EP0069393A1 - Method for the early detection of carbonic fires in recipients containing dust of brown coal by detection of methane - Google Patents
Method for the early detection of carbonic fires in recipients containing dust of brown coal by detection of methane Download PDFInfo
- Publication number
- EP0069393A1 EP0069393A1 EP82106076A EP82106076A EP0069393A1 EP 0069393 A1 EP0069393 A1 EP 0069393A1 EP 82106076 A EP82106076 A EP 82106076A EP 82106076 A EP82106076 A EP 82106076A EP 0069393 A1 EP0069393 A1 EP 0069393A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- dust
- fires
- detection
- gas
- gases
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000000428 dust Substances 0.000 title claims abstract description 40
- 239000003077 lignite Substances 0.000 title claims abstract description 29
- 238000001514 detection method Methods 0.000 title claims abstract description 16
- 238000000034 method Methods 0.000 title claims description 12
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title claims description 8
- 239000007789 gas Substances 0.000 claims abstract description 42
- 229930195733 hydrocarbon Natural products 0.000 claims abstract description 7
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 7
- 239000001257 hydrogen Substances 0.000 claims abstract description 6
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 6
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims abstract description 5
- 239000000523 sample Substances 0.000 claims description 15
- 239000004215 Carbon black (E152) Substances 0.000 claims 2
- 230000015572 biosynthetic process Effects 0.000 abstract description 6
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 18
- 229910002091 carbon monoxide Inorganic materials 0.000 description 18
- 241000273930 Brevoortia tyrannus Species 0.000 description 9
- 238000002474 experimental method Methods 0.000 description 7
- 238000012360 testing method Methods 0.000 description 6
- 238000003763 carbonization Methods 0.000 description 3
- 238000005259 measurement Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- OFBQJSOFQDEBGM-UHFFFAOYSA-N n-pentane Natural products CCCCC OFBQJSOFQDEBGM-UHFFFAOYSA-N 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 125000000524 functional group Chemical group 0.000 description 2
- 238000009533 lab test Methods 0.000 description 2
- 239000004484 Briquette Substances 0.000 description 1
- OTMSDBZUPAUEDD-UHFFFAOYSA-N Ethane Chemical compound CC OTMSDBZUPAUEDD-UHFFFAOYSA-N 0.000 description 1
- 241000220317 Rosa Species 0.000 description 1
- 230000006978 adaptation Effects 0.000 description 1
- 230000004323 axial length Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 239000001273 butane Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 230000001413 cellular effect Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000007857 degradation product Substances 0.000 description 1
- -1 ethane (C 2 H 6 ) Chemical class 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 238000011005 laboratory method Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- IJDNQMDRQITEOD-UHFFFAOYSA-N n-butane Chemical compound CCCC IJDNQMDRQITEOD-UHFFFAOYSA-N 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000001294 propane Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Images
Classifications
-
- G—PHYSICS
- G08—SIGNALLING
- G08B—SIGNALLING OR CALLING SYSTEMS; ORDER TELEGRAPHS; ALARM SYSTEMS
- G08B17/00—Fire alarms; Alarms responsive to explosion
- G08B17/10—Actuation by presence of smoke or gases, e.g. automatic alarm devices for analysing flowing fluid materials by the use of optical means
- G08B17/117—Actuation by presence of smoke or gases, e.g. automatic alarm devices for analysing flowing fluid materials by the use of optical means by using a detection device for specific gases, e.g. combustion products, produced by the fire
Definitions
- the invention relates to a method for the detection of smoldering fires in containers containing lignite dust, with the aid of which certain gases which form in the lignite dust and possibly escape therefrom can be measured with a suitable detector and used as "indicator gases" for early detection of smoldering fire.
- the method of measuring the carbon monoxide (CO) formed underground is used successfully for the early detection of fires or smoldering fires in hard coal.
- CO carbon monoxide
- BK dust brown coal dust
- the carbon monoxide content of the gas volume above the bed is currently also being determined.
- the results of this method are not entirely clear, since CO and carbon dioxide (C0 2 ) occur as degradation products of functional groups in brown coal even when the ignition temperature of the brown coal has not yet been reached.
- CO or C0 2 can, however, also occur as a decomposition product of functional groups in lignite if the ignition temperature of the coal has not yet been reached. This fact makes for practice, e.g. B. for a dust bunker, the specification of a limit concentration is necessary, from which the probability of the existence of a smoldering fire in a lignite dust bed is given.
- H 2 and CH 4 only appear when a smoldering fire has occurred in the bed.
- This detection of a smoldering fire by detecting H 2 and CH 4 is, in addition to the previous early detection via CO, a further developed method for the detection of smoldering fires in lignite dust. It is not absolutely necessary to state a limit concentration for H 2 and CH 4 , since these gases are specific for the presence of a smoldering fire. However, since it is difficult to measure the hydrogen content under operational conditions, the measurement of CH 4 is particularly suitable for the detection of smoldering fires.
- a detector for detecting the gases in question is attached to the container containing lignite dust in such a way that it either probes into the discharge nozzle of the loading device engages container or in the interior above the emptying nozzle, wherein the probe can reach both in the area of the dumping height and in the gas space above the dumping height.
- a plurality of such probes can also be provided spaced apart from one another and / or distributed in the circumferential direction over the length of the container.
- the probes can either have detectors themselves or can be provided with connections which supply a mostly small amount of gas required for measurement to a suitable device, for example a gas chromatograph or other gas analyzer.
- a suitable device for example a gas chromatograph or other gas analyzer.
- the method according to the invention was first tested in the laboratory. For this purpose, smoldering fires were generated in a dust bed by heating the bed and introducing air.
- the aim of the laboratory method was to compare the composition of the gases formed by a smoldering fire in the lignite dust with a gas that is formed when there is no smoldering fire.
- the temperature in the bed was measured using thermocouples. After the above-mentioned temperatures in the bed had been reached, preheated air was introduced into the BK dust bed over a period of approximately 7.5 hours. The air flow rate was approx. 0.1 l / min.
- the composition of the gas leaving the test apparatus was determined by gas chromatography with regard to H 21 CH 4 , CO and CO 2 .
- FIG. 1 The results of the tests are shown in a diagram in FIG. 1.
- the representation is not to scale, and in view of the relatively low values for hydrogen and methane.
- the diagram shows the proportions of the individual gas components H 2 ' CH 4' CO and C0 2 in volume percent (vol.%) Depending on the test temperature.
- H 2 and CH 4 While the gas components CO and C0 2 are already present at temperatures below the ignition temperature, H 2 and CH 4 only appear when the ignition temperature is reached in order to reach a maximum value relatively quickly and then decrease in concentration again. The relatively pronounced increase in the concentration of gases H 2 and CH 4 is therefore particularly well suited for the early detection of a smoldering fire.
- the most suitable detection is the gas which has the highest concentration in the carbonization gas.
- a smoldering fire detection of the gases CO and CO 2 which are present in higher concentrations, is problematic in practice, since a limit concentration must be defined, which, as stated, again depends on many individual influences.
- the "indicator gases” H 2 and CH 4 and higher hydrocarbons can largely be used specifically for smoldering fire identification. Due to the higher concentration of H 2 in the carbonization gas, this gas should be more suitable than CH 4 . However, if a selection is made between the two "indicator gases” after practical determination or identification, only CH 4 remains as the “indicator gas” of choice.
- a lignite dust bunker 1 narrows in its lower part to form a funnel 2 which opens into an outlet element 3.
- This outlet member 3 consists in detail of a cellular wheel 4 with drive 5 and a bellows 6 for adaptation to different customers.
- the dust bunker 1 at the level of its funnel 2 has a ring line 7 for supplying compressed air, so that the bed inside the dust bunker can be loosened if necessary.
- a CH 4 -IR gas analyzer (not shown) reaches with a probe 8 into the emptying neck of the container.
- three identical probes 9 are attached at almost the same distance and possibly distributed in the circumferential direction over the axial length of the container, the probes projecting both into the area of the dust bed 10 and into the gas space 11 above the bed. These probes are also connected to a CH 4 -IR gas analyzer. Between probe 8 or probes 9 and the CH 4 -IR-. Gas analyzers are built-in dust filters (not shown) to protect the measuring devices.
- the basic CH 4 value determined in probe 9 in the bunker was 5-33 ppm
- the basic CH 4 value measured in probe 8 when the bunker was emptied was approximately 10 ppm.
Landscapes
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Business, Economics & Management (AREA)
- Emergency Management (AREA)
- Physics & Mathematics (AREA)
- General Physics & Mathematics (AREA)
- Sampling And Sample Adjustment (AREA)
- Investigating Or Analyzing Materials Using Thermal Means (AREA)
- Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
- Investigating Or Analysing Materials By Optical Means (AREA)
- Investigating Or Analyzing Materials By The Use Of Fluid Adsorption Or Reactions (AREA)
- Processing Of Solid Wastes (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
Abstract
Description
Die Erfindung betrifft ein Verfahren zum Nachweis von Schwlebränden in Braunkohlenstaub enthaltenden Behältern, mit dessen Hilfe bestimmte, sich in dem Braunkohlenstaub bildende und ggf. draus austretende Gase mit einem geeigneten Detaktor gemessen und als "Indikator-Gase" zur Schwelbrand-Früherkennung verwendet werden können.The invention relates to a method for the detection of smoldering fires in containers containing lignite dust, with the aid of which certain gases which form in the lignite dust and possibly escape therefrom can be measured with a suitable detector and used as "indicator gases" for early detection of smoldering fire.
Für die Früherkennung von Bränden oder Schwelbränden in der Steinkohle wird die Methode der Messung des dabei gebildeten Kohlenmonoxids (CO) unter Tage erfolgreich angewandt. Zur Schwelbrandfrüherkennung während der Lagerung von Braunkohlenstaub (BK-Staub) in Bunkern wird gegenwärtig ebenfalls der Kohlenmonoxid-Gehalt des über der Schüttung befindlichen Gasvolumens bestimmt. Die Ergebnisse dieser Methode sind jedoch nicht vollkommen eindeutig, da CO und Kohlendioxid (C02) als Abbauprodukte funktioneller Gruppen der Braunkohle auch dann auftreten, wenn die Zündtemperatur der Braunkohle noch nicht erreicht ist.The method of measuring the carbon monoxide (CO) formed underground is used successfully for the early detection of fires or smoldering fires in hard coal. For early detection of smoldering fire during the storage of brown coal dust (BK dust) in bunkers, the carbon monoxide content of the gas volume above the bed is currently also being determined. However, the results of this method are not entirely clear, since CO and carbon dioxide (C0 2 ) occur as degradation products of functional groups in brown coal even when the ignition temperature of the brown coal has not yet been reached.
Für die sichere Lagerung, den Transport und den Umfang mit Braunkohlenstaub ist es jedoch wegen dessen Eigenschaft der leichten Entzündbarkeit bzw. Neigung zur Selbstentzündung unbedingt erforderlich, das Vorhandensein von Schwelbränden im Staub möglichst frühzeitig zu erkennen. Die Frühzeitigkeit der Erkennung ist besonders geboten, da einmal in Brand geratener Braunkohlenstaub nur mit Mühe wieder gelöscht werden kann.For safe storage, transport and the extent of lignite dust, however, it is due to its property of easy flammability or tendency to Self-ignition is absolutely necessary to detect the presence of smoldering fires in the dust as early as possible. Early detection is particularly advisable, since lignite dust that has caught fire can only be extinguished with difficulty.
Die Zunahme der kommerziellen Nutzung von Braunkohlenstaub in den letzten Jahren hat es erforderlich gemacht, den Staub auf Vorrat zu lagern, zwischenzulagern und meistens auch über bisweilen weite Strecken zu transportieren.The increase in the commercial use of lignite dust in recent years has made it necessary to store the dust in stock, to store it temporarily and, in most cases, to transport it over long distances.
Die Einhaltung der notwendigen Sicherheitsbestimmungen führte zur Formulierung der der Erfindung zugrunde liegenden Aufgabe, wonach eine Methode anzugeben ist, die das Vorhandensein von Schwelbränden innerhalb von in Behältern befindlichem Braunkohlenstaub zu einem möglichst frühen Zeitpunkt und mit grosser betrieblicher Sicherheit gewährleistet.Compliance with the necessary safety regulations led to the formulation of the object on which the invention is based, according to which a method is to be specified which guarantees the presence of smoldering fires within brown coal dust contained in containers at the earliest possible point in time and with great operational safety.
Bei der Beobachtung der Schüttungen von Braunkohlenstaub wurde nun gefunden, dass darin Wasserstoff (H2) bzw. Methan (CH4) enthaltende Gase.normalerweise fast überhaupt nicht oder nur in fast nicht mehr nachweisbar geringen Mengen auftreten. Anders verhält es sich mit CO bzw. C02, die stets vorhanden sind.When observing the fillings of lignite dust, it was found that gases containing hydrogen (H 2 ) or methane (CH 4 ) normally do not occur at all or only in small amounts that are almost undetectable. It is different with CO or C0 2 , which are always present.
Grössere Mengen an CO bzw. C02 können sich erst in dem Augenblick bilden, in dem innerhalb der Staubschüttung ein Schwelbrand entsteht.Larger amounts of CO or C0 2 can only form at the moment when a smoldering fire occurs within the bed of dust.
CO bzw. C02 können aber als Abbauprodukt funktioneller Gruppen der Braunkohle auch dann auftreten, wenn die Zündtemperatur der Kohle noch nicht erreicht ist. Dieser Sachverhalt macht für die Praxis, z. B. für einen Staubbunker, die Angabe einer Grenzkonzentration notwendig, ab der die Wahrscheinlichkeit des Vorhandenseins eines Schwelbrandes in einer Braunkohlenstaub-Schüttung gegegeben ist.CO or C0 2 can, however, also occur as a decomposition product of functional groups in lignite if the ignition temperature of the coal has not yet been reached. This fact makes for practice, e.g. B. for a dust bunker, the specification of a limit concentration is necessary, from which the probability of the existence of a smoldering fire in a lignite dust bed is given.
Grundsätzlich ist es so, dass die Werte für Grenzkonzentration an jedem Staubbehälter und für jede Staubsorte unterschiedlich sein und auch noch vom jeweiligen Füllungsgrad eines Behälters abhängen können.It is basically the case that the values for the limit concentration on each dust container and for each dust type are different and can also depend on the respective degree of filling of a container.
Es wurde in Laborversuchen festgestellt, dass H2 und CH4 erst dann auftreten, wenn ein Schwelbrand in der Schüttung entstanden ist. Dieser Nachweis eines Schwelbrandes über eine Detektion von H2 und CH4 ist neben der bisherigen Früherkennung über CO eine weiterentwickelte Methode zur Erkennung von Schwelbränden in Braunkohlenstaub. Die Angabe einer Grenzkonzentration ist für H2 und CH4 nicht unbedingt notwendig, da diese Gase für das Vorhandensein eines Schwelbrandes spezifisch sind. Da jedoch eine Messung des Wasserstoffgehaltes unter betrieblichen Bedingungen schwierig ist, bietet sich die Messung von CH4 zur Detektion von Schwelbränden als besonders geeignet an.It was found in laboratory tests that H 2 and CH 4 only appear when a smoldering fire has occurred in the bed. This detection of a smoldering fire by detecting H 2 and CH 4 is, in addition to the previous early detection via CO, a further developed method for the detection of smoldering fires in lignite dust. It is not absolutely necessary to state a limit concentration for H 2 and CH 4 , since these gases are specific for the presence of a smoldering fire. However, since it is difficult to measure the hydrogen content under operational conditions, the measurement of CH 4 is particularly suitable for the detection of smoldering fires.
Infolgedessen konnte zur Lösung der der Erfindung zugrunde liegenden Aufgabe angegeben werden, dass die Anwesenheit von CH4 und/oder höhere Kohlenwasserstoffe enthaltenden Gasen in Braunkohlenstaub gemessen wird.As a result, to achieve the object on which the invention is based, it was possible to state that the presence of gases containing CH 4 and / or higher hydrocarbons in lignite dust is measured.
Bei einer Vorrichtung zur Durchführung des erfindungsgemässen Verfahrens wird an dem Braunkohlenstaub enthaltenden Behälter ein Detektor zum Aufspüren der in Frage kommenden Gase derart angebracht, dass er mit einer Sonde entweder in den Entleerungsstutzen des Behälters eingreift oder in den Innenraum oberhalb des Entleerungsstutzens, wobei die Sonde sowohl im Bereich der Schütthöhe als auch in den Gasraum oberhalb der Schütthöhe hineingreifen kann. Selbstverständlich können über die Länge des Behälters auch mehrere derartige Sonden im gegenseitigen Abstand voneinander und/oder auch in Umfangsrichtung verteilt vorgesehen sein.In a device for carrying out the method according to the invention, a detector for detecting the gases in question is attached to the container containing lignite dust in such a way that it either probes into the discharge nozzle of the loading device engages container or in the interior above the emptying nozzle, wherein the probe can reach both in the area of the dumping height and in the gas space above the dumping height. Of course, a plurality of such probes can also be provided spaced apart from one another and / or distributed in the circumferential direction over the length of the container.
Die Sonden können entweder selbst Detaktoren aufweisen oder aber mit Anschlüssen versehen sein, welche eine zur Messung erforderliche, meist geringe Gasmenge einem geeigneten Gerät, beispielsweise einem Gaschromatographen oder anderen Gasanalysatoren zuführen.The probes can either have detectors themselves or can be provided with connections which supply a mostly small amount of gas required for measurement to a suitable device, for example a gas chromatograph or other gas analyzer.
Das erfindungsgemässe Verfahren wurde zunächst labormässig erprobt. Hierzu wurden in einer Staubschüttung Schwelbrände dadurch erzeugt, dass die Schüttung aufgeheizt und Luft eingeleitet wurde. Dabei hatte das labormässige Verfahren zum Ziel, die Zusammensetzung der durch einen Schwelbrand im Braunkohlenstaub gebildeten Gase mit einem Gas zu vergleichen, das dann gebildet wird, wenn kein Schwelbrand vorhanden ist.The method according to the invention was first tested in the laboratory. For this purpose, smoldering fires were generated in a dust bed by heating the bed and introducing air. The aim of the laboratory method was to compare the composition of the gases formed by a smoldering fire in the lignite dust with a gas that is formed when there is no smoldering fire.
Bei dem Versuch wruden ca. 1200 bis 1300 g BraunkohlenStaub aus der Produktion einer Brikettfabrik in ein von aussen beheizbares Glasgefäss'geschüttet, welches ein Fassungsvermögen von ca. 2,5 1 aufweist.In the experiment, approximately 1200 to 1300 g of lignite dust from the production of a briquette factory were poured into a glass vessel which can be heated from the outside and which has a capacity of approximately 2.5 l.
Danach wurde der Staub auf die in nachfolgender Tabelle wiedergegebenen Anfangstemperaturen erhitzt:
Die Temperatur in der Schüttung wurde mit Hilfe von Thermoelementen gemessen. Nachdem die oben angegebenen Temperaturen in der Schüttung erreicht waren, wurde vorgewärmte Luft über einen Zeitraum von ungefähr 7,5 Stunden in die BK-Staubschüttung eingeleitet. Der Luftdurchsatz betrug ca. 0,1 l/min. Die Zusammensetzung des die Versuchsapparatur verlassenden Gases wurde gaschromatographisch hinsichtlich H21 CH4, CO und C02 ermittelt.The temperature in the bed was measured using thermocouples. After the above-mentioned temperatures in the bed had been reached, preheated air was introduced into the BK dust bed over a period of approximately 7.5 hours. The air flow rate was approx. 0.1 l / min. The composition of the gas leaving the test apparatus was determined by gas chromatography with regard to H 21 CH 4 , CO and CO 2 .
Während der Versuche 1 bis 3 bildeten sich durch Selbstoxidation, verbunden mit einem raschen Temperaturanstieg in den Staubschüttungen Schwelbrände. Im Verlauf der Versuche 4 bis 6 konnten auch nach 7,5 Stunden Luftzufuhr keine Schwelbrände beobachtet werden. Die die Schüttung verlassenden Gase wurden analysiert; bei den Versuchen 1 - 3 wurde festgestellt, dass H2 und CH4 austraten und der Anteil an CO und CO2 bei Bildung eines Schwelbrandes auf einen Maximalwert anstieg.During
Hohe H2-Konzentrationen wurden jedoch nur im Zusammenhang mit der Ausbildung von Schwelbränden festgestellt, dagegen war bei Abwesenheit eines Schwelbrandes kein H2 nachzuweisen (Versuche 4 - 6). Ein ähnliches Verhalten wie das von H2 konnte auch für CH4 festgestellt werden. Beispielsweise stieg der H2-Gehalt des Schwelgases im Verlauf des Versuches 1 (Anfangstemperatur 172° C) nach 1 h Luftzufuhr von 0 auf 2,16 Vol.%, während der CH4-Gehalt unter den gleichen Bedingungen von 0 auf 0,15 Vol.% anstieg. Wie die Versuche klar bestätigen, ist das Auftreten von höheren H2- und CH4-Konzentrationen im Abgas immer mit der Ausbildung eines Schwelbrandes gekoppelt. Dieses schliesst jedoch nicht vollkommen aus, dass Spuren dieser Gase im Gasvolumen oberhalb grosser Braunkohlenmengen (Bunker) ebensowohl festgestellt werden können.However, high H 2 concentrations were only found in connection with the formation of smoldering fires, whereas no H 2 was found in the absence of a smoldering fire (experiments 4 - 6). A behavior similar to that of H 2 was also found for CH 4 . For example, the H 2 content of the carbonization gas rose in the course of experiment 1 (initial temperature 172 ° C.) after 1 h of air supply from 0 to 2.16% by volume, while the CH 4 content rose from 0 to 0.15% by volume under the same conditions. As the tests clearly confirm, the occurrence of higher H 2 and CH 4 concentrations in the exhaust gas is always coupled with the formation of a smoldering fire. However, this does not completely exclude that traces of these gases in the gas volume above large quantities of lignite (bunkers) can be detected as well.
Die Ergebnisse der Versuche sind in der Fig. 1 in einem Diagramm dargestellt. Die Darstellung ist nicht maßstäblich, und zwar mit Rücksicht auf die im Verhältnis geringen Werte für Wasserstoff und Methan. Das Diagramm zeigt die Anteile der einzelnen Gaskomponenten H2' CH4' CO und C02 in Volumenprozenten (Vol.%) in Abhängigkeit von der Versuchstemperatur.The results of the tests are shown in a diagram in FIG. 1. The representation is not to scale, and in view of the relatively low values for hydrogen and methane. The diagram shows the proportions of the individual gas components H 2 ' CH 4' CO and C0 2 in volume percent (vol.%) Depending on the test temperature.
Alle Kurven zeigen einen im wesentlichen ähnlichen, glockenförmigen Verlauf mit nach oben gerichtetem Scheitelpunkt; von einer bestimmten Versuchstemperatur ab nimmt die Konzentration des jeweiligen Gases stetig zu, um nach Durchschreiten eines Maximalwertes, welcher für jedes untersuchte Gas unterschiedlich ist, wieder leicht abzufallen. Bei der Temperatur von 150° C setzte die Zündung bzw. Bildung eines Schwelbrandes ein; diese Temperatur ist durch eine vertikale, gestrichelte Linie markiert; sie wurde über ein Thermoelement ermittelt. In Abhängigkeit von den bei der Entzündung jeweils vorliegenden Bedingungen, wie Grösse des Behälters, Feuchtigkeitsgehalt des Braunkohlenstaubes und dgl. kann die Zündtemperatur auch grösser oder kleiner sein, so dass man hier von einem Temperaturbereich auszugehen hat, innerhalb dessen die Zündung einsetzt.All curves show an essentially similar, bell-shaped course with an apex pointing upwards; from a certain test temperature, the concentration of the respective gas increases steadily in order to drop slightly again after passing through a maximum value, which is different for each gas examined. At the temperature of 150 ° C the ignition or formation of a smoldering fire started; this temperature is marked by a vertical dashed line; it was determined using a thermocouple. Depending on the conditions at the time of ignition, such as the size of the container, moisture content of the lignite dust and the like, the ignition temperature can also be higher or lower, so that one has to start from a temperature range within which the ignition starts.
Bemerkenswert ist in diesem Zusammenhang in Fig. 1 zu erkennen, dass mit dem Erreichen des für die Zündung massgeblichen Temperaturbereiches die Konzentrationen von CO bzw. C02 ihren Maximalwert erreicht haben bzw. kurz davor stehen, um anschliessend wieder abzunehmen, während die Bildung der "Indikatorgase" H2 bzw. CH4 in diesem Temperaturbereich erst einsetzt und seine Maximalkonzentrationen entsprechend'später erreicht. Dabei konnte beobachtet werden, dass sich die Bildung und das Ansteigen der Konzentration von höherwertigen Kohlenwasserstoffen wie Äthan (C2H6), Propan (C3H8), Butan (C4H10), Pentan (C5H12) usw., solange diese Stoffe gasförmig vorlagen, zu höheren Temperaturbereichen hin verschob. Messungen in solchen Temperaturbereichen können beispielsweise dann von Interesse sein, wenn sich die äusseren Bedingungen, wie z. B. Druck, Feuchtigkeitsgehalt des Braunkohlenstaubes, Volumen des Behälters sowie die Atmosphäre im bzw. am Braunkohlenstaub enthaltenden Behälter geändert haben.It is noteworthy in this connection in FIG. 1 that when the temperature range relevant for the ignition is reached, the concentrations of CO or CO 2 have reached their maximum value or are about to do so, in order to subsequently decrease again, while the formation of the " Indicator gases "H 2 or CH 4 only start in this temperature range and reach their maximum concentrations accordingly later. It was observed that the formation and the increase in the concentration of higher-value hydrocarbons such as ethane (C 2 H 6 ), propane (C 3 H 8 ), butane (C 4 H 10 ), pentane (C 5 H 12 ) etc ., as long as these substances were in gaseous form, shifted to higher temperature ranges. Measurements in such temperature ranges can be of interest, for example, when the external conditions, such as e.g. B. pressure, moisture content of the lignite dust, volume of the container and the atmosphere in or on the lignite dust-containing container have changed.
Während die Gaskomponenten CO und C02 bereits bei Temperaturen unterhalb der Zündtemperatur vorliegen, treten H2 und CH4 erst bei Erreichen der Zündtemperatur auf, um verhältnismässig schnell einen Maximalwert zu erreichen und anschliessend in der Konzentration wieder abzunehmen. Der relativ stark ausgeprägte Konzentrationsanstieg der Gase H2 und CH4 ist daher besonders gut zur Früherkennung eines Schwelbrandes geeignet.While the gas components CO and C0 2 are already present at temperatures below the ignition temperature, H 2 and CH 4 only appear when the ignition temperature is reached in order to reach a maximum value relatively quickly and then decrease in concentration again. The relatively pronounced increase in the concentration of gases H 2 and CH 4 is therefore particularly well suited for the early detection of a smoldering fire.
An sich gilt zwar, dass eine Detektion desjenigen Gases am geeignetsten ist, welches die höchste Konzentration im Schwelgas aufweist. Ein Schwelbrandnachweis über die zwar in höheren Konzentrationen vorliegenden Gase CO und CO2 ist jedoch für die Praxis problematisch, da eine Grenzkonzentration festgelegt werden.muss, die, wie ausgeführt, wiederum von vielen einzelnen Einflüssen abhängt. Die "Indikatorgase" H2 und CH4 sowie höhere Kohlenwasserstoffe hingegen sind weitgehend spezifisch zur Schwelbrandidentifizierung einsetzbar. Aufgrund der höheren Konzentration an H2 im Schwelgas müsste sich dieses Gas eher eignen als CH4. Wird jedoch eine Auswahl zwischen beiden "Indikator-Gasen" nach praxisgerechter Bestimmung oder Identifikation getroffen, so bleibt nur CH4 als "Indikator-Gas" der Wahl übrig.It is true per se that the most suitable detection is the gas which has the highest concentration in the carbonization gas. However, a smoldering fire detection of the gases CO and CO 2 , which are present in higher concentrations, is problematic in practice, since a limit concentration must be defined, which, as stated, again depends on many individual influences. The "indicator gases" H 2 and CH 4 and higher hydrocarbons, on the other hand, can largely be used specifically for smoldering fire identification. Due to the higher concentration of H 2 in the carbonization gas, this gas should be more suitable than CH 4 . However, if a selection is made between the two "indicator gases" after practical determination or identification, only CH 4 remains as the "indicator gas" of choice.
In einem weiteren Versuch wurde die bis dahin labormässige Durchführung des erfindungsgemässen Verfahrens an einem mit Braunkohlenstaub gefüllten Bunker bei Vorliegen eines künstlich erzeugten Schwelbrandes erprobt. Die Anordnung ist in der Fig. 2 dargestellt.In a further experiment the previously laboratory-based implementation of the method according to the invention was tested on a bunker filled with brown coal dust in the presence of an artificially produced smoldering fire. The arrangement is shown in FIG. 2.
Ein Braunkohlenstaubbunker 1 verengt sich in seinem unteren Teil zu einem Trichter 2, der in ein Auslassorgan 3 mündet. Dieses Auslassorgan 3 besteht im einzelnen aus einem Zellenrad 4 mit Antrieb 5 und einem Faltenbalg 6 zur Anpassung an unterschiedliche Abnehmer. Weiterhin weist der Staubbunker 1 in der Höhe seines Trichters 2 eine Ringleitung 7 zur Zufuhr von Pressluft auf, damit die Schüttung im Inneren des Staubbunkers ggf. aufgelockert werden kann. Ein CH4-IR-Gasanalysator (nicht gezeigt) greift mit einer Sonde 8 in den Entleerungsstutzen des Behälters. Zusätzlich sind über die axiale Länge des Behälters drei gleichartige Sonden 9 in nahezu gleichem Abstand und ggf. in Umfangsrichtung verteilt angebracht, wobei die Sonden sowohl in den Bereich der Staubschüttung 10 als auch in den Gasraum 11 oberhalb der Schüttung hineinragen. Auch diese Sonden sind mit jeweils einem CH4-IR-Gasanalysator verbunden. Zwischen der Sonde 8 bzw. den Sonden 9 und den CH4-IR- . Gasanalysatoren sind Staubfilter (nicht gezeigt) zum Schutz der Messgeräte eingebaut.A
Im Verlauf der einzelnen Versuche betrug der über die Sonde 9 ermittelte CH4-Grundwert im Bunker 5 - 33 ppm der über die Sonde 8 gemessene CH4-Grundwert bei der Entleerung des Bunkers ca. 10 ppm.In the course of the individual tests, the basic CH 4 value determined in
Nach Erzeugung eines Schwelbrandes stieg der über die Sonden 9 gemessene CH4-Gehalt deutlich an. Ebenso nahm der während der Bunkerentleerung über die Sonde 8 registrierte CH4-Wert zu.After a smoldering fire had been generated, the CH 4 content measured by the
Durch diese praxisnahen Untersuchungen wurden die zunächst labormässigen Versuche vollständig bestätigt.Through these practical investigations, the initially laboratory tests were fully confirmed.
Claims (3)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT82106076T ATE16429T1 (en) | 1981-07-08 | 1982-07-07 | PROCEDURE FOR EARLY DETECTION OF Smoldering Fires in Containers Containing Lignite Dust by Detection of Methane. |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3126864 | 1981-07-08 | ||
DE3126864A DE3126864C2 (en) | 1981-07-08 | 1981-07-08 | Process for the early detection of smoldering fires in containers containing lignite dust |
Publications (2)
Publication Number | Publication Date |
---|---|
EP0069393A1 true EP0069393A1 (en) | 1983-01-12 |
EP0069393B1 EP0069393B1 (en) | 1985-11-06 |
Family
ID=6136361
Family Applications (2)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP82902156A Pending EP0082867A1 (en) | 1981-07-08 | 1982-07-07 | Method for the early detection of fires smouldering in containers containing lignite dust by methane detection |
EP82106076A Expired EP0069393B1 (en) | 1981-07-08 | 1982-07-07 | Method for the early detection of carbonic fires in recipients containing dust of brown coal by detection of methane |
Family Applications Before (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP82902156A Pending EP0082867A1 (en) | 1981-07-08 | 1982-07-07 | Method for the early detection of fires smouldering in containers containing lignite dust by methane detection |
Country Status (8)
Country | Link |
---|---|
EP (2) | EP0082867A1 (en) |
AT (1) | ATE16429T1 (en) |
AU (1) | AU557814B2 (en) |
CA (1) | CA1187718A (en) |
CS (1) | CS245771B2 (en) |
DD (1) | DD207438A1 (en) |
DE (2) | DE3126864C2 (en) |
WO (1) | WO1983000247A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105510175A (en) * | 2015-12-08 | 2016-04-20 | 辽宁工程技术大学 | Method for measuring inhibition performance of inhibitor |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE9417289U1 (en) * | 1994-10-27 | 1995-01-26 | Meinke, Peter, Prof. Dr.-Ing., 82319 Starnberg | Detector device, detector system and immunosensor for detecting fires |
DE19808663C2 (en) * | 1998-03-02 | 2001-05-23 | Epcos Ag | Fire detection system and operating procedures for this system |
CN114813635B (en) * | 2022-06-28 | 2022-10-04 | 华谱智能科技(天津)有限公司 | Method for optimizing combustion parameters of coal stove and electronic equipment |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE539562C (en) * | 1929-01-24 | 1931-12-10 | Hermann Heinicke | Device for the determination of methane and other hydrocarbons in mixed gases by catalytic combustion |
FR1321819A (en) * | 1961-05-05 | 1963-03-22 | Zd Y Prumyslove Automatisace | Device for the control and analysis of gas and in particular for the detection of methane in mines and devices conforming to those fitted with the device or similar device |
BE647714A (en) * | 1964-05-11 | 1964-08-31 | ||
DE2331984A1 (en) * | 1973-06-16 | 1975-01-09 | Bergwerksverband Gmbh | Methane and carbon monoxide monitoring appts. for coal mines - cuts electric power to the affected areas |
CH586940A5 (en) * | 1974-10-03 | 1977-04-15 | Anglo Amer Corp South Africa | New method of fire detection in mines - obtains continuous measurement of carbon dioxide concentration gives alarm when given value is exceeded |
FR2374637A2 (en) * | 1976-12-15 | 1978-07-13 | Consolidation Coal Co | COMBUSTIBLE GAS DETECTION CIRCUIT IN THE ATMOSPHERE OF A MINE |
US4129030A (en) * | 1977-10-13 | 1978-12-12 | Ads Systems, Inc. | Sensing apparatus and method |
-
1981
- 1981-07-08 DE DE3126864A patent/DE3126864C2/en not_active Expired
-
1982
- 1982-06-04 CS CS824164A patent/CS245771B2/en unknown
- 1982-07-06 DD DD82241440A patent/DD207438A1/en not_active IP Right Cessation
- 1982-07-07 AT AT82106076T patent/ATE16429T1/en not_active IP Right Cessation
- 1982-07-07 EP EP82902156A patent/EP0082867A1/en active Pending
- 1982-07-07 EP EP82106076A patent/EP0069393B1/en not_active Expired
- 1982-07-07 DE DE8282106076T patent/DE3267275D1/en not_active Expired
- 1982-07-07 WO PCT/DE1982/000142 patent/WO1983000247A1/en not_active Application Discontinuation
- 1982-07-07 CA CA000406836A patent/CA1187718A/en not_active Expired
- 1982-07-07 AU AU86886/82A patent/AU557814B2/en not_active Ceased
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE539562C (en) * | 1929-01-24 | 1931-12-10 | Hermann Heinicke | Device for the determination of methane and other hydrocarbons in mixed gases by catalytic combustion |
FR1321819A (en) * | 1961-05-05 | 1963-03-22 | Zd Y Prumyslove Automatisace | Device for the control and analysis of gas and in particular for the detection of methane in mines and devices conforming to those fitted with the device or similar device |
BE647714A (en) * | 1964-05-11 | 1964-08-31 | ||
DE2331984A1 (en) * | 1973-06-16 | 1975-01-09 | Bergwerksverband Gmbh | Methane and carbon monoxide monitoring appts. for coal mines - cuts electric power to the affected areas |
CH586940A5 (en) * | 1974-10-03 | 1977-04-15 | Anglo Amer Corp South Africa | New method of fire detection in mines - obtains continuous measurement of carbon dioxide concentration gives alarm when given value is exceeded |
FR2374637A2 (en) * | 1976-12-15 | 1978-07-13 | Consolidation Coal Co | COMBUSTIBLE GAS DETECTION CIRCUIT IN THE ATMOSPHERE OF A MINE |
US4129030A (en) * | 1977-10-13 | 1978-12-12 | Ads Systems, Inc. | Sensing apparatus and method |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105510175A (en) * | 2015-12-08 | 2016-04-20 | 辽宁工程技术大学 | Method for measuring inhibition performance of inhibitor |
CN105510175B (en) * | 2015-12-08 | 2018-04-06 | 辽宁工程技术大学 | A kind of method for determining retardant resistanceization performance |
Also Published As
Publication number | Publication date |
---|---|
DE3267275D1 (en) | 1985-12-12 |
EP0069393B1 (en) | 1985-11-06 |
CS245771B2 (en) | 1986-10-16 |
AU557814B2 (en) | 1987-01-08 |
CA1187718A (en) | 1985-05-28 |
DE3126864A1 (en) | 1983-01-27 |
DE3126864C2 (en) | 1986-01-02 |
EP0082867A1 (en) | 1983-07-06 |
WO1983000247A1 (en) | 1983-01-20 |
AU8688682A (en) | 1983-02-02 |
DD207438A1 (en) | 1984-02-29 |
ATE16429T1 (en) | 1985-11-15 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
DE2461585A1 (en) | DEVICE, METHOD AND MEANS FOR DETECTING FREE WATER IN HYDROCARBONS | |
EP0069393B1 (en) | Method for the early detection of carbonic fires in recipients containing dust of brown coal by detection of methane | |
DE102016007825A1 (en) | Method and device for monitoring the quality of gaseous media | |
DE102009017932B4 (en) | A method for the continuous quantitative determination of an oxidizable chemical compound in an assay medium | |
DE2430940A1 (en) | METHOD AND APPARATUS FOR QUANTITATIVE MEASUREMENT OF THE CONCENTRATION OF OZONE IN A GAS SAMPLE | |
EP2172531A1 (en) | Function test for a gas alarm system | |
DE3687974T2 (en) | METHOD AND DEVICE FOR CHARACTERIZING AN ORGANIC MATERIAL EXTRACTABLE WITH AT LEAST ONE SOLVENT UNDER SUPERCRITICAL PRESSURE AND TEMPERATURE CONDITIONS. | |
DE840613C (en) | Method for the continuous measurement and recording of the changing proportions of a component of a gas mixture | |
DE1207117B (en) | Method and device for testing the air for flammable additions, in particular methane | |
DE1592889A1 (en) | Process and device for regulating gas soot apparatus | |
DE2841307C2 (en) | Radiation measurement method and device for determining the concentration of fat in meat masses | |
DE1673308B2 (en) | Method and device for determining the carbon potential of furnace atmospheres in annealing furnaces | |
DE2113425A1 (en) | Furnace carbon black mfr - with continuous control of particle size by ir analysis of outlet gas | |
DE730977C (en) | Device for measuring a component in the air, in particular carbonic acid, through absorption | |
DE1175464B (en) | Method for differential thermal analysis of soil samples | |
DE1872900U (en) | DEVICE FOR CHECKING THE READINESS FOR USE OF ELECTRIC GAS MEASURING DEVICES. | |
DE673087C (en) | Device for the volumetric rapid determination of the carbon after the combustion process as well as for the rapid determination of the carbonic acid which can be released by glowing and acid exposure | |
DE1013204B (en) | Procedure for the early detection of pit fire | |
DE859563C (en) | Procedure for checking the loading status of filter inserts | |
DE4202089A1 (en) | Gas detection, determn. and/or combustion esp. in gas explosion prevention - includes using 1 or more combustion chambers into which vapour or gas is supplied | |
DE174800C (en) | ||
DE536333C (en) | Device for displaying flammable gases in the air | |
DE72759C (en) | Method and apparatus for the determination of combustible gases and vapors contained in the air | |
DD219662A1 (en) | PROCESS FOR STORAGE MANAGEMENT IN CORE LAYERING | |
DD249335A1 (en) | METHOD FOR DETERMINING ABRAUM ALLOYS AND SLAG CONSTRUCTIONS |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PUAI | Public reference made under article 153(3) epc to a published international application that has entered the european phase |
Free format text: ORIGINAL CODE: 0009012 |
|
AK | Designated contracting states |
Designated state(s): IT |
|
17P | Request for examination filed |
Effective date: 19830125 |
|
RBV | Designated contracting states (corrected) |
Designated state(s): AT BE CH DE FR IT LI LU |
|
XX | Miscellaneous (additional remarks) |
Free format text: VERBUNDEN MIT 82902156.7/0082867 (EUROPAEISCHE ANMELDENUMMER/VEROEFFENTLICHUNGSNUMMER) DURCH ENTSCHEIDUNG VOM 13.09.84. |
|
ITF | It: translation for a ep patent filed | ||
GRAA | (expected) grant |
Free format text: ORIGINAL CODE: 0009210 |
|
AK | Designated contracting states |
Designated state(s): AT BE CH DE FR IT LI LU |
|
REF | Corresponds to: |
Ref document number: 16429 Country of ref document: AT Date of ref document: 19851115 Kind code of ref document: T |
|
XX | Miscellaneous (additional remarks) |
Free format text: VERBUNDEN MIT 82902156.7/0082867 (EUROPAEISCHE ANMELDENUMMER/VEROEFFENTLICHUNGSNUMMER) DURCH ENTSCHEIDUNG VOM 13.09.84. |
|
REF | Corresponds to: |
Ref document number: 3267275 Country of ref document: DE Date of ref document: 19851212 |
|
ET | Fr: translation filed | ||
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: LU Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 19860731 |
|
PLBE | No opposition filed within time limit |
Free format text: ORIGINAL CODE: 0009261 |
|
STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: NO OPPOSITION FILED WITHIN TIME LIMIT |
|
26N | No opposition filed | ||
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: FR Payment date: 19890525 Year of fee payment: 8 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: LU Payment date: 19890607 Year of fee payment: 8 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: CH Payment date: 19890928 Year of fee payment: 8 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: LI Effective date: 19900731 Ref country code: CH Effective date: 19900731 |
|
REG | Reference to a national code |
Ref country code: CH Ref legal event code: PL |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: FR Effective date: 19910329 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: AT Payment date: 19910523 Year of fee payment: 10 |
|
REG | Reference to a national code |
Ref country code: FR Ref legal event code: ST |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: BE Payment date: 19910703 Year of fee payment: 10 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: AT Effective date: 19920707 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: BE Effective date: 19920731 |
|
BERE | Be: lapsed |
Owner name: RHEINISCHE BRAUNKOHLENWERKE A.G. Effective date: 19920731 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: DE Payment date: 19950901 Year of fee payment: 14 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: DE Effective date: 19970402 |