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10 pages, 798 KiB  
Article
The Determination of the Rapid and Effective Activity of an Air Sanitizer against Aerosolized Bacteria Using a Room-Sized Aerobiology Chamber
by Bahram Zargar, M. Khalid Ijaz, Anthony Kevek, Mark Miller, Julie McKinney and Syed A. Sattar
Microorganisms 2024, 12(10), 2072; https://doi.org/10.3390/microorganisms12102072 - 16 Oct 2024
Viewed by 700
Abstract
Air sanitization is an important non-pharmaceutical intervention for mitigating the risk of indoor pathogen spreading. A dipropylene glycol-containing air sanitizer was tested against aerosolized Staphylococcus aureus and Klebsiella pneumoniae. The bacteria, suspended in a soil load, were aerosolized using a six-jet Collison [...] Read more.
Air sanitization is an important non-pharmaceutical intervention for mitigating the risk of indoor pathogen spreading. A dipropylene glycol-containing air sanitizer was tested against aerosolized Staphylococcus aureus and Klebsiella pneumoniae. The bacteria, suspended in a soil load, were aerosolized using a six-jet Collison nebulizer with pressurized air. The 25-m3 (~900 ft3) aerobiology chamber was maintained at 22 ± 2 °C and 50 ± 5% relative humidity per the U.S. Environmental Protection Agency’s 2012 Guidelines on air sanitizers. An initial 2-min air sample was collected from the chamber using a slit-to-agar sampler containing 150-mm Petri plates, with Trypticase soy agar (TSA) containing neutralizers to quench the microbicidal activity of the air sanitizer, to determine the initial bacterial challenge in the air. The air sanitizer was sprayed into the chamber from pressurized cans. Additional air samples were collected from the chamber over 10 min to detect surviving bacteria. The TSA plates were then incubated aerobically at 36 ± 1 °C for 90 ± 4 h and scored for bacterial colony-forming units. A 30-s spray of the air sanitizer reduced infectious S. aureus and K. pneumoniae titers by 3.0 log10 (99.9%) in 3.2 ± 0.3 min and 1.2 ± 0.0 min, respectively. Based on these findings, the EPA granted registration of the air sanitizer as the first product of its kind for indoor air sanitization. Full article
(This article belongs to the Special Issue Disinfection and Sterilization of Microorganisms (2nd Edition))
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Figure 1
<p>Decay curve of dipropylene glycol (DPG) in the chamber air following a 30-s spray of the air sanitizer. Values shown are the means ± standard deviations for <span class="html-italic">n</span> = 3 determinations per time point, with each point on the graph representing the efficacy outcome from an independent test run for that spray duration (i.e., 5 s, 10 s, 15 s, 20 s, 25 s, and 30 s). *, Significantly different from time 0 min value, <span class="html-italic">p</span> &lt; 0.05; **, significantly different from time 5 min value, <span class="html-italic">p</span> &lt; 0.05 (two-tailed <span class="html-italic">t</span>-test assuming equal variances).</p>
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<p>Dose response for the bactericidal efficacy of varying durations of spraying the air sanitizer against <span class="html-italic">S. aureus</span>. Values indicate the determined log<sub>10</sub> reductions in <span class="html-italic">Staphylococcus aureus</span> (<span class="html-italic">S. aureus</span>) titer in the aerobiology chamber air samples collected 10 min following the indicated spray durations (<span class="html-italic">n</span> = 1 per spray duration).</p>
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<p>Bacterial concentration in the air of the aerobiology chamber following aerosolization from suspending medium containing the soil load in the absence of the air sanitizer. Three independent runs were performed. A plot of the average results from the three runs for each type of bacteria (black symbols, <span class="html-italic">Klebsiella pneumoniae</span>; red symbols, <span class="html-italic">Staphylococcus aureus</span>) is included, along with the standard deviations. The associated linear regression lines for the control average plots are shown in the figure, and the equations are <span class="html-italic">y</span> = −0.0201<span class="html-italic">x</span> + 4.3910 (R<sup>2</sup> = 0.9917) and <span class="html-italic">y</span> = −0.0053<span class="html-italic">x</span> + 4.4327 (R<sup>2</sup> = 0.9774) for <span class="html-italic">K. pneumoniae</span> and <span class="html-italic">S. aureus</span>, respectively.</p>
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<p>Time kinetics for the bactericidal activity of the air sanitizer against aerosolized <span class="html-italic">Klebsiella pneumoniae</span> suspended in a medium containing a soil load in a room-sized aerobiology chamber. The black symbols indicate mean ± standard deviation (<span class="html-italic">n</span> = 3 independent runs) for the stability of aerosolized <span class="html-italic">K. pneumoniae</span> in the absence of the air sanitizer. The red symbols represent the bacterial concentration vs. time during efficacy testing of three sanitizer batches (mean ± standard deviation for <span class="html-italic">n</span> = 9 independent runs). The blue arrow shows the time associated with a 3-log<sub>10</sub> reduction in viable concentration, accounting for the decay of the bacteria in the absence of the air sanitizer. The black dotted line displays the linear regression line fitting the <span class="html-italic">K. pneumoniae</span> concentration in the absence of the air sanitizer. The red dotted line shows the linear regression line fitting the <span class="html-italic">K. pneumoniae</span> concentration in the presence of the air sanitizer.</p>
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<p>Time kinetics for bactericidal activity of the air sanitizer against aerosolized <span class="html-italic">Staphylococcus aureus</span> suspended in a medium containing a soil load in a room-sized aerobiology chamber. The black symbols indicate mean ± standard deviation (<span class="html-italic">n</span> = 3 independent runs) for the stability of aerosolized <span class="html-italic">S. aureus</span> in the absence of the air sanitizer. The red symbols represent the bacterial concentration vs. time during efficacy testing of the three sanitizer batches (mean ± standard deviation for <span class="html-italic">n</span> = 9 independent runs). The blue arrow shows the time associated with a 3-log<sub>10</sub> reduction in viable concentration, accounting for the decay of the bacteria in the absence of the air sanitizer. The black dotted line displays the linear regression line fit to the <span class="html-italic">S. aureus</span> concentration in the absence of the air sanitizer. The red dotted line shows the linear regression line fitting the <span class="html-italic">S. aureus</span> concentration in the presence of the air sanitizer.</p>
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15 pages, 956 KiB  
Article
Healthiness and Safety of Smart Environments through Edge Intelligence and Internet of Things Technologies
by Rafiq Ul Islam, Pasquale Mazzei and Claudio Savaglio
Future Internet 2024, 16(10), 373; https://doi.org/10.3390/fi16100373 - 14 Oct 2024
Viewed by 726
Abstract
Smart environments exploit rising technologies like Internet of Things (IoT) and edge intelligence (EI) to achieve unseen effectiveness and efficiency in every tasks, including air sanitization. The latter represents a key preventative measure–made even more evident by the COVID-19 pandemic–to significantly reduce disease [...] Read more.
Smart environments exploit rising technologies like Internet of Things (IoT) and edge intelligence (EI) to achieve unseen effectiveness and efficiency in every tasks, including air sanitization. The latter represents a key preventative measure–made even more evident by the COVID-19 pandemic–to significantly reduce disease transmission and create healthier and safer indoor spaces, for the sake of its occupants. Therefore, in this paper, we present an IoT-based system aimed at the continuous monitoring of the air quality and, through EI techniques, at the proactively activation of ozone lamps, while ensuring safety in sanitization. Indeed, these devices ensure extreme effectiveness in killing viruses and bacteria but, due to ozone toxicity, they must be properly controlled with advanced technologies for preventing occupants from dangerous exposition as well as for ensuring system reliability, operational efficiency, and regulatory compliance. Full article
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<p>System architecture.</p>
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<p>UV-C lamp effectiveness vs. lifetime (hours) [<a href="#B27-futureinternet-16-00373" class="html-bibr">27</a>].</p>
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<p>The ozonizer machine CRJ O3-UV-500.</p>
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<p>The Node-Red flow.</p>
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<p>Snapshot of the PostgreSQL database for collecting the sensors’ data.</p>
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11 pages, 2077 KiB  
Article
A Copper-Based Coating for the Control of Airborne Viable Bacteria in a Prison Environment
by Sebastián Fuentes-Alburquenque, Walter Cañón-Mancisidor, Álvaro Toledo, Alejandro Mendoza, Patricia Soto-Rioseco and Katherine Delgado
Coatings 2024, 14(10), 1281; https://doi.org/10.3390/coatings14101281 - 8 Oct 2024
Viewed by 644
Abstract
Infections in confined environments can spread by direct contact, contaminated surfaces, and airborne transmission. This is critical in prison facilities, where cleaning and sanitary conditions are inadequate. An alternative is the development of antimicrobial surfaces. A new antimicrobial coating was developed by incorporating [...] Read more.
Infections in confined environments can spread by direct contact, contaminated surfaces, and airborne transmission. This is critical in prison facilities, where cleaning and sanitary conditions are inadequate. An alternative is the development of antimicrobial surfaces. A new antimicrobial coating was developed by incorporating copper microparticles into a standard commercial paint, aiming to reduce the concentration of bacteria on surfaces by granting antimicrobial properties to surfaces. The copper additive comprised Cu2Cl(OH)3 deposited on polyhedral zeolite. The efficacy of this coating was evaluated in detention cells in a police station, which are temporary prisons and inherently dirty environments. The experiment compared a cell painted with the copper additive coating and a control cell with the standard paint. Viable coliforms were measured on different surfaces and in the air for five months under normal usage. Bacterial load was reduced by ca. 68% by the copper-amended paint on cement surfaces. Surprisingly, airborne viable coliforms were reduced by ca. 87% in the detention cell treated with the copper coating. This research highlights the potential of antimicrobial coatings in controlling the spread of infections through contact with contaminated surfaces and emphasizes the significant reduction in airborne bacterial load. It is especially relevant for controlling infections where sanitization is limited but can be extended to other built environments, such as healthcare facilities. Full article
(This article belongs to the Special Issue Women’s Special Issue Series: Coatings)
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Figure 1
<p>Schematic diagram of the study. The synthesis and chemical characterization of CuAd were followed by its incorporation into standard paint used in detention cells. The study design included two detention cells: one with the CuAd paint and the other with the control paint. The sample type and location are depicted in red. S: seat; F: floor; W: wall; B: steel bars; A: air. Each cell was 2.8 × 2.8 × 2.6 m (20.4 m<sup>3</sup>).</p>
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<p>SEM micrography of copper incorporated on polyhedral zeolite microparticles of size 2 to 3 µm.</p>
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<p>PXRD of copper incorporated on zeolite, showing the presence of Cu<sub>2</sub>Cl(OH)<sub>3</sub>.</p>
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<p>Total viable coliform load on surfaces and in the air of the detention cells. The coating with CuAd shows a lower coliform load compared to the coating without CuAd. Boxplot for a 5-month period (20 weeks). Samples included air, steel bars, floor, seat, and wall.</p>
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25 pages, 18967 KiB  
Article
Good People Do Not Eat Others?! Moral Ambiguity in Japanese Fairytales from the Late Nineteenth Century
by Tian Gao
Humanities 2024, 13(5), 127; https://doi.org/10.3390/h13050127 - 1 Oct 2024
Viewed by 704
Abstract
In 2015, the Japanese public broadcaster NHK aired an educational series that re-examined traditional fairy tales by putting their characters on trial for their immoral behavior, such as revenge, violence, and dishonesty. These tales, rooted in premodern Japanese folklore, were widely available in [...] Read more.
In 2015, the Japanese public broadcaster NHK aired an educational series that re-examined traditional fairy tales by putting their characters on trial for their immoral behavior, such as revenge, violence, and dishonesty. These tales, rooted in premodern Japanese folklore, were widely available in various book formats by the late nineteenth century and, unlike modern adaptations, they did not sanitize violence or evil. This study analyzes four miniature picture books from the late nineteenth century that recount the story, Kachikachi yama (The Crackling Mountain). This analysis focuses on both verbal and visual representations of good and evil, with attention to themes of loyalty, filial piety, and virtuous revenge. The findings reveal that these picture books presented young readers with complex moral lessons, where the boundaries between good and evil were blurred. Additionally, they illuminate the prevailing image of children during that era, depicting them as “little adults” expected to be educated and prepared for the practical realities of the adult world. Full article
(This article belongs to the Special Issue Depiction of Good and Evil in Fairytales)
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<p>The opening scene of <span class="html-italic">Kachikachi yama</span> 1993, 4.</p>
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<p>The rabbit is in the role of the accused. <span class="html-italic">Kachikachi yama</span> in <span class="html-italic">The Fairytale Court</span>.</p>
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<p><span class="html-italic">Snake and ladders: on old folk tales in red-cover format</span> (<span class="html-italic">Mukashi banashi akahon sugoroku</span> 昔咄赤本壽語禄), published by Izumiya Ichibei 和泉屋市兵衛, 1860. Retrieved from <span class="html-italic">Bakumatsu Meiji mamehon shūsei</span> 幕末明治豆本集成, edited by Katō Yasuko, 378, 2004. <span class="html-italic">Kachikachi yama</span> highlighted in red.</p>
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<p><span class="html-italic">New edition of children’s play</span> (<span class="html-italic">Shinban kodomo asobi</span> 新板子どもあそび), created by Kobayashi Ikuhide 小林幾英, published by Akiyama Bu-emon 秋山武右衛門, 1884. <span class="html-italic">Kachikachi yama</span> highlighted in blue.</p>
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<p>The rabbit comes up with the plan of using spicy miso and determines it will kill the <span class="html-italic">tanuki</span>, Late-Edo 2.</p>
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<p>The beginning of an early modern <span class="html-italic">Kachikachi yama</span> work. The text highlighted in blue indicates that “here, we can see the rabbit’s strong loyalty” (此ところうさぎのちうぎつよきところをゑかくなり). <span class="html-italic">Kachikachi yama</span>, Edo 1, 1v.</p>
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<p>The rabbit is portrayed as a samurai carrying a sword (highlighted in red and blue) in most of the scenes in <span class="html-italic">Kachikachi yama</span>, Edo 2, 1v. 4v-5r.</p>
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<p>Left: the rabbit is portrayed as a samurai carrying a sword (highlighted in green) in <span class="html-italic">Kachikachi yama</span> 1881. 5v. Right: the rabbit is portrayed as a samurai carrying a sword (highlighted in green) in <span class="html-italic">Kachikachi yama</span> 1886. 6v.</p>
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<p>The <span class="html-italic">tanuki</span> (7v-8r) is killed in the same manner as he killed the old woman (<a href="#humanities-13-00127-f010" class="html-fig">Figure 10</a>, 1v-2r), Late-Edo 1.</p>
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<p>The <span class="html-italic">tanuki</span> (<a href="#humanities-13-00127-f009" class="html-fig">Figure 9</a>, 7v-8r) is killed in the same manner as he killed the old woman (1v-2r), Late-Edo 1.</p>
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<p>The rabbit beats the <span class="html-italic">tanuki</span> with the oar, Late-Edo 2, 7v-8r.</p>
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<p>The <span class="html-italic">tanuki</span> (1v-2r) is killed in the same manner as he killed the old woman (<a href="#humanities-13-00127-f013" class="html-fig">Figure 13</a>, 6v-7r), Meiji 1.</p>
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<p>The <span class="html-italic">tanuki</span> (<a href="#humanities-13-00127-f012" class="html-fig">Figure 12</a>, 1v-2r) is killed in the same manner as he killed the old woman (6v-7r), Meiji 1.</p>
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<p>The rabbit beats the <span class="html-italic">tanuki</span> with the oar, Meiji 2, 4v-5r.</p>
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<p>The <span class="html-italic">tanuki</span> is tied up (highlighted in red), Late-Edo 2, 1v-2r.</p>
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<p>The <span class="html-italic">tanuki</span> rips out the flesh around the old woman’s jaw (highlighted in red), Late-Edo 2, 2v-3r.</p>
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<p>The <span class="html-italic">tanuki</span> is using its testicles to smother the old lady, Meiji 2, 1v.</p>
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<p><span class="html-italic">Namazu hyōtan kindama</span> 鯰瓢箪金玉, created by Utagawa Kuniyoshi 歌川国芳, 1843–44. Museum of Fine Arts Boston (Asia, Prints and Drawing 11.36714), Boston.</p>
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<p><span class="html-italic">Tanuki no geki sumidagawa hanami</span> 狸の戯角田川花見, created by Kawanabe Kyōsai 河鍋暁斎, 1864. Osaka art museum 大阪市立美術館, Osaka.</p>
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<p>“The latest <span class="html-italic">tanuki</span> entertainments” (志ん板狸あそび <span class="html-italic">Shinpan tanuki asobi</span>), created by Kobayashi Eijirō 小林英次郎, published by Higuchi Ginjiro 樋口銀太郎, 1884. Cotsen Children’s Library Princeton University Library (Special Collections 45036), Princeton.</p>
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<p>Ebisu who suppresses a catfish (鯰をおさえる恵比寿 <span class="html-italic">Namazu o osaeru ebisu</span>) from the picture album <span class="html-italic">Ansei ōjishin-e</span> 安政大地震絵. National Diet Library Digital Collection 国立国会図書館デジタルコレクション, Tokyo.</p>
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<p>The old man reaching out for the “<span class="html-italic">tanuki</span> soup”, Meiji 1, 2r-3v.</p>
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<p>The old man is “innocently” enjoying his wife’s flesh with great relish (<b>right</b>) and the old man checks the bones under the veranda (<b>left top</b>). Meiji 2, 2v-1r.</p>
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<p>The old man is weeping bitterly and the rabbit is aflame with indignation, surrounded by empty bowls and plates (highlighted in blue), Late-Edo 1, 2v-3r.</p>
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<p>The old man is weeping bitterly and the rabbit is aflame with indignation, Late-Edo 2, 3v-4r. Empty bowls and plates are highlighted in blue.</p>
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<p>The <span class="html-italic">tanuki</span>’s back is engulfed in flames, Late-Edo 1, 4v-5r.</p>
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<p>The <span class="html-italic">tanuki</span>’s back is engulfed in flames, Meiji 1, 5v-4r.</p>
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<p>The <span class="html-italic">tanuki</span>’s back is engulfed in flames, Meiji 2, 3v-2r.</p>
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<p>The twofold revenge in <span class="html-italic">mamehon</span> versions <span class="html-italic">Kachikachi yama</span>.</p>
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<p>The acts of revenge in the contemporary <span class="html-italic">Kachikachi yama</span> story.</p>
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17 pages, 7993 KiB  
Article
Design and Analysis of Small Fallen Leaf Collection, Crushing, and Recycling Vehicle
by Xiaowen Zhang, Haibin Liu, Chang Liu, Zhengyu Zhao, Wenchao Han, Lvfa Yin and Anfu Guo
Processes 2024, 12(9), 2011; https://doi.org/10.3390/pr12092011 - 19 Sep 2024
Viewed by 585
Abstract
Leaf recycling, a crucial component of urban environmental protection, aims to systematically collect and reuse fallen leaves on streets. At present, fallen leaves are usually cleaned manually by sanitation workers, and environmental protection departments then use special cars to transport fallen leaves to [...] Read more.
Leaf recycling, a crucial component of urban environmental protection, aims to systematically collect and reuse fallen leaves on streets. At present, fallen leaves are usually cleaned manually by sanitation workers, and environmental protection departments then use special cars to transport fallen leaves to treatment stations for incineration. This not only requires a significant amount of labor and material resources but also causes air pollution and wastes fallen leaves. In this study, a collecting, crushing, and recycling vehicle was designed to solve this problem. The proposed device significantly improves the efficiency of collecting fallen leaves and facilitates their secondary utilization. The design process is described in detail, including the working design of the entire device, static analysis, and transmission system design. The entire vehicle model was 3D printed to verify that the initial design concept satisfies the assembly and production requirements of the device. Full article
(This article belongs to the Section Advanced Digital and Other Processes)
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Figure 1
<p>Overall structure of small fallen leaf collection, crushing, and recycling vehicle. 1. Telescopic hob wheel; 2. Telescopic side brush; 3. Electromechanical coupling system; 4. Collection of fallen leaves for crushing and recycling institutions.</p>
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<p>Structure diagram of telescopic hob wheel based on iris structure. 1. Pinion; 2. Gear ring; 3. Hob; 4. Inner hub of iris; 5. Motor pinion; 6. NEMA+17 stepper motor.</p>
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<p>Wheel structure diagram of retractable hob controlled by gear transmission based on iris structure: (<b>a</b>) diagram of wheel model on uneven road surface and (<b>b</b>) diagram of wheel model on smooth road.</p>
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<p>Cloud maps of wheel stress, strain, and displacement: (<b>a</b>) displacement of the wheel, (<b>b</b>) strain of the wheel, and (<b>c</b>) stress of the wheel.</p>
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<p>Structure diagram of retractable brush: (<b>a</b>) side view and (<b>b</b>) front view. 1. Chassis; 2, 5, 16, 20. Hydraulic cylinder; 3, 18. Hydraulic rotation shaft; 4, 19. Motor; 6, 10, 13, 15. Long connecting rod; 7, 11, 17. Short connecting rod with brush; 8, 12, 26, 27. Roller brush; 9, 14, 25. Short connecting rod; 11. Brush short connecting rod; 16. Hydraulic cylinder; 21–24. Current solenoid.</p>
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<p>Cloud maps of retractable collection brush stress, strain, and displacement: (<b>a</b>) displacement of the retractable collection brush, (<b>b</b>) strain of the retractable collection brush, and (<b>c</b>) stress of the retractable collection brush.</p>
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<p>Structure diagram of litter collection, crushing, and recycling device. 1. Shell; 2. Upper motor; 3. Absorption fan blade; 4. Blower fan blade; 5. Right motor; 6. Transfer fan blade; 7. Shunt fan; 8. Reamer; 9. Support frame; 10. Leaf suction mouth; 11. Blowing outlet.</p>
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<p>Cloud map of reamer stress, strain, and displacement: (<b>a</b>) displacement of the reamer, (<b>b</b>) strain of the reamer, and (<b>c</b>) stress of the reamer.</p>
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<p>Structure diagram of power coupling device. 1. First drive shaft; 2. Second drive shaft; 3. First motor; 4. Second motor; 5. Third motor; 6. Differential; 7. Planetary gear mechanism; 8. Sun gear; 9. Planetary rack; 10. Tooth ring; 11. Planetary gear; 12. Third drive shaft; 13. Clutch III; 14. Clutch VI; 15. Clutch I; 16. Clutch IV; 21. Sun wheel transmission components; 22. Planetary frame transmission components; 23. Gear ring transmission components; 24. First brake; 25. Second brake; 26. Third brake; 21-4. Clutch VII; 22-3. Clutch V; 23-4. Clutch II; 17 (18, 19, 20, 21-1, 21-2, 21-3, 22-1, 22-2, 23-1, 23-2, 23-3). Transmission gear.</p>
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<p>Model slice state diagram: (<b>a</b>) front of car, (<b>b</b>) rear of car, (<b>c</b>) rear of pulverizer, (<b>d</b>) front of pulverizer, (<b>e</b>) retractable collection brush, and (<b>f</b>) wheel.</p>
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<p>Photographs of printer status: (<b>a</b>) three-dimensional printer, (<b>b</b>) printing process.</p>
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<p>The 3D-printed parts.</p>
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<p>Integral 3D-printed model.</p>
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11 pages, 238 KiB  
Review
Is Pollution the Primary Driver of Infectious Syndemics?
by Merrill Singer
Pathogens 2024, 13(5), 370; https://doi.org/10.3390/pathogens13050370 - 30 Apr 2024
Cited by 2 | Viewed by 1411
Abstract
Syndemics, the adverse interaction of two or more coterminous diseases or other negative health conditions, have probably existed since human settlement, plant and animal domestication, urbanization, and the growth of social inequality beginning about 10–12,000 years ago. These dramatic changes in human social [...] Read more.
Syndemics, the adverse interaction of two or more coterminous diseases or other negative health conditions, have probably existed since human settlement, plant and animal domestication, urbanization, and the growth of social inequality beginning about 10–12,000 years ago. These dramatic changes in human social evolution significantly increased opportunities for the spread of zoonotic infectious diseases in denser human communities with increased sanitation challenges. In light of a growing body of research that indicates that anthropogenic air pollution causes numerous threats to health and is taking a far greater toll on human life and wellbeing than had been reported, this paper proposes the possibility that air pollution is now the primary driver of infectious disease syndemics. In support of this assertion, this paper reviews the growth and health impacts of air pollution, the relationship of air pollution to the development and spread of infectious diseases, and reported cases of air pollution-driven infectious disease syndemics, and presents public health recommendations for leveraging the biosocial insight of syndemic theory in responding to infectious disease. Full article
15 pages, 757 KiB  
Article
Ultraviolet-C Light and Peracetic Acid Extend the Shelf Life of Fresh and Frozen Strawberries
by Iolanda Nicolau-Lapeña, Jordi Ortiz, Inmaculada Viñas, Maribel Abadias, Gloria Bobo and Ingrid Aguiló-Aguayo
Horticulturae 2024, 10(5), 452; https://doi.org/10.3390/horticulturae10050452 - 29 Apr 2024
Viewed by 1117
Abstract
The postharvest life of strawberries is short, and disinfection processes for fresh-cut and frozen strawberries are needed to address the risk posed by foodborne pathogens in this kind of product. For this, a process involving immersion in a 40 mg L−1 peracetic [...] Read more.
The postharvest life of strawberries is short, and disinfection processes for fresh-cut and frozen strawberries are needed to address the risk posed by foodborne pathogens in this kind of product. For this, a process involving immersion in a 40 mg L−1 peracetic acid (PA) solution accompanied by the use of an emerging technology, ultraviolet-C for 2 min, was studied for its impact on strawberry quality and microbial load as a novel alternative method to chlorine sanitation. The shelf life of the washed strawberries was evaluated in fresh (whole or fresh-cut) product for 11 days at 4 °C and in product that had been frozen for 12 months at –20 °C (air or modified atmosphere, 20% CO2, 5% O2, and 75% N2). After washing, total aerobic mesophylls, yeast, and mold decreased by 0.5–1.0 log units and these counts remained low during storage. The fresh and fresh-cut fruits’ firmness (2.3 ± 0.5 N at day 11) and lightness (expressed by L*, averaging 31.0 ± 0.1) were maintained. Although antioxidant activity, expressed by the amount of radical 2,2-diphenyl-1-picrylhydrazyl (DPPH), decreased during storage in fresh-cut samples, total ferric reducing antioxidant power (FRAP), total phenolic content, and total anthocyanin content were maintained in all the formats during storage (averaging 1.33 ± 0.04 g kg−1 ascorbic acid equivalents, 0.212 ± 0.01 g kg−1 gallic acid equivalents, and 0.03 ± 0.01 g kg−1 pelargonidine-3-glucoside). An increase in red color (from 32.1 to 39.3 a* values) and a loss of firmness of up to 46.8% was observed after the first month of frozen storage with no changes in the nutritional quality. Considering the sanitizing effect of water UV-C with peracetic acid (WUVPA) and the results obtained in the present study, the addition of this process in the production chain of strawberries could be an effective method to maintain the shelf life of the fruits, especially for fresh-cut strawberries. Full article
(This article belongs to the Section Fruit Production Systems)
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<p>Freezing parameters and curves of strawberry samples during supercooling in a freezing cabinet functioning with liquid nitrogen (N<sub>2</sub>), using the Mini Batch CM-85/1090 model from the brand Metal Carbide.</p>
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<p>Color, expressed as L*a*b* coordinates, in fresh and whole (<b>A</b>) or fresh and fresh-cut strawberries (<b>B</b>), after control (black lines) or WUVPA treatment (grey lines). (<b>C</b>) Color, expressed as L*a*b* coordinates, in frozen strawberries (−25 °C), with modified gas composition (black lines) or air composition (grey lines). Values are the mean of three repetitions ± standard deviation. Different letters show statistically significant differences (<span class="html-italic">p</span> &lt; 0.05) among storage time (4 °C) within the same treatment (Tukey’s HSD test), and asterisks show statistically significant differences (<span class="html-italic">p</span> &lt; 0.05) between treatments on the same day.</p>
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15 pages, 1300 KiB  
Article
Eco-Friendly Sanitization of Indoor Environments: Effectiveness of Thyme Essential Oil in Controlling Bioaerosol Levels and Disinfecting Surfaces
by Daniela Sateriale, Giuseppina Forgione, Giuseppa Anna De Cristofaro, Leonardo Continisio, Chiara Pagliuca, Roberta Colicchio, Paola Salvatore, Marina Paolucci and Caterina Pagliarulo
BioTech 2024, 13(2), 12; https://doi.org/10.3390/biotech13020012 - 26 Apr 2024
Viewed by 1989
Abstract
Bioaerosols and pathogens in indoor workplaces and residential environments are the primary culprits of several infections. Techniques for sanitizing air and surfaces typically involve the use of UV rays or chemical sanitizers, which may release chemical residues harmful to human health. Essential oils, [...] Read more.
Bioaerosols and pathogens in indoor workplaces and residential environments are the primary culprits of several infections. Techniques for sanitizing air and surfaces typically involve the use of UV rays or chemical sanitizers, which may release chemical residues harmful to human health. Essential oils, natural substances derived from plants, which exhibit broad antimicrobial properties, could be a viable alternative for air and surface sanitation. The objective of this study has been to investigate the efficacy of thyme essential oil (TEO) in environmental sanitation processes. In Vitro assays through agar well diffusion, disk volatilization and tube dilution methods revealed significant antimicrobial activity of TEO 100% against foodborne and environmental isolates, with both bacteriostatic/fungistatic and bactericidal/fungicidal effects. Therefore, aqueous solutions of TEO 2.5% and 5% were formulated for air sanitation through nebulization and surface disinfection via direct contact. Bioaerosol samples and surface swabs were analyzed before and after sanitation, demonstrating the efficacy of aqueous solutions of TEO in reducing mesophilic and psychrophilic bacteria and environmental fungi levels in both air and on surfaces. The obtained results prove the antimicrobial potential of aqueous solutions of TEO in improving indoor air quality and surface cleanliness, suggesting thyme essential oil as an effective and safe natural sanitizer with minimal environmental impact compared to dangerous chemical disinfectants. Full article
(This article belongs to the Section Environmental Biotechnology)
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<p>Graphic representation, not to scale, of the indoor environment utilized in the experimental sanitization procedures; asterisks indicate the bioaerosol sampling sites.</p>
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<p>Total microbial levels in indoor bioaerosols before (control) and after sanitization with TEO 2.5% and 5% and H<sub>2</sub>O<sub>2</sub> 0.5%. The number of colonies for plates is expressed as the mean ± standard deviation of a triplicate assay conducted at three sampling points. TEO, thyme essential oil; H<sub>2</sub>O<sub>2</sub>, hydrogen peroxide. Statistical significance was examined by the two-way ANOVA test with Tukey’s correction (<span class="html-italic">p</span> &lt; 0.05) for comparisons with the control. For mesophilic bacteria, asterisks indicate the statistical significance with respect to the positive control (**** <span class="html-italic">p</span> &lt; 0.0001); for psychrophilic bacteria, hashtags indicate the statistical significance compared to the control (<sup>####</sup> <span class="html-italic">p</span> &lt; 0.0001); the absence of symbols indicates the absence of significance. Letters (a–c) indicate the statistical differences between different values; results with no significant differences receive the same letter.</p>
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<p>Microbial levels on stainless-steel (<b>a</b>) and monolithic stoneware (<b>b</b>) surfaces, before (control) and after sanitization with TEO 2.5% and 5% and sodium NaClO 3%. The mean values ± standard deviation, obtained from triplicate analyses, are expressed as colony-forming units (CFU) per 1 square centimeter of sampled surface. Statistical significance was examined by the two-way ANOVA test with Dunnett correction (<span class="html-italic">p</span> &lt; 0.05) for comparisons with each control. Asterisks indicate the statistical significance with respect to the positive control (**** <span class="html-italic">p</span> &lt; 0.0001; *** <span class="html-italic">p</span> &lt; 0.001; ** <span class="html-italic">p</span> &lt; 0.01); the absence of asterisks indicates the absence of significance. Letters (a,b) indicate the statistical differences between different values; results with no significant differences receive the same letter.</p>
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20 pages, 2702 KiB  
Review
Microfiber Fragment Pollution: Sources, Toxicity, Strategies, and Technologies for Remediation
by James McCay and Sunidhi Mehta
Sustainability 2024, 16(7), 3077; https://doi.org/10.3390/su16073077 - 8 Apr 2024
Cited by 3 | Viewed by 2580
Abstract
With the pervasive consumption (currently >65% of total market shares and steadily increasing) of petroleum-derived synthetic textiles, the escalating concern of microfiber fragment (MF) pollution has emerged as a formidable menace to our ecological equilibrium. Over the lifetime (pre- and post-consumption) of these [...] Read more.
With the pervasive consumption (currently >65% of total market shares and steadily increasing) of petroleum-derived synthetic textiles, the escalating concern of microfiber fragment (MF) pollution has emerged as a formidable menace to our ecological equilibrium. Over the lifetime (pre- and post-consumption) of these textiles, they shed tiny fibers recognized as MFs. These MFs are carriers of persistent organic pollutants and have been linked to cytotoxicity, oxidative stress, and genotoxicity, even at minimal exposures via air and water sources. Grounded in the state-of-the-art literature, this review discusses the primary and secondary sources of MF release, their fate, transport, environmental impacts, and novel technologies for MF pollutant remediation. Our results infer that MF pollution is a multifactorial issue with serious environmental and public health implications, as studies reported their presence in human blood, feces, and urine samples. We recommend a multifaceted approach to increase sanitation coverage, ensuring adequate wastewater treatment prior to environmental discharge for MF pollution mitigation. Additionally, transformation is warranted for consumers’ use, care, and purchase behavior of textile products. Government regulation of fast fashion (a major user of synthetic textiles), exemplified by recent French legislation, is essential to preventing microfiber pollution. We urge similar policy-making efforts globally to safeguard public health. Full article
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<p>The market shares and chemical structures of the most popular synthetic polymers used in the textile industry. The source for statistical figures is the latest annual report published by Textile Exchange [<a href="#B6-sustainability-16-03077" class="html-bibr">6</a>]. Accumulation [<a href="#B5-sustainability-16-03077" class="html-bibr">5</a>]. PET textiles alone are responsible for 35% of the total MP in aquatic ecosystems [<a href="#B7-sustainability-16-03077" class="html-bibr">7</a>], with the remaining 65% attributed to other sources of MP such as personal-care-product packaging, fishing and aquaculture, agriculture, road transport, plastic manufacturing, and tourism industries [<a href="#B7-sustainability-16-03077" class="html-bibr">7</a>].</p>
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<p>Increasing trend in overall global fiber production rates in Mt (million tons) from 1975 to 2022 with estimated projection through 2030. The inner pie chart shows the overall market share of each of the main fiber categories [<a href="#B6-sustainability-16-03077" class="html-bibr">6</a>].</p>
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<p>Key factors impacting MF shedding during the laundering process. The factors are presented in the order of impact, with the highest impact factor being closest to the figure core and the lowest impact factor being the farthest [<a href="#B31-sustainability-16-03077" class="html-bibr">31</a>,<a href="#B39-sustainability-16-03077" class="html-bibr">39</a>,<a href="#B40-sustainability-16-03077" class="html-bibr">40</a>,<a href="#B42-sustainability-16-03077" class="html-bibr">42</a>,<a href="#B43-sustainability-16-03077" class="html-bibr">43</a>,<a href="#B45-sustainability-16-03077" class="html-bibr">45</a>,<a href="#B50-sustainability-16-03077" class="html-bibr">50</a>,<a href="#B51-sustainability-16-03077" class="html-bibr">51</a>,<a href="#B52-sustainability-16-03077" class="html-bibr">52</a>,<a href="#B53-sustainability-16-03077" class="html-bibr">53</a>,<a href="#B54-sustainability-16-03077" class="html-bibr">54</a>,<a href="#B55-sustainability-16-03077" class="html-bibr">55</a>,<a href="#B56-sustainability-16-03077" class="html-bibr">56</a>].</p>
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<p>Annual MF influent from home laundering and post-treatment effluent released in the environment in Northern America [<a href="#B47-sustainability-16-03077" class="html-bibr">47</a>] (images are copied from pixabay.com under CC0 license).</p>
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<p>Sources and existence of MF emissions within the environment, their exposure pathways to humans, and the health impacts stemming from the prolonged exposure [<a href="#B86-sustainability-16-03077" class="html-bibr">86</a>,<a href="#B87-sustainability-16-03077" class="html-bibr">87</a>] (individual images are copied from pixabay.com under CC0 license).</p>
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<p>Essential pre- and post-consumer strategies to mitigate MF emissions into the environment and thereby minimize their impact.</p>
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14 pages, 3735 KiB  
Article
Transfer and Inactivation of Listeria monocytogenes during Pilot-Scale Dicing and Flume Washing of Onions
by Andrew M. Scollon, Haiqiang Wang and Elliot T. Ryser
Appl. Microbiol. 2024, 4(1), 439-452; https://doi.org/10.3390/applmicrobiol4010030 - 27 Feb 2024
Viewed by 1070
Abstract
This study assessed the extent of L. monocytogenes transfer from onions to the surface of a commercial dicer, from inoculated onions to uninoculated onions, and the efficacy of various sanitizers during the subsequent flume washing of diced onions. Spanish yellow onions (Allium [...] Read more.
This study assessed the extent of L. monocytogenes transfer from onions to the surface of a commercial dicer, from inoculated onions to uninoculated onions, and the efficacy of various sanitizers during the subsequent flume washing of diced onions. Spanish yellow onions (Allium cepa L.) were dip-inoculated in a 3-strain avirulent L. monocytogenes cocktail (5.9 or 4.2 log CFU/50 g) and air-dried. After dicing one 2.2 kg batch of onions inoculated at ~5.9 log CFU/50 g followed by ten uninoculated batches of 2.2 kg each, L. monocytogenes progressively decreased from 4.6 to 2.6 log CFU/50 g in baches 1 through 10, respectively. After onions inoculated at ~4.0 log CFU/g were diced and flume washed for 2 min in tap water, electrolyzed water containing 55 ppm free chlorine, 80 ppm free chlorine from a commercial sanitizer, or 80 ppm peroxyacetic acid and dewatered on a mechanical shaker table, L. monocytogenes populations decreased 0.4, 0.3, 1.4, and 1.0 log, respectively, with populations of ~1.2 log CFU/mL in water for all three sanitizers. These findings should be useful in future risk assessments and aid in the development of improved industry guidelines to better enhance the safety of diced onions. Full article
(This article belongs to the Special Issue Applied Microbiology of Foods, 2nd Edition)
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<p>(<b>A</b>) Commercial dicer. (<b>B</b>) Commercial dicer sampling locations: slicer blade (1), paddles (2, 3), and drum (4, 5). (<b>C</b>) Commercial dicer sampling locations: rolling dicer blades (6) and cross-cut blades (7). (<b>D</b>) Commercial dicer sampling location: chute (8).</p>
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<p>(<b>A</b>) Commercial dicer. (<b>B</b>) Commercial dicer sampling locations: slicer blade (1), paddles (2, 3), and drum (4, 5). (<b>C</b>) Commercial dicer sampling locations: rolling dicer blades (6) and cross-cut blades (7). (<b>D</b>) Commercial dicer sampling location: chute (8).</p>
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<p>Processing equipment: (<b>A</b>) 3.6 m flume tank and (<b>B</b>) dewatering shaker table.</p>
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<p>Processing equipment: (<b>A</b>) 3.6 m flume tank and (<b>B</b>) dewatering shaker table.</p>
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<p><span class="html-italic">L. monocytogenes</span> transfer from inoculated onions (5.9 or 4.2 log CFU/50 g) to different dicer components. Values were compared between components at the same inoculation level. Bars with different letters are significantly different.</p>
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<p><span class="html-italic">Listeria</span> populations remaining on the different dicer surfaces after dicing one inoculated (4.2 log CFU/50 g) followed by 10 uninoculated batches of onions. Populations were compared across the different components after dicing with A denoting no significant difference.</p>
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<p><span class="html-italic">Listeria</span> populations remaining on the different dicer surfaces after dicing one inoculated (5.9 log CFU/50 g) followed by 10 uninoculated batches of onions. After dicing bars with different letters are significantly different.</p>
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<p>(<b>A</b>). Predicted <span class="html-italic">L. monocytogenes</span> transfer from one batch of inoculated onions batch (4.2 log CFU/50 g) to 10 batches of uninoculated onions. ypred is the prediction line; yobs is the observed line; CB is the confidence band for the prediction line. (<b>B</b>). Predicted <span class="html-italic">L. monocytogenes</span> transfer from one batch of inoculated onions batch (5.9 log CFU/50 g) to 10 batches of uninoculated onions. ypred is the prediction line; yobs is the observed line; CB is the confidence band for the prediction line.</p>
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<p>(<b>A</b>). Predicted <span class="html-italic">L. monocytogenes</span> transfer from one batch of inoculated onions batch (4.2 log CFU/50 g) to 10 batches of uninoculated onions. ypred is the prediction line; yobs is the observed line; CB is the confidence band for the prediction line. (<b>B</b>). Predicted <span class="html-italic">L. monocytogenes</span> transfer from one batch of inoculated onions batch (5.9 log CFU/50 g) to 10 batches of uninoculated onions. ypred is the prediction line; yobs is the observed line; CB is the confidence band for the prediction line.</p>
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<p>(<b>A</b>). <span class="html-italic">Listeria</span> populations on diced onions during washing and shaker table dewatering. * Denotes significant difference between treatment and water control. (<b>B</b>). <span class="html-italic">Listeria</span> populations in water during washing and shaker table dewatering of diced onion.</p>
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14 pages, 3621 KiB  
Article
Reducing Storage Losses of Organic Apples by Plasma Processed Air (PPA)
by Robert Wagner, Thomas Weihe, Hauke Winter, Christoph Weit, Jörg Ehlbeck and Uta Schnabel
Appl. Sci. 2023, 13(23), 12654; https://doi.org/10.3390/app132312654 - 24 Nov 2023
Cited by 1 | Viewed by 1074
Abstract
The consumer demand for organic food including apples is increasing worldwide. Despite favorable environmental and health benefits, organic farming bears also disadvantages like high amounts of fruit losses due to storage rot. A novel treatment with plasma-processed air (PPA) to sanitize organic apples [...] Read more.
The consumer demand for organic food including apples is increasing worldwide. Despite favorable environmental and health benefits, organic farming bears also disadvantages like high amounts of fruit losses due to storage rot. A novel treatment with plasma-processed air (PPA) to sanitize organic apples is investigated. The plasma source for the generation of PPA was operated at a frequency of 2.45 GHz, a power output of 1.1 kW and a gas flow of 18 standard liters per minute. The antimicrobial efficiency of the PPA was tested on the natural load of organic apples (cultivar Natyra) with a load ranging from 104 to 106 CFU/mL in an experimental laboratory setup. A larger application was applied on artificially inoculated (Pseudomonas fluorescens~108 CFU/mL and Pezicula malicorticis~106 CFU/mL) organic apples to test the up-scalability of the PPA treatment. The apples were photographically documented and their texture was analyzed during the 26-day storage phase to investigate the influence of the PPA treatment on the appearance of the apples. The laboratory experiments resulted in a log10-reduction of one to two log10 levels compared to untreated and compressed-air-treated apples. For apples inoculated with P. fluorescens, the up-scaled procedure resulted in up to four levels of log10 reduction. In apples inoculated with P. malicorticis, the up-scaled procedure resulted in no reduction. This indicates that the application of PPA to organic apples can be effective for bacteria but needs to be optimized for fungi. Therefore, further testing is needed to validate the results. Full article
(This article belongs to the Special Issue Microorganisms in Foods and Food Processing Environments)
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<p>Artificial inoculation process of organic apples. The samples, which were investigated during the experiments, were contaminated with <span class="html-italic">P. fluorescens</span> and <span class="html-italic">P. malicorticis</span>.</p>
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<p>A tumbler was used for the PPA treatment of apples. The apples were placed on a grid during every treatment. The tumbler did not tumble as long as apples were loaded.</p>
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<p>Picture of the Decon-Box used for the up-scaled experiments.</p>
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<p>Diagram describing the processes in the antimicrobial immersion process in the Decon-Box. The samples, which were investigated during the experiments, were contaminated with <span class="html-italic">P fluorescens</span> and <span class="html-italic">P. malicorticis</span>. All samples were compared with untreated references.</p>
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<p>(<b>a</b>) Results for the native bacterial load on the apple surface investigated under lab-scaled conditions. The picture shows the survivors after a PPA treatment of apples.; (<b>b</b>) That picture shows the reduction factors (RF) obtained after a lab-scaled PPA treatment. All experiments with n = 3.</p>
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<p>(<b>a</b>) Results for the native bacterial load on the apple surface investigated under lab-scaled conditions. The picture shows the survivors after a PPA treatment of apples.; (<b>b</b>) That picture shows the reduction factors (RF) obtained after a lab-scaled PPA treatment. All experiments with n = 3.</p>
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<p>(<b>a</b>) Survivors of <span class="html-italic">P. fluorescens</span> in CFU/mL of PPA-treated apples in up-scaled experiments. The treated apples are compared with untreated references. (<b>b</b>) Survivors of <span class="html-italic">P. malicorticis</span> in CFU/mL of PPA-treated apples in up-scaled experiments. The treated apples are compared with untreated references. (<b>c</b>) Reduction factors (RF) obtained for <span class="html-italic">P. fluorescens</span> and <span class="html-italic">P. malicorticis</span> inoculated samples in up-scaled experiments. All experiments with n = 2.</p>
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<p>(<b>a</b>) Survivors of <span class="html-italic">P. fluorescens</span> in CFU/mL of PPA-treated apples in up-scaled experiments. The treated apples are compared with untreated references. (<b>b</b>) Survivors of <span class="html-italic">P. malicorticis</span> in CFU/mL of PPA-treated apples in up-scaled experiments. The treated apples are compared with untreated references. (<b>c</b>) Reduction factors (RF) obtained for <span class="html-italic">P. fluorescens</span> and <span class="html-italic">P. malicorticis</span> inoculated samples in up-scaled experiments. All experiments with n = 2.</p>
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<p>(<b>a</b>) Texture measurement of PPA-treated apples on the laboratory scale, which are artificially inoculated with <span class="html-italic">P. fluorescens</span> and <span class="html-italic">P. malicorticis</span>. The treated apples have been compared with their untreated counterparts (reference); (<b>b</b>) texture measurements of PPA-treated apples in the up-scaled experiments, which were conducted in the Decon-Box. Two different PPA treatment times (20 min and 30 min) are compared with their untreated references.</p>
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<p>Condition of the apples after storage. On the left side are images of control apples (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) after 1 day (<b>a</b>), 14 days (<b>c</b>), 49 days (<b>e</b>), and 56 days (<b>g</b>) of storage. On the right side are images of PPA- treated apples (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) after 1 day (<b>b</b>), 14 days (<b>d</b>), 49 days (<b>f</b>), and 56 days (<b>h</b>) of storage.</p>
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<p>Condition of the apples after storage. On the left side are images of control apples (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) after 1 day (<b>a</b>), 14 days (<b>c</b>), 49 days (<b>e</b>), and 56 days (<b>g</b>) of storage. On the right side are images of PPA- treated apples (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) after 1 day (<b>b</b>), 14 days (<b>d</b>), 49 days (<b>f</b>), and 56 days (<b>h</b>) of storage.</p>
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11 pages, 1034 KiB  
Article
Occupational Exposure to Biological Agents in a Typical Restaurant Setting: Is a Photocatalytic Air Purifier Helpful?
by Matteo Ratti, Daniele Ceriotti, Rabia Bibi, Andrea Conti and Massimiliano Panella
Safety 2023, 9(4), 81; https://doi.org/10.3390/safety9040081 - 21 Nov 2023
Cited by 1 | Viewed by 1834
Abstract
According to many national legislations, biological agents represent an occupational hazard that must be managed in order to ensure safety at workplace. Bioaerosols have been associated to many pathological conditions but, despite many efforts, precise threshold limit values (TLV) are still undefined. We [...] Read more.
According to many national legislations, biological agents represent an occupational hazard that must be managed in order to ensure safety at workplace. Bioaerosols have been associated to many pathological conditions but, despite many efforts, precise threshold limit values (TLV) are still undefined. We planned and conducted an environmental study concerning a typical restaurant that aimed to evaluate: (1) the occupational exposure to bacterial and fungal bioaerosol; (2) the efficacy of a photocatalytic air purifier device in mitigating such exposure. This observational study evaluated two dining rooms (Area 1 and Area 2) of a restaurant which can be considered typical during two consecutive weeks. Based on a national protocol, we monitored total bacterial and mycotic loads searching for two typologies of bacteria, psychrophilic bacteria (environmental contamination) along with mesophilic bacteria (human or animal origin source), and two types of fungi, mold and yeast. Baseline total bacterial load was 346.8 CFU/m3 for Area 1 and 412.9 CFU/m3 for Area 2. When the sanitizing device was operative, the total bacterial load decreased to 202.7 CFU/m3 (−41.50%—p value: <0.01) for Area 1 and to 342.2 CFU/m3 (17.10%—p value: 0.06) for Area 2. Considering the fungal load, the mean baseline value was 189.7 CFU/m3 for Area 1 and 141.1 CFU/m3 for Area 2. When the device was kept on, the total fungal load was 108.0 CFU/m3 (43.10%—p value: 0.055) for Area 1 and 205.0 CFU/m3 (+45.30%—p value: 0.268) for Area 2. Our findings supported the conclusion that, concerning the occupational risk derived from biological agents, a typical restaurant should be considered relatively safe. In order to mitigate or limit any possible increase of such risk, a photocatalytic device may be helpful, but not against the pollution caused by mold or yeasts. Our research also reaffirmed the need of further research assessing the kind of relationship between diseases and exposure levels, before considering the need of setting precise threshold limit values. Full article
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Figure 1
<p>Planimetry of the restaurant facility. The location of the sanitizing devices is marked with two green stars. The HVAC system has been highlighted in blue.</p>
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<p>Boxplot of the total bacterial load retrieved in the restaurant. The measurements were paired according to the day of the week and the hour of the sample. The reference categories are taken from [<a href="#B9-safety-09-00081" class="html-bibr">9</a>,<a href="#B14-safety-09-00081" class="html-bibr">14</a>].</p>
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<p>Boxplot of the total fungal load retrieved in the restaurant. The measurements were paired according to the day of the week and the hour of the sample.The reference categories are taken from [<a href="#B9-safety-09-00081" class="html-bibr">9</a>,<a href="#B14-safety-09-00081" class="html-bibr">14</a>].</p>
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13 pages, 543 KiB  
Review
Eco-Friendly and COVID-19 Friendly? Decreasing the Carbon Footprint of the Operating Room in the COVID-19 Era
by Christos Tsagkaris, Hamayle Saeed, Lily Laubscher, Anna Eleftheriades, Sofoklis Stavros, Eirini Drakaki, Anastasios Potiris, Dimitrios Panagiotopoulos, Dimos Sioutis, Periklis Panagopoulos and Ahsan Zil-E-Ali
Diseases 2023, 11(4), 157; https://doi.org/10.3390/diseases11040157 - 2 Nov 2023
Cited by 1 | Viewed by 2532
Abstract
Surgery is one of the most energy-intensive branches of healthcare. Although the COVID-19 pandemic has reduced surgical volumes, infection control protocols have increased the ecological footprint of surgery owing to the extensive use of personal protective equipment, sanitation, testing and isolation resources. The [...] Read more.
Surgery is one of the most energy-intensive branches of healthcare. Although the COVID-19 pandemic has reduced surgical volumes, infection control protocols have increased the ecological footprint of surgery owing to the extensive use of personal protective equipment, sanitation, testing and isolation resources. The burden of environmental diseases requiring surgical care, the international commitment towards environmental sustainability and the global efforts to return to the pre-pandemic surgical workflow call for action towards climate-friendly surgery. The authors have searched the peer-reviewed and gray literature for clinical studies, reports and guidelines related to the ecological footprint of surgical care and the available solutions and frameworks to reduce it. Numerous studies concede that surgery is associated with a high rate of energy utilization and waste generation that is comparable to major non-medical sources of pollution. Recommendations and research questions outlining environmentally sustainable models of surgical practices span from sanitation and air quality improvement systems to the allocation of non-recyclable consumables and energy-efficient surgical planning. The latter are particularly relevant to infection control protocols for COVID-19. Paving the way towards climate-friendly surgery is a worthy endeavor with a major potential to improve surgical practice and outcomes in the long term. Full article
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<p>The carbon footprint of surgical operations.</p>
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10 pages, 3747 KiB  
Article
Atmospheric Plasma Sources as Potential Tools for Surface and Hand Disinfection
by Wolfram M. Brück, Alain Savary, Martine Baudin, Martine Emery Mabillard and Gilles Courret
Hygiene 2023, 3(4), 406-415; https://doi.org/10.3390/hygiene3040030 - 26 Oct 2023
Viewed by 1341
Abstract
Good hand hygiene has proven to be essential in reducing the uncontrolled spread of human pathogens. Cold atmospheric plasma (CAP) may provide an alternative to disinfecting hands with ethanol-based handrubs when handwashing facilities are unavailable. CAP can be safely applied to the skin [...] Read more.
Good hand hygiene has proven to be essential in reducing the uncontrolled spread of human pathogens. Cold atmospheric plasma (CAP) may provide an alternative to disinfecting hands with ethanol-based handrubs when handwashing facilities are unavailable. CAP can be safely applied to the skin if the energy is well controlled. In this study, radio frequency (RF) and direct current (DC) plasma sources were built with a pin-to-mesh electrodes configuration inside a fused silica tube with a 5 mm inner diameter. Microbiological assays based on EN 13697:2015+A1:2019 using Escherichia coli DSM 682 or Staphylococcus epidermidis DSM 20044 were used to examine the antimicrobial effect of various plasma conditions. Metal and silicone disks that model skin were used as inoculation matrices. The prototype air RF CAP achieved significant disinfection in the MHz range on stainless steel and silicone substrates. This is equivalent to half the performance of direct current CAP, which is only effective on conductive substrates. Using only electricity and air CAP could, with further optimization to increase its efficacy, replace or complement current hand disinfection methods, and mitigate the economic burden of public health crises in the future. Full article
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<p>Overview of RF plasma jet and nozzle outlet temperature.</p>
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<p>Optical emission spectra obtained with (<b>a</b>) DC, (<b>b</b>) DBD and (<b>c</b>) RF plasmas.</p>
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<p>Direct DC-type CAP treatment on stainless steel for 0 s (control), 30 s, 60 s and 120 s. The vertical scale is logarithmic (unit: log<sub>10</sub> cfu/25 cm<sup>2</sup>). Uncertainty bars indicate standard deviations.</p>
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<p>RF CAP disinfection (15.6 MHz) on stainless steel and artificial skin (silicone) for 75 s. The vertical scale is logarithmic (unit: log<sub>10</sub> cfu/mL). Uncertainty bars indicate standard deviations. (<b>a</b>) RF power at 50 W and (<b>b</b>) RF power at 90 W (right).</p>
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19 pages, 634 KiB  
Article
Exploring the Impact of Silicosis Incidence on Tuberculosis Mortality and Morbidity: A Multi-Country Study
by Muayad Albadrani
Med. Sci. 2023, 11(4), 63; https://doi.org/10.3390/medsci11040063 - 1 Oct 2023
Viewed by 2268
Abstract
Introduction: There are several risk factors attributed to tuberculosis (TB) mortality and morbidity. There are few studies and systematic reviews showing the association of silicosis and tuberculosis at a country level. Very limited studies have been conducted using multi-country data in studying the [...] Read more.
Introduction: There are several risk factors attributed to tuberculosis (TB) mortality and morbidity. There are few studies and systematic reviews showing the association of silicosis and tuberculosis at a country level. Very limited studies have been conducted using multi-country data in studying the association of incidence of silicosis with TB mortality and morbidity. Hence, the aim of this research was to explore the association of incidence of silicosis and other important risk factors with TB mortality and morbidity using multi-country data. Methods: Data from 217 WHO region countries were utilized, sourcing TB-related statistics from the Institute of Health Metrics and Evaluation and additional risk factors from the Demographic and Health Survey, Global Burden of Disease, and World Bank for 2019. Regression analysis was conducted to examine the association between silicosis incidence and TB outcomes. Results: The study found an average silicosis incidence of 121.92 per 100,000 population. Additionally, 62.69% of the sample population are exposed to air pollution from solid fuel cooking. Sanitation access stands at an average of 59.67%. Regression outcomes indicate that while alcohol consumption’s influence on TB is not statistically significant, a unit increase in silicosis incidence significantly elevates TB deaths (235.9, p = 0.005), YLL (9399.3, p = 0.011), and YLD (910.8, p = 0.002). Conclusion: The burden of silicosis is found to be one of the important determinants of deaths, YLL, and YLD due to tuberculosis. Country-specific strategies to prevent and control silicosis is a need of the hour. Full article
(This article belongs to the Section Pneumology and Respiratory Diseases)
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<p>Analytic framework.</p>
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<p>Conceptual framework of occupational exposure and tuberculosis disease.</p>
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