- Environmental scanning electron microscope
The environmental scanning electron microscope or ESEM is a scanning electron microscope (SEM) that allows for the option of collecting electron micrographs of specimens that are "wet," uncoated, or both by allowing for a gaseous environment in the specimen chamber.
Although there were earlier successes at viewing wet specimens in internal chambers in modified SEMs, the ESEM with its specialized electron detectors (rather than the standard Everhart-Thornley detector) and its differential pumping systems to allow for the transfer of the electron beam from the high vacuums in the gun area to the high pressures attainable in its specimen chamber make it a complete and unique instrument designed for the purpose of imaging specimens in their natural state. The instrument was designed originally by Gerasimos Danilatos while working at the University of New South Wales.
Early attempts have been reported on the examination of specimens inside "environmental" cells with water or atmospheric gas, in conjunction with conventional and scanning transmission types of electron microscopes. However, the first images of wet specimens in an SEM were reported by Lane in 1970 when he injected a fine jet of water vapor over the point of observation at the specimen surface; the gas diffused away into the vacuum of the specimen chamber without any modification to the instrument. Further, Shah and Beckett reported the use of differentially pumped cells or chambers to presumably maintain botanical specimens conductive in order to allow the use of the absorbed specimen current mode for signal detection in 1977 and in 1979. Spivak et al. reported the design and use of various environmental cell detection configurations in a SEM including differential pumping, or the use of electron trasparent films to maintain the specimens in their wet state in 1977. Those cells, by their nature, had only limited application use and no further development was done. In 1974, an improved approach was reported by Robinson with the use of a backscattered electron detector and differential vacuum pumping with a single aperture and the introduction of water vapor around 600 Pa pressure at the freezing point of temperature. However, neither of those approaches produced a stable enough instrument for routine operation. Starting work with Robinson in 1978 at the University of New South Wales in Sydney, Danilatos undertook a thorough quantitative study and experimentation that resulted in a stable operation of the microscope at room temperature and high pressures up to 7000 Pa, as reported in 1979. In the following years, Danilatos, working independently, reported a series of works on the design and construction of an environmental or atmospheric scanning electron microscope (ASEM) capable of working at any pressure from vacuum up to one atmosphere. These early works involved the optimization of the differential pumping system together with backscattered electron (BSE) detectors until 1983, when he invented the use of the environmental gas itself as a detection medium. The decade of 1980 closed with the publication of two major works comprehensively dealing with the foundations of ESEM and the theory of the gaseous detection device (GDD). Furthermore, in 1988, the first commercial ESEM was exhibited in New Orleans by ElectroScan Corporation, a venture capital company wishing to commercialize the Danilatos ESEM. The company placed an emphasis on the secondary electron (SE) mode of the GDD and secured the monopoly of the commercial ESEM with a series of additional key patents. Philips and FEI companies succeeded ElectroScan in providing commercial ESEM instruments. With the expiration of key patents and assistance by Danilatos, new commercial instruments have been recently added to the market by LEO (succeeded by Carl Zeiss SMT). Further improvements have been reported to date from work on the original experimental prototype ESEM in Sydney and from numerous other workers using the commercial ESEM in a wide variety of applications worldwide. An early comprehensive bibliography was compiled in 1993 by Danilatos, whilst a more recent survey can be found in a Ph.D. Thesis by Morgan (2005).
How it works
An ESEM employs a scanned electron beam and electromagnetic lenses to focus and direct the beam on the specimen surface in an identical way as a conventional SEM. A very small focused electron spot (probe) is scanned in a raster form over a small specimen area. The beam electrons interact with the specimen surface layer and produce various signals (information) that are collected with appropriate detectors. The output of these detectors modulates, via appropriate electronics, the screen of a monitor to form an image that corresponds to the small raster and information, pixel by pixel, emanating from the specimen surface. Beyond these common principles, the ESEM deviates substantially from a SEM in several respects, all of which are important in the correct design and operation of the instrument. The outline below highlights these requirements and how the system works.
The specimen chamber sustaining the high-pressure gaseous environment is separated from the high vacuum of the electron optics column with at least two small orifices customarily referred to as pressure-limiting apertures (PLA). The gas leaking through the first aperture (PLA1) is quickly removed from the system with a pump that maintains a much lower pressure in the downstream region (i.e. immediately above the aperture). This is called differential pumping. Some gas escapes further from the low pressure region (stage 1) through a second pressure limiting aperture (PLA2) into the vacuum region of the column above, which constitutes a second stage differential pumping (stage 2). A schematic diagram shows the basic ESEM gas pressure stages including the specimen chamber, intermediate cavity and upper electron optics column. The corresponding pressures achieved are p0>>p1>>p2, which is a sufficient condition for a microscope employing a tungsten type of electron gun. Additional pumping stages may be added to achieve an even higher vacuum as required for a LaB6 and field emission type electron guns. The design and shape of a pressure limiting aperture are critical in obtaining the sharpest possible pressure gradient (transition) through it. This is achieved with an orifice made on a thin plate and tapered in the downstream direction as shown in the accompanying isodensity contours of a gas flowing through the PLA1. This was done with a computer simulation of the gas molecule collisions and movement through space in real time. We can immediately see in the figure of the isodensity contours of gas through aperture that the gas density decreases by about two orders of magnitude over the length of a few aperture radii. This is a quantitatively vivid demonstration of a first principle that enables the separation of the high-pressure specimen chamber from the low pressure and vacuum regions above.
By such means, the gas flow fields have been studied in a variety of instrument situations, in which subsequently the electron beam transfer has been quantified.
Electron beam transfer
By the use of differential pumping, an electron beam is generated and propagated freely in the vacuum of the upper column, from the electron gun down to PLA2, from which point onwards the electron beam gradually loses electrons due to electron scattering by gas molecules. Initially, the amount of electron scattering is negligible inside the intermediate cavity, but as the beam encounters an increasingly denser gas jet formed by the PLA1, the losses become significant. After the beam enters the specimen chamber, the electron losses increase exponentially at a rate depending on the prevailing pressure, the nature of gas and the accelerating voltage of the beam. The fraction of beam transmitted along the PLA1 axis can be seen by a set of characteristic curves for a given product p0D, where D is the aperture diameter. Eventually, the electron beam becomes totally scattered and lost, but before this happens, a useful amount of electrons is retained in the original focused spot over a finite distance, which can still be used for imaging. This is possible because the removed electrons are scattered and distributed over a broad area like a skirt surrounding the focused spot. Because the electron skirt width is orders of magnitude greater than the spot width, with orders of magnitude less current density, the skirt contributes only background (signal) noise without partaking in the contrast generated by the central spot. The particular conditions of pressure, distance and beam voltage over which the electron beam remains useful for imaging purposes has been termed oligo-scattering regime in distinction from single-, plural- and multiple-scattering regimes used in prior literature.
For a given beam accelerating voltage and gas, the distance L from PLA1, over which useful imaging is possible, is inversely proportional to the chamber pressure p0. As a rule of thumb, for a 5 kV beam in air, it is required that the product p0L = 1 Pa·m or less. By this second principle of electron beam transfer, the design and operation of an ESEM is centered on refining and miniaturizing all the devices controlling the specimen movement and manipulation, and signal detection. The problem then reduces to achieving sufficient engineering precision for the instrument to operate close to its physical limit, corresponding to optimum performance and range of capabilities.
The electron beam impinges on the specimen and penetrates to a certain depth depending on the accelerating voltage and the specimen nature. From the ensuing interaction, signals are generated in the same way as in a SEM. Thus, we get secondary and backscattered electrons, X-rays and cathodoluminescence (light). All of these signals are detected also in the ESEM but with certain differences in the detector design and principles used.
The conventional secondary electron detector of SEM (Everhart-Thornley detector) cannot be used in the presence of gas because of an electrical discharge (arcing) caused by the kilovolt bias associated with this detector. In lieu of this, the environmental gas itself has been used as a detector for imaging in this mode:
Gaseous detection device
In a simple form, the gaseous detection device (GDD) employs an electrode with a voltage up to several hundred volts to collect the secondary electrons in the ESEM. The principle of this detector is best described by considering two parallel plates at a distance d apart with a potential difference V generating a uniform electric field E = V/d as shown in the accompanying diagram of the GDD. This configuration is taken from the theory of the detector and a book chapter on ESEM. Secondary electrons released from the specimen at the point of beam impingement are driven by the field force towards the anode electrode but the electrons also move radially due to thermal diffusion from collisions with the gas molecules. The variation of electron collection fraction R within anode radius r vs. r/d, for fixed values of anode bias V, at constant product of (pressure·distance) p·d = 1 Pa·m, is given by the accompanying characteristic curves of efficiency of the GDD. All of the secondary electrons are detected if the parameters of this device are properly designed. This clearly shows that practically 100% efficiency is possible within a small radius of collector electrode with only moderate bias. At these levels of bias, no catastrophic discharge takes place. Instead, a controlled proportional multiplication of electrons is generated as the electrons collide with gas molecules releasing new electrons on their way to the anode. This principle of avalanche amplification operates similarly to proportional amplifiers used in nuclear physics detectors. The signal thus picked up by the anode is further amplified and processed to modulate a display screen and form an image as in SEM. Notably, in this design and the associated gaseous electron amplification, the product p·d is an independent parameter, so that there is a wide range of values of pressure and electrode geometry which can be described by the same characteristics. The consequence of this analysis is that the secondary electrons are possible to detect in a gaseous environment even at high pressures, depending on the engineering efficacy of any given instrument.
As a further characteristic of the GDD, a gaseous scintillation avalanche also accompanies the electron avalanche and, by detection of the light produced with a photo-multiplier, corresponding SE images can be routinely made. The frequency response of this mode has allowed the use of true TV scanning rates. This mode of the detector has been employed by a latest generation of commercial instruments.
The novel GDD has become possible first in the ESEM and has produced a practically 100% SE collection efficiency not previously possible with the Everhadt-Thornley SE detector where the free trajectories of electrons in vacuum cannot all be bent towards the detector. As is further explained below, backscattered electrons can also be detected by the signal-gas interactions, so that various parameters of this generalized gaseous detector must be controlled to separate the BSE component out of the SE image. In this connection, some workers and the manufacturer have taken care to produce nearly pure SE images with their detectors, to which they have referred as ESD (environmental secondary detector) and GSED (gaseous secondary electron detector).
The backscattered electrons are conventionally associated with those electrons emanating from the beam-specimen interaction by having energies greater than 50 eV up to the primary beam energy for reflected electrons. For the detection and imaging with these electrons, scintillating and solid state materials have been used in the SEM. These materials have been adapted and used also in ESEM in addition to the use of the GDD for BSE detection and imaging.
Gaseous detection device
The BSE operate in the gaseous volume between the electrodes of the GDD and generate additional ionization and avalanche amplification. There is an inner volume where the secondary electrons dominate with small or negligible BSE contribution, whilst the outer gaseous volume is acted upon mainly by the BSE. It is possible to separate the corresponding detection volumes so that near pure BSE images can be made with the GDD. The relationship of relative strength of the two signals, SE and BSE, has been worked out by detailed equations of charge distribution in the ESEM. The analysis of plane electrodes is essential in understanding the principles and requirements involved and by no means indicate the best choice of electrode configuration, as discussed in the published theory of the GDD.
Despite the above developments, devoted BSE detectors in the ESEM have played an important role, since the BSE remain a most useful detection mode yielding information not possible to obtain with SE. The conventional BSE detection means have been adapted to operate in the gaseous conditions of the ESEM. The BSE having a high energy are self-propelled to the corresponding detector without significant obstruction by the gas molecules. Already, annular or quadrant solid-state detectors have been employed for this purpose but their geometry is not easily adaptable to the requirements of ESEM for optimum operation. As a result, no much use has been reported of these detectors on genuine ESEM instruments at high pressure. However, plastic scintillating materials being easily adaptable have been used for BSE and made to measure according to the strictest requirements of the system. Such work culminated in the use of a pair of wedge-shaped detectors saddling a conical PLA1 and abutting to its rim, so that the dead detection space is reduced to a minimum, as shown in the accompanying figure of optimum BSE detectors. The photon conduction is also optimized by the geometry of the light pipes, whilst the pair of symmetrical detectors allow the separation of topography (signal subtraction) and atomic number contrast (signal addition) of the specimen surface to be displayed with the best ever signal-to-noise-ratio. This scheme has further allowed the use of color by superimposing various signals in a meaningful way. These simple but special detectors became possible in the conditions of ESEM, since bare plastic does not charge by the BSE. However, a very fine wire mesh with appropriate spacing has been proposed as a GDD when gas is present and to conduct negative charge away from the plastic detectors when the gas is pumped out, towards a universal ESEM. Furthermore, since the associated electronics involve a photomultiplier with a wide frequency response, true TV scanning rates are readily available. This is an essential attribute to maintain with an ESEM that enables the examination of processes in situ in real time. In comparison, no such imaging has been reported with the electron avalanche mode of the GDD yet.
The use of scintillating BSE detectors in ESEM is compatible with the GDD for simultaneous SE detection, in one way by replacing the top plane electrode with a fine tip needle electrode (detector), which can be easily accommodated with these scintillating BSE detectors. The needle detector and cylindrical geometry (wire) have also been extensively surveyed.
Cathodoluminescence is another mode of detection involving the photons generated by the beam-specimen interaction. This mode has been demonstrated to operate also in ESEM by the use of the light pipes after they were cleared of the scintillating coating previously used for BSE detection. However, not much is known on its use outside the experimental prototype originally tested. Clearly, ESEM is more powerful and meaningful under this detection mode than SEM, since the natural surface of any specimen can be examined in the imaging process. Cathodoluminescence is a materials property, but with various specimen treatments required and other limitations in SEM the properties are obscured or altered or impossible to detect and hence this mode of detection has not become popular in the past. The advent of ESEM with its unlimited potential may provoke more interest in this area too, in the future.
The characteristic elemental X-rays produced also in the ESEM can be detected by the same detectors used in the SEM. However, there is an additional complexity arising from the X-rays produced from the electron skirt. These X-rays come from a larger area than in SEM and the spatial resolution is significantly reduced, since the “background” X-ray signals cannot be simply “suppressed” out of the probe interaction volume. However, various schemes have been proposed to solve this problem. These methods involve spot masking, or the extrapolation technique by varying the pressure and calibrating out the effects of skirt, whereby considerable improvement has been achieved.
In vacuum SEM, the specimen absorbed current mode is used as an alternative mode for imaging of conductive specimens. Specimen current results from the difference of electron beam current minus the sum of SE and BSE current. However, in the presence of gas and the ensuing ionization, it would be problematic to separate this mode of detection out of the generally operating gaseous detection device. Hence this mode, by its definition, may be considered as unsustainable in the ESEM. Shah and Becket assumed the operation of the specimen absorbed current mode if the conductivity of their specimen was assured during the examination of wet botanical samples; in fact, Shah by 1987 still considered the ionisation products in gas by SE and BSE as a formidable obstacle, since he believed that the ionisation did not carry any information about the specimen. However, he later embraced to correct role of gaseous ionisation during image formation.
The electron beam impinging on insulating specimens accumulates negative charge, which creates an electrical potential tending to deflect the electron beam from the scanned point in conventional SEM. This appears as charging artifacts on the image, which are eliminated in the SEM by depositing a conductive layer on the specimen surface prior to examination. In lieu of this coating, the gas in the ESEM being electrically conductive prevents negative charge accumulation. The good conductivity of the gas is due to the ionization it undergoes by the incident electron beam and the ionizing SE and BSE signals. This principle constitutes yet another fundamental deviation from conventional vacuum electron microscopy, with enormous advantages.
Contrast and resolution
As a consequence of the way ESEM works, the resolution is preserved relative to the SEM. That is because the resolving power of the instrument is determined by the electron beam diameter which is unaffected by the gas over the useful travel distance before it is completely lost. This has been demonstrated on the commercial ESEMs that provide the finest beam spots by imaging test specimens, i.e. customarily gold particles on a carbon substrate, in both vacuum and gas. However, the contrast decreases accordingly as the electron probe loses current with travel distance and increase of pressure. The loss of current intensity, if necessary, can be compensated by increasing the incident beam current which is accompanied by an increased spot size. Therefore, the practical resolution depends on the original specimen contrast of a given feature, on the design of the instrument that should provide minimal beam and signal losses and on the operator selecting the correct parameters for each application. The aspects of contrast and resolution have been conclusively determined in the referenced work on the foundations of ESEM. Further, in relation to this, we have to consider the radiation effects on the specimen.
The majority of available instruments vent their specimen chamber to the ambient pressure (100 kPa) with every specimen transfer. A large volume of gas has to be pumped out and replaced with the gas of interest, usually water vapor supplied from a water reservoir connected to the chamber via some pressure regulating (e.g. needle) valve. In many applications this presents no problem, but with those ones requiring uninterrupted 100% relative humidity, it has been found that the removal of ambient gas is accompanied by lowering the relative humidity below the 100% level during specimen transfer. This clearly defeats the very purpose of ESEM for this class of applications. However, such a problem does not arise with the original prototype ESEM using an intermediate specimen transfer chamber, so that the main chamber is always maintained at 100% relative humidity without interruption during a study.. The specimen transfer chamber (tr-ch) shown in the diagram of ESEM gas pressure stages contains a small water reservoir so that the initial ambient air can be quickly pumped out and practically instantaneously replaced with water vapor without going through a limited conductance tube and valve. The main specimen chamber can be maintained at 100% relative humidity, if the only leak of vapor is through the small PLA1, but not during violent pumping with every specimen change. Once the wet specimen is in equilibrium with 100% relative humidity in the transfer chamber, within seconds, a gate valve opens and the specimen is transferred in the main specimen chamber maintained at the same pressure. An alternative approach involving controlled pumping of the main chamber may not solve the problem entirely either because the 100% relative humidity cannot be approached monotonically without any drying, or the process is very slow; inclusion of a water reservoir inside the main chamber means that one cannot lower the relative humidity until after all of the water is pumped out (i.e. a defective control of the relative humidity).
During the interaction of an electron beam with a specimen, changes to the specimen at varying degrees are almost inevitable. These changes, or radiation effects, may or may not become visible both in SEM and ESEM. However, such effects are particularly important in the ESEM claiming the ability to view specimens in their natural state. Elimination of the vacuum is a major success towards this aim, so that any detrimental effects from the electron beam itself require special attention. The best way around this problem is to reduce these effects to an absolute minimum with an optimum ESEM design. Beyond this, the user should be aware of their possible existence during the evaluation of results. Usually, these effects appear on the images in various forms due to different electron beam-specimen interactions and processes.
The introduction of gas in an electron microscope is tantamount to a new dimension. Thus, interactions between electron beam and gas together with interactions of gas (and its byproducts) with specimen usher a new area of research with as yet unknown consequences. Some of these may at first appear disadvantageous but later overcome, others may yield unexpected results. The liquid phase in the specimen with mobile radicals may yield a host of phenomena again advantageous or disadvantageous.
The presence of gas around a specimen creates new possibilities unique to ESEM: (a) Hydrated specimens can be examined since any pressure greater than 609 Pa allows water to be maintained in its liquid phase for temperatures above 0 °C, in contrast to the SEM where specimens are desiccated by the vacuum condition. (b) Electrically non-conductive specimens do not require the preparation techniques used in SEM to render the surface conductive, such as the deposition of a thin gold or carbon coating, or other treatments, techniques which also require vacuum in the process. Insulating specimens charge up by the electron beam making imaging problematic or even impossible. (c) The gas itself is used as a detection medium producing novel imaging possibilities, as opposed to vacuum SEM detectors. (d) Plain plastic scintillating BSE detectors can operate uncoated without charging. Hence, these detectors produce the highest possible signal-to-noise-ratio at the lowest possible accelerating voltage, because the BSE do not dissipate any energy in an aluminium coating used for the vacuum SEM.
As a result, specimens can be examined faster and more easily, avoiding complex and time consuming preparation methods, without modifying the natural surface or creating artifacts by the preceding preparation work, or the vacuum of the SEM. Gas/liquid/solid interactions can be studied dynamically in situ and in real time, or recorded for post processing. Temperature variations from subzero to above 1000 °C and various ancillary devices for specimen micro-manipulation have become a new reality. Biological specimens can be maintained fresh and live. Therefore, ESEM constitutes a radical breakthrough from conventional electron microscopy, where the vacuum condition precluded the advantages of electron beam imaging becoming universal.
The main disadvantage arises from the limitation of the distance in the specimen chamber over which the electron beam remains usable in the gaseous environment. The useful distance of the specimen from the PLA1 is a function of accelerating voltage, beam current, nature and pressure of gas, and of the aperture diameter used. This distance varies from around 10 mm to fraction of a millimeter as the gas pressure may vary from low vacuum to one atmosphere. For an optimum operation, both the manufacturer and the user must conform, in the design and operation, to satisfy this fundamental requirement. Furthermore, as the pressure can be lowered to a very low level, the ESEM will revert to a typical SEM operation without the above disadvantage. Therefore, one may trade-off the ESEM disadvantage with the SEM advantages/disadvantages operating in vacuum. A reconciliation of all these disadvantages and advantages can be attained by a properly designed and operated universal ESEM.
Concomitant with the limitation of useful specimen distance is the minimum magnification possible, since at very high pressure the distance becomes so small that the field of view is limited by the PLA1 size. In the very low magnification range of SEM, overlapping the upper magnification of a light microscope, the superior field is limited to a varying degree by the ESEM mode. The degree of this limitation strongly depends on instrument design.
As X-rays are also generated by the surrounding gas and also come from a larger specimen area than in SEM, special algorithms are required to deduct the effects of gas on the information extracted during analysis.
The presence of gas may yield unwanted effects in certain applications, but the extent of these will only become clear as further research and development is undertaken to minimize and control radiation effects.
No commercial instrument is as yet (by 2009) available in conformity with all the principles of an optimum design, so that any further limitations listed are characteristic of the existing instruments and not of the ESEM technique, in general.
Some representative applications of ESEM are in the following areas:
An early application involved the examination of fresh and living plant material including a study of Leptospermum flavescens. The advantages of ESEM in studies of microorganisms and a comparison of preparation techniques have been demonstrated..
Medicine and medical
In conservation science, it is often necessary to preserve the specimens intact or in their natural state.
ESEM studies have been performed on fibers in the wool industry with and without particular chemical and mechanical treatments.. In cement industry, it is important to examine various processes in situ in the wet and dry state.
Studies in-situ can be performed with the aid of various ancillary devices. These have involved hot stages to observe processes at elevated temperatures, microinjectors of liquids and specimen extension or deformation devices.
General materials science
The ESEM has appeared under different manufacturing brand names. The term ESEM is a generic name first publicly introduced in 1980 and afterwards unceasingly used in all publications by Danilatos and almost all users of all ESEM type instruments. The ELECTROSCAN ESEM trademark was obtained intermittently until 1999, when it was allowed to lapse. The word “environmental” was originally introduced in continuation to the prior (historical) use of “environmental” cells in transmission microscopy, although the word “atmospheric” has also been used to refer to an ESEM at one atmosphere pressure (ASEM) but not with any commercial instruments. Other competing manufacturers have used the terms “Natural SEM” (Hitachi), “Wet-SEM” (ISI), “Bio-SEM” (short-lived, AMRAY), “VP-SEM” (variable-pressure SEM; LEO/Zeiss-SMT), “LVSEM” (low-vacuum SEM, often also denoting low-voltage SEM; JEOL), all of which seem to be transient in time according to prevailing manufacturing schedules. Until recently, all these names referred to instruments operating up to about 100 Pa and with BSE detectors only. Lately, the Zeiss-SMT VP-SEM has been extended to higher pressure together with a gaseous ionization or gaseous scintillation as the SE mechanism for image formation. Therefore, it is improper to identify the term ESEM with one only brand of commercial instrument in juxtaposition to other competing commercial (or laboratory) brands with different names, as some confusion may arise from past use of trademarks.
Similarly, the term GDD is generic covering the entire novel gaseous detection principle in ESEM. The terms ESD and GSED, in particular, have been used in conjunction with a commercial ESEM to denote the secondary electron mode of this detector.
- ^ Ardenne M und Beischer D (1940). "Untersuchung von Metalloxyd-rauchen mit dem Universal-Elektronenmikroskop". Zeits. F. Elektrochem. 46: 270–277.
- ^ Abrams I M and McBain J W (1944). "A closed cell for electron microscopy". Journal of Applied Physics 15: 607–609. doi:10.1063/1.1707475.
- ^ Stoyanova I G (1961). "Use of gas microcells in electron microscopy". Akademiya Nauk SSSR Isvestiya, ser. Fizicheskaya 25: 715–721.
- ^ Swif J A and Brown A C (1970). "An environmental cell for the examination of wet biological specimens at atmospheric pressure by transmission scanning electron microscopy". J. Phys. E 3 (11): 924–926. doi:10.1088/0022-3735/3/11/426. PMID 5483870.
- ^ Parsons D F, Matricardi V R, Moretz R C and Turner J N (1974). "Electron microscopy and diffraction of wet unstained and unfixed biological objects". Adv. Biol. Med. Phys. 15 (0): 161–271. PMID 4135010.
- ^ Lane, W.C. (1970). The environmental control stage. Scanning Electron Microsc.. pp. 43–48.
- ^ Shah JS (1977). Improvements in or relating to specimen stages for electron beam instruments. GB Patent No. 1477458.
- ^ a b Shah, J; Beckett, A (1979). "A preliminary evaluation of moist environment ambient temperature scanning electron microscopy". Micron (1969) 10: 13. doi:10.1016/0047-7206(79)90015-3.
- ^ Spivak GV, Rau EI, Karelin NM, Mishustina IE (1977). Scanning electron microscopy of moist, live, and frozen objects. Izv. Akad. Nauk SSSR, Ser. Fiz. 41, 11:2238–2251 (Russian).
- ^ Robinson, V.N.E. (1974). "A wet stage modification to a scanning electron microscope". 8th Int. Congr. El. Microsc., Australian Academy of Science II: 50–51.
- ^ Danilatos, G.D., and Robinson, V.N.E. (1979). "Principles of scanning electron microscopy at high specimen pressures". Scanning 2: 72–82. http://www.danilatos.com/principles/pr72.html.
- ^ Danilatos, G.D. (1981). "Design and construction of an atmospheric or environmental SEM (part 1)". Scanning 4: 9–20. http://www.danilatos.com/part1/parti09.html.
- ^ Danilatos, G.D., and Postle, R. (1983). "Design and construction of an atmospheric or environmental SEM (part 2)". Scanning 14: 41–52. http://www.danilatos.com/part2/partii41.html.
- ^ a b c d Danilatos, G.D. (1985). "Design and construction of an atmospheric or environmental SEM (part 3)". Scanning 7: 26–42. http://www.danilatos.com/part3/partiii26.html.
- ^ Danilatos, G.D. (1990). "Design and construction of an environmental SEM (part 4)". Scanning 12: 23–27. http://www.danilatos.com/part4/partiv23.html.
- ^ Danilatos, G.D. (1988). Foundations of Environmental Scanning Electron Microscopy. Advances in Electronics and Electron Physics. 71. Academic Press. pp. 109–250. ISBN 0120146711. http://books.google.com/?id=virp-xnk_08C&pg=PA109.
- ^ a b c d Danilatos, G.D. (1990). "Theory of the Gaseous Detector Device in the ESEM". Advances in Electronics and Electron Physics. 78. Academic Press. pp. 1–102. http://www.danilatos.com/gdd/gdd001.html.
- ^ History of Electron Microscopy, 1980s
- ^ J.F. Mancuso, W.B. Maxwell, G.D. Danilatos U.S. Patent 4,785,182 filed May 21, 1987. "Secondary electron detector for use in a gaseous atmosphere"
- ^ G.D. Danilatos "Method and apparatus for an atmospheric scanning electron microscope" U.S. Patent 4,596,928 filed May 14, 1984
- ^ G.D. Danilatos "Multipurpose gaseous detector device for electron microscope" U.S. Patent 4,992,662 filed Sep. 13, 1989
- ^ G.D. Danilatos, G.C. Lewis "Integrated electron optical/differential pumping/imaging signal detection system for an environmental scanning electron microscope " U.S. Patent 4,823,006 filed Feb. 19, 1988
- ^ G.D. Danilatos "Electron detector for use in a gaseous environment" U.S. Patent 4,897,545 filed October 14, 1988
- ^ a b History of Electron Microscopy 1990s
- ^ Danilatos, G. D. (1993). "Bibliography of environmental scanning electron microscopy". Microscopy Research and Technique 25 (5–6): 529. doi:10.1002/jemt.1070250526. PMID 8400449. http://www.danilatos.com/MRTDAN1.pdf.
- ^ Scott Warwick Morgan (2005). Gaseous secondary electron detection and cascade amplification in the environmental scanning electron microscope. Ph.D. Thesis, University of Technology, Sydney, Australia.]
- ^ a b Danilatos GD (1997). PL Gai. ed. Environmental Scanning Electron Microscopy. In-Situ Microscopy in Materials Research. Kluwer Academic Publishers, Dordrecht. pp. 14–44. http://www.danilatos.com/kluver.pdf.
- ^ Danilatos GD (2000). "Direct simulation Monte Carlo study of orifice flow. Rarefied Gas Dynamics: 22nd Intern. Symp., Sydney, (Eds. TJ Bartel and MA Gallis)". AIP Conference Proceedings 585: 924–932. doi:10.1063/1.1407658. http://www.danilatos.com/orifice_flow/orifice924.html.
- ^ a b c d e Danilatos, G.D. (2009). "Optimum beam transfer in the environmental scanning electron microscope". Journal of Microscopy 234 (1): 26–37. doi:10.1111/j.1365-2818.2009.03148.x. PMID 19335454.
- ^ Danilatos GD (2001). "Electron beam loss at the high-vacuum-high-pressure boundary in the environmental scanning electron microscope". Microsc. and Microanal 7: 397–406. http://www.danilatos.com/beamloss/beamloss397.html.
- ^ a b Danilatos 1988, pp. 138–170
- ^ Danilatos 1988, p. 158
- ^ Danilatos, G.D. (1992). "Secondary-electron imaging by scintillating gaseous detection device". Proc. 50th Annual Meeting EMSA (Eds. GW Bailey, J Bentley and JA Small) (San Francisco Press): 1302–1303. http://www.danilatos.com/scintSE.pdf.
- ^ Collins SP, Pope RK, Scheetz RW, Ray RI, Wagner Pa (1993). "Advantages of environmental scanning electron microscopy in studies of microorganisms". Microsc. Res. Technique 25 (5–6): 398–405. doi:10.1002/jemt.1070250508. PMID 8400431.
- ^ Yung YC and Bhushan B (2007). "Wetting behaviour during evaporation and condensation of water microdroplets on superhydrophobic patterned surfaces". Journal of Microscopy 229 (Pt 1): 127–140. doi:10.1111/j.1365-2818.2007.01875.x. PMID 18173651.
- ^ Danilatos, G.D. (1990). "Equations of charge distribution in the ESEM". Scanning Microscopy 4 (4): 799–823. http://www.danilatos.com/eqs/Eq799s.html.
- ^ Danilatos, G.D. (1986). "Colour micrographs for backscattered electron signals in the SEM". Scanning 8: 9–18. http://www.danilatos.com/scancol/scancol09.html.
- ^ Danilatos, G.D. (1993). "Universal ESEM". Proc. 51st Annual Meeting MSA, (Eds. GW Bailey and LC Rieder) (San Francisco Press): 786–787. http://www.danilatos.com/UniESEM/UniESEM786.html.
- ^ Danilatos, G.D. (1986). "Cathodoluminescence and gaseous scintillation in the environmental SEM". Scanning 8: 279–284. http://www.danilatos.com/scintillation/scint279.html.
- ^ Bolon, R.B., Roberstson, C.D. (1990). "X-ray and microstructural ESEM analysis of non conducting materials in gaseous environments". Scanning 90 Abstracts, FACMS Inc.: 80–81.
- ^ Bolon, R.B. (1991). "ESEM, the technique and application to materials characterization. Proc. Scanning '91". Scanning 13, Suppl. I: 86–87.
- ^ Bolon, R.B. (1991). D.G. Howitt. ed. X-ray microanalysis in the ESEM. Microbeam Analysis. San Francisco Press. pp. 199–200.
- ^ Danilatos, G.D. (1994). "Environmental scanning electron microscopy and microanalysis". Microchimica Acta 114/115: 143–155. doi:10.1007/BF01244538. http://www.danilatos.com/microanalysis/anal143.html.
- ^ Shah J (1987). Electronmicroscopy comes to life. No. 208/1987/SPECTRUM/6, published by Central Office of Information obtainable through British Embassy, High Commission or Consulate
- ^ Farley AN and Shah JS (1988). Inst. Phys. Conf. Ser. No 93, Vol. 1(241–242).
- ^ Moncrieff, D.A., Robinson, V.N.E., and Harris, L.B. (1978). "Charge neutralisation of insulating surfaces in the SEM by gas ionisation". J. Phys. D 11: 2315–2325. doi:10.1088/0022-3727/11/17/002.
- ^ Danilatos, G.D. (1993). "Environmental scanning electron microscope-some critical issues". Scanning Microscopy International Supplement 7: 57–80. http://www.danilatos.com/Critical_issues/crit_issues57.html.
- ^ a b Cameron, R. E. & Donald, A. M. (1994). "Minimizing sample evaporation in the environmental scanning electron microscope". Journal of Microscopy 173: 227–237.
- ^ Danilatos 1988, pp. 238–240
- ^ Danilatos, G.D. (1986). "Beam-radiation effects on wool in the ESEM". Proc. 44th Annual Meeting EMSA: 674–675. http://www.danilatos.com/Radiation/Radiation674.html.
- ^ Danilatos, G.D. (1981). "The examination of fresh or living plant material in an environmental scanning electron microscope". J. Microsc. 121: 235–238. http://www.danilatos.com/plants/plants235.html.
- ^ Collins SP, Pope RK, Sheetz RW, Ray RI and Wagner PA (1993). "Advantages of environmental scanning electron microscopy in studies of microorganisms". Microsc. Res. Technique 25 (5–6): 398–405. doi:10.1002/jemt.1070250508. PMID 8400431.
- ^ Uwins PJR, Murray M and Gould RJ (1993). "Effects of four different processing techniques on the microstructure of potatos: Comparison with fresh samples in ESEM". Microsc. Res. Technique 25 (5–6): 312–418. doi:10.1002/jemt.1070250510. PMID 8400433.
- ^ Doehne E and Stulik DC (1990). "Application of the environmental scanning electron microscope to conservation science". Scanning Microscopy 4: 275–286.
- ^ Danilatos, G.D., and Brooks, J.H. (1985). "Environmental SEM in wool research – present state of the art". Proc. 7th Int. Wool Textile Research Conference, Tokyo, I: 263–272. http://www.danilatos.com/woolesem.pdf.
- ^ Lange, D.A., Sujata, K., and Jennings, H.M. (1990). "Characterization of cement-water systems". Scanning 90: 75–76.
- ^ Baker, J.C., Uwins, P.J.R., and Mackinnon, I.D.R. (1993). "ESEM study of authigenic chlorite acid sensitivity in sandstone reservoirs". Journal of Petroleum Science and Engineering 8: 269–277. doi:10.1016/0920-4105(93)90004-X.
- ^ Koopman N (1993). "Application of ESEM to Fluxless soldering". Microsc. Res. Technique 25 (5–6): 493–502. doi:10.1002/jemt.1070250521. PMID 8400444.
- ^ Danilatos, G.D., and Brancik, J.V. (1986). "Observation of liquid transport in the ESEM". Proc. 44th Annual Meeting EMSA: 678–679. http://www.danilatos.com/microinjector/microinjector.pdf.
- ^ Diridollou S, Hallegot P, Mainwaring P, Leroy F, Barbosa VH and Zaluzec NJ (2007). "In-Situ Tensile Testing of Hair Fibers in An Environmental Scanning Electron Microscope (ESEM)". Microsc Microanal 13(Suppl 2): 1490CD–1491CD. doi:10.1017/S1431927607071917.
- ^ Little, B., Wagner, P., Ray, R.I., Pope, R. and Scheetz, R. (1991). "Biofilms: Artifacts introduced during SEM preparation evaluated by ESEM.". J. Industrial Microbiology 8: 213–222. doi:10.1007/BF01576058.
- ^ Robin E de la Parra A (1993). "method to detect variations in the wetting properties of microporous polymer membranes". Microsc. Res. Technique 25 (5–6): 362–373. doi:10.1002/jemt.1070250504. PMID 8400427.
- ^ Gilbert LC and Doherty RE (1993) (1993). "Using ESEM and SEM to compare the performance of dentin conditioners". Microsc. Res. Technique 25 (5–6): 419–423. doi:10.1002/jemt.1070250511. PMID 8400434.
- ^ Hoyberg K and Kruza KG (1993). "Application of environmental scanning electron microscope in the development of detergent and personal care". Microsc. Res. Technique 25 (5–6): 424–428). doi:10.1002/jemt.1070250512. PMID 8400435.
- ^ Danilatos, G.D. (1980). "An atmospheric scanning electron microscope (ASEM)". Scanning 3: 215–217. http://www.danilatos.com/ASEM/ASEM215.html.
- ^ Danilatos, G.D., Robinson, V.N.E., and Postle, R. (1980). "An environmental scanning electron microscope for studies of wet wool fibres". Proc. Sixth Quinquennial Wool Textile Research Conference, Pretoria, II: 463–471. http://www.danilatos.com/ESEM_Pretoria/pretoria462.html.
- ^ M. Yamada and K. Kuboki. "Development of natural SEM and some applications". Hitachi. http://actamicroscopica.ivic.ve/images1/2193-01.pdf.
- ^ Chance DL and Mawhinney TP (2006). "Employing “Wet SEM” Imaging to Study Co-Colonizing Mucosal Pathogens". Microscopy and Microanalysis 12 (Suppl. 02): 308–309. doi:10.1017/S1431927606063367.
- ^ Myers BD, Pan Z and Dravid VP (2008). Beam skirting effects on energy deposition profile in VP-SEM. Microscopy and Microanalysis. 14 (Suppl. 2). pp. 1208–1209.
- ^ Tinkara Kopar and Vilma Ducmana (2007). Low-vacuum SEM analyses of ceramic tiles with emphasis on glaze defects characterisation Materials Characterization. 58. pp. 1133–1137.
- ^ Pawley JB. "LVSEM for High Resolution Topographic and Density Contrast Imaging". Aadvances in electonics and electron physics 83: 203–274.
- Danilatos, G.D. (1988). "Foundations of Environmental Scanning Electron Microscopy". In Hawkes, Peter W. Advances in Electronics and Electron Physics. 71. Academic Press. pp. 109–250. ISBN 0120146711. http://books.google.com/?id=virp-xnk_08C&pg=PA109.
Gallery of ESEM images
The following are examples of images taken using an environmental scanning electron microscope (ESEM).
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