O2, and PAA were negligible. These results provide mechanistic insights into bacterial inactivation and fate of ARGs during UV-AOPs, and shed light on the suitability of quantitative polymerase chain reaction (qPCR) and flow cytometry in assessing disinfection performance.

The search for robust, reliable biomarkers of schizophrenia remains a high priority in psychiatry. Biomarkers are valuable because they can reveal the underlying mechanisms of symptoms and monitor treatment progress and may predict future risk of developing schizophrenia. Despite the existence of various promising biomarkers that relate to symptoms across the schizophrenia spectrum, and despite published recommendations encouraging multivariate metrics, they are rarely investigated simultaneously within the same individuals. In those with schizophrenia, the magnitude of purported biomarkers is complicated by comorbid diagnoses, medications and other treatments. Here, we argue three points. First, we reiterate the importance of assessing multiple biomarkers simultaneously. Second, we argue that investigating biomarkers in those with schizophrenia-related traits (schizotypy) in the general population can accelerate progress in understanding the mechanisms of schizophrenia. We focus on biomarkers of sensory and working memory in schizophrenia and their smaller effects in individuals with nonclinical schizotypy. Third, we note irregularities across research domains leading to the current situation in which there is a preponderance of data on auditory sensory memory and visual working memory, but markedly less in visual (iconic) memory and auditory working memory, particularly when focusing on schizotypy where data are either scarce or inconsistent. Together, this review highlights opportunities for researchers without access to clinical populations to address gaps in knowledge. We conclude by highlighting the theory that early sensory memory deficits contribute negatively to working memory and vice versa. This presents a mechanistic perspective where biomarkers may interact with one another and impact schizophrenia-related symptoms.

6PPD, a tire rubber antioxidant, poses substantial ecological risks because it can form a highly toxic quinone transformation product (TP), 6PPD-quinone (6PPDQ), during exposure to gas-phase ozone. Important data gaps exist regarding the structures, reaction mechanisms, and environmental occurrence of TPs from 6PPD ozonation. To address these data gaps, gas-phase ozonation of 6PPD was conducted over 24-168 h and ozonation TPs were characterized using high-resolution mass spectrometry. The probable structures were proposed for 23 TPs with 5 subsequently standard-verified. Consistent with prior findings, 6PPDQ (C18H22N2O2) was one of the major TPs in 6PPD ozonation (∼1 to 19% yield). Notably, 6PPDQ was not observed during ozonation of 6QDI (N-(1,3-dimethylbutyl)-N'-phenyl-p-quinonediimine), indicating that 6PPDQ formation does not proceed through 6QDI or associated 6QDI TPs. Other major 6PPD TPs included multiple C18H22N2O and C18H22N2O2 isomers, with presumptive N-oxide, N,N'-dioxide, and orthoquinone structures. Standard-verified TPs were quantified in roadway-impacted environmental samples, with total concentrations of 130 ± 3.2 μg/g in methanol extracts of tire tread wear particles (TWPs), 34 ± 4 μg/g-TWP in aqueous TWP leachates, 2700 ± 1500 ng/L in roadway runoff, and 1900 ± 1200 ng/L in roadway-impacted creeks. These data demonstrate that 6PPD TPs are likely an important and ubiquitous class of contaminants in roadway-impacted environments.

Recently, roadway releases of N,N'-substituted p-phenylenediamine (PPD) antioxidants and their transformation products (TPs) received significant attention due to the highly toxic 6PPD-quinone. However, the occurrence of PPDs and TPs in recycled tire rubber products remains uncharacterized. Here, we analyzed tire wear particles (TWPs), recycled rubber doormats, and turf-field crumb rubbers for seven PPD antioxidants, five PPD-quinones (PPDQs), and five other 6PPD TPs using liquid chromatography-tandem mass spectrometry. PPD antioxidants, PPDQs, and other TPs were present in all samples with chemical profiles dominated by 6PPD, DTPD, DPPD, and their corresponding PPDQs. Interestingly, the individual [PPDQ]/[PPD] and [TP]/[PPD] ratios significantly increased as total concentrations of the PPD-derived chemical decreased, indicating that TPs (including PPDQs) dominated the PPD-derived compounds with increased environmental weathering. Furthermore, we quantified 15 other industrial rubber additives (including bonding agents, vulcanization accelerators, benzotriazole and benzothiazole derivatives, and diphenylamine antioxidants), observing that PPD-derived chemical concentrations were 0.5-6 times higher than these often-studied additives. We also screened various other elastomeric consumer products, consistently detecting PPD-derived compounds in lab stoppers, sneaker soles, and rubber garden hose samples. These data emphasize that PPD antioxidants, PPDQs, and related TPs are important, previously overlooked contaminant classes in tire rubbers and elastomeric consumer products.

We here report chemical characteristics relevant to the fate and transport of the recently discovered environmental toxicant 6PPD-quinone (2-((4-methylpentan-2-yl)amino)-5-(phenylamino)cyclohexa-2,5-diene-1,4-dione or "6PPDQ"). 6PPDQ is a transformation product of the tire rubber antioxidant 6PPD that is ubiquitous in roadway environments, including atmospheric particulate matter, soils, runoff, and receiving waters, after dispersal from tire rubber use and wear on roadways. The aqueous solubility and octanol-water partitioning coefficient (i.e. log KOW) for 6PPDQ were measured to be 38 ± 10 μg L-1 and 4.30 ± 0.02, respectively. Within the context of analytical measurement and laboratory processing, sorption to various laboratory materials was evaluated, indicating that glass was largely inert but loss of 6PPDQ to other materials was common. Aqueous leaching simulations from tire tread wear particles (TWPs) indicated short term release of ∼5.2 μg 6PPDQ per gram TWP over 6 h under flow-through conditions. Aqueous stability tests observed a slight-to-moderate loss of 6PPDQ over 47 days (26 ± 3% loss) for pH 5, 7 and 9. These measured physicochemical properties suggest that 6PPDQ is generally poorly soluble but fairly stable over short time periods in simple aqueous systems. 6PPDQ can also leach readily from TWPs for subsequent environmental transport, posing high potential for adverse effects in local aquatic environments.

Free chlorine disinfection is widely applied to inactivate viruses by reacting with their biomolecules, which include nucleic acids, proteins, and lipids. Knowing the reactivities of viral genomes with free chlorine and the protection that encapsidation provides would ultimately help predict virus susceptibility to the disinfectant. The relative reactivities of different viral genome types and the impact of viral higher order structure with free chlorine are poorly characterized. Here, we studied the reactivity of viral genomes representing four genome types from virus particles with diverse structures, namely, (+)ssRNA (MS2), dsRNA (φ6), ssDNA (φX174), and dsDNA (T3) with free chlorine. We compared the reactivities of these viral nucleic acids when they were suspended in phosphate buffer solutions (naked forms) and when they were in the native virus particles (encapsidated forms). The reactivities of nucleic acids were tracked by polymerase chain reaction (PCR)-based assays. The naked dsDNA of T3 was the least reactive with free chlorine, with an average second order rate constant normalized by the number of bases in the measured regions (in M-1 s-1 b-1) that was 34×, 65×, and 189× lower than those of the dsRNA of φ6, ssRNA of MS2, and ssDNA of φX174, respectively. Moreover, different regions in the ssRNA genome of MS2 and the dsRNA genome of φ6 exhibited statistically different reaction kinetics. The genomes within virus particles reacted slower than the naked genomes overall, but the extent of these differences varied among the four viruses. The results on viral nucleic acid reactivity help explain different susceptibilities of viruses to inactivation by free chlorine and also provide a valuable comparison of the susceptibilities of different nucleic acids to oxidants.

Transformation products (TPs) originating within tire tread wear particles (TWPs) are likely pervasive contaminants of roadway environments although their formation, fate, and risks are poorly characterized. Here, we investigated TP formation occurring during heterogeneous reaction of gas-phase ozone with the common tire rubber antioxidant 6PPD (N-(1,3-dimethylbutyl)-N '-phenyl-p-phenylenediamine); exposures included both pure compound and TWP rubbers. Oxidative transformation occurred during ozonation (similar to 360 ppbv), with up to 81% of 6PPD mass reacting over 6 h. Conversion of 6PPD to 6PPD-quinone (6PPDQ)-a recently reported highly toxic TP-was confirmed at a 9.7% molar yield for pure 6PPD and a 0.95% molar yield for 6PPD present within TWPs, representing likely minima over these time scales and conditions. Leveraging high-resolution mass spectrometry, we identified 19 probable 6PPD-derived TPs in both ozonated 6PPD and TWP samples, underscoring formation of diverse TPs from this antioxidant. By screening environmental samples, nine 6PPD-derived TPs were detected within roadway runoff. The data confirm that when tire rubber antioxidants react with ozone, as intended, they form and release various TPs to surrounding environments.

Breakpoint chlorination, an important chemical process relevant to chlorine-based advanced oxidation processes for potable reuse and to traditional water treatment, was investigated for its oxidative capacity, generation of reactive species, and potential impacts on organic contaminant degradation. This work describes a newly recognized HO• radical generation pathway during breakpoint chlorination that may play an important role in water treatment and examines the behavior of the HO• radical and other related reactive species and their potential formation pathways. Experimental data showed that the removal of 1,4-dioxane (1,4-D) positively correlated with chlorine-to-ammonia molar ratio until a molar ratio of ~1.5–2.0 was reached, above which removal efficiency rapidly decreased. Peroxynitrite (ONOO–) and peroxynitrous acid (ONOOH) are proposed as important radical sources that lead to the formation of HO• in the breakpoint process. This is supported by application of tert-butanol as a selective HO• scavenger and the observation that the amendment of reaction solutions with carbonate species suppressed oxidative capacity to a much greater extent than expected based solely on scavenging of HO• by H2CO3 * /CO2 and HCO3– (apparently due to selective scavenging of ONOOH/ONOO– by dissolved CO2). These experiments also provided evidence that reactive species other than HO• contributed to 1,4-D oxidation. The results of this study suggest that breakpoint chlorination can lead to significant degradation of organic contaminants via ONOOH/ONOO–-mediated formation of HO• and other reactive species and may potentially be optimized for enhanced removal of recalcitrant organic contaminants in the context of water reuse, though with due caution to the potential for enhancement of nitrogenous and other disinfection byproduct formation under such conditions.

This study investigated antibiotic resistance gene (ARG) degradation kinetics in wastewaters during bench- and full-scale treatment with UV light and chlorine─with the latter maintained as free available chlorine (FAC) in low-ammonia wastewater and converted into monochloramine (NH2Cl) in high-ammonia wastewater. Twenty-three 142-1509 bp segments (i.e., amplicons) of seven ARGs (blt, mecA, vanA, tet(A), ampC, blaNDM, blaKPC) and the 16S rRNA gene from antibiotic resistant bacteria (ARB) strains Bacillus subtilis, Staphylococcus aureus, Enterococcus faecium, Escherichia coli, Pseudomonas aeruginosa, and Klebsiella pneumoniae were monitored as disinfection targets by qPCR. Rate constants for ARG and 16S rRNA gene amplicon degradation by UV, FAC, and NH2Cl were measured in phosphate buffer and used to expand and validate several recently developed approaches to predict DNA segment degradation rate constants based solely on their nucleotide contents, which were then applied to model ARG degradation during bench-scale treatment in buffer and wastewater matrixes. Kinetics of extracellular and intracellular ARG degradation by UV and FAC were well predicted up to ∼1-2-log10 elimination, although with decreasing accuracy at higher levels for intracellular genes, while NH2Cl yielded minimal degradation under all conditions (agreeing with predictions). ARB inactivation kinetics varied substantially across strains, with intracellular gene degradation lagging cell inactivation in each case. ARG degradation levels observed during full-scale disinfection at two wastewater treatment facilities were consistent with bench-scale measurements and predictions, where UV provided ∼1-log10 ARG degradation, and chlorination of high-ammonia wastewater (dominated by NH2Cl) yielded minimal ARG degradation.

Degradation kinetics of antibiotic resistance genes (ARGs) by free available chlorine (FAC), ozone (O3), and UV254 light (UV) were investigated in phosphate buffered solutions at pH 7 using a chromosomal ARG (mecA) of methicillin-resistant Staphylococcus aureus (MRSA). For FAC, the degradation rates of extracellular mecA (extra-mecA) were accelerated with increasing FAC exposure, which could be explained by a two-step FAC reaction model. The degradation of extra-mecA by O3 followed second-order reaction kinetics. The degradation of extra-mecA by UV exhibited tailing kinetics, which could be described by a newly proposed kinetic model considering cyclobutane pyrimidine dimer (CPD) formation, its photoreversal, and irreversible (6-4) photoproduct formation. Measured rate constants for extra-mecA increased linearly with amplicon length for FAC and O3, or with number of intrastrand pyrimidine doublets for UV, which enabled prediction of degradation rate constants of extra-mecA amplicons based on sequence length and/or composition. In comparison to those of extra-mecA, the observed degradation rates of intracellular mecA (intra-mecA) were faster for FAC and O3 at low oxidant exposures but significantly slower at high exposures for FAC and UV. Differences in observed extra- and intracellular kinetics could be due to decreased DNA recovery efficiency and/or the presence of MRSA aggregates protected from disinfectants.

The reaction of hypochlorous acid (HOCl) with superoxide radical (O-2(center dot-)) - a source of hydroxyl radical (HO center dot) and various reactive chlorine species (RCS) - was investigated as the basis for a novel nonphotochemical advanced oxidation process (AOP). Moderately stable (t(1/2) similar to minutes) aqueous O(2)(center dot- )stocks were prepared by several approaches at pH>12 and either (a) added directly to aqueous free available chlorine (FAC; i.e., HOCl/OCl-) at circumneutral pH, or (b) premixed with alkaline FAC and then acidified to pH 7, to degrade various organic probe compounds via in situ generated HO and RCS. Radical production was optimal at [HO2 center dot/O-2 center dot(-)](0)/[FAC](0 )similar to 2 with similar to 0.8 mol HO formed/mol FAC consumed, and HO and RCS exposures reaching similar to 5x10(-19) and similar to 10(-9) Mx s, respectively. Similar trends were observed in natural waters and organic matter-amended phosphate buffer containing up to 5 mgC/L of dissolved organic carbon. Direct formation of oxyhalides, trihalomethanes (THMs), and haloacetic acids (HAAs), was minimal, though THM and HAA formation was moderately enhanced during post-chlorination of O-2(center dot-) /FAC-treated solutions. This process could provide a beneficial addition to the range of available AOPs due to its high radical exposures, simplicity, rapid time-scales, potential for on-site O-2(center dot-) generation, and widespread accessibility of FAC and other reagents. (C) 2021 Elsevier Ltd. All rights reserved.

Direct numerical simulations (DNS) of the evaporation of interface-resolved n-heptane fuel droplets in forced homogeneous isotropic turbulence (HIT) are performed at 10 bar and 348 K. A parametric study is conducted in which the ratio of initial droplet diameter to Kolmogorov lengthscale and the liquid volume fraction are varied in the ranges 0 < d(0)/eta <= 17 and 10(-4) <= alpha(l) <= 10(-2), respectively. The DNS results are validated against experimental data for an isolated droplet evaporating in HIT. Our results show that increasing the liquid volume fraction of droplets decreases the evaporation rate and causes the evaporation rate to deviate from the classical d(2)-law. Evaporation models based on the Frossling correlation are tested in an a priori study using the DNS results. It is shown that, in general, the Frossling correlation is inaccurate when predicting the droplet Sherwood number in turbulent conditions. Modeling aspects of the Spalding number in the context of multiple interacting droplets are discussed. (C) 2021 Elsevier Ltd. All rights reserved.

Tire tread particles turn streams toxic For coho salmon in the U.S. Pacific Northwest, returning to spawn in urban and suburban streams can be deadly. Regular acute mortality events are tied, in particular, to stormwater runoff, but the identity of the causative toxicant(s) has not been known. Starting from leachate from new and aged tire tread wear particles, Tian et al. followed toxic fractions through chromatography steps, eventually isolating a single molecule that could induce acute toxicity at threshold concentrations of ∼1 microgram per liter. The compound, called 6PPD-quinone, is an oxidation product of an additive intended to prevent damage to tire rubber from ozone. Measurements from road runoff and immediate receiving waters show concentrations of 6PPD-quinone high enough to account for the acute toxicity events. Science , this issue p. 185

This work investigated degradation (measured by qPCR) and biological deactivation (measured by culture-based natural transformation) of extra- and intracellular antibiotic resistance genes (eARGs and iARGs) by free available chlorine (FAC), NH2Cl, O3, ClO2, and UV light (254 nm), and of eARGs by •OH, using a chromosomal ARG ( blt) of multidrug-resistant Bacillus subtilis 1A189. Rate constants for degradation of four 266-1017 bp amplicons adjacent to or encompassing the acfA mutation enabling blt overexpression increased in proportion to #AT+GC bps/amplicon, or in proportion to #5'-GG-3' or 5'-TT-3' doublets/amplicon, with respective values ranging from 0.59 to 2.3 (×1011 M-1 s-1) for •OH, 1.8-6.9 (×104 M-1 s-1) for O3, 3.9-9.2 (×103 M-1 s-1) for FAC, 0.35-1.2(×101 M-1 s-1) for ClO2, and 2.0-8.8 (×10-2 cm2/mJ) for UV at pH 7, and from 1.7-4.4 M-1 s-1 for NH2Cl at pH 8. For FAC, NH2Cl, O3, ClO2, and UV, ARG deactivation paralleled degradation of amplicons approximating a ∼800-1000 bp acfA-flanking sequence required for natural transformation in B. subtilis, whereas deactivation outpaced degradation for •OH. At practical disinfectant exposures, eARGs and iARGs were ≥90% degraded/deactivated by FAC, O3, and UV, but recalcitrant to NH2Cl and ClO2. iARG degradation/ deactivation always lagged cell inactivation. These findings provide a quantitative framework for evaluating ARG fate during disinfection/oxidation, and support using qPCR as a proxy for tracking ARG deactivation under carefully selected circumstances.

A simple and rapidmethod employing non-suppressed ion chromatographywith electrospray ionization tandem mass spectrometry has been developed for the direct determination of trace-level haloacetic acids (HAAs) in water samples. Using 70/30 (v/v) acetonitrile/1 M aqueous methylamine as the mobile phase, three IC columns - AS16, AS18 and AS24 from Thermo-Scientific - were tested, respectively, with the AS16 column exhibiting the best overall performancewith respect to resolution and retention time. To assess the effects ofmobile phase composition on retention time of HAAs, the AS16 column was further tested using (i) different proportions of acetonitrile to aqueous methylamine, (ii) different proportions of acetonitrile to aqueous solution at fixed methylamine concentrations, and (iii) different concentrations of methylamine at fixed proportions of acetonitrile to aqueous solution. With a low proportion of aqueous solution, van der Waals and/or hydrogen-bonding interactions appeared to play an important role in governing HAA retention, i.e., HAAs with relatively higher apparent logK(ow)* caused by elevated solvents (s)(s)pK(a) exhibited longer retention times; whereaswith a high proportion of aqueous solution, ionic interactions appeared to dominate retention of HAAs, with the more polarizable HAAs exhibiting longer retention times. Using 70/30 (v/v) acetonitrile/1 M aqueous methylamine, the method detection limitswere in the range of 0.090-0.216 mu g/L for the 11 selected chloro-, bromo- and iodoacetic acids. Finally, this method was applied to monitor HAAs yields in laboratory chlorination experiments and to determine concentrations of HAAs in tap water and wastewater effluent samples. (C) 2020 Published by Elsevier B.V.

Ensemble perception utilizes our visual system's natural abilities to extract summary statistics from sets of similar objects. Our perceptual system can accurately detect the mean of these ensembles. However, previous research has shown that our visual system is biased to overestimate variability. This bias to overestimate variability was stronger when the objects were more similar to each other. This prior research concerned variability of line orientations. We extended this work to explore whether this overestimation bias is a general phenomenon and therefore applies to other visual features as well. Using the method of adjustment, participants made judgments about the variability of line orientation, size, and hue in sets of ensembles (lines and circles). Participants viewed 9 target circles of various sizes presented one-at-a-time, then adjusted the sizes of five comparison circles presented simultaneously to match the variability in the target display. A similar task was used to assess how participants estimated variability in line orientation and hue. Participants overestimated variability, and this was true for all 3 features. Moreover, participants overestimated variability to a greater extent when there was less variability in the display for circle size (95% overestimation), line orientation (51% overestimation), and hue (155% overestimation) compared to high levels of variability (-11%, -10%, -3%, respectively). Understanding how we perceive variability in ensembles is essential when making judgments about critical information in medical images. For instance, how distributed calcifications are within a mammogram informs whether a radiologist diagnoses a patient with cancer. Further research will attempt to elucidate the mechanisms of ensemble perceptual and test the robustness of the bias to overestimate variability.

This study investigated the degradation and deactivation of an extracellular ampicillin resistance gene (ampR) encoded in plasmid pUC19 during exposure to UV254, •OH (generated by UV>290/H2O2), and combined exposure to UV254 and •OH (and/or SO4•-) using UV254/H2O2 and UV254/S2O82-. The degradation rates of ampR measured by quantitative polymerase chain reaction increased with increasing target amplicon length (192-851 bps). The rate constants for the degradation of pUC19 (2686 bps) were calculated as 0.26 cm2/mJ for UV254 and 1.5 × 1011 M-1s-1 for •OH, based on the degradation rates of ampR amplicons and assuming an equal sensitivity of DNA damage across the entire plasmid. DNA repair-proficient Escherichia coli (E. coli) AB1157 strain (wild-type) and its repair-deficient mutants including AB1886 (uvrA-), AB2463 (recA-), AB2480 (uvrA-, recA-), and DH5α (recA-, endA-) were applied as recipient cells in gene transformation assays. Results suggested that the elimination efficiency of transforming activity during UV254 and •OH exposure was dependent on the type of DNA repair genes in recipient E. coli strains. Losses of transforming activity were slower than the degradation of pUC19 by a factor of up to ∼5 (for E. coli DH5α), highlighting the importance of DNA repair in recipient cells. The degradation rates of ampR amplicons were much larger (by a factor of ∼4) in UV254/H2O2 and UV254/S2O82- than UV254 direct photolysis, indicating the significant contribution of •OH and SO4•- to the gene degradation. Not only UV254 and SO4•-, but also •OH contributed to the degradation of ampR during UV254/S2O82-, which was attributed to the conversion of SO4•- to •OH and a 10-fold larger reactivity of •OH towards ampR as compared to SO4•-. However, the enhanced gene degradation by radicals did not lead to a faster elimination of gene transforming activity during UV254/H2O2 and UV254/S2O82-, suggesting that UV254- and radical-induced DNA damage were not additive in their contributions to losses of gene transforming activity. Wastewater effluent organic matter (EfOM) accelerated the degradation of ampR during UV254 irradiation by means of reactive species production through indirect photolysis reactions, whereas EfOM mainly acted as a radical scavenger during UV254/H2O2 and UV254/S2O82- treatments.

Since the seminal work of Yarbus, multiple studies have demonstrated the influence of task-set on oculomotor behavior and the current cognitive state. In more recent years, this field of research has expanded by evaluating the costs of abruptly switching between such different tasks. At the same time, the field of classifying oculomotor behavior has been moving toward more advanced, data-driven methods of decoding data. For the current study, we used a large dataset compiled over multiple experiments and implemented separate state-of-the-art machine learning methods for decoding both cognitive state and task-switching. We found that, by extracting a wide range of oculomotor features, we were able to implement robust classifier models for decoding both cognitive state and task-switching. Our decoding performance highlights the feasibility of this approach, even invariant of image statistics. Additionally, we present a feature ranking for both models, indicating the relative magnitude of different oculomotor features for both classifiers. These rankings indicate a separate set of important predictors for decoding each task, respectively. Finally, we discuss the implications of the current approach related to interpreting the decoding results.

Green and healthy building certification systems increasingly motivate stakeholder decision making and serve as influential guides for sustainable design and construction. These codes promote water-use efficiency through measures such as low-flow features and rainwater reuse. Health-oriented guidelines like WELL particularly emphasize water quality. However, reduced flow and increased water age can produce a variety of negative water quality outcomes, posing occupant health risks including increased opportunistic pathogen growth in premise plumbing systems. Notably, there is little research on the influence of green and healthy building guidelines on resulting water quality and safety. This preliminary literature review summarizes current academic knowledge of water quality and microbial concerns in low-flow systems and the present and potential roles of green and healthy building codes and certification programs in effecting in-building water quality outcomes. Based on this review, notable research, industry, and policy gaps and key points for further research are identified. Priority topics for future investigations should include appropriate risk-evaluation methodologies; the impacts of specific technical and management interventions, such as the relationship of water heater temperature and microbial growth risk; and advancing exploration of the mitigation avenues which could be advantageously promoted through green and healthy building codes.