Application of 2D FFT Spectra and Correlation-Spectral Analysis to Assess Micro-Meteorological and Microbiological Weathering the Pavement Lights, Sidewalk Prisms and Other Anidolic Optics in Water
Oleg V Gradov* and Theodor K Orekhov
NN Semenov Federal Research Center for Chemical Physics of the Russian Academy of Sciences, Moscow 119991, Russia.
Submission:December 04, 2024;; Published: January 09, 2025
*Corresponding author: Oleg V Gradov, NN Semenov Federal Research Center for Chemical Physics of the Russian Academy of Sciences, Moscow 119991, Russia.
How to cite this article: Oleg V G, Theodor K O. Application of 2D FFT Spectra and Correlation-Spectral Analysis to Assess Micro-Meteorological and Microbiological Weathering the Pavement Lights, Sidewalk Prisms and Other Anidolic Optics in Water. Adv Biotech & Micro. 2025; 18(4): 555994. DOI:10.19080/AIBM.2025.18.555994
Abstract
Pavement lights, also known as sidewalk prisms or anidolic optics, play a crucial role in urban infrastructure by providing natural illumination to underground spaces while enhancing pedestrian safety. However, the effective performance and longevity of these lighting systems are heavily dependent on their resistance to environmental factors, particularly moisture and corrosion. In civil engineering and hydraulic engineering, the implications of inadequate moisture protection are profound. Pavement lights are often installed in environments exposed to rain, snow, and other forms of precipitation. Without proper sealing and corrosion resistance, these fixtures can suffer from water infiltration, leading to electrical failures, rust, and the degradation of materials. To ensure durability and reliability, it is imperative that pavement lights comply with established protection standards, such as IP67 or IP68. Adhering to these standards is essential for preventing corrosion and biological weathering, which can severely compromise the structural integrity and functionality of pavement lights. Biological weathering, which can occur when moisture facilitates the growth of mold or algae on or within the lighting fixtures, further exacerbates the problem. Firstly, we offer a complete overview of the mechanisms of effects accompanying the degradation of glass in such pavement lamps, and secondly, we offer methods for analysing the behaviour of lamps based on 2D FFT and correlation-spectral analysis methods, including in the time-resolved ones.
Keywords: Pavement Lights; Sidewalk Prisms; Anidolic Optics; Anidolic Lightings; Biogenic Weathering; Geochemical Weathering; Correlation-Spectral Analysis; 2D Fourier Spectra; Hydraulic Engineering; Civil Engineering; Glass Chemistry.
Introduction
A general problem of the design of existing outdoor lighting systems, including built-in systems of architectural and artistic lighting of buildings (and especially those whose glass parts are at the ground or sidewalk level) is the problem of degradation of the transparent glass and/or polymer (either aesthetic or protective) coating, due to the condensate formation and leakage, which first leads to a decrease in the efficiency and a change in the lighting pattern, and then to the failure of the lighter. Together with the degradation of the transparent part of the lighting device (which most actively occurs in the case of operation in a harsh climate with high gradients of the climatic parameters) degradation of the metal structures and electrical connects or fittings also occurs, but, as a rule, attention is paid to them only at the pronounced stages of corrosion and geochemical weathering, since before the critical point of these stages they either do not affect, or have less influence on the direct lighting indicators.
The main technical reason for the failure of conventional luminaires is often considered to be the non-compliance of the IP67 standard with the climatic conditions of their operation in northern countries. This is true from the corrosimetric point of view, and attempts are being made all over the world to optimize the classes of metal materials for such luminaires, as well as many other structures that comply with IP67 standards. For both luminaires and other electrical systems, special emphasis is maed on optimizing the materials of power supply circuits, in particular - connectors and metal boxes in which the luminaire is mounted. Due to the "technical fashion", in-depth development within the IP67 standard is carried out for mobile devices, in particular, those for biomedical/telemedicine purposes, even where this protection class is not required [1-7]. It is noteworthy that the glass degradation or weathering is not considered from the point of view of IP67 standard as a key process for the failure of the luminaire under the operation conditions. When fixing the cause of failure of a lighting device, usually only degradation or wear of the conductive parts by thermal cycling is fixed. However, in the case of a device located in a natural environment, it is not reasonable to reduce the diagnosis to an epicrisis of the cause of the terminal stage, since the deterioration of the lamp condition, the efficiency of its operation, begins long before its complete inoperability (due to the loss of the optical properties of the glass transmitting light).
Therefore, it is necessary to move from the statement of the phenomenology of the last stage to a physically consistent, and, ideally, physical-chemical consideration of the set of phenomena that entailed the initial decrease in the qualimetric characteristics of the luminaire, and then to their stage correlation with the pre-terminal processes in its electrical circuit. Since the target function of the built-in luminaire is the light supply and its angular concentration within the large solid angles due to the optimal scattering in accordance with the geometry, it is logical, first of all, to analyse the processes affecting the optical transmission and scattering of radiation passing through the glass of the illuminator, as the earliest superficially perceptible descriptors of the degradation process of the latter.
According to the IP criteria map of the protection degree of luminaires from the environment, the first digit nomenclature includes the limit description of the granulometric composition (dust/abrasives/particles and solids of the macroscopic sizes from 6 to 1), which quite accurately meets the real operating conditions of the luminaire (excluding special issues of the material resistance), but the second digit is not so well annotated. A complete protection of the optical and conducting parts of the luminaire is not limited to the protection from waves or jets at different angles, as well as protection during temporary or complete immersion in water. From the physicochemical positions, temperature, pressure, ionic strength of the medium, specific electrical conductivity, the presence/absence of surfactants, electrochemical potential in relation to the metal surfaces, wettability (hydrophilicity/hydrophobicity) of the surfaces, condensation (not limited to measuring the dew point), biocorrosion, and gradient (i.e. reaction-diffusion) characteristics of the weathering effect should also be taken into account. Therefore, a lamp formally manufactured in accordance with the requirements of the protection standards (IP67 or even IP68) is, in fact, defenceless against the geochemistry and hydrochemistry of the surrounding environment, which changes depending on the time of day and season.
The first criterion of this "defencelessness" visible to the user is condensation on the glass and, as a consequence of this humidification, the formation of geochemical deposits or biofilms on the inner surface. Moisture condensation on the glass surface leads to the droplet formation and dispersed patterns that scatter light [8], preventing energy-efficient lighting [9]. Depending on the hydrophilicity/hydrophobicity of the "transparent" surface (which is the carrier of the pattern with condensate from the point of view of optics) and characterized by different contact angles of the drops on the surface, condensation is different for different glass and polymer materials [10]. In particular, it differs significantly in the ordinary glass and glass with an antireflective or biocidal coating. The same effect is characteristic of the greenhouses/hotbeds [11], where the excess condensate and heat, as a rule, leads to the progression of parasitic, including fungal, microflora. As is known from classical physical chemistry, similar condensation on the surfaces of glass and similar materials is characteristic of gases and/or vapors [12], therefore the understanding of corrosion and condensation weathering in the natural atmosphere can be deepened from the reaction-diffusion positions.
Despite the long (more than a century-long) history of studying condensation on glass, which began in the second half of the 19th century, in the works of R. Bunsen [13] (known to the lighting engineers as the author of the Bunsen burner), the study of condensation for all glasses relevant to the lighting engineering has not yet been carried out. A number of authors, starting from 1907 [14], consider the "condensate pattern" formation as a phase transition regulated by the type of surface and its inhomogeneities. However, unfortunately, this concept has not received development, predicting the shape or topology of the pattern based on the nature of the glass and environmental conditions, despite the availability of the computational approaches, starting with CALPHAD (popular in the 1980s and claiming even astronomical scales of the substance condensation [15]), and ending with the multiphysical COMSOL models, which also reproduce the condensation processes [16]. Studies of moisture condensation on the surface of glass of different dimensions (from two-dimensional surfaces of three-dimensional objects to one-dimensional glass wool and model-zero-dimensional dispersed granulates) have been going on for more than a century [17,18], but the influence of the condensate morphology/topology on the transmittance of the glass of lamps (including the so-called anidolic “waveguide” and their modern Fiber-optic light-guide modifications) not only has not been solved, but, in fact, has not been posed.
The studies of condensation energy on the surface of metals, glasses, and other substrates have been separately conducted since the 1950s, more than half a century ago [19], and the effect of the emission (outflow) of the metal corrosion products (formed after moisture condensation on it) on further condensation of moisture on the surface of glass or polymer coating in contact with it has not been studied to date for the natural operating conditions of the built-in luminaires. Unfortunately, effectively studying complex condensation processes in exotic conditions (for example, capillary condensation on high-temperature porous glasses, in porous glass membranes [20,21], including for non-aqueous solvents), we often miss interesting and complex processes in simple condensation conditions, occurring on glass in the natural environment upon "thermocycling". Physical chemistry of the above phenomena favors defectoscopic registration of the results upon completion of the destruction process, which appears to be separated from the condensation process in the cause-and-effect relationship schemes, since it is easier to study condensation in glass cracks than its degradation upon condensation leading to the emergence of such cracks [22]. The study of condensation phenomena and patterns depending on temperature and baric gradients is carried out within the boundary conditions selected ad hoc (for example, capillary tubes [23]), while condensation on a planar surface in the natural geochemical environment, which is much more often observed, remains outside the scope of study, since it is mistakenly considered to be an “old and well-studied problem”. The few works that could serve to resolve the problem posed in this paper considered the outer glass surface [24], while the hanging drop approximation is more suitable for studying condensation patterns on the inner glass surface (above the lamp) [25,26]. The most empirically close works of our Chinese colleagues, who studied condensation on a thermodynamically nonequilibrium interface, appealed to the forced cooling, which is usually absent in the conventional lamps [27]. In this regard, a full-fledged analysis of the periodic patterns of moisture condensation on glass (within the approximations adequate to the requirements of lighting engineering) has not yet been carried out (the only exception in terms of 3D visualization of condensation patterns is the work [28]).
Therefore, in this paper we propose an alternative approach for measurement and evaluation of the quality of condensation patterns from the standpoint of applied lighting engineering (considering the microstructure geometry and dynamics/kinetics of condensation [29] which affects the light scattering, sometimes improving, rather than worsening, the lighting effect and surface visualization [30,31]). From the standpoint of diffraction and microprism optics, which have recently been frequently used to improve the quality of lighting [32,33], condensates can synergistically affect their own diffraction and microprism masks (in the surface layer of the glass transparent of the lumonaire), due to which single glass hydrophobization [34], which prevents the condensate formation, is not enough to improve the quality of lighting. This does not remove either the problem of the climate impact and IP6x regulation, or the economic problems, but it allows to reproduce some natural phenomena that contribute to the formation of the effective optical structures and surfaces under various conditions of the native environment, which corresponds to the main principles of “geonics” and “geomimetics” [35] developed similarly to the conceptual ideas of “bionics” or “biomimetics” which used to be widely applied in lighting engineering earlier [36,37].
The second criterion of non-fatal damage to the glass surface is the optical effect of biofilm formation on its surface, which correlates with the same weather and phenological conditions as the formation of condensate patterns. A biofilm often grows along the concentration gradient of the elements accumulated during periodic condensate evaporation and the emergence of new drips. Humid conditions that favor condensation, together with the temperature differences increasing the surface degradation, are optimal conditions for the growth of the microorganism cultures, and microcracks, from the standpoint of conventional "capillary chemistry" [38,39], contribute to the formation of new nanophases from the drip materials and favor some contact (cyto)physiological processes in the cell cultures developing in the material. The first data on the cytologically-relevant capillary-chemical phenomena refer to the works of G. Freundlich - the author of the adsorption isotherm [40]. Despite the skepticism of a number of the light engineering specialists regarding the role of microorganisms/microbial biofilms in the deterioration of the lighting quality, this factor cannot be neglected, since the elements of biofilms with microorganisms of various biological taxonomies, as a rule, accompany the structure formation on the lamp surface, which are usually considered as drips, condensates, and the products of evaporite sedimentation and quasi-template biomineralization on the glass surface.
In the most general microbiological context, biofilms on glass are formed by dozens of genera of microorganisms, such as Salmonella [41], Pseudomonas [42], Aeromonas [43,44], Listeria [45], Streptococcus [46], etc. However, for the natural conditions that do not imply the presence of pure cultures, but imply the presence of microecological links between the contaminating organisms and those interacting with them, it should be taken into account that some green algae [47] (Scenedesmus) and fungi [48] (genus Candida) can also participate in the biofilm formation in contact with glass. The biofilm formation is as fatal as condensation, since it can occur both on the seals (including the most resistant Teflon ones [49]) and on the metal parts which are in contact with the film zone, and therefore contaminated by it [50] at the surfaces with different temperature. The metabolic chemistry of the biofilm microorganisms can be different, which will affect the film adhesion [51], but it is extremely difficult to achieve such a chemical environment that is strictly negative for the biofilm growth.
Mineralization/local salinization of the environment does not hinder, but often promotes effective trophism and development of the biofilms [52], especially if it acts synergistically with the chemoautotrophy of these species in the given environmental and climate conditions. The key redox characteristics (oxygen concentration and pH), along with the changes in specific conductivity in terms of a single salt (usually NaCl, although, really, the medium salinity is provided by many different ions), vary widely at different stages of the biofilm development [53,54], due to which they are not informative outside the phenological context of the film development. The active biofilm growth in an aquatic environment, corresponding to the eutrophication stage of a reservoir with the increasing content of the nitrogen compounds, occurs after biomass accumulation of the microorganisms’ producing biofilms on the glass surface [55]. Therefore, without a stage-by-stage understanding of the mechanisms of the biofilm formation on a non-imaging optical or a light-transmitting glass of the illuminators/portholes/pavement lights (vault lights, floor lights) or sidewalk prisms, it is impossible to predict the effect of a biofilm on the luminous flux, even with the known surrounding environmental parameters.
The lack of understanding of the mechanisms and stages of microbiological and bacterial fouling does not allow one to effectively combat it. General experimental studies with the predictable conclusions (for example, on the need to combat the water hardness at the level of its source, including selectively for calcium [56]) cannot be used in architectural lighting conditions, since it is impossible to vary the precipitation hardness by the known methods, and the buildings themselves, in terms of materials and binders, are the sources of calcium washed out during geo-/hydrochemical weathering (not differing in this aspect from the calcium-containing bone and dental tissues, which do not prevent the biofilm formation on their surface [57]). Therefore, limiting ourselves to separating mature biofilms from the glass substrate on the lamp surface (using either abrasives or detergents) [58,59] and performing simple disinfection and deterioration of the glass surface [60,61], in real practice we will constantly face the physicochemical cause of the bacterial contamination and film growth, without being able to combat it, symptomatically carrying out only the simplest aesthetic renewal of the corresponding lighting system.
In fact, even at the normal temperatures-from the room one to the human’s body temperature [62,63]-not to mention regular daily (“circadian”) thermal cycling, the adaptability of biofilms to the disinfection measures can increase. Necessary and sufficient (at the level of the glass material) measures for the biofilm growth inhibition are economically unprofitable nuclear-chemical and nano chemical methods (such as irradiation using Marx or Van der Graaff generators with particle beams with an energy up to 6-8 MeV with the introduction of the ultrafine particles of heavy metals into the glass matrix) [64]. The currently available alternative methods for combating biofilms using modification of the glass structure are focused on a strictly narrow range of medical devices and limited taxa of the biofilm forming microorganisms- [65,66]. Examples are photocurable glass ionomer cements [67,68] or glass-containing composites, the optical properties of which, as well as the properties of illuminating glass, are strongly affected by the biofilms [69]. But their use, as a rule, is associated with the in situ selection for a specific category of films, which corresponds to different bactericidal agents introduced into the composition, often expensive ones (from the relatively cheap, but unstable on the time scale of operation of the street glass chlorhexidine [70-72], to the stable, but irrational for a mass introduction silver ions [73-75]), which excludes their use in the composition of the mass-produced glass, where it is usually impossible to predict the taxonomic composition of the fouling biofilm. The release of many ions that can participate in the antimicrobial activity of the composite (such as fluoride ion [76] or zinc [77]) can cause "chain ecological reactions" that exceed the negative effect of biofilms on the glass. For this reason, selective pretreatment of the glass surface, which provides bactericidal and fungicidal preventive effects (for example, against Candida fungi [78]) [79] is becoming increasingly popular. Therefore, it is necessary to look for the methods and approaches in a simpler physicochemical field and in the optimization of the lighting modes consistent with the properties of this type of biofilms (it is quite obvious that for the biofilms formed by the algae-containing microbial communities, by definition, possessing light sensitivity due to the presence of photosynthetic pigments, the requirements for the irradiation mode are quite different from those for non-photosynthetic microbial communities that perceive only the thermal component of irradiation without spectral selectivity in the visible range) and spectrochemical or photochemical properties of the glass itself, achieved during its processing, including at the stage of the glass production.
However, in order to select an effective strategy for influencing the material or coating spontaneously formed on it in certain (bio)geochemical conditions, first of all, it is necessary to understand what type of contamination or structural defects of the glass surface we are faced with, that is, to have a quantitative "fingerprint" of its current state (without extracting it from the operation conditions), which contains information that can be compared with a database of different states of the glass surface under natural conditions in order to identify its belonging to a particular state and predict the corresponding risk group of the material in the case of continued exposure under current conditions. Due to the need for unification, distinguishing between mechanical, chemical, and biological defects of glass, this fingerprint cannot be chemical (as the specific markers on biofilms [80-82]), but must be structural, identifying the nature of the defect by the surface structure. For example, the result of a texture analysis can be proposed as an identification descriptor, which can be implemented in the simplest form of a two-dimensional Fourier spectrum [83]. In the methodological part of this paper, we proceed from the universality of this 2D textural approach, appealing to the integral spatial characteristics, calculated directly on the basis of the 2D Fourier spectrum.
Methods
The measurements can be carried out in three main versions:
Ø In real time using a tablet or a laptop with a webcam placed on a movable table with wheels to ensure parallelism to the ground, which is necessary during imaging (for example, medical procedure wheeled tables with removable shelves can be used for this purpose, such as SI-03/1, SIP-2S, SP 3G and their foreign analogues).
Ø In the telemetric version of the real time mode, when the video stream from an autonomous camera is transmitted via a radio frequency channel to a stationary laptop without moving it (this is an optimal mode for a rainy or frosty weather, since it prevents the measuring complex from damaging).
Ø In the mobile version when registration is carried out by a camera built into a camera phone with a memory card, and a real-time operation mode is not required, although it can be achieved by ensuring data transmission via some Internet messenger with the real-time processing software installed on the receiving laptop/stationary PC.
In all the real-time versions data processing is performed using QAVIS software (developed by A.A. Goncharov and V.K. Fishchenko from the Pacific Oceanological Institute FEB RAS), which provides direct visualization of 2D Fourier spectra and calculation of the integral frequency characteristics and integral spatial characteristics from them, with the color highlighting of the remarkable periods-descriptors of the order of the structure studied. However, the computing capabilities of this software are optimal for the coating qualimetry, but not for its metrological assessment, for which another program developed by the same authors should be used-KSAImage, which allows calculating periodograms from the images, performing measurements in spectra, approximating integral frequency characteristics using the least square method with various theoretical dependences of spectra, which are a superposition of the spectral densities of the first and second types, analyzing the spectra anisotropy based on the integral spatial characteristics, performing correlation analysis and deposition of spectra and other calculated characteristics of the images to various databases for AI/machine learning based identification.
For ensuring comparability of the measurement results, one should compare only data obtained using the sensors with identical resolvometric characteristics. Therefore, a sufficiently correct comparison can be achieved within one measurement option with the same sensor type. However, this is typical, as a rule, for the "metrological" interpretation of correlation-spectral analysis (preformed using KSAImage), and not for its evaluative "qualimetric" version (performeed using QAVIS).

Results
Full dataset "Weathering and biodegradation of the surface/coating of light fixtures near the State Hermitage Museum" (DOC1: Fourier spectra; DOC2: Integral Spatial Characteristics & Integral Frequency Characteristics; DOC3: Statistical characteristics and histograms) was deposited in the "Knowledge Network for Biocomplexity" of the National Center for Ecological Analysis and Synthesis (NCEAS, Santa Barbara, CA) [DOI: 10.5063/F1FJ2F3G]. Experimental results shown below were obtained using mobile camera-phone image recordings/imaging (without additional camera leveling with an accuracy exceeding the accuracy of the built-in magnetometer/gyroscope of the phone), with the primary qualimetric processing using QAVIS software, which recorded 2D Fourier spectra (Figure 1-3).

Discussion
As can be seen from the above data, using physicochemical approaches proposed, solution of the problems of detecting and preventing biological fouling of glass can revive interest in the anidolic optics, which has significantly decreased recently [84-90] mostly due to the unresolved climatic problems [91]. In our opinion, this monitoring solution will be especially relevant for the tropical and subtropical conditions [92-95], including the regions with regular rainy seasons, as well as for the climates with contrasting temperature and humidity conditions. If you install a lamp into the ground, and after some time condensation appears in it, the lamp leaks and fails. This happens because most street lamps currently available in the market comply only with the IP67 protection standard. This standard guarantees the lamp operation only with a short-term immersion in water and does not guarantee its operation in the snow/ice. In contrasting climates with the ice formation (Finland, Norway, Russia in the Palearctic latitudes, Iceland, Greenland, Spitsbergen, Alaska, etc.) ground lamps must operate in the frozen ground in winter, buried into the frozen soil, and in spring and autumn-fully immersed in water, therefore the IP67 standard is obviously not enough for such extreme operation conditions [96-102]. Of particular importance will be a synchronous solution for monitoring and preventing physical condensation (as a well-known phenomenon studied since the 19th century [103]) and microbiological degradation and biofouling activity caused by the condensed moisture (formation of physicochemically active biofilms degrading the lamp material on the glass surface), which can be prevented at an early stage, and the glass surface can be recycled for further use upon the regular cleaning [104]. All the phenomena described above become controllable when using the QAVIS real-time software [105-109].
- Mori T (2003) IP67-compatible manifold VQC series. Hydraulic and Pneumatic Technology/Hydraulic and Pneumatic Technology Editorial Committee 42(1): 20-22.
- Kaneko R (2016) Waterproof and dustproof grommet "One-touch grommet" series: IP67 compliant, excellent workability. Piping Technology = The piping engineering/Piping Technology Editorial Committee 58(2): 70-73.
- Weiss C, Feldman B, Fitzgerald Q, Georgiades C, Raderman E (2022) Inventors; Custom Club Inc, assignee. Oral device container and oral device sanitation system. United States patent US 11: 344-644.
- White A, Hornby A (2003) New IP67 protective housings extend non-contact safety into wash down areas. Assembly Automation 23(1): 005.
- Sala D (2003) Optimization of the wiring and electrical components installation procedure for industrial IP67 control networks: a model-based approach (Thesis, Laurea Magistrale, Scuola di Ingegneria Industriale e dell'Informazione, Polytechnica Milano).
- Moerman F, Holah J (2024) Hygienic Design of Processing Lines. In: Prevention of the Biological Contamination of Food: Processing/ Distribution and Consumer Usage.
- Neenan MA, Smith R (2022) Inventors; Parsec Technologies Inc, assignee. Emergency portable hot spot with antennas built into cover. United States patent US 11: 329-363.
- Levengood WC (1955) Study of Moisture‐Condensation Patterns on Glass and Crystalline Surfaces. Journal of the American Ceramic Society 38(5): 178-183.
- Werner A, Roos A (2007) Condensation tests on glass samples for energy efficient windows. Solar energy materials and solar cells 91(7): 609-615.
- Pieters JG, Deltour JM, Debruyckere MJ (1997) Light transmission through condensation on glass and polyethylene. Agricultural and forest meteorology 85(1-2): 51-62.
- Pollet I, Pieters J (2000) Condensation and radiation transmittance of greenhouse cladding materials, part 3: Results for glass plates and plastic films. Journal of agricultural engineering research 77(4): 419-428.
- Shereshefsky JL, Weir CE (1956) Adsorption of Gases and Vapors on Glass Spheres. Two-Dimensional Condensation of Oxygen. The Journal of Physical Chemistry 60(9): 1162-1164.
- Bunsen R XXII (1884) On the condensation of carbonic acid on smooth glass surfaces. The London, Edinburgh, and Dublin Philosophical Magazine and Journal of Science 17(105): 161-173.
- Trouton FT (1907) On the two modes of condensation of water vapour on glass surfaces, and their analogy with James Thomson’s curve of transition from gas to liquid. Proceedings of the Royal Society of London. Series A Containing Papers of a Mathematical and Physical Character 79(531): 383-390.
- Petaev MI (2009) The GRAINS thermodynamic and kinetic code for modeling nebular condensation. Calphad 33(2): 317-327.
- Petkovska M, Antov-Bozalo D, Markovic A, Sullivan P (2007) Multiphysics modeling of electric-swing adsorption system with in-vessel condensation. Adsorption 13: 357-372.
- Pickering H (1915) Preventing Accumulation of Moisture of Condensation Upon Glass or Other Protected Surfaces. Industrial & Engineering Chemistry 7(5): 458.
- Dodd LE (1916) A Curve of Moisture Condensation on Glass Wool. Proceedings of the Iowa Academy of Science 23(1): 195-199.
- Benjamin P, Weaver C (1959) Condensation energies for metals on glass and other substrates. Proceedings of the Royal Society of London. Series A. Mathematical and Physical Sciences 252(1270): 418-430.
- Abeles B, Chen LF, Johnson JW, Drake JM (1991) Capillary condensation and surface flow in microporous Vycor glass. Israel journal of chemistry 31(2): 99-106.
- Uchytil P, Petrickovic R, Seidel-Morgenstern A (2005) Study of capillary condensation of butane in a Vycor glass membrane. Journal of membrane science 264(1-2): 27-36.
- Ciccotti M, George M, Ranieri V, Wondraczek L, Marliere C (2008) Dynamic condensation of water at crack tips in fused silica glass. Journal of non-crystalline solids 354(2-9): 564-568.
- Iiyama K, Kaneko A, Abe Y, Suzuki Y (2009) Experimental Study on Thermal Hydraulic Characteristics of Steam Condensation in Capillary Glass Tubes. Proc. ASME 43901: 119-128.
- Palková A, Palko M (2016) Condensation on the Exterior Surface of Glass System. Applied Mechanics and Materials 820: 293-298.
- Savino R, Monti R (1996) Buoyancy and surface-tension-driven convection in hanging-drop protein crystallizer. Journal of crystal growth 165(3): 308-318.
- Valenzuela MA, Garcia JA, Diaz JL (2010) Analysis of sensitivity to vibration of the method of measurement of surface tension by hanging drop. Revista Mexicana de Fisica 56(4): 334-338.
- Xiyu LJ, Guanlong L (2010) Condensation on Glass Surface of Refrigerated Display Case. Journal of Refrigeration Pp.
- Leriche M, Roessner W, Weigand B (2015) Modelling of the Condensation/Evaporation of Water Droplet on Glass Surface: Application to the Defogging. In Proceedings of the ASME-ATI-UIT 2015 Conference on Thermal Energy Systems: Production Storage, Utilization and the Environment, Napoli, Italy Pp: 17-20.
- Klemm AJ, Klemm P, Rozniakowski K, Galbraith G (2002) Non-contact methods of measuring moisture concentration in external layers of building partitions. I-The influence of geometrical microstructure on the kinetics of moisture condensation on glass surfaces. Building and environment 37(12): 1215-1220.
- Langer MS, Bülthoff HH (2000) Depth discrimination from shading under diffuse lighting. Perception 29(6): 649-660.
- Lash DJ (2000) Performance benefits of highly reflective diffuse materials in lighting fixtures. Journal of the Illuminating Engineering Society 29(1): 11-16.
- Lee CC, Ting YS, Fang W (2012) Development of passive and active microprism arrays to change the radiation pattern of solid-state lighting. Journal of Micromechanics and Microengineering 22(10): 105038.
- Cornelissen HJ, de Boer DK, Tukker T (2013) Diffraction gratings for Lighting applications. Proc. SPIE 8835: 97-104.
- Blackman LC, Harrop R (1968) Hydrophilation of glass surfaces I. Investigation of possible promoters of filmwise condensation. Journal of Applied Chemistry 18(2): 37-43.
- Lesovik V, Volodchenko A, Glagolev E, Lashina I, Fischer HB (2019) Geonics (geomimetics) as a theoretical basis for new generation compositing. In 14th International Congress for Applied Mineralogy (ICAM2019) Belgorod State Technological University named after VG Shukhov Pp: 23-27.
- Liya LIU (2009) On the Lighting into the Design of Biomimetic. Art and Design 12: 82.
- Yuan Y, Yu X, Yang X, Xiao Y, Xiang B, et al. (2017) Bionic building energy efficiency and bionic green architecture: A review. Renewable and sustainable energy reviews 74: 771-787.
- Freundlich H (1922) Kapillarchemie, eine Darstellung der Chemie der Kolloide und verwandter Gebiete.
- Pawlow P (1911) Die allgemeine Phasenregel und deren Anwendung auf Systeme der Kapillarchemie. Zeitschrift für Physikalische Chemie 75(1): 48-74.
- Freundlich H (1907) Kapillarchemie and Physiologie.
- Prouty AM, Gunn JS (2003) Comparative analysis of Salmonella enterica serovar Typhimurium biofilm formation on gallstones and on glass. Infection and immunity 71(12): 7154-7158.
- Jer̀ábková H, Králová B, Náhlı́k J (1999) Biofilm of Pseudomonas C12B on glass support as catalytic agent for continuous SDS removal. International biodeterioration & biodegradation 44(4): 233-241.
- Bechet M, Blondeau R (2003) Factors associated with the adherence and biofilm formation by Aeromonas caviae on glass surfaces. Journal of applied microbiology 94(6): 1072-1078.
- Ormanci S, Yucel N (2017) Biofilm formation on polystyrene and glass surface by Aeromonas species isolated from different sources. Journal of food processing and preservation 41(6): e13223.
- Adetunji VO, Isola TO (2011) Crystal violet binding assay for assessment of biofilm formation by Listeria monocytogenes and Listeria spp on wood, steel and glass surfaces. Global Veterinaria 6(1): 6-10.
- Wang SP, Ge Y, Zhou XD, Xu HH, Weir MD, et al. (2016) Effect of anti-biofilm glass-ionomer cement on Streptococcus mutans biofilms. International journal of oral science 8(2): 76-83.
- Zheng Y, Huang Y, Liao Q, Zhu X, Fu Q, et al. (2016) Effects of wettability on the growth of Scenedesmus obliquus biofilm attached on glass surface coated with polytetrafluoroethylene emulsion. International Journal of Hydrogen Energy 41(46): 21728-21735.
- Malm A, Chudzik B, Piersiak T, Gawron A (2010) Glass surface as potential in vitro substratum for Candida famata biofilm. Annals of Agricultural and Environmental Medicine 17(1): 115-118.
- Van der Kooij D, Veenendaal HR, Baars-Lorist C, van der Klift DW, Drost YC (1995) Biofilm formation on surfaces of glass and teflon exposed to treated water. Water research 29(7): 1655-1662.
- Yurudu NO (2012) Study of biofilm associated bacteria on polyvinyl chloride, stainless steel and glass surfaces in a model cooling tower system with different microbiological methods. European Journal of Biology 71(1): 63-76.
- Wollersheim R (1989) Adhesion and biofilm development of acetate-, propionate-, and butyrate-degrading microorganisms on glass surfaces. Biotechnology letters 11: 749-752.
- Kwon KK, Lee HS, Jung SY, Yim JH, Lee JH, et al. (2002) Isolation and identification of biofilm-forming marine bacteria on glass surfaces in Dae-Ho Dike, Korea. Journal of microbiology 40(4):260-266.
- Moraes JO, Cruz EA, Pinheiro Í, Oliveira TC, Alvarenga V, et al. (2019) An ordinal logistic regression approach to predict the variability on biofilm formation stages by five Salmonella enterica strains on polypropylene and glass surfaces as affected by pH, temperature and NaCl. Food microbiology 83: 95-103.
- Almeida VG, Trein MP, Oppermann RV, Rösing CK (2008) In situ biofilm formation on enamel and glass ionomer cement in different oxygen tensions. Revista Odonto Ciência 23(1): 48-52.
- Park HI, Kim JS, Kim DK, Pak D (2004) Autohydrogenotrophic denitrification of high nitrate concentration in a glass bead biofilm reactor. Journal of Korean Society on Water Environment 20(3): 236-240.
- Hijnen WA, Schultz F, Harmsen DJ, Brouwer-Hanzens AH, van der Wielen PW, et al. (2016) Calcium removal by softening of water affects biofilm formation on PVC, glass and membrane surfaces. Water Science and Technology: Water Supply 16(4): 888-895.
- Elliott D, Pratten J, Edwards M, Crowther J, Petrie A, et al. (2005) Bacterial biofilm development on hydroxyapatite-coated glass. Current microbiology 51: 41-45.
- Vatanyoopaisarn S (2001) Comparison of detachment methods for biofilm removal on glass and stainless-steel surfaces. J KMITNB 11: 14-24.
- Safari A, Tukovic Z, Cardiff P, Walter M, Casey E, et al. (2016) Interfacial separation of a mature biofilm from a glass surface-A combined experimental and cohesive zone modelling approach. Journal of the mechanical behavior of biomedical materials 54: 205-218.
- Armon R, Arbel T, Green M (1998) A quantitative and qualitative study of biofilm disinfection on glass, metal and PVC surfaces by chlorine, bromine and bromochloro-5, 5 dimethylhydantoin (BCDMH). Water science and technology 38(12): 175-179.
- Munro WA, Thomas CL, Simpson I, Shaw J, Dodgson J (1996) Deterioration of pH electrode response due to biofilm formation on the glass membrane. Sensors and Actuators B: Chemical 37(3): 187-194.
- Muazu A, Rahman NI, Abdullahi UF, Aliyu S, Ogidi JA, et al. (2015) Assessment of chemical disinfectants efficacy against Escherichia coli biofilm developed on glass and wood at refrigeration and room temperatures. Journal of Applied Pharmaceutical Science 5(12): 074-079.
- Anas M, Rahman NI, Umar AF, Ogidi JA (2016) Evaluation of chemical disinfectants efficacy against escherichia coli biofilm developed at 37°c on glass and stainless steel. Journal of Science and Mathematics Letters 4: 1-9.
- Jadhav VS, Bankar A, Zinjarde S, Bhoraskar VN, Dhole SD (2012) Size control of Cu nanoparticles in ion-exchanged soda-lime glass by 6 MeV electron irradiation and its application in biofilm inhibition. International Journal of Green Nanotechnology 4(4): 455-463.
- Fúcio SB, Paula AB, Sardi JC, Duque C, Correr-Sobrinho L, et al. (2016) Streptococcus mutans biofilm influences on the antimicrobial properties of glass ionomer cements. Brazilian dental journal 27(6): 681-687.
- Coughlan A, Ryan MP, Cummins NM, Towler MR (2011) The response of Pseudomonas aeruginosa biofilm to the presence of a glass polyalkenoate cement formulated from a silver containing glass. Journal of Materials Science 46: 285-287.
- Krämer N, Schmidt M, Lücker S, Domann E, Frankenberger R (2018) Glass ionomer cement inhibits secondary caries in an in vitro biofilm model. Clinical oral investigations 22: 1019-1031.
- Souza BM, Santos DM, Magalhães AC (2018) Antimicrobial and anti-caries effect of new glass ionomer cement on enamel under microcosm biofilm model. Brazilian Dental Journal 29(6): 599-605.
- Hyun HK, Ferracane JL (2016) Influence of biofilm formation on the optical properties of novel bioactive glass-containing composites. Dental Materials 32(9): 1144-1151.
- Huang X, Yang T, Zhao S, Huang C, Du X (2012) Anti-biofilm effect of glass ionomer cements incorporated with chlorhexidine and bioactive glass. Journal of Wuhan University of Technology-Mater Sci Ed 27: 270-275.
- de Oliveira Becci AC, Marti LM, Cilense Zuanon AC, Brighenti FL, Palomari Spolidorio DM, et al. (2016) Analysis of the biofilm formed on the surface of a glass-ionomer cement associated with different concentrations of chlorhexidine diacetate. American Journal of Dentistry 29(5): 277-281.
- Yan H, Yang H, Li K, Yu J, Huang C (2017) Effects of chlorhexidine-encapsulated mesoporous silica nanoparticles on the anti-biofilm and mechanical properties of glass ionomer cement. Molecules 22(7): 1225.
- Sahal G, Nasseri B, Bilkay IS, Piskin E (2015) Anti-biofilm effect of nanometer scale silver (NmSAg) coatings on glass and polystyrene surfaces against P. mirabilis, C. glabrata and C. tropicalis strains. Journal of Applied Biomaterials & Functional Materials 13(4): 351-355.
- El-Wassefy NA, El-Mahdy RH, El-Kholany NR (2018) The impact of silver nanoparticles integration on biofilm formation and mechanical properties of glass ionomer cement. Journal of Esthetic and Restorative Dentistry 30(2): 146-152.
- Wilkinson HN, Iveson S, Catherall P, Hardman MJ (2018) A novel silver bioactive glass elicits antimicrobial efficacy against Pseudomonas aeruginosa and Staphylococcus aureus in an ex vivo skin wound biofilm model. Frontiers in microbiology 9: 1450.
- Chau NP, Pandit S, Jung JE, Cai JN, Yi HK, et al. (2016) Long-term anti-cariogenic biofilm activity of glass ionomers related to fluoride release. Journal of Dentistry 47: 34-40.
- Esfahanizadeh N, Nourani MR, Bahador A, Akhondi N, Montazeri M (2018) The anti-biofilm activity of nanometric zinc doped bioactive glass against putative periodontal pathogens: An in vitro study. Biomedical glasses 4(1): 95-107.
- Rossoni RD, De Barros PP, Lopes LA, Ribeiro FC, Nakatsuka T, et al. (2019) Effects of surface pre-reacted glass-ionomer (S-PRG) eluate on Candida spp.: antifungal activity, anti-biofilm properties, and protective effects on Galleria mellonella against C. albicans infection. Biofouling 35(9): 997-1006.
- Shimazu K, Oguchi R, Takahashi Y, Konishi K, Karibe H (2016) Effects of surface reaction-type pre-reacted glass ionomer on oral biofilm formation of Streptococcus gordonii. Odontology 104: 310-317.
- DeForest JL, Drerup SA, Vis ML (2016) Using fatty acids to fingerprint biofilm communities: a means to quickly and accurately assess stream quality. Environmental monitoring and assessment 188(5): 277.
- Humbert F, Quilès F, Delille A (2009) In situ assessment of drinking water biostability using nascent reference biofilm ATR-FTIR fingerprint. In: Current Research Topics in Applied Microbiology and Microbial Biotechnology Pp: 268-272.
- Leme AP, Bellato C, Koo H, Bedi G, Tabchoury C, et al. (2004) Proteins in Dental Biofilm Formed in situ in the Presence of Sucrose Identified by Peptide Mass Fingerprint. Caries Research 38(4): 369.
- Solberg AH, Gelius LJ (2011) New texture attributes from local 2D Fourier spectra. In: SEG International Exposition and Annual Meeting Pp: 1165-1169.
- Courret G, Paule B, Scartezzini JL (1996) Anidolic zenithal openings: Daylighting and shading. International Journal of Lighting Research and Technology 28(1): 11-17.
- Courret G, Scartezzini JL, Francioli D, Meyer JJ (1998) Design and assessment of an anidolic light-duct. Energy and buildings 28(1): 79-99.
- Molteni SC, Courret G, Paule B, Michel L, Scartezzini JL (2001) Design of anidolic zenithal lightguides for daylighting of underground spaces. Solar Energy 69: 117-129.
- Altherr R, Gay JB (2002) A low environmental impact anidolic facade. Building and Environment 37(12): 1409-1419.
- Scartezzini JL, Courret G (2002) Anidolic daylighting systems. Solar energy 73(2): 123-135.
- Wittkopf SK (2007) Daylight performance of anidolic ceiling under different sky conditions. Solar Energy 81(2): 151-161.
- Linhart F, Wittkopf SK, Scartezzini JL (2010) Performance of Anidolic Daylighting Systems in tropical climates-Parametric studies for identification of main influencing factors. Solar Energy 84(7): 1085-1094.
- Wittkopf SK, Yuniarti E, Soon LK (2006) Prediction of energy savings with anidolic integrated ceiling across different daylight climates. Energy and buildings 38(9): 1120-1129.
- Roshan M, Kandar MZ, Najafpour H, Ossen DR, Ghasemi M, et al. (2014) Analysis of anidolic daylighting system parameters in tropical climate. Life Science Journal 11(8): 171-176.
- Binarti F, Satwiko P (2015) Long-term monitoring and simulations of the daylighting and thermal performance of an anidolic daylighting system on a tropical urban house. Energy Procedia 78: 1787-1792.
- Binarti F, Satwiko P (2016) An east-facing anidolic daylighting system on a tropical urban house. Indoor and Built Environment 25(4): 691-702.
- Binarti F, Satwiko P (2018) Assessing the energy saving potential of anidolic system in the tropics. Energy Efficiency 11(4): 955-974.
- Cabeza LF, DiMaio G, Brown EM, Marmer WN, Carrio R, et al. (1998) Processing of leather waste: Dn25 Pulse and 4-20mA Output PTFE Lining SS316L Electrode Remote Type IP68 Flow Meter Water Flow Meter, Part I. Mini Bar Countertop Beverage Energy Drink Small Fridge. The Journal of the American Leather Chemists Association (JALCA) 93(3): 61.
- Garcia EE, Kimura C, Martins AC, Rocha GO, Nozaki J (1999) Dn25 Pulse and 4-20mA Output PTFE Lining SS316L Electrode Remote Type IP68 Flow Meter Water Flow Meter. Brazilian Archives of Biology and Technology 42(3): 281-290.
- Condell RA, Hanko VP, Larenas EA, Wallace G, McCullough KA (1993) Analysis of native collagen monomers and oligomers by size-exclusion high-Dn25 Pulse and 4-20mA Output PTFE Lining SS316L Electrode Remote Type IP68 Flow Meter Water Flow Meter. Analytical Biochemistry 212: 436-445.
- Dobiecki J (2000) Pewny pomiar pH. Połączenie między elektrodą a przetwornikiem o stopniu ochrony IP68. Napędy i Sterowanie 2(9): 56-57.
- Grigorieva E, Gradov O, Gradova M, Maklakova I (2022) Towards Multi-Angle Multispectral Optical 3D Porometry and Lens-Less Porometry of Civil Engineering Composites and Geocomposites Including Biodegradable Ones. Advances in Transdisciplinary Engineering 31: 101-113.
- Orekhov FK, Gradov OV (2023) Target Chip Based Single-Cell Biotyping and Telemetric Bioluminescence Lensless Microscopy of the Buried Sandwich-Slides as a Novel Way for Measurement, Mapping and Molecular Imaging of Biodegradation/Biofouling of Plastic Surfaces in Real Soils. Advances in Transdisciplinary Engineering 38: 417-425.
- Alekseev V (2016) IP68 connecting devices manufactured by TTAF for outdoor electrical equipment. Semiconductor Lighting 5(43): 60-64.
- Bottomley JT (1885) I. Note on the condensation of gases at the surface of glass. Proceedings of the Royal Society of London 38(235-238): 158-161.
- Björnsson L, Mattiasson B, Welander T (1997) Supports made from recycled glass as biofilm carriers in anaerobic packed bed treatment of high-strength wastewaters. Resource and environmental biotechnology 1: 243-256.
- Goncharova AA, Fischenko VK (2011) QAVIS-program for quick image and video analysis. In Proceedings of 8th Open German Russian Workshop on Pattern Recognition and Image Understanding (OGRW-8 2011) Pp: 85.
- Goncharova AA, Fischenko VK, Dubina VA (2012) Use the express-analysis program QAVIS for the satellite monitoring. Current problems in re-mote sensing of the Earth from space 9(3): 293-298.
- Gradov OV, Nasirov FA, Goncharova AA, Fishchenko VK, Yablokov AG (2018) The technologies of the lensless holographic trichoscopy and trichometry on the chip are microinterference, 2D Fourier spectral (integral frequency and spatial) and correlational techniques in clinical trichology. Morphologia 12(2): 7-21.
- Fischenko VK, Goncharova AA, Dolgikh GI, Zimin PS, Subote AE, et al. (2021) Express image and video analysis technology QAVIS: application in system for video monitoring of Peter the Great Bay (Sea of Japan/East Sea). Journal of Marine Science and Engineering 9(10): 1073.
- Fischenko V, Mitnik L, Dolgikh G, Goncharova A, Zimin P, et al. (2022) QAVIS technology: Measuring wave processes in coastal zones based on the analysis of internet video broadcast. InIGARSS 2022-2022 IEEE International Geoscience and Remote Sensing Symposium Pp: 6801-6804.