矿井通风煤矿瓦斯利用中英文对照外文翻译文献
煤矿软岩巷道支护强度优化外文文献翻译、中英文翻译
英文原文The optimal support intensity for coal mine roadway tunnelsin soft rocksC. Wang*Mining Engineering Program, Western Australian School of Mines, PMB 22, KalgoorlieWA6430, Australia1. IntroductionThe essence of underground roadway support is to provide the surrounding rocks of an underground roadway with assistance to help them achieve stress and strain equilibrium and ultimately stability of deformation.The approaches to this goal are either to reinforce the rock mass by rock bolting or injection(internal rock stabilization) or to provide the surrounding rocks with a support resistance with a magnitude being described as the support intensity (external rock stabilization).When an underground roadway is located in soft rocks which are too soft to be reinforced by bolting and/or unsuitable for rock injection because of restraints imposed by either the rock mass impermeability or rock mass deterioration when water is encountered, external rock support, such as steel sets, therefore becomes the only option for the stability control of the roadway. Under this circumstance, the support intensity means a support force acting per unit surface area of the surrounding rocks of the roadway. In soft rock engineering practice, the design of a support pattern for a roadway in underground coal mining is normally based on rules of thumb. In most cases, heavy support measures are adopted to secure a successful roadway.Fig. 1(a) demonstrates the excellent condition of a sub-level roadway within soft rocks at an underground coal mine in north China, where an excessive capital cost was applied for the achievement of roadway stability. In some cases, such as a service roadway driven in soft rocks at the same mine (Fig. 1(b)), insufficient support intensity was specified as a result of a lack of relevant experience and design codes. Consequently, failure of the roadway stability was inevitable and an extra cost was incurred when the subsequent roadway repair or rehabilitation was undertaken.The critical issue in both cases lies in the determination of an optimal support intensity which is the function of the geometry and dimension of a roadway and its geotechnicalconditions including rock mass properties, stress conditions and hydrological status.Physical modelling using simulated materials based on the theory of similarity provides a direct perceptional methodology for mining geomechanics study [1-6].Using simulated materials of the same composition to construct a roadway and its soft surrounding rocks, applying a certain magnitude of simulated support intensity to the surface of a roadway under simulated stress conditions, the three-dimensional physical modelling method depicted in this Note emonstrates a quantitative solution for strategic design of roadway support concerned with soft rocks. A relation between the support intensity and deformation of the surrounding rocks of a roadway has been established after a series of simulation tests had been conducted. A discussion on the optimal support intensity for a roadway in soft rocks is also given.Fig. 1. Examples of successful and unsuccessful support of underground roadways within soft rocks: (a) Good condition of a sublevel roadway, (b) Unsuccessful support of a service roadway.2. Features of the three-dimensional physical modellingA physical modelling study of the interaction between support intensity and roadway deformation was carried out using the three dimension physical modelling system (see Fig.2) at the Central Laboratory of Rock Mechanics and Ground Control, China University of Mining and Technology. Features of this system are described in the following sub-sections.Fig. 2.Three-dimensional loaded physical modelling system at the Central Laboratory of Rock Mechanics and Ground Control, China University of Mining and Technology.2.1. Size of the physical modelThe effective size of a physical model is 1000 mm wide, 1000 mm high and 200 mm thick.2.2. Three dimensional active loading capabilitySix flatjacks are used to apply loads to the six sides of the physical model in the form of a rectangular prism. Each flatjack was designed to cover the full area of one of the six sides and be capable of applying a pressure of up to 10 MPa on to the surface of the simulated rock mass. This means that the flatjacks are capable of applying an active load of up to 1000 tonnes and 200 tonnes simultaneously on the front and back facets, the top andbottom, and the two side facets of a model, respectively.2.3. Long-term continuous loading capabilityA high-pressure, nitrogen-operated, hydraulic pressure stabilising unit was employed to maintain a consistent magnitude of load applied to the model so that the physical modelling test is able to last continuously for weeks, months or even years without interruption. This feature ensures that the study of the long-term rheological behaviour of soft rocks can be carried out.3. Physical modelling testsPhysical modelling of an underground roadway/ tunnel within soft rocks with a hydrostatic stress condition was carried out. The same simulated materials were repeatedly used six times to construct six physical models. Each roadway model was provided with adifferent magnitude of support intensity.3.1. Geotechnical conditions for the prototype and the modelling scaleA specified underground roadway within soft rocks was assumed to be the prototype for the modelling study. Detailed geotechnical conditions of the roadway and its surrounding rocks are:circular roadway with a diameter (D) of 4.5 m and cross-sectional area of 16 m2;UCS (Rc ) of the surrounding rock was 20 MPa;bulk density of the surrounding rock was 2500 kg/m3;depth of the roadway location was 500 m below surface;rock mass stress (s0 ) was 12.5 MPa in all directions;support intensity(pa) to be applied to the roadway was 0.1, 0.2, 0.3, 0.4, 0.5 and 0.6 MPa, respectively.The geotechnical modelling scale (Cl ) determined was 1 : 25. The bulk density (gm )of the simulated rock mass materials was 1600 kg/m3.Therefore, all the related simulation constants are:similarity constant for bulk density: Cg ¼ 1600/2500=0.64;similarity constant for strength: Cs ¼ ClCg ¼ 0:256;similarity constant for load: CF ¼ CgC1 ¼ 4:096 10ÿ5 ;similarity constant for time: Ct ¼ C l:5 ¼ 0:2:Geotechnical conditions of the simulated rock massand roadway were derived from those of the prototype rock mass as presented below: strength of the simulated rock mass: Rm=RcCs=0.512;diameter of the simulated roadway: Dm=DCl=180 mm;load intensity on the facets of the model: pm=s0Cs=0.32 MPa;Simulated support intensity: pam=paCs=0.00256, 0.00516, 0.00768, 0.01024, 0.0128and 0.01536 MPa; respectively.3.2. Realization of support intensity in physical modellingDue to the restraints of the small dimensions of the model roadway on the simulation of support structure, the support pattern and structure were unable to be simulated. Instead, an equivalent support intensity was simulated and applied to the surface of the surrounding rock of the model roadway. A Static Water Support and Deformation Measurement System (SWSDMS) was designed specially. Fig. 3 illustrates the SWSDMS being installed in the model roadway. The mechanism of SWSDMS is to use 4 separate water capsules to apply a support intensity to the surface of the roadway roof, two side walls and floor. Four rubber tubes, each of which was linked to a water capsule and filled with water, were used to generate a water pressure at the capsule/rock interface and measure it through the water level reading.A certain constant simulated support intensity was achieved by applying a certain height of static water pressure. A change to support intensity could be made by changing the water height in the rubber tube. The volume change of each of the four water capsules was measured at the due time by collectingand weighing the water overflow. The volume of water coming from each of the four water capsules was used to calculate the radial deformation of roadway surrounding rock, i.e., roof subsidence, wall-to-wall closure and floor heave. The proposed simulated supportintensities, i.e., Pam ¼ 0:00256, 0.00516, 0.00768, 0.01024, 0.0128 and 0.01536 MPa, were achieved by adjusting the static water level to 256, 516, 768, 1024, 1280 and 1536 mm high, respectively.Fig. 3. Static Water Support and Deformation Measurement System (SWSDMS) being accommodated in a roadway model in the real 3-D loaded physical modellingsystem.3.3. Construction of physical modelThe compositions and properties of materials to be used for the construction of physical models were studied prior to the physical model construction. Given the significant rheological deformation of roadways excavated in soft rock, sand and paraffin wax were chosen for the simulated soft rock. The properties of a series of sand/paraffin wax mixtures were studied in laboratory and are presented in Table 1.Table 1 Compositions and properties of sand/paraffin wax mixturesAccording to the geotechnical conditions of the prototype rock mass and the model scale, a mixture of sand/paraffin wax of 100 : 3 was selected to construct the rock massmodel. The procedures involved in the model construction include cold mixing of the sandand paraffin wax, oven heating the sand/wax mixture and constructing the physical modelusing the hot sand/wax mixture.3.4. Process of physical modellingThe real process of an underground roadway excavation, support installation and deformation of the surrounding rocks with time was simulated in the laboratory physical modelling. After the model had cooled down, prestressing the model, excavation of the roadway under pressure, installation of the SWSDMS device and measurement of the roadway deformation were carried out step by step. The whole process of modelling was strictly conducted according to the time similarity constant. Each physical modelling step lasted for 10-25 days in the laboratory, which were equivalent to a real time period of 50-125 days approximately.4. Relations between support intensity and roadway deformationComparable results of the six physical modelling tests conducted with the identical materials and geotechnical conditions revealed the significance of the support intensity inunderground roadway/tunnel support.4.1. Effect of support intensity on the deformation characteristics of a roadwayThe deformation characteristics of an identical roadway with different support intensityis graphically presented in Fig. 4(a) and (b). It can be seen that the influence of supportintensity on the deformation characteristics is significant. With a support intensity of 0.1MPa, the roadway experienced a large eformation for a period of 118 days after theroadway excavation and the provision of support intensity. During this period, an average of828 mm deformation was accumulated. Following this period, the wall-to-wall closure androof-to-floor convergence stayed steady at a level of 4.4 mm/day. By contrast, when a support intensity of 0.6 MPa was provided to the identical roadway, its post-excavation deformation merely lasted for 36 days with an accumulative closure/convergence of 40 mm, followed by a rheological deformation of 0.08 mm/day, which was continuously reducing withFig. 4. Deformation of roadway with a series of support intensities:(a) Deformation of roadway with time, (b) Deformation rate of roadway with time.time. The comparison shows that the deformation magnitude of the latter was only 4.8% that of the former.A negative exponential relation between the deformation rate and support intensity can also be deduced from the curve of deformation rate vs. support intensity presented in Fig. 5 and be mathematically expressed as: v ¼ 0:023pa2:4 :where v is the rheological deformation rate of the surrounding rock of a roadway in mm/day, pa is the support intensity in MPa provided to the surrounding rock.Fig.5 Relations between rheological deformation rate and support intensity of aroadway in soft rocks.4.2. Optimal support intensity for a roadway in soft rocksRequirements on the control of roadway deformation depend on the usage and service life of the roadway. It is known that a zero deformation rate is impossible practically to target in supporting a roadway in soft rocks. A wise approach is to exercise a designprinciple that the roadway deformation is allowed to take place to a degree within an acceptable limit. Physical modelling results indicated that an increase of support intensity from 0.1 to 0.5 MPa can markedly reduce the deformation rate of the surrounding rocks. A further increase of support intensity from 0.5 to 0.6 MPa, however, did not bring about as much reduction of deformation rate as that created by the support intensity increase of from 0.1 to 0.2 MPa or from 0.3 to 0.4 MPa. This means that a reasonable range of support intensity exists and an increase of support intensity can be rewarded with a significant reduction of roadway deformation if the actual support intensity is within this range.Further increases of support intensity can only cause less reduction of roadway deformation. Therefore, if both technical and economical considerations are taken into account, a support intensity of from 0.3 to 0.5 MPa would be appropriate for most temporary tunnels such as roadways in underground coal mining. With this support intensity, the rheological deformation rate of the surrounding rocks can be controlled within a range of from 0.1 to 0.4 mm/day, with which an ordinary temporary roadway can be maintained safely for years to one decade.5. ConclusionsThe three-dimensional physical modelling method provides a ‘co nceptual approach to quantitative design’of roadway support associated with soft rocks. With lack of knowledge of the constitutive relations, especially for the rheological mechanisms, in rock engineering practice, the modelling results could serve as a foundation on which a scientific design of underground roadway/tunnel support is developed, particularly when a large amount of rock mass deformation is concerned.The experimental study conducted with a series of support intensities revealed that a reasonable support intensity exists. Its value depends on the geotechnical and geometric conditions of the underground roadway/tunnel concerned and the requirements applied by the roadway/tunnel safe use specifications and the roadway/tunnel service life span. The results indicate that a support intensity of 0.3 to 0.5 MPa can securely control the closure rate for the conditions tested within a magnitude of 0.1 to 0.4 mm/day for a medium size underground roadway/tunnel driven in soft rocks of around 20 MPa at a depth of about 500 m below surface.References[1] Internal Research Report. Study on the technology of large deformation control for roadways within soft rocks. China University of Mining and Technology, 1995 [in Chinese].[2] Wang C. Study on the supporting mechanism and technology for roadways in soft rocks. PhD thesis, China University of Mining and Technology, 1995 [in Chinese].[3] Internal reference (1993). Properties of simulated materials for physical geomechanical modelling. The Central Laboratory of Rock Mechanics and Ground Control, China University of Mining and Technology [in Chinese].[4] Lin Y. Simulated materials and simulation for physical modelling. Publishing House of China Metallurgy Industry, Beijing, China, 1986 [in Chinese].[5] Duro ve J, Hatala J, Maras M, Hroncova E. Support’s design based on physical modelling. Proceedings of the International Conference of Geotechnical Engineering of Hard Soils } Soft Rocks. Rotterdam: Balkema, 1993.[6] Singh R, Singh TN. Investigation into the behaviour of a support system and roof strata during sub-level caving of a thick coal seam. Int J Geotech Geol. Engng. 1999;17:21-35.中文译文煤矿软岩巷道支护强度优化C. Wang采矿工程专业,西澳矿业学校,港口及航运局22卡尔古利W A6430,澳大利亚1引言地下巷道支护的实质是给巷道围岩提供支撑以实现应力应变平衡,并最终使变形稳定。
煤矿井下瓦斯治理技术的应用外文翻译、中英文翻译、外文文献翻译
【外文文献】2Coal mine mine shaft gas government technology applicationFirst, surveyEvil of the gas, shocking, gas government, imminent.The coal mine mine shaft gas ultra limits with the gas agglomeration occurs repeatedly, even some coal mine mine shaft also has the gas explosion, is seriously threatening jobholders' safety and the coal mine safety in production.All coal mine mine shaft all is equipped with the coal bin, the coal mine mine shaft coal bin name slides the coal shaft or “the counter-well”.The coal bin role mainly is the storage, the reprint, the cushion coal amount, is the coal mine mine shaft storage and transport coal important link, to realizes the coal output high production to play the positive role.A small mine pit mine shaft coal bin quantity is equipped with 3~8, a large-scale mine pit mine shaft coal bin quantity achieved 10~20, giant mine pit mine shaft coal bin quantity are more, therefore in the national coal mine mine pit, mine shaft coal bin quantity many may reach 1,000,000.These mine shaft coal bin in the storage, the reprint, the cushion coal amount process simultaneously is agglomerating the massive gas, in its mine shaft coal bin gas density according to the coal amount, the anthrax different may achieve 3~20 ﹪, the gas density surpasses "Coal mine safety Regulations" to stipulate greatly.The such high gas density meets friction spark, static electricity spark, stray currents, collision spark and so on kindling materials, extremely easy to cause the gas explosion.Coal mine mine shaft coal bin existence serious security hidden danger, also is the significant dangerous source, is seriously threatening jobholders' safety and the coal mine mine shaft safety in production.Since long ago the coal mine mine shaft coal bin gas agglomeration question continuously has not obtained the very good solution significant hidden danger and the significant dangerous source, becomes the long-term puzzle coal mine safety production a big difficult problem.In order to solve this kind of problem, the traditional solution is installs the axis in the mine shaft coal bin place above tunnel to flow the type ventilator to dilute in the coal bin the upside gas, the axis flows the type ventilator also only to be able to dilute on the coal bin the 3~5m place gas, cannot dilute regarding the 20~30m high mine shaft coal bin majority of gas, is also unable solve.Moreover the axis flows the massive gas which the type ventilator discharges in some people to work transports in the coal lane, because transports in the coal lane to have the electromechanical device and the staff, has slightly can create the gas explosion accident or the personnel carelessly suffocates the fatal accident.The axis flows the type ventilator to dilute in the coal bin the gas for to transport in the coal lane to cause the enormous harm, the dangerous harm factor still exists.Although this to solved the mine shaft coal bin gas ultra to limit certain function, but the above equipment facility government expense was expensive, also fundamentally has not solved the hidden danger which the gas agglomeration created, still existed has the gas explosion accident hidden danger, affected the coal mine mine shaft safety in production, might say these negative measures fundamentally have not solved the gas explosion problem.In order to solve the coal mine mine shaft coal bin gas agglomeration problem, eliminates the significant security hidden danger, eliminates the significant dangerous source, the coal profession ore advocates peace the engineers and technicians to spend and not to solve.The coal mine mine shaft coal bin gas government installment mainlyaims at the solution existing coal mine mine shaft coal bin existence the gas agglomeration to exceed the allowed figure easy to create the gas explosion and the government expense expensive technology difficulty Second, mine shaft coal bin gas government installment research and designThe coal mine mine shaft coal bin gas government installment goal is the solution existing coal mine mine shaft coal bin existence gas exceeds the allowed figure easy to create the gas explosion and the government expense expensive technology difficulty, and provides one kind to be able to govern the coal mine mine shaft coal bin gas agglomeration and the elimination gas also the government expense low coal mine mine shaft coal bin gas agglomeration government installment.The coal mine mine shaft coal bin gas government installment the technical plan which uses for the solution above question is: It by or a two gas separator, the gas leads the air hose, three forks a row of wind and foehn the ventilator is composed.The gas separator is located in the coal mine mine shaft coal bin coal body, three forks a row of wind to be located in above the coal bin in the air return way, foehn the ventilator is located in underneath the coal bin, leads the air hose using the gas to lead to picks the area air return way or the main air return way.It by the coal bin gas separator, the gas leads the air hose, three forks the whole synthesis installment which a row of wind and foehn the ventilator is composed.States the coal mine mine shaft coal bin foehn ventilator by foehn constitutions and so on curve body, modified line body, collection air flue, the main function forms the formidable foehn effect, forms foehn enters the gas separator loosely, leads the gas separator in gas the gas to lead the air hose, according to the direction which requests using the gas leads the air hose the gas to arrange again to the coal mine mine shaftcoal bin outside picks the area air return way or the main air return way.Foehn the ventilator is located in lower part the coal mine mine shaft coal bin.States the coal mine mine shaft coal bin gas separator by the tube body, the gas release hat, the gas releases Kong He to take the constitution, the gas release hat is located in the tube body body department, the gas releases Kong He to take is located in evenly on the tube body.The gas separator leads the air hose with foehn the ventilator and the gas to connect, is located in on the coal mine mine shaft coal bin warehouse sidewall.States the coal mine mine shaft coal bin gas release hole is the rectangular filtration hole, the concentric circle filters Kong He to forbid the symbol filtration hole; States takes lacks for the garden the shape eaves, takes is located the gas release hole the place above, is for the purpose of causing the coal (rock) to separate with the gas.States the coal mine mine shaft coal bin gas to lead the air hose for the anti-static electricity glass fiber reinforced plastic circular pipe.The coal bin gas leads the air hose and the gas separator and three forks a row of wind to connect, is located in on in the coal mine mine shaft coal bin air return way place above side.States the coal mine mine shaft coal bin three to fork a row of wind for the flabelliform tubing cross anti-static electricity glass cylinder body.Three forks a row of wind and the gas separator leads the air hose by the tube body or the gas to connect, is located in on in the coal mine mine shaft coal bin air return way place above side.Because the coal mine mine shaft coal bin gas government installment has used or a two gas separator, the gas leads the air hose, three forks the whole synthesis installment which a row of wind and foehn the ventilator composes, can reduce the coal mine mine shaft coal bin thecomplete gas, governs the coal mine mine shaft coal bin gas agglomeration thoroughly the question, and the government expense is low, the economic efficiency is good, has the government gas thorough, the energy conservation environmental protection, the government expense low and the economic efficiency good and so on the merits.Pointed out specially this equipment is does not have the noise, the nonmotile, the non-pollution well ventilated structure facility, belongs to the environmental protection energy conservation product purely.Third, executes the security effectFollowing union implementation makes the further description.As shown in Figure 1, in this implementation example coal mine mine shaft coal bin gas agglomeration government installment position arrangement structure schematic drawing.It by the coal mine mine shaft coal bin foehn ventilator, the gas separator, the gas leads the air hose, three forks a row of wind, the coal mine mine shaft coal bin coal body, the coal bin tube wall, the coal bin bottom coal, the coal bin coaling, the coal bin slides on the coal mouth, the coal bin returns to lower part the wind lane, the coal bin transports the big lane constitution.The coal mine mine shaft coal bin gas government installment, used a gas separator, the gas has led the air hose, three forks a row of wind and foehn the ventilator composition whole synthesis installment.The coal mine mine shaft coal bin foehn ventilator and the gas separator, the gas lead the air hose, three fork a row of wind and foehn the ventilator compose an organic whole together, has formed the whole synthesis installment, together completes the coal mine mine shaft coal bin gas dilution task.The coal mine mine shaft coal bin coal body, the tube wall, the bottom coal, the coaling, on the smooth coal mouth, the coal bin returns to lower part the wind lane, the coal bin transports the big lane is the coal mine mine shaft coal bin important constituent, they are affecting the gasgovernment effect directly.Its effect is: Coal mine mine shaft coal bin coal body how many decision coal bin gas content and gas density size; The coal bin tube wall quality is deciding in the coal bin the gas separator installment quality; The coal bin bottom coal how many decision coal bin well ventilated situation is affecting the gas separator the function; Coal bin coaling model function influence gas agglomeration degree; The coal bin slides in the coal mouth size influence coal bin the gas release; On the coal bin returns to the wind lane the amount of wind and the cross section size is deciding on the coal bin the gas release rate; Lower part the coal bin transports the big lane amount of wind and the cross section size is deciding lower part the coal bin the loose speed namely pressure produced by the fan or the strength of draft.These coal bin structure is affecting the gas government effect directly, all to coal bin in gas density and gas agglomeration government direct or indirect function.A gas separator end and the gas lead the wind or three fork a row of wind to connect directly, another end connects with foehn the ventilator.The gas separator function is the gas which agglomerates in the coal mine mine shaft coal bin in coal and the coal bin separates, separates after the gas to enter the gas separator to lead the air hose to the gas to arrange to the coal bin outside the air return way, achieves in the dilution the gas goal.Three forks a row of wind for the flabelliform tubing cross anti-static electricity glass cylinder body, three forks a row of wind and the gas leads the air hose to connect, three forks a row of wind to be located in picks the area air return way or the main air return way, three forks the row of wind 3 functions is guaranteed the gas forever according to the request loose direction movement, prevented the loose direction reverses.The coal mine mine shaft coal bin gas agglomeration governmentinstallment, it belongs to one kind to govern the coal mine mine shaft coal bin gas the equipment.Mainly is the solution existing coal mine mine shaft coal bin existence gas agglomeration exceeds the allowed figure easy to create the gas explosion and the government expense expensive technology difficulty.In order to solve the technical plan which the above question uses is: The coal mine mine shaft coal bin gas agglomeration government installment, it by or a two coal bin gas separator, the gas leads the air hose, three forks the whole synthesis installment which a row of wind and foehn the ventilator is composed, can reduce the coal mine mine shaft coal bin the complete gas, governs under thoroughly the mining coal mine pit the coal bin gas agglomeration question, and the government expense is low, the energy conservation environmental protection, the economic efficiency is good.The coal mine mine shaft coal bin gas agglomeration government installment, is located in the coal mine mine shaft coal bin and above the coal mine mine shaft coal bin returns to the wind lane direction, leads the air hose using the gas to lead to picks the area to return to the wind lane or the main air return way.Has reliable, the economy safely practical, the structure simple, the management convenient, does not need to increase the power the structure facility; Has technological advance, the science reasonable, the government gas effective, the energy conservation environmental protection, the government expense low and the economic efficiency good and so on the merits, thus achieves the coal mine mine shaft safety in production the goal.The coal mine mine shaft coal bin gas agglomeration government installment guards against pounds the problem analysis to be as follows: 1st, coal bin (counter-well) if between 10~20m, the mining coal area major part mine shaft coal bin in this altitude, this practical new coal mine mine shaft coal bin gas agglomeration government installmentcomparison adapts highly, slides in the coal or the gangue size has the direct influence including gangue quantity how many to this equipment, the gangue gravity acceleration to this equipment impulse is G=mg=(1~20) ×9.8= (9.8~ 196) N, the gangue max impulse is 196 N, this equipment material quality uses the stress is 389~468N.Therefore, this equipment can withstand the gangue the impulse, cannot harm breaks off.If hits continuously can create the fatigue damage to affect the installment service life, the mine shaft coal bin service life most length is about a year, this equipment material quality service life may guarantee for a year including the corrosion.2nd, coal bin if between 20~90m, this practical new coal mine mine shaft coal bin gas agglomeration government installment not too adapts highly, easy to create big curving and the buckle, but in mining coal area because the geostatic pressure influence mine shaft coal bin (counter-well) very little designs this altitude.Fourth, installment characteristicSummarizes the coal mine mine shaft coal bin gas agglomeration government installment, has following characteristic:1st, the coal mine mine shaft coal bin gas agglomeration government installment technical invention belonged to the domestic origination, the world is advanced, has technological advance, the science is reasonable, has filled our country coal mine mine shaft coal bin gas government blank 2nd, coal mine mine shaft coal bin gas agglomeration government installment use effective government coal mine mine shaft coal bin gas agglomeration question.It will develop successfully opens a new way to all coal mine mine shaft coal bin gas government.3rd, the coal mine mine shaft coal bin gas agglomeration government installment will be the security, the economy, forever the solid structure facility, an installment, the permanent use, the economy will bepractical.4th, the coal mine mine shaft coal bin gas agglomeration government installment structure is simple, manages conveniently, does not have to service frequently, easy to do and easy, does not need the specialist to operate, easy to promote the use.5th, the coal mine mine shaft coal bin gas agglomeration government installs this new technical the success to utilize designs general to have the profound significance to our country large-scale coal mine mine shaft coal bin gas agglomeration government.Has provided the advanced new technology to the later large-scale coal mine mine shaft coal bin design.6th, the coal mine mine shaft coal bin gas government installment founded our country nonmotile government gas new experience.7th, the coal mine mine shaft coal bin gas agglomeration governs the equipment safely reliable.This equipment will be forever is solid, the nonmotile structure facility, guarantees this system the security.8th, the coal mine mine shaft coal bin gas government installment, its economic efficiency huge, the social efficiency has, the reality significance profoundly.9th, pointed out specially this practical new coal mine mine shaft coal bin gas government installment is: Does not have the noise, the nonmotile, the non-pollution well ventilated structure facility, belongs to the environmental protection energy conservation product purely.Fifth, uses the value and the significanceThe new installment has filled our country coal mine mine shaft coal bin gas government blank, founded our country nonmotile government gas new experience and the precedent, opened a new way to all coal mine mine shaft coal bin gas government, has provided the advanced new technology for later coal mine mine shaft coal bin gas government design, has realized the coal mine mine shaft coal bin gas government permanent gasgovernment.Because simultaneously this series equipment structure is simple, manages conveniently, does not have to service frequently, does not need the specialist to operate, has, the economy easyly to do and easy practical, safe reliable and so on the merits, for changes the coal mine image, the elimination society gets up the positive role to the coal mine safety not good impression, therefore easy in the national coal profession promotion use, has the profound practical significance.This equipment principle, may develop all needs to exhaust, the pollution discharge construction, the factory, the mine, as well as residents, kitchen nonmotile exhaust device and so on domains.Sixth, conclusionThe coal mine mine shaft coal bin gas government installment in national and even the world promotion use, founded our country gas government pioneer, guarantees this system the security.Has the promotion use value【中文翻译】2煤矿井下瓦斯治理技术的应用一、概况瓦斯之害,骇人听闻,瓦斯治理,迫在眉睫。
关于采煤煤炭方面的外文翻译、中英文翻译、外文文献翻译
关于采煤煤炭方面的外文翻译、中英文翻译、外文文献翻译附录AProfile : Coal is China's main energy in the country's total primary energy accounted for 76% and above. Most coal strata formed and restore the environment, coal mining in the oxidizing environment, Flow iron ore mine with water and exposed to the air, after a series of oxidation and hydrolysis, so that water acidic. formation of acidic mine water. On groundwater and other environmental facilities, and so on have a certain impact on the environment and destruction. In this paper, the acidic mine water hazards, and the formation of acid mine water in the prevention and treatment of simple exposition. Keywords : mining activities acidic mine water prevention and correction of the environmental impact of coal a foreword is China's main energy, China accounted for one-time energy above 76%, will conduct extensive mining. Mining process undermined the seam office environment, the reduction of its original environment into oxidizing environment. Coal generally contain about 0.3% ~ 5% of sulfur, mainly in the form of pyrite, sulfur coal accounts for about 2 / 3. Coal mining in the oxidizing environment, flow and iron ore mine water and exposed to the air, after a series of oxidation, hydrolysis reaction to produce sulfuric acid and iron hydroxide, acidic water showed that the production of acid mine water. PH value lower than the six said acidic mine water mine water. Acid mine water in parts of the country in the South in particular coal mine were more widely. South China coal mine water in general pH 2.5 ~ 5.8, sometimes 2.0. Low pH causes and coal of high sulfur closely related. Acid mine water to the formation of ground water have caused serious pollution, whilealso corrosion pipes, pumps, Underground rail, and other equipment and the concrete wall, but also serious pollution of surface water and soil, river shrimp pictures, soil compaction, crops wither and affect human health. An acidic mine water hazards mine water pH is below 6 is acidic, metal equipment for a certain corrosive; pH is less than 4 has strong corrosive influence on the safety in production and the ecological environment in mining areas serious harm. Specifically, there are the following : a "corrosive underground rail, rope and other coal transport equipment. If rail, rope by the pH value "4 acidic mine water erosion, 10 days to Jishitian its intensity will be greatly reduced, Transport can cause accidents; 2 "prospecting low pH goaf water, Quality Control iron pipes and the gate under the flow erosion corrosion soon.3 "acidic mine water SO42-content high, and cement production of certain components interact water sulfate crystallization. These salts are generated when the expansion. After determination of when SO42-generation CaSO4 ? 2H2O, the volume increased by 100%; Formation MgSO4.7H2O, v olume increased 430%; Volume increases, the structure of concrete structures.4 "acidic mine water or environmental pollution. Acid mine water is discharged into rivers, the quality of pH less than 4:00, would fish died; Acidic mine water into the soil, damage granular soil structure, soil compaction, arid crop yields fall, affecting workers and peasants; Acid mine water humans can not drink that long-term exposure, people will limbs broken, eyes suffering, enter the body through the food chain. affect human health. 2 acidic mine water and the reasons are mostly coal strata formed in the reduction environment, containing pyrite (FeS2) formed inthe seam-reduction environment. Coal generally contain about 0.3% ~ 5% of sulfur, mainly in the form of pyrite, sulfur coal accounts for about 2 / 3. Coal mining in the oxidizing environment, flow and iron ore mine water and exposed to the air, after a series of oxidation, hydrolysis reaction to produce sulfuric acid and iron hydroxide, acidic water showed that the production of acid mine water. Acidic mine water that is the main reason for forming the main chemical reaction as follows : a "pyrite oxidation and free sulfate ferrous sulfate : 2FeS2 O2 +7 +2 +2 H2O 2H2SO4 FeSO4 2 "ferrous sulfate in the role of oxygen free Under into sulfate : 4FeSO4 +2 Cp'2Fe2 H2SO4 + O2 (SO4) 3 +2 H2O 3 "in the mine water The oxidation of ferrous sulfate, sometimes not necessarily need to sulfate : 12FeS2 O2 +6 +3 H2O 4Fe2 (SO4) 3 +4 Fe (OH) 3 4 "mine water Sulfate is further dissolved sulfide minerals in various roles : Fe2 (SO4) 3 + MS + H2O + / 2 + O2 M SO4 H2SO FeSO4 +5 " ferric sulfate in the water occurred weak acid hydrolysis sulfate produced free : Fe2 (SO4) 3 +6 H2O two Fe (OH) 3 +3 H2SO4 6 "deep in the mine containing H2S high, the reduction of conditions, the ferrous sulfate-rich mine water can produce sulfuric acid free : 2FeSO4 +5 FeS2 H2S 2 +3 +4 S + H2O H2SO4 acidic mine water in addition to the nature and sulfur coal on the other, with the mine water discharge, confined state, ventilation conditions, seam inclination, mining depth and size, water flow channels and other geological conditions and mining methods. Mine Inflow stability, stability of acidic water; Confined poor, good air circulation, the more acidic the water, Fe3 + ion content more; Instead, the acid is weak, the more Fe2 + ion; more deep mining of coal with a sulfur content higher; The larger the area of mining, water flowsthrough the channel longer, oxidation, hydrolysis reactions from the more full, the water more acidic strong, If not weak. 3 acidic mine water prevention and control ? a three acidic mine water under the Prevention of acidic mine water formation conditions and causes from source reduction, reductions, reduced when three aspects to prevent or mitigate damage. 1 "by the source : the seizure election made use of mineral acid, being the case. The main coal-bed mineral create acid when in a mixture of coal pyrite nodules and coal with a sulfur content itself. Coal mining rate is low and residual coal pillars or floating coal lost, abandoned pyrite nodules underground goaf, in which long-term water immersion, Acidic water produced is a major source. Face to reduce the loss of float coal, theuse of positive seized election pyrite nodules, can reduce the production of acidic water substances. Intercept surface water, reduce infiltration. For example, the filling of waste, control of roof to prevent collapse fissures along the surface water immersion goaf. In Underground, particularly old or abandoned wells closed shaft, the mine water discharge appropriate antibacterial agent, kill or inhibit microbial activity, or reduce the microbial mine water quantity. By reducing microbial sulfide on the effective role and to control the generation of acid mine drainage purposes. 2 "reduced discharge : the establishment of specialized drainage system, centralized emission acidic water, and storing up on the surface, it evaporated, condensed, then to be addressed to remove pollution. 3 "to reduce emissions of acid water in time : to reduce the underground mine water in the length of stay, in a certain extent, to reduce the microbial coal oxidation of sulphides, thus helping to reduce acid mine water. Containing pyrite, sulfur, surface water leakage conditions for agood shallow seam, or have formed strong acidic water stagnant water in the old cellar, the pioneering layout to weigh the pros and arrangements, not early in the mine prospecting or mining, leaving the end of mine water treatment avoid long-term emissions acidic water. ? 2 3 acidic mine water treatment in certain geological conditions, Acidic water with calcium sulfate rock or other basic mineral occurrence and the reaction decreases acidity. Neutralizer with caustic soda used for less, less sludge is generated, but the total water hardness is often high, while reducing the acidity of the water. However, an increase in the hardness, and the high cost is no longer. Currently, treatment for a neutralizer to the milk of lime, limestone for the neutralizer and limestone -- lime, microbiological method and wetlands treatment. Neutralizer milk of lime treatment method applicable to the handling of a strong acid, Inflow smaller mine water; Limestone -- lime applied to various acidic mine water. especially when acidic mine water Fe2 + ions more applicable, but also can reduce the amount of lime; microbiological method applied when the basic tenets of iron oxide bacterial oxidation than iron, bacteria from the aquatic environment intake of iron, then to form ferric hydroxide precipitation-iron in their mucus secretions, Acidic water at the low iron into high-iron precipitates out and then reuse limestone and free sulfuric acid, can reduce investment, reduce sediment. Wetlands Act also known as shallow marshes, this method is low cost and easy operation, high efficiency, specific methods not go into details here. Conclusions Most coal strata formed and restore the environment, coal mining in the oxidizing environment, Flow iron ore mine with water and exposed to the air, after a series of oxidation and hydrolysis, so that water acidic. formation of acidicmine water. On groundwater and other environmental facilities, and so on have a certain impact on the environment and destruction, Meanwhile harmful to human health caused some influence. Based on the acidic mine water cause analysis, and to take certain preventive and treatment measures, reduce acid mine water pollution in the groundwater, environmental and other facilities and the damage caused to human health effects. References : [1] Wang Chun compiled, "hydrogeology basis," Geological Press, Beijing. [2] Yuan Ming-shun, the environment and groundwater hydraulics research papers on the topic, the Yangtze River Academy of Sciences reported that 1994,3.[3], Lin Feng, Li Changhui, Tian Chunsheng, "environmental hydrogeology," Beijing, geological Press, 1990,21.附录B简介:煤炭是我国的主要能源,在我国一次性能源中占76%以上。
煤矿矿井通风系统中英文对照外文翻译文献
中英文对照翻译比较美国煤矿矿井通风系统的效率摘要随着能源消耗的加剧,提高煤矿通风系统的效率成为了一个日益重要的课题。
因为通风机的耗能占了煤矿能耗的一大部分,因此建立一个高效的通风系统是煤矿主动降低生产成本的重要途径。
通常,衡量矿井通风系统效率的方法是计算其容积效率,简记作用于矿井生产的有效风量占矿井总风量的比例。
这个衡量标准的目的是用数据来对美国的矿井通风系统做一次全国性的比较。
这项研究的成果旨在揭示当今煤矿通风系统的效率以及哪些因素可能导致矿井通风系统效率的或高或低。
容积效率的定义矿井通风系统的容积效率定义为矿井的有效风量与矿井总风量的比值。
大家对“有效风量”的组成还是众说纷纭。
McPherson把有效风量定义为:“到达工作面的风和那些用于稀释例如:机电硐室、水泵房和充电站等硐室内空气的风的总和”。
然而,Hartman则认为有效风量包括总回风石门风量和带区内风量的总和。
本次研究中,我们认为矿井空气中的有效风量包括用于稀释工作面空气的风,还有用于主要生产设备(例如机电硐室、泵房以及充电站等)用风点的风量之和。
在确定矿井主要风机总风量和矿井有效风量总和之后,下列公式可以用来计算矿井通风系统效率。
%100⨯=主要风机总风量矿井有效风量通风系统效率 (1) 通风系统效率值会在一个很大的范围内波动。
McPherson 的陈述中透露通风效率值可以从75%降至10%。
本次研究中,矿井通风系统的效率值在14.5%到71.6%的范围内。
当矿井通风系统的效率值在一个较低的水平时,意味着主要通风机鼓出的大量的风没有起到作用,导致了大量潜在的能源浪费。
导致通风系统效率降低的因素造成容积效率低下最主要的两个因素包括漏风和流经废弃工作面、采空区而损失的风。
由于石门和填充物而产生的漏风可以通过改善矿井的建设以及加强维护来实现最小化。
然而,无论矿井建设的质量有多么棒,在那些使用了大量填充物的矿井中想要避免漏风是不可能的。
另外,随着通风机风压上升,漏风也自然而然的就会增多,因此,在高风压风机的矿井中更易于产生漏风。
煤矿的环境问题及其解决方案外文文献翻译
英文原文Environmental issues from coal mining and their solutionsBIAN Zhengfu, Inyang Hilary I, DANIELS John L, OTTO Frank, STRUTHERS SueInstitute of Land Resources, China University of Mining & Technology, Xuzhou 221008, ChinaAbstract: The environmental challenges from coal mining include coal mine accidents, land subsidence, damage to the water environment, mining waste disposal and air pollution. These are either environmental pollution or landscape change. A conceptual framework for solving mine environmental issues is proposed. Clean processes, or remediation measures, are designed to address environmental pollution. Restoration measures are proposed to handle landscape change. The total methane drainage from 56 Chinese high methane concentration coal mines is about 101.94 million cubic meters. Of this methane, 19.32 million, 35.58 million and 6.97 million cubic meters are utilized for electricity generation, civil fuel supplies and other industrial purposes, respectively. About 39% of the methane is emitted into the atmosphere. The production of coal mining wastes can be decreased 10% by reuse of mining wastes as underground fills, or by using the waste as fuel for power plants or for raw material to make bricks or other infrastructure materials. The proper use of mined land must be decided in terms of local physical and socio-economical conditions. In European countries more than 50% of previously mined lands are reclaimed as forest or grass lands. However, in China more than 70% of the mined lands are reclaimed for agricultural purposes because the large population and a shortage of farmlands make this necessary. Reconstruction of rural communities or native residential improvement is one environmental problem arising from mining. We suggest two ways to reconstruct a farmer’s house in China.Keywords:mine environment; management of mining wastes; reuse of mine gas; mined land reclamation; clean coal mining1 IntroductionWhile coal makes an important contribution to worldwide energy generation, its environmental impact has been a challenge. In essence, the coal energy production system consists of coal mining, preparation or processing and energy generation. Fig.1 shows the complete process of the coal energy system. Environmental issues arise at every stage of the process.This paper will discuss environmental issues due to coal mining. In fact, environmental problems from coal mining have been studied since coal mining became industrialized. Nevertheless, environmental issues from coalmining have become important concerns only since the 1970’s. The majority of the available literature related to mining and the environment date from the end of the 1970’s to the end of the 1980’s. However, coal production has changed significantly since the beginning of th e 1990’s and, as a result, the way and the extent that mining operations impact the environment are also different now. Fig. 2 shows the change in worldwide coal production over time, which illustrates that coal production increased strikingly after 2000. Six countries, the USA, Russia,India, China, Australia and South Africa, produced 81.9% of the total coal extracted throughout the world in 2006. These same countries have about 90% of the World’s coal reserves. Coal production in China accounted for 38.4% of the worldwide total and has increased about 66% over the past five years from 1.38 billion tons in 2001 to 2.3 billion tons in 2006. During the same time period the number of coal mines was reduced by 50%. The annual production of the Daliuta Coal Mine, one of the underground mines operated by the Shendong Coal Mining Company, reached 20 million tons from only two longwall work faces in 2007. In the U.S. the situation is similar to China. There were 2475 coal mines with a total production of 945424 thousand short tons in 1993 but 1438 coal mines producing 1162750 thousand short tons in 2006.China consumes more coal than Europe, Japan and the United States combined; 40% of the world’s total.China’s coal use continues to grow every year and it is estimated that 90% of the rise in world coal consumption is from increased activity in China. As a result, mining intensity in some coalfields is ten times greater than it was in the past. Therefore, the impact of mining on the environment today is significantly different from that in the 1980’s. Thus, this paper focuses on environmental issues due to coal mining in the context of current mining operations.2 Importance of coal mining to energy systems worldwide and challenges to the environmentThe main use of coal in the United States is to generate electricity. Coal generates half of the electricity used in the United States[3]. Today, 91.9% of all the coal in the United States is used for electricity production. In contrast, less than 50% of all the coal mined in China was used for electricity generation in 2005 when 82% of the electricity used in China came from coal fired plants. Coal accounts for approximately 74% of China’s primary energy consumption. Coal is recognized as a dirty source of energy and has been rendered obsolete in many European countries. For example, France closed all coal mines in 2004 and, in early 2007, the German government announced that subsidies for coal production would be completely phased out by 2018. Whether this will mark the end of deep mining in Germany remains to be seen. Some experts and institutions forecast that coal will continue to underpin the economic and social development of the world’s biggest economies in both the developed and developing world[4]. The World Bank Group estimated that coal is one of the World’s most plentiful energy resources and that its use is likely to quadruple by 2020[5]. Global recoverable coal deposits exceed 1 trillion tons with enough deposits to last for the next 270 years at current consumption rates. Hence, it is reasonable to conclude that coal will continue to be an important energy source andthat coal mining is not a sunset industry. This will be especially true in those countries with abundant coal reserves and increased energy demands for their development. Using coal as an energy source requires addressing environmental challenges from mining. This includes coal mine accidents, land subsidence, water pollution, air pollution, spoil heaps, acid mine drainage, disturbance of hydro-geology and so on. The impact of coal mining on the environment varies in severity depending on whether the mine is active or abandoned, the mining methods used and the geological conditions.2.1 Coal mine accidentsEvery year nearly 80% of the World’s total deaths due to coal mine accidents occur in China[7]. The main causes of coal mine accidents are gas leaks, roof cave-ins, fires, blasts and floods/water bursting. Table 1 shows accident statistics for Chinese coal mines for the years 2006 and 2007. This data was compiled by the corresponding author from the State Administration for Coal Mine Safety safety bulletins. It is easy to see that coal dust and methane blasts are in the absolute majority. In addition, 117 of the 374 deaths in 2006, and 92 of the 399 deaths in 2007, occurred in coal mines with a production of less than 200 thousand tons. It was reported that coal mines with small scale production account for one third of total production, two third of the total coal mine accidents and 75% of the deaths.2.2 Land subsidenceApproximately 60% of the world’s coal production comes from underground mines. Since 95% of the coal production in China is from underground mines and, in 2007, Chinese production was 2523 million tons, which accounts for more than one-third of the world’s production, China accounts for much of the underground operation, see Table 2.Land subsidence over underground mines is one important adverse impact of mining on the environment. About 1 million hectares of subsided land exists today. Mining ten thousand tons of raw coal will result in 0.2 hectares of subsiding land in China. Land subsidence not only reduces crop production but also causes other environmental problems, such as utility failures, plant death, surface fracture and soil loss, drainage system failure, building damage and so on.Subsidence falls into two forms of deformation: continuous and discontinuous. Continuous, or trough, subsidence involves the formation of a smooth surface profile free of steps. Discontinuous subsidence is characterized by large surface displacements over a limited surface area and by the formation of steps or discontinuities in the surface profile. Mining subsidence will affect land use or the environment differently depending upon the context of the terrain, groundwater level and the original type of land use.For example, in eastern China, which has plain land-form, shallow groundwater levels and was prime farmland before mining, mining subsidence has resulted in large area flooding. After this the land use was changed as buildings, roads and croplands were seriously damaged by major incidents of land subsidence. Mining subsidence in mountain areas will induce slope failurecausing the loss of water and soil from the formation of surface cracks and overburden fracture from mining.3 A conceptual framework and potential solutions to the mine environment3.1 A conceptual framework for solving mine environmental issuesThe key words green mining, ecological mines, recycling economy, industrial ecology, site characterization for remediation of abandoned mine lands and life cycle assessment were proposed by environmentalists, economists and scholars working in the field of mining science. The core ways to solve mine environmental problems may fall into two types. One is the taking of measures to lessen the impact of mining on the environment during mining. The other is the taking of measures to clean or remediate or restore or reclaim the environment post mining.3.2 Use of mine gasThe Ministry of Environmental Protection and the General Administration of Quality Supervision,Inspection and Quarantine of China have jointly issued the Emission Standard of Coalbed Methane/Coal Mine Gas (on trial). The Standard requires that measures to drain and utilize the mine gas must be taken before mining. Coal mining operations may only be implemented after the methane content in the coal seam is reduced to less than eight cubic meters per ton of coal. If the concentration of methane is higher than 30% atmospheric release is prohibited. There are currently two ways to drain mine gas in China. One is by drilling wells through the coal seam at the coalfield before mining operations begin. The concentration of methane obtained this way is higher than 90% the other method is to drill boreholes through the goaf after coal has been mined. Methane concentrations obtained in this way are higher than 30%.3.3 Conservation and restoration of the mine water environmentWe developed some mining techniques that make full use of water leaking from fractured aquifers that preserve the aquifer. For coal mines in western China constructing a concrete wall along mined lanes and cavities and channeling water resulting from mining into an underground reservoir has proved useful. The Bulianta coal mine operated by the Shendong Branch Company of the Shenhua Group, which has an annual coal production of about 20 million tons and is located in Inner Mongolia, collects 4000 tons of water per day from underground mining operations after constructing such an underground reservoir. For coal mines in eastern China we proposed that key strata should be controlled to prevent fracture, or be restored by grouting after fracture, to prevent water burst into the mined space.3.4 Management of mining wastesCoal mining generates huge amounts of waste, indeed this is the largest source of solid waste accounting for 40% of all solid wastes in China. The waste consists of materials that must be removed to gain access to the coal resource such as topsoil, overburden or waste rock as well as wastes from coal preparation and gangue from underground mining. A series of accidents in recent years has highlighted the significance of reuse of these mining wastes and the urgent need for better waste management procedures. Management of mining wastes involves their reduction, recycle and reuse. This method goes by many other names such as cleaner production, clean technology, waste minimization, pollution prevention, waste recycling, resource utilization, residue utilization, TRU (Total Resource Utilisation) and TPD (Total Project Development). Innovative mining techniques are the main way to reduce the production of mining wastes.4 Strengthening cooperation between parties to solve environmental problems from coal miningCoal is a dirty energy source because of land disturbance; subsidence; AMD and water pollution that occur during mining. There is also the emission of CO2 during coal utilization to consider. But coal is also cheap, affordable, abundant and available. It is easy to transport and secure and will be with us for the long term. It must be considered that the present energy structure in some countries can not be changed over the short term because of the natural deposits of energy resources. For example, China predominantly relies on coal resources for energy not because China does not want to use more clean energy, such as natural gas or oil, but because these are not abundant enough to meet the needs of rapid social and economic development. Demand for coal continues to grow and coal reserves are adequate to ensure that demand can be met far into the future. Therefore, it is necessary to strengthen cooperation between multiple parties to solve the environmental problems due to coal mining.5 Conclusionscoal is one of the World’s most plentiful energy resources. It is today and will be in the future the most important global source of electricity. This is likely to be true for the next 50 years in light of available natural resources and technological advances. Coal mining and utilization will inevitably cause negative environmental effects including coal mine accidents, land subsidence, pollution of water environments, disposal of mine waste and air pollution. Current Chinese coal production and its environmental impacts were analyzed under the context of worldwide coal mining.中文译文煤矿的环境问题及其解决方案卞正富,希拉里·殷阳,约翰·丹尼尔斯,奥托·富兰克,STRUTHERS Sue 土地资源研究所,中国矿业大学,徐州,中国摘要:煤炭开采的环境挑战包括煤矿事故,地面沉降,水环境的损害,采矿废物处置和空气污染。
矿井通风煤矿瓦斯利用中英文对照外文翻译文献
矿井通风煤矿瓦斯利用中英文对照外文翻译文献中英文对照外文翻译弗吉尼亚州和西弗吉尼亚州的8个煤矿已经成功开发了瓦斯回收利用工程。
维吉尼亚州的康索尔煤矿最有见证的例子。
在1995年,康索尔的3个煤矿生产了大约688×106m3的可销售瓦斯。
在这些煤矿的瓦斯回收率高达60%。
2.3.3西南部地区直到1994年瓦斯市场价格走低,犹他州的士兵峡谷煤矿煤矿每年都回收大约10.9×106m3的瓦斯用于销售。
2.3.4小结以上描述的矿井已经和高效率的、经济的回收瓦斯,但为了安全地、高量地生产的目的,分离瓦斯的努力依然很有诱惑。
在美国,许多瓦斯矿井被限制抽放瓦斯甚至不允许。
2.4德国1995年,德国生产将近540万吨硬煤,全部来自地下开采。
其中的430万吨由德国西北部的鲁尔区盆地开采得到,并且其余的大部分由德国西南部的萨尔河盆地开采得到。
直到最近,在德国硬煤开采得到大量补贴,煤炭业的将来成为问题。
即使煤矿被关闭,在相当一段时间里,它们依然会释放瓦斯。
粗略估计,在德国每年由于地下采煤活动释放1.8×109m3的瓦斯。
其中的520×106m3,即其中的30%是抽放出来的。
(63IEA,1994)大约371×106m(即抽放瓦斯的71%)主要用于加热或发电。
政府部门提议:由于开采煤而涌出的瓦斯的45%都可以抽放并以各种形式利用。
目前,提高瓦斯回收利用的主要障碍是混合气体中瓦斯浓度低。
德国安全规程规定:如果瓦斯浓度低于25%,那么禁止了利用。
25中英文对照外文翻译如果想进一步提高德国的瓦斯利用效率,那么有必要采取一些措施以高浓度瓦斯形式回收利用。
3降低瓦斯释放量的障碍通过增加煤矿瓦斯利用来降低瓦斯释放的障碍重重。
有技术因素,如煤的渗透性差,还有一些传统因素,像瓦斯价格低廉。
许多年来,一些国家或地区面临特殊障碍,但大多的情况是许多国家面临着共同的困难。
这一部分将探讨增加煤矿瓦斯利用方法及克服种种障碍的可行方法。
采矿工程中英文对照外文翻译文献
中英文对照外文翻译文献(文档含英文原文和中文翻译)译文:新技术和新理论的采矿业跨世纪发展摘要:煤炭产业需要更长远的发展,对工作中所讨论的热点在工业中出现新的理论和高科技成功使用在二十世纪末是最美好的,作为被关心的问题需要较快一步的发展,在20世纪中后期产生的新型、高速的新技术是最有吸引力和标志性的,即使在所有行业中不同的冲击变得起来越相关以及部门间彼此合作并明确地叙述许多新的理论,煤炭行业的新科技和新理论是不可避免的,并且包括一切的不可能性。
作者在这篇文章中阐述了他关于采矿学的发展问题的意见,举出了许多令人信服的事实,并对大部分新的情况予以求证。
关键字:采矿工程,矿业产业, 矿业经济学,新技术和高科技1.采矿在国民经济中的重要性今天,科技世界的发展已经引起了对采矿空前的不容忽视,空间工程,信息工程,生物工程和海洋工程的发展,新能源的发现和研究与发展以及新原料在目前和将来逐渐地改变着人类生活的每个方面。
“科学技术是第一生产力”指出了新科技在国民经济的中扮演了重要的角色。
在全球的一些大的国家中,互相竞争为的是努力探测外部的空间,我们不应该忘记基本的事实:有超过五十亿个人生活在地球上。
想要保住地球上的人类,我们必须做到以下四个方面:也就是营养物,原料,燃料和环境。
营养物主要是空气、水、森林、谷物和各种植物,它们都是来自于自然。
原料有铁、铁的金属,稀罕的金属,宝贵的化学的原料和建材的金属。
燃料如:煤炭,石油,天然气,铀,放射性金属元素和其他的发光要素。
这些也在自然界中发生。
最后一种是靠人类来维持的生态环境。
在上述中三个必要的物质中,原料和燃料从地球表面经过采矿学取出服务人类。
生态学的环境和采矿已及上述的三个必要的财产抽出有莫大的关系。
然而,随着新技术和它们进入煤炭行业成果的提高,逐渐使它由朝阳产业变成当日落业并逐渐地褪色消失。
如采矿产业是最古老的劳工即强烈传统的产业,因此,那里没落是在一个民族的特定部份需要的印象而且要再作任何的更高深的研究,并在此之上发展采矿。
常用“矿井通风与空气调节”英汉专业词汇
常用“矿井通风与空气调节”英汉专业词汇为了便于一些同学阅读矿井通风与空调方面的英文参考资料和为以后撰写英文论文发表,下面给出了一些常见的矿井通风与空调中英文专业词汇。
---------------------------------------Abandoned workings 废弃坑道Absolute pressure 绝对压力Acceptable accuracy 允许精度Active regulation 主动调节(增压调节)Actual characteristic curves实际特征曲线Adiabatic and isentropic processes等熵线绝热的过程Adiabatic saturation process 绝热饱和过程Aerofoils风板Aerosol particles 气溶胶粒子Air crossings 风桥Air mover 鼓风机Air power空气动力Air pressure management 风压管理Air quantity survey空气质量调查Air regulators 风窗Airborne pollutants空气污染物Airflow measurements 风流测定Airflow reversal反向风流Airlock 气闸Airlocks 风门Airway resistance curve风路阻力曲线Alpha, beta and gamma radiation阿尔法、贝塔和伽玛辐射Altimeters 高度计Angular velocity角速度Asbestos 石棉Atkinson equation阿特金森方程式Atmospheric conditions 大气状态Atmospheric pressure 大气压力Auxiliary ventilation 辅助通风Axial fan轴流风机Axial impeller轴向式叶轮Backfill material 充填材料Barometers 气压计Barometric pressure at inlet 入口气压Becquerel (Bq) 贝克勒尔Bernoulli's equation for ideal fluids 理想流体伯努力方程Biot number 比奥数Blackdamp 窒息气体Blast fume炮烟Booster fans 局扇Boreholes 钻孔Branch resistance分支阻力Branch tree分支树Brattice curtain 风帘Brattices 风帘Bronchioles 细支气管Brownian motion 布朗运动Buoyancy (natural draft) effect浮力作用Burying the fire掩埋火源Cage and skip 罐笼和箕斗Carbon dioxide produced生成二氧化碳Carbon dioxide 二氧化碳Carbon monoxide 一氧化碳Carcinogenic (cancer causing) dusts 致癌粉尘Carnot cycle 卡诺循环Centrifugal fan离心风机Centrifugal impeller离心叶轮Chemical absorption化学吸收Chézy-Darcy equation谢兹-达西方程Chilled water spray chamber 冷却液体喷雾室Choke effect瓶颈效应Circular airway 循环风路Closed loop闭环Closed path回路Coal workers' pneumoconiosis (CWP) 煤工尘肺病Coefficient of drag阻力系数Coefficient of dynamic viscosity动力粘度系数Coefficient of friction摩擦系数Compressed air-assisted sprays 压气助喷雾Compressible flow可压缩流Computational fluid dynamics计算流体力学Condenser cooling tower 凝气器降热塔Condenser 冷凝器Consolidation 固结Contaminants 污染物Continuity equation 连续方程Controlled partial recirculation 受控开路循环通风Controlled recirculation in headings 掘进面受控循环通风Convected energy 扩散能Convective heat transfer 对流换热Conveyance运输工具Copper orebody 铜矿体Cross section of a duct or airway 管道或风路断面Curie, Ci 居里Cylindrical cyclone重力旋流器Dealing with a spontaneous heating 处理自热Degrees Celsius 摄氏度Degrees Kelvin绝对温度Density of gases 气体密度Desorption kinetics解吸动力学Dew point hygrometers 露点毛发湿度计Diaphragm gauge 隔膜片仪表Diesel emissions柴油机排放物Diesel exhaust fume柴油机尾气Diesel particulate matter柴油机颗粒物质Differential pressure instruments 微压差计Dimensionless无量刚Disaster management 灾害管理District systems 分区通风系统Dose rates 剂量率Downcast shaft入风井Droplet diameter雾滴直径Duct system风管系统Dust suppression 降尘Dynamic behavior of molecules 分子运动特征Electrochemical methods电化学方法Electrostatic precipitators 电除尘器Emanation of radon 氡的辐射Empirical method 经验方法Energy recovery device 能量回收装置Enthalpy of moist air潮湿空气的焓Enthalpy 焓Entry and exit losses 入口和出口阻力损失Environmental engineering 环境工程Equivalent length当量长度Equivalent resistance等效风阻Equivalent resistance等效阻力Equivalent sand grain roughness相当砂粒粗糙度Escape way 逃生通道;安全通道Euler's equation欧拉方程Evaporator蒸发器Excavating the fire挖掘火源Exhausting air 抽出空气Exhausting system 抽出式通风系统Explosive dusts 爆炸粉尘Explosives炸药Fan characteristic curve风机特征曲线Fan maintenance 风机维护Fan performance 风机性能Fan static pressure风机静压Fan total pressure风机全压Fan velocity pressure风机速度压Fibrogenic dusts 矿渣粉尘Filament and catalytic oxidation (pellistor) detectors丝状催化氧化探测器Fire triangle 火三角Firedamp 甲烷Firefighting with water 以水灭火First law of thermodynamics 热力学第一定律Fixed point measurement固定点测量Fixed quantity branch固定风量分支Flame safety lamps灯具安全火焰Flexible tubing 柔性风筒Flooded orifice scrubber 水淹孔洗涤器Flooding and sealing off 溢出和密封作用Flow work 流动功Fluid mechanics 流体力学Fluid pressure 流体压力Fog 雾Fogged air 雾气Forcing air压入空气Forcing or blowing system 压入式通风系统Fourier number傅里叶数Fragmented rock 破碎岩石Free crystalline silica (quartz, sand stones, flint)游离硅晶体Friction factor摩擦系数Frictional flow 摩擦流动Frictional losses摩擦损失Frictional pressure drop摩擦压降Frictional resistance 摩擦阻力Frictionless manner 无摩擦状态Gas adsorbents 气体吸收剂Gas chromatography气相色谱Gas constants 气体常数Gas drainage 瓦斯抽放Gas laws 气体定律Geothermic gradient 地热梯度Gob drainage采空区抽放气体Grab samples 样品收集Gravitational field 重力场Gravitational settlement of particles 引力沉降颗粒Gravitational settlement 重力沉降Hair hygrometers 毛发湿度计Hardy-Cross technique哈代克劳斯技术Haulage airways 运输风路Haulage level 运输平巷Heat capacity 热容Heat cramps 中暑痉挛Heat diffusivity 热扩散系数Heat exchanger 换热器Heat exchange换热Heat exhaustion 热量消耗Heat fainting 热昏厥Heat flux 热通量Heat illness 中暑Heat rash 热疹Heat stroke 中暑Heat tolerance 耐热性Heat transfer coefficient 传热系数High expansion foam高倍数泡沫High pressure tapping高压测压孔Hoisting shaft提升竖井Hot wire anemometer热线风速仪Hydraulic radius水力半径Hydrogen sulfide硫化氢气Hydrolift system 水力提升系统Hydropower 水电Ice system 冷却系统Ideal gas 理想空气Ideal isothermal compression理想恒温压缩Immediate response 应急反应Induction 感应Industrial Hygienists 工业卫生学家Inhalation rate吸入速度Initiation of explosions引发爆炸Injection of inert gases注射惰性气体Inlet and outlet ducts入口和出口管In-situ measurement 现场测量Intake airway 进风风路Interception and electrostatic precipitation 截留和静电沉淀Interference factor干扰因素Interferometers干涉计Internal Energy 内能Ionization smoke detectors离子感烟探测器Iron pyrites黄铁矿Jet fan 射流风机Junction节点Kata thermometer 卡它计Kinetic energy 动能Kirchhoff's Laws 基尔霍夫定律Laminar and turbulent flow层流和紊流Laminar resistance 层流阻力Laminar sublayer层流次边界层Laser spectroscopy激光光谱学Latent (or hidden) heat of the air空气的潜热Layout of mine 矿井布置Leakage control漏风控制Legislation 法规Level workings阶段工作面Loading station装运站Longitudinal fittings纵向装备Longwall长壁开采法Machine mounted gas monitors悬挂式气体检测器Main fans 主扇Main haulage route主运输道Main return 主(总)回风道Manometers 压差计Mass flow 质量流量Mass spectrometers质谱仪Mean free path 平均自由程Mean velocity of air 平均风速Mesh selection网孔选择Mesh网Metabolic heat balance 代谢热量平衡Metabolic heat代谢热Metal mine fires金属矿井火灾Meteorology 气象Methane drainage瓦斯排放Methane 甲烷Method of mining 采矿方法Mine climate 矿井气候Mine resistance 矿井阻力Mine ventilation 矿井通风Mist eliminator 除雾器Mist 雾Moisture content (specific humidity) of air空气的含湿量Momentum 动量Monitoring systems 监测系统Moving traverses运动线路Natural ventilating effect自然通风影响Natural ventilation 自然通风Neutral skin temperature 中性表皮温度Nikuradse's curves 尼库拉则曲线Nondispersive infra-red gas analyzer非分散红外线气体分析仪Nuisance dusts 粉尘污染Numerical method数值方法Nusselt number努塞尔数Old workings老工作面One standard atmosphere 一个标准大气压Open and concealed fires 明火和隐蔽火灾Ore pass 放矿溜井Ore production矿石生产Orebody deposit 矿体Outbursts from roof and floor 顶板和底板瓦斯突出Overlap systems of auxiliary ventilation 混合式局部通风Oxides of nitrogen氧化氮Oxygen Consumption耗氧量Parallel network or circuit并联网络或回路Paramagnetic analyzer 顺磁分析仪Passive regulator 可调风窗Pellistor methanometers瓦斯检定器Peripheral velocity圆周速度Permanent environmental monitors 持久环境监控Permeability 渗透率Personal dosemeters 个人剂量计Personal respirators 个体呼吸器Phases of oxidation氧化反应阶段Photometric (light-scattering) methods 分光光度Physical adsorption物理吸附Physical thermodynamics 物理热力学Pick face flushing and jet-assisted cutting 锯齿面冲洗与喷气助推器切割Piezoelectric instruments 压电仪器Pitot-static tube皮托静压管Polyvinyl chloride (PVC)聚氯乙烯Potential energy 势能Prandtl number 普兰特尔数Precautions against spontaneous combustion自燃预防Pressure energy 压能Pressure head 压头Pressure surveys压力调查Pressure transducers 压力传感器Pressure-volume surveys压力容积测量Profilometer轮廓仪Psychrometric chart 温湿图Psychrometric measurements 干湿度测量Push-pull system 压-抽混合式通风系统Radial velocity径向速度Radiation 辐射Radiative heat transfer 辐射传热Radioactive decay and half-life放射衰变和半衰期Radon daughters氡子体Radon decay constant 氡的衰变常数Radon, Rn氡气Ramp 斜坡道Rates of heat production 生产率Rates of oxygen consumption 氧气消耗率Refrigerant fluid 制冷液Refrigeration cycle制冷循环Refrigeration systems 制冷系统Refuge chambers避难洞室Regulator 调节器Relative humidity and percentage humidity相对湿度和湿度率Removal of dust from air 气体除尘Re-opening a sealed area重开封闭区Respirable dust呼吸性粉尘Respiratory system 呼吸系统Return airway 回风巷Reynolds Number雷诺数Room and pillar房柱式Rotating vane anemometer旋转叶片风速表Rough pipes 粗管Roughness粗糙度Safety and Health 安全卫生Saturation vapor pressure 饱和蒸汽压Sealants密封剂Seals 密闭Second law of thermodynamics 热力学第二定律Self-heating temperature (SHT) 自热温度Self-rescuers 自救器Sensible heat of the air 空气的显热Series network or circuit串连网络或回路Shaft fittings 井筒装备Shaft wall井壁Shear stress 剪切应力Shock loss factor冲击损耗系数Shock losses 冲击损失Short-Term Exposure Limit (STEL) 短时间接触阈限值SI system of units 国际标准单位体系Sigma heat 西格玛热Smoke tube烟筒Smoking and flame safety lamps 烟火安全灯Smooth concrete lined光滑混凝土内衬Specific heat (thermal capacity)比热容Specific heats 比热Spontaneous combustion of sulfide ores硫化矿自燃Spontaneous combustion自燃Spontaneous heating 自热Spot cooler 现场冷却器Spray fan 喷雾风机Steady flow energy equation稳流能量方程Steady flow physical thermodynamics稳流物理热力学Steady-flow thermodynamics 稳定流热力学Stokes' diameter斯托克斯粒径Stoping areas 回采区Stoppings 密闭Subsurface openings 地下空间Subsurface ventilation 地下通风Sulfide dust explosions 硫化矿粉尘爆炸Sulfur dioxide二氧化硫Sulfuric acid vapor硫酸雾Swinging vane anemometer摆动叶片风速表Tangential velocity at outlet出口切向速度Temperature-entropy diagram温熵图Temporary stopping暂时停止Terminal velocities 自由沉降速度The square law平方定律Thermal conductivity of insulation 绝缘导电温度Thermal conductivity导热系数Thermal equilibrium 热平衡Thermodynamic state 热力学状态Thermoluminescent dosemeters (TLD) 热释光剂量计Thermoregulation 体温调节Threshold limit values (TLV) 阈限值Through-flow ventilation 贯穿通风Time-Weighted Average (TWA)时间加权平均Total energy balance 总能量守恒Total shaft resistance 井筒总阻力Tube bundle systems 管束系统Turbulent resistance紊流阻力U tube manometers U型压差计U tube U型管Uncontrolled recirculation 无控循环通风Underground ventilation system 地下通风系统Unloading station卸载站Upcast shaft出风井Uranium mines 铀矿Vasodilation 血管舒张Velocity contour等流速线Velocity limit速度限值Velocity pressures 动压Velometer速度计Ventilation circuit 通风回路Ventilation door 风门Ventilation engineers 通风工程师Ventilation network analysis通风网络分析Ventilation planning 通风设计Ventilation raise 通风天井Ventilation survey team 通风测量术语Ventilation survey通风测量Venturi scrubber文丘里洗涤器Vertex顶点Viscosity 粘度Viscous drag粘性阻力Volume flow 体积流量Volumetric efficiency 容积效率Vortex-shedding anemometer漩涡式风速表Water gauge pressure 水柱压力Water infusion 注水(水封孔)Water mass flowrate 水质量流量Water vapor content 水蒸气含量Wet and dry bulb hygrometers (psychrometers)干湿球温度表Wet bulb thermometer 湿球温度计Wet Kata thermometer湿球卡他温度表Wet scrubbers湿式除尘器Wetting agents 润湿剂Worked-out area采空区Working face工作面Working level month, WLM 工作水平月Working Level 开采水平Zinc blende闪锌矿——上述词汇摘录自:吴超主编。
煤矿井下瓦斯涌出控制外文文献翻译、中英文翻译
Control of gas emissions in underground coal minesKlaus Noack*DMT-Gesellschaft für Forschung und Prüfung mbH, Institut für Bewetterung, Klimatisierung und Staubbekämpfung, Franz-Fischer-Weg 61, Essen, Germany Received 2 August 1996; accepted 24 February 1997. Available online 24 November 1998.AbstractA high level of knowledge is now available in the extremely relevant field of underground gas emissions from coal mines. However, there are still tasks seeking improved solutions, such as prediction of gas emissions, choice of the most suitable panel design, extension of predrainage systems, further optimization of postdrainage systems, options for the control of gas emissions during retreat mining operations, and prevention of gas outbursts. Research results on these most important topics are presented and critically evaluated. Methods to predict gas emissions for disturbed and undisturbed longwall faces are presented. Prediction of the worked seam gas emission and the gas emission from headings are also mentioned but not examined in detail. The ventilation requirements are derived from the prediction results and in combination with gas drainage the best distribution of available air currents is planned. The drainage of the gas from the worked coal seam, also referred to as predrainage, can be performed without application of suction only by over or underworking the seam. But in cases where this simple method is not applicable or not effective enough, inseam-boreholes are needed to which suction is applied for a relatively long time. The reason for this is the low permeability of deep coal seams in Europe. The main influences on the efficiency of the different degasing methods are explained. Conventional gas drainage employing cross measure boreholes is still capable of improvement, in terms of drilling and equipment as well as the geometrical borehole parameters and the operation of the overall system. Improved control of gas emissionsat the return end of retreating faces can be achieved by installation of gas drainage systems based on drainage roadways or with long and large diameter boreholes. The back-return method can be operated safely only with great difficulty, if at all. Another method is lean-gas drainage from the goaf. The gas outburst situation in Germany is characterized by events predominantly in the form of ‘non-classical' outbursts categorized as ‘sudden liberation of significant quantities of gas'. Recent research results in this field led to a classification of these phenomena into five categories, for which suitable early detection and prevention measures are mentioned.Author Keywords: gas emission; prediction; pre-degassing; gas drainage; gas outbursts1. IntroductionCoal deposits contain mine gas (mostly methane) in quantities which are functions of the degree of coalification and permeability of the overburden rocks. This is the reason why the gas content of coal seams (and rock layers) varies from 0 m3/t in the flame coal and gas-flame coal of the northwestern Ruhr Basin to >25 m3/t in the anthracite of Ibbenbüren in Germany.When influenced by mining activities this gas is emitted into the coal mine. For better understanding of this process a distinction has been established between basic and additional gas emissions. Basic gas emission is the gas influx from the worked coal seam, which is the equivalent of a partial influx in a multi-seam deposit and of the total gas influx in a single-seam deposit. Additional gas emission represents gas influx coming from neighbouring coal seams (in the case of a multi-seam deposit) and from associated rock layers. The additional gas emission may be in excess of ten times the basic gas emission. So it is mostly the additional gas emission which determines the measures to control the gas emission.In Germany the gas emission is considered to be under control if the gas concentration of the mine air can be kept permanently at all relevant places under 1% CH4. This value is at an adequate distance to the lower explosion limit of methane-air mixtures, which under normal conditions is 4.4% CH4. In exceptional cases, thepermissible limit value can be raised to 1.5% CH4. For historical reasons, different permissible limits sometimes apply in other countries, for example 1.25% CH4 in the United Kingdom and up to 2% CH4 in France.Basically, the options for control of gas emission are as follows:(1) Total avoidance of gas release from the deposit. This is only possible with regard to the additional gas emission and only for mining procedures which do not affect stability; hence permeability of the overlying and underlying strata (e.g., room-and-pillar mining where the pillars are left standing during the development phase).(2) Removal of the gas from the deposit before working. For this purpose, all procedures for pre-degassing, either by vertical or by deflected cross measure boreholes drilled from the surface, or by inseam-holes drilled below ground, are technically suitable provided the natural or induced gas permeability permitspre-degassing.(3) Capture and drainage of the gas during mining operations before it mixes with the air flow. This is a classic procedure developed for capturing the additional gas using drainage boreholes, drainage roadways or drainage chambers.(4) Homogenize and evacuate the gas influx after diluting it with sufficient amount of air. This involves panel design, air supply, air distribution, and the prevention of gas outbursts.The following discussions concentrate on problems which are currently given priority in the European Union (EU) funded research. They also cover a significant portion of the gas emission problems worldwide. Problems from non-EU states (e.g., Australia, the Community of Independent States (CIS), South Africa and the United Stated of America (USA)) are also taken into consideration, as far as the author's knowledge permits it. This subject matter is presented in a condensed form under the following headings: prediction of gas emissions; measures taken to control gas emissions; pre-degassing of coal seams; optimization of conventional gas drainage; control of gas emissions for retreating faces; and prevention of gas outbursts.2. Prediction of gas emissionsPrediction of firedamp emission has been practized for many years in the German hardcoal industry (Winter, 1958; Schulz, 1959; Noack, 1970 and Noack, 1971; Flügge, 1971; Koppe, 1975) so that several prediction methods are now available. Among these, the following methods are mentioned:(1) the calculation of the amount of gas emission (Koppe, 1976; Noack, 1985), as used to deal with emission from both the worked coal seam and adjacent seams, which are disturbed by earlier mining activities;(2) the calculation of the reduction of gas pressure (Noack and Janas, 1984; Janas, 1985a and Janas, 1985b), as used in undisturbed parts of the deposit; and(3) prediction methods for the worked coal seam gas emission from longwall faces, for the gas emission from headings and for the gas emission from coal seams cut through during drifting.The first two methods provide a prediction of the specific gas emission from a mine working, expressed in cubic metres of gas per ton of saleable coal production. The gas influx to the mine working in cubic metres of gas per unit time, which is a relevant factor for mine planning, can be derived from multiplying the predicted result by the scheduled production volume.Both methods determine the mean gas emission from a coal face area for a nearly constant face advance rate during a sufficiently long period of time (several months). The prediction assumes that the zone from which the gas is emitted is fully developed, in other words the coal face starting phase has been passed. Furthermore, the coal face has to be above a critical length (i.e., longer than 180–190 m at 600 m working depth and longer than 220–240 m at 1000 m depth).The influx of gas to a coal face area (both into the mine air current and into the gas drainage system) is defined by the following factors: (1) the geometry and size of the zone from which gas is emitted, both in the roof and the floor of the face area, including the number and thickness of gas-bearing strata in that zone; (2) the gas content of the strata; (3) the degree of gas emission, as a function of time- andspace-related influences; and (4) the intensity of mining activities. The geometry and size of the zone from which additional gas is emitted are simplified forming a parallelepiped above and below the worked area; its extension normal to the stratification depends on the prediction method.The number and location, type, and thickness of the strata in the zone from which additional gas is emitted can be derived from existing boreholes, staple-shafts, and roadways inclined to the stratification. The gas content of the strata (Paul, 1971; Janas, 1976; Janas and Opahle, 1986) is difficult to determine. There are two alternatives for direct gas content determination available for coal seams (VerlagGlückauf GmbH, 1987). One alternative uses samples of drillings frominseam-boreholes (for developed seams) and the other alternative uses core samples from boreholes inclined to the stratification (for undeveloped seams). Since a suitable method of determining the gas content of rock is not yet available, a double prediction is made with the first prediction neglecting the rock altogether and the second prediction using the assumption of an estimated gas content of the rock strata.The methods for predicting the proportion of gas content emitted are basically divergent. On the one hand the prediction, which is based on the degree of gas emission, assumes that the emitted gas proportion is not a function of the initial gas content but rather of the geometric location of the relevant strata towards the coal face area. The other method, which relies on gas pressure, commences with a fixed residual gas pressure, hence residual gas content. Its value depends on the geometric location of the strata. This means that the emitted proportion of the gas content, representing the balance against the initial gas content, depends on the latter.2.1. Prediction for previously disturbed conditionsThe method to predict the total gas make from longwalling in a previously disturbed zone in shallow to moderately inclined deposits (dip between 0 and 40 gon) is based on the degree of gas emission (Fig. 1). It uses the degree of gas emission curve designated as PFG for the roof (considering an attenuation factor of 0.016) and the curve designated as FGK for the floor.Fig. 1. PFG/FGK method.For practical reasons the upper boundary of the zone from which gas is emitted is assumed to be at h=+165 m, whereas, the lower boundary is at h=−59 m. In the absence of empirical data a mean degree of gas emission of 75% in the worked coal seam is assumed. Above the seam, from the h=+0 m level to the h=+20 m level, and below the seam from the h=−0 m level to the h=−11 m level, the degree of gas emission is assumed to be 100%.For the purpose of prediction, the surrounding rock strata are considered as fictitious coal seams for which reduced gas contents are assumed. The reduction factors are 0.019 (for mudstone), 0.058 (for sandy shale) or 0.096 (for sandstone).2.2. Prediction for previously undisturbed conditionsThe method to predict the total gas make from longwalling in a previously undisturbed zone is based on the residual gas pressure profiles shown in Fig. 2. There are three zones visible in the roof and two in the floor, which are characterized by varying residual gas pressure gradients. The upper and lower boundaries of the zone from which gas is emitted (hlim and llim, respectively) are defined by the intersection of the residual gas pressure lines and the level of initial gas pressure pu, thus aredependent on the latter.Fig. 2. Gas pressure method: residual gas pressure lines dependent on thicknessof the worked coal seam.The breaking points of the residual gas pressure profile for 1 m of worked coal seam thickness (continuous line) are defined by the coordinates in Table 1, whereas the lines are characterized by the residual gas pressure gradients also in Table 1.Table 1. Parameters for the gas pressure methodFull-size table (<1K)View Within ArticleThe dotted line on Fig. 2 applies to 1.5 m of worked coal seam thickness and shows that the h1 and h2 ordinate levels relating to the roof increase in linear proportion to the thickness of the worked coal seam, with gradients declining correspondingly. There is no dependence on coal seam thickness in the floor, where the value of l1 remains constant at −33 m.Based on the illustrated residual gas pressure profile, the residual gas pressures are first determined layer by layer in accordance with the mean normal distance of a layer from the worked coal seam and afterwards they are converted to residual gas contents using Langmuir's sorption isotherm. The difference between the initial and residual gas contents finally represents the emitted proportion of the adsorbed gas which is the required value. To this value will then be added the free gas, the proportion of which is found by multiplying the effective porosity of the strata under review by its thickness and gas pressure difference. Empirical values have to be used for the effective porosity of coal and rock for methane. Typical values for the coal are between 1 and 10%, and for the rock they are between 0.3 and 1.3%. The values vary in a wide range and depend on chronostratigraphy. In the absence of empirical values for the proportion of gas emission from the worked coal seam a value of 40% would be assumed.2.3. Comparison of the two methodsThe gas pressure method may claim the following advantages over the prediction based on the degree of gas emission: There are no rigid delimitations of the upper and lower zones from which gas is emitted. They rather depend on the value of the initial gas pressure and on the type of strata. In the roof the effect of the thickness of the worked coal seam is considered in the profile of residual gas pressure. The prediction takes into account not only the adsorbed gas but also the free gas; this is for both, the coal seams and the surrounding strata. The total gas content rather than the desorbable proportion is used for the prediction.2.4. Other methodsThe prediction methods for the worked coal seam gas emission in longwalls and for inseam-headings as well as for coal seam cut through operations during drifting with tunneling machines cannot be explained in detail. For further information refer to the following papers: Noack, 1977; Janas and Stamer, 1987; Noack and Janas, 1988; Noack and Opahle, 1992.It should be mentioned that DMT is testing the prediction of gas emission in machine-driven headings on the base of the INERIS method. Fig. 3 shows an excellent conformity between calculated and measured values (Tauziède et al., 1992).Fig. 3. Comparison between calculated and measured values of gasemission.煤矿井下瓦斯涌出控制摘要:一种先进的方法已在与煤矿井下瓦斯涌出极其相关的领域获得。
煤矿瓦斯预防治理中英文对照外文翻译文献
煤矿瓦斯预防治理中英文对照外文翻译文献(文档含英文原文和中文翻译)翻译:西班牙Riosa–Olloniego煤矿瓦斯预防和治理摘要矿井中一直控制存在不同的气体在采矿环境。
这些气体中,甲烷是最重要的,他伴随着煤的产生而存在。
尽管在技术在近几十年来的发展,瓦斯灾害尚未完全避免。
瓦斯气体随着开采深度的增加而增多,甲烷排放量高的地方,也适用于其他采矿有关的情况,如生产的增长率及其后果:难以控制的甲烷浓度增加,机械化程度提高,使用炸药和不重视气控制系统。
本文的主要目的是建立实地测量,使用一些不标准的采矿控制风险评估方法的一部分,并分析了深部煤层瓦斯矿井直立的行为,以及防止发生瓦斯事故的关键参数。
最终目标是在开采条件的改善,提高矿井的安全性。
为此,设置了两个不同的地雷仪表进行矿井控制和监测。
这两个煤矿属于Riosa-Olloniego煤田,在西班牙阿斯图里亚斯中央盆地。
仪器是通过subhorizontal能级开采的,一个约1000米的山Lusorio根据实际深度覆盖的地区。
在本研究中,一个是有利于瓦斯突出的易发煤(第八层),测定其气体压力及其变化,这将有助于提供以前的特征以完成数据,并评估第一次测量的网站潜在的爆发多发地区提供一些指导。
本文运用一个气体测量管设计了一套用于测量一段时间由于附近的运作的结果,计算低渗气压力以及其变化。
本文建立了作品的重叠效应,但它也表明了两个预防措施和适用功效,即高压注水和一个保护煤层(第七层)的开采,必须优先开采保护层以防止瓦斯气体的涌出。
这两项措施构成的开采顺序,提高矿井安全性。
因此,应该完成系统的测量控制风险:在8煤层瓦斯压力影响的其他地区,要建立最合适的时刻进行开采作业。
进一步的研究可以把重点放在确定的渗透,不仅在瓦斯爆炸危险区,而且在那些还没有受到采矿的工作和更精细的调整过载时间的影响范围和矿井第7煤层和第8煤层之间的瓦斯气体。
关键词:煤矿,煤层气,气体压力渗透率瓦斯突出1 简介近年来,煤层气体和煤矿瓦斯研究蓬勃发展。
煤炭火灾外文文献翻译、中英文翻译
英文原文Coal firesA coal fire is the underground smouldering of a coal seam or coal mine. They are emerging as a global threat with significant economic, social and ecological impacts. Coal seam fires Prevention ExtinctionCoal seam fires may be categorized into near surface fires in outcropping seams that are supported by oxygen from direct contact to the atmosphere and mine fires supported by oxygen from the artificial mine ventilation.Spontaneous coal firesThe final reason for all fires is the chemical reaction of the hydrocarbon molecules of the fuel with oxygen of the air. This exothermal reaction can take place at any temperature. The reaction velocity however is strongly temperature dependent and increases with temperature nearly exponential. If the fuel is broken up in small particles or porous, oxygen has access everywhere and the entire volume may act as a heat source.The situation is not critical if the heat energy transported to the surface by either conduction or convection and finally lost to the environment is larger than the heat produced by the reaction. If the heat produced by the reaction however is over longer time larger than the heat loss to the environment the system will turn to be critical. Temperatures will rise continuously, the reaction will accelerate and finally the fuel will start burning spontaneously.Two factors will finally be responsible: The surrounding temperature and the volume of fuel involved:∙If the surrounding temperatures are higher the oxidation processes will run faster and thus the heat production is higher within the fuel volume.∙If the fuel volume is larger the heat produced inside can hardly flow to the surface and into the environment, the fuel is more likely to start burning. In addition material broken up in small part or porous material usually has a low heat conduction coefficient and may act like thermal isolators.The most important parameter characterizing self ignition is the self ignition temperature. This is not a material constant, but dependent on volume and shape, more specific on the relation of volume and surface. Self ignition temperatures decrease strongly with volume. Furthermore this temperature is dependent on many fuel material parameters as caloric value, heat conduction coefficient, particle size. In case of coal it depends further more on the coal type and rank; for hard coal its generally higher the for brown coal or lignite.If the fuel volume is sufficient spontaneous ignition may happen at room temperatures or at temperature at the yearly average temperature. The time needed for the fire to develop may be month or even years.Brown coal or lignite may start burning at 40 °C to 60 °C whereas anthracite will start (under the same conditions!) at 140 °C. The smouldering will usually start several decimeters below the surface in a depth where the permeability of the coal allows the access of enough air but the air flow is slow enough to not extract the produced heat by convection. Due to the low heat conductance coefficient of coal heat extraction by conduction alone is not sufficient.Factors influencing spontaneous induction are beside others:Air circulationClimate (arid, semiarid)Coal quality coal type (carbon content, gas content, ash content, rank)Particle size (small particles have larger surface/volume relation)Geological geomorphologic settingsMining influence (Openings, fractures, subsidence)Hydro geological settings (moisture content)Spontaneous ignition needs time. How much depends on many factors, as temperature, volume, particle size. Finally the time to ignition is another parameter to describe the addiction of coal to burn. For larger volumes the temperature needed is smaller but the time needed larger. Normally it will take months before coal will start smouldering.If coal seams outcrop to the surface, air has access for long times, at those location seams will start to burn spontaneous and continue burning for decades. Globally at least 20 to 30 million tons are burned by those fires. The coal being made inaccessible for further mining is about the times more.Heat producing reactionsThere are two know heat producing adsorption reactions:Physisorption of oxygen. This takes place at temperatures up to 50 °C and delivers 42kJ/mol.Chemisorptions of oxygen. This produces several chemical compounds after overcome the activation energy of the coal surface. From carbon-, hydrogen- and oxygen atoms peroxides are formed and about 100 kJ/mol of heat energy is produced. The newly built molecules may oxidize further and produce heat with increasing temperatures and finally exhaust as carbon dioxide, carbon monoxide and water (vapor).The most important reactions are:C und O2 form CO2 (394 kJ/mol)2C und O2 form 2CO (170 kJ/mol)Coal seam fires not spontaneously ignitedNearly all coal seam fire started spontaneously. In some case however external ignition is possible. Finally we may not see if a certain fire started spontaneous or not. This is in any case true for fires in deep mines, but also for fires close to the surface as long as mining is involved. Possible sources for ignition are electrical machinery, bad maintained bearings as well as handling of explosives or wrong application of welding or beveling.In many reported cases leaving back coal in mining application or accumulation of coal dust was the final reason for a fire. Consequent acceptance of mining regulation may avoid most of those fires.Mine fire may interact with methane explosions or coal dust explosions in mines. Near surface coal fires may interact with forest fires. This was reported from the USA and especially from Sumatra, Indonesia.Global coal seam firesCoal fires are reported from coal mining districts all over the world. The most important are the following:IndiaBesides the areas of Ranigani and Singareni coal seam fires rage in Jharia (North West India). In an area of about 700 km2 about 160 fires are burning. As a consequence of the fires hang slides, sink holes and subsidence is reported. As this area is densely populated pollution is severe.Coal mining supports the development of fires it give air better access. On the other hand coal fires imitate the mining and may even stop it. It is estimated that in India 70% of the fires are due to mining.USAMany coal mining areas in the USA suffer from spontaneous coal seam fires. The Federal Office of Surface Mining (OSM) provides a data base (AMLIS) that lists 150 fire zones (1999). Those are not only in Kentucky, Pennsylvania and West Virginia in the east of the Appalachian-coal district, but also in Colorado and the Rocky Mountains.In Pennsylvania 45 fire zones are reported. The most known is Centralia Mine, in the anthracite- coal area of Columbia County. This fire burn since 1962 and develop below the city. There was some effort to extinguishing the fires but finally the city was lost.In Colorado some spontaneous coal fires are due to annual changes in the water table. Those changes may rise water temperatures by 30 °C, and thus start the self ignition process.In Powder River Basin in Wyoming und Montana about 800 billion tons of lignite is known. Already the Lewis-und-Clark-Expedition (1804 to 1806) reported on coal fires in that region. Here we have also coal fires from geological times. They are three million years old and shaped the landscape to a certain extend. An area of 4.ooo km2 is covered with clinker or scoria, part of the laying in the c. Well known and spectacular is the outlook from the scoria point on an extended area of fire red clinker. GermanyIn Planitz near Zwickau a coal seam burned from 1476 and was finally not extinguished before 1860. Ernst August Geitner started in 1479 a green house with tropical plants above the known Planitz fire zone and was possible the first in using energy from coal fires commercially. In Dudweiler (Saar) 1668 a coal seam started to burn and developed to a tourist attraction named 'Burning Mountain', even visited and described by Goethe. Equally known is the so called 'Smelling Wall' at the east slopes of 'Hohe Meissner', where after closing the lignite mining some seams started burning centuries ago and exhaust gases escaped to the surface causing the 'smell'. The hard rock mining was accompanied all time by coal- mainly mine fires. Reported are about two fires per year on average. As the coal mining concentrated in Germany on the Ruhr- and Saar Area, fire prevention technologies were developed in those areas. Today most of the coal fires here are due to unwanted ventilation in abandoned parts of the mines. Those measures were principally successful and heavy mine fires with loss of human life did not occur.After closing the last deep lignite mines in Hirschberg close to Grossalmerode in Hessen in 2003, lignite is mined in Germany in open pits only, in the Rheinische Revier, in the Mitteldeutschen Revier and in the Lausitzer Revier. In the last years no coal fires were reported from these areas as complex strategies of prevention are successful.Rest of Europe and RussiaReported coal fires in those areas are decreasing parallel to the decrease of mining activity in general. Some burning is reported from Poland, Czech Republic and Ukraine. In Ukraine 2.000 million tons are laying on dumps and 74 fire zones are reported. This is mainly in the basins of Kuzbass, Petschora and Donezk.In Kosovo (Serbia) and Bosnia-Herzegovina coal seams are burning close to open pit or deep mining.AfricaThe big coal mining districts of Africa are in the south of the continent, in South Africa, Zimbabwe, Botswana, Mozambique and Zambia. Coal fires are reported from all that regions.AustraliaFive kilometers north of the city of Wingen in New South Wales (NSW) the Burning Mountain is a tourist place since thousands of years. Actually the fire is 30m below surface and advances about 1m per year. Overall it moved about 6 kilometers. Many more fire zones are reported in Australia.ChinaChina is the larges coal producer (and consumer) world wide: It produces about 1.8 billion tons in 2006. As a result coal fires are a severe problem in China. It is estimated that 10-20 million tons are directly burned by coal seam fires and 100-200 million tons of coal are lost for the mining industry. The fire zones are located in a belt covering the entire north of China. More than 100 burning areas are known divided in several burning zones each. Concentrations are in the provinces (autonomous regions) Xinjiang, Inner Mongolia and Ningxia. Besides the loss of energy resources those fires cause air and water pollution and emit enormous amounts of green house gases (carbon dioxide and methane). This mainly causes the international interest in those fires. China is the only country in the world starting and performing enormous activities for extinction. Several fires are already extinguished. New methods are developed within a Sino-German Research Initiative.中文译文煤炭火灾煤炭火灾是指煤层或煤矿的煤炭在地下焖燃的现象。
安全专业本科毕业论文外文文献(煤矿安全方向)中英文对照PDF
附录A非线性矿井通风网络的控制Yunan Hu a,1 , Olga I. Koroleva b,*, Miroslav Krstic ba深空探测研究中心,哈尔滨工业大学,哈尔滨100051 ,中华人民共和国b机械航空工程系,加州大学,圣地亚哥,9500 Gilman Dr. MC0411, La Jolla, CA 92093-0411, 美国摘要:煤矿通风网络的重要作用是使爆炸性或有毒气体(如甲烷)维持在低浓度。
由于其目的是控制流体的流动,所以矿井通风网络是高阶非线性系统。
过去在这一方面的研究是基于多变量线性模型。
本文提出的是一个非线性模型。
开发两个控制算法。
一个人操纵所有的网络分支机构就可实现全球性调控的结果。
其他人只操纵网络中不属于树图的分行,实现监管(非无穷小)工作点的附近区域。
这种针对矿井通风网络提出的方法,也适用于其他类型的流体网络,如燃气或水的分销网络,灌溉网络,并有可能建立起通风系统。
关键词:非线性控制;矿井通风网络;流量控制;暖通空调1.简介石油储备枯竭后,煤作为矿物燃料能源还会保持一段相当长的时间。
煤矿开采的一个主要困难是因为地下的煤矿存在有毒且易爆的气体甲烷。
煤矿事故血的教训从古至今未曾间断。
现代煤矿有的许多调节甲烷浓度的通风设施。
在这种通风系统中通常不是直接控制空气流动,而是通过通风网络的个别部分来控制。
可以在通风网络的重要位置(往往直接连接到外部环境)安置几台风机/压缩机来驱动空气,也可以在网络的分支上用“风门” 来控制。
控制矿井通风的问题在20世纪70年代和80年代才受到相当的重视。
无疑,矿井通风网络是一个分支能影响其他分支的流程的一个多变量控制问题。
为此,作为一个流体网络(这与模拟一个电路非常相像)和一个多变量控制的问题,矿井通风需要接近基于模型的方式。
早期在这个题目上做研究的是Kocic。
他认为矿井通风网络是一个线性化的,各参量混在一起的动态模型并且发现了用线性反馈的规则来研究。
ProfessionalEnglish 矿井通风术语(中英对照)
V ocabulary in Mine VentilationA暗井blind pit安全(保安)措施safety measures 安全范围safe range安全警报safety alarm安全设备safety accessory安全装置safety apparatussafety applianceB饱和能力saturation ability爆破力blasting power爆炸事故explosive accident爆破/ 爆炸explosion崩落区collapse area崩落法开采区block-caved area 闭合回路close path边缘巷道outside airway并联巷道parallel heading并联作业parallel operation不透气的airproof不可压缩流体incompressible fluid捕尘能力dust-catching powerC柴油机diesel采矿工作mining activity采矿工作面片帮事故face-fall accident采空区gob area / mined-out采掘水平extracting levelmining level采取措施, 设法take measures 层流laminar flow抽出式通风exhaust ventilation充电硐室charge room串联通风series ventilation串联作业series operation串联巷道series heading垂直巷道vertical workings粗糙度coarsenessD单位重量流体的能量损失energy loss of per unit of weight of fluid 氮气nitrogen氮氧化物的nitric地压earth pressureground pressure低速风流测量low-velocity airflow measure 调度室deployment room动能差kinetic energy differential 动态参数dynamic parameter动压力/ 动压强dynamic pressure动压velocity pressure动压差dynamic pressure differential 硐室型风流room pattern airflow 独立通风/ 分区通风separate ventilation毒气中毒事故gas-poisoning accident独头巷道blind workingsblind heading断面cross section对角式通风diagonal ventilation 对流convectionE二氧化碳carbon dioxide二氧化氮nitrogen dioxide二氧化硫sulfur dioxide二氧化硅silicon dioxideF反向通风inverted ventilation防毒气anti-gas防止爆炸anti-detonation防止坠落anti-falling放矿水平draw level放炮区blast area废井abandoned well分区通风blocking ventilation分压力, 部分压力partial pressure 分支风路branch airway分支巷道branch heading风井airshaft / air pit风轮式风速计wind mill anemometer风机的构造和分类structure and classification of fan风量分配air-distribution风量平衡定律air-quantity balance law风量air-quantity / amount of air 风流边界airflow boundary风路air path风桥air-bridge / air-crossing风速计air-meter风速计/风表anemometer 风速airspeed风巷(风道)airway风压ventilation pressureair-pressure风压降air pressure drop风压平衡定律辅助(局部)通风secondary ventilationsupplementary ventilation 辅扇secondary / auxiliary fan air-pressure balance law 负气压, 空气负压力negative air pressureG高速风速计high-speed anemometer 隔离区isolated area隔墙abatis工业事故industrial accident 工作原理principle of work工作区(工地)workplace工作面通风face ventilationface airing工作强度power of work固定边界regular boundary贯穿通风through ventilation 罐笼井cage shaft硅肺病silicosisH含尘空气dusty air含氧酸oxygen acid恒压constant pressure横巷cross level洪水位flood level回风井up-cast shaft, up-cast pit 回采工作面working face回采巷道breakage heading回风巷道return heading混合井combined shaft火区burning area火灾警报fire alarmJ基本原理basic principle基准面basal level / datum level 箕斗井skip shaft技术参数technical parameter机械能mechanical energy架线式电机车运输巷道haulage-way角联通风网路diagonal ventilation network 节点joint进风井downcast shaft, cold pit;进风巷道intake workings;intake airway;进风inlet air / intake air尽头巷道blind room金属矿metal mine紧急通风emergency ventilation;井底车场shaft-bottom;井下空气调节air-conditioning井下空气underground air井下火灾事故mine fire accident 净面积neat area / net area静压差static pressure differential 静水压力static pressure静止状态stationary state局扇local fan 局部阻力local resistance局部气流速度local airspeed;局部通风local ventilation;绝对压力, 绝对压强absolute pressure绝对静压absolute static pressure 绝对湿度absolute humidityK开采区mining area开拓巷道development heading抗爆、抗震antiknock空气调节air-conditioning空气密度压力air-density pressure 空气测量, 通风测量air measure 空气静压static air pressure控制噪声noise abatement控制通风controlled ventilation矿井涌水事故mine flooding accident矿内空气/ 井下空气mine air矿山安全设备mine safety appliance矿井通风阻力曲线mine resistance curve矿井通风网路ventilation network;矿井通风阻力mine resistance矿井自然通风mine natural ventilation矿山(矿井)通风mine ventilation;扩散通风diffusion ventilation;L拉底水平floor level联络风巷air room联合通风系统/ 混合式通风系统combined ventilation离心式风机centrilation fan,wheel-type fan硫磺sulfur硫sulphur硫酸sulphuric硫化物sulphide硫化氢hydrogen sulphide流态fluid state流体动压hydrodynamic pressure流体压力, 流体静压fluid pressure漏风fugitive air / leakage air露点dewpointM冒顶事故roof- fall accident摩擦系数friction coefficient摩擦阻力friction resistance摩擦阻力定律friction resistance lawN能量方程式energy equation粘附力adhesive power浓度consistencyP排水巷道drainage workings排尘系统dust-exhaust system 炮烟toxic smoke平硐free level / adit平均功率mean power坡度阻力grade/slope resistance 破碎水平breaking level 破碎车间crusher roomQ热线风速计hot-wire anemometer 气流air-current气流air-steam, airflow气流测量, 风流测量airflow measure轻伤事故minor accident倾斜巷道inclined workings全压total pressureR人工通风artificial ventilation;S扇风机特性曲线fan performance curve扇风机(机械)通风fan ventilation扇风机静压fan static pressure扇风机速度压力,(扇风机出风口平均速度) fan velocity pressure 上行(上向)通风upward ventilation上行风桥overcast air-bridge设计原理principle of design设计参数design parameter生产平巷production heading湿度humidity湿空气moist air湿气damp石门水平crosscut level输入功率input power输出功率output power水平巷道level workings死亡事故fatal accidentT特征参数characteristic parameter 特性曲线characteristic curve停滞stagnant停滞空气stagnant air通风小巷air head;通风平巷air heading;通风测量, 通风测定ventilation measurement通风压力降air pressure drop通风平巷, 通风水平ventilation level通风网络结构ventilation network structure 通风动力ventilation power通风阻力ventilation resistance通风平硐air adit统计参数statistical parameter统一通风unity ventilation突然扩大sudden expansion突然缩小sudden reduceW弯道阻力curve resistance位能差potential energy differential 位置高差potential pressure未污染的空气uncontaminated air 紊流turbulent flow稳定流能量方程式static flow energy equation 稳定流steady flow温度计thermometer温差thermal differential 污浊空气contaminated air/foul air 无尘空气dust-free air无风的airlessX陷落区caved area相对湿度relative humidity相对静压relative static pressure 相似原理principle of similitude 相似参数similarity parameter巷道workings巷道型风流lane pattern airflow 巷道掘进heading advance巷道片帮事故side falling accident硝酸nitric acid新鲜空气fresh air稀释dilute吸水井absorbing well;吸收功率absorbed power吸引力attractive power下部水平bottom level下行风桥under-cast air-bridge性能参数performance parameterY压力降, 压差differential pressure 压能差pressure energy differential压入与抽出联合通风系统combined pressure andexhaust ventilation压入式通风blowing ventilation 压缩空气compressed air氧化oxidate氧气oxygen氧气罩oxygen mask叶式风速计vane anemometer一氧化碳carbon monoxide易燃的inflammable抑制粉尘dust abatement隐患near accident应急措施emergency measures有效面积effective area诱导(人工)通风induced ventilation;有毒的noxious有效措施effective measures运输巷道going heading;运输水平haulage level有效功率effective / active / actual powerZ责任事故human element accident 炸药库powder room炸药explosive真空vacuum正面阻力head resistance正压(常压); 法向压力normal pressurepositive pressure支巷branch heading窒息suffocate中间平巷, 中间水平intermediate level中央通风central ventilation中央式通风middle ventilation中速风流测量moderate velocity airflow measure中毒poisoning / toxicosis 主回风巷道main return airway 主进风巷道main intake airway 主风巷道main airway主平巷gallery heading主平硐main adit主扇main fan主要开采水平principal mining level主运输巷道main haulage-way 轴流式风机axial fan,propeller-type fan转杯式风速计cup-type anemometer转叶式风速计swinging-vane anemometer 自然通风natural ventilation;自然通风压力natural-draft pressure,natural ventilation pressure 自救呼吸器self-rescue总面积gross area总体布置general arrangement 总压力(全压=静压力+速度压力)total pressure。
煤矿开采煤矿安全中英文对照外文翻译文献
中英文对照外文翻译(文档含英文原文和中文翻译)外文:Mine safetyCoal mining historically has been a hazardous occupation but, in recent years, tremendous progress has been made in reducing accidental coal mine deaths and injuries.the main aspect is as following:⑴ Safety of mine ventilation•Purposes of Mine Ventilation•Properly engineered control of the mine atmosphere is required to: •provide fresh air (oxygen) for men to breathe•provide a source of oxygen for internal combustion engines in machinery •dilute atmospheric contaminants to acceptable levels•maintain temperature and humidity within acceptable limits•remove atmospheric contaminants from the mine.Mine ventilation is twofold in purpose: first, it maintains life, and secondly it carries off dangerous gases. The historic role of ventilation was to provide a flow of fresh air sufficient to replace the oxygen consumed by the miners working underground. Today's mine ventilation primarily deals with noxious gases (mainly generated by trackless equipment underground).Canaries are said to have been used to detect gas in coal mines in the early stages of coal mining. This sensitive bird would be taken into the workings and, if it perished, the colliers would immediately leave the mine.In the 1920s the hand-turned fans were replaced with air-powered small turbine fans. Large fans of the suction type were placed on the surface and gradually increased in size. Air from surface compressors was piped into the mine to power machinery and to assist in ventilation.Unless the air is properly distributed to the face, the mine ventilation system is not performing its primary function [1]. While it has always been recognized that this last part of ventilation is the most import, it is also the most difficult to achieve.The primary means of producing and controlling the airflow are also illustrated on Figure 1. Main fans, either singly or in combination, handle all of the air that passesthrough the entire system.These are usually, but notnecessarily, located onsurface, either exhaustingair through the system asshown on Figure 1 or, alternatively, connected to downcast shafts or main intakes and forcing air into and through the system. Because of the additional hazards of gases and dust that may both be explosive, legislation governing the ventilation of coal mines is stricter than for most other underground facilities. In many countries, the main ventilation fans for coal mines are required, by law, to be placed on surface and may also be subject to other restrictions such as being located out of line with the connected shaft or drift and equipped with "blow-out" panels to help protect the fan in case of a mine explosion.Stoppings and Seals:In developing a mine, connections are necessarily made between intakes and returns. When these are no longer required for access or ventilation, they should be blocked by stoppings in order to prevent short-circuiting of the airflow. Stoppings can be constructed from masonry, concrete blocks or fireproofed timber blocks. Prefabricated steel stoppings may also be employed. Stoppings should be well keyed into the roof, floor and sides, particularly if the strata are weak or in coal mines liable to spontaneous combustion. Leakage can be reduced by coating the high pressure face of the stopping with a sealant material and particular attention paid to the perimeter. Here again, in weak or chemically active strata, such coatings may be extended to the rock surfaces for a few metres back from the stopping. In cases where the airways are liable to convergence, precautions should be taken to protect stoppings against premature failure or cracking. These measures can vary from "crush pads" located at the top of the stopping to sliding or deformable panels on prefabricated stoppings. In all cases, components of stoppings should be fireproof and should not produce toxicfumes when heated.As a short term measure, fire-resistant brattice curtains may be tacked to roof, sides and floor to provide temporary stoppings where pressure differentials are low such as in locations close to the working areas.Where abandoned areas of a mine are to be isolated from the current ventilation infrastructure, seals should be constructed at the entrances of the connecting airways. If required to be explosion-proof, these consist of two or more stoppings, 5 to 10 metres apart, with the intervening space occupied by sand, stone dust, compacted non-flammable rock waste, cement-based fill or other manufactured material. Steel girders, laced between roof and floor add structural strength. Grouting the surrounding strata adds to the integrity of the seal in weak ground. In coal mines, mining law or prudent regard for safety may require seals to be explosion-proof.Doors and airlocks:Where access must remain available between an intake and a return airway, a stopping may be fitted with a ventilation door. In its simplest form, this is merely a wooden or steel door hinged such that it opens towards the higher air pressure. This self-closing feature is supplemented by angling the hinges so that the door lifts slightly when opened and closes under its own weight. It is also advisable to fit doors with latches to prevent their opening in cases of emergency when the direction of pressure differentials may be reversed. Contoured flexible strips attached along the bottom of the door assist in reducing leakage, particularly when the airway is fitted with rail track.Ventilation doors located between main intakes and returns are usually built as a set of two or more to form an airlock. This prevents short-circuitingwhen one door is opened for passage of vehicles or personnel. The distance between doors should be capable of accommodating the longest train of vehicles required to pass through the airlock. For higher pressure differentials, multiple doors also allow the pressure break to be shared between doors. Mechanized doors, opened by pneumatic or electrical means are particularly convenient for the passage of vehicular traffic or where the size of the door or air pressure would make manual operation difficult. Mechanically operated doors may, again, be side-hinged or take the form of rollup or concertina devices. They may be activated manually by a pull-rope or automatic sensing of an approaching vehicle or person. Large doors may be fitted with smaller hinged openings for access by personnel. Man-doors exposed to the higher pressure differentials may be difficult to open manually. In such cases, a sliding panel may be fitted in order to reduce that pressure differential temporarily while the door is opened. Interlock devices can also be employed on an airlock to prevent all doors from being opened simultaneously.Cfd applied to ventilation sys tems:Due to recent advances in computer processing power CFD has been used to solve a wide range of large and complex flow problems across many branches of engineering (Moloney et. al. 1997/98/99). The increase in processor speed has also enabled the development of improved post processing and graphical techniques with which to visualize the results produced by these models. Recent research work has employed CFD models, validated by scale and full-scale experiments, to represent the ventilation flows and pollutant dispersion patterns within underground mine networks. In particular, studies by Moloney (1997) demonstrated that validated CFD models were able tosuccessfully replicate the ventilation flows and gaseous pollutant dispersion patterns observed within auxiliary ventilated rapid development drivages. CFD has proven a capable method by which to identify detailed characteristics of the flow within critical areas such as the cutting face. The results produced by the CFD models were able to demonstrate the relative efficiency of the different auxiliary ventilation configurations in the dilution, dispersion and transport of the methane and dust from the development face. Further recent studies by Moloney et. al. (1999) have demonstrated that such validated CFD models may be used to simulate the airflow and pollutant dispersion data for a wide range of mining and ventilation configurations. Each simulation exercise produces large sets of velocity, pressure and pollutant concentration data.⑵ Fires Methods of ControlFires that occur in mine airways usually commence from a single point of ignition. The initial fire is often quite small and, indeed, most fires are extinguished rapidly by prompt local action. Speed is of the essence. An energetic ignition that remains undetected, even for only a few minutes, can develop into a conflagration that becomes difficult or impossible to deal with. Sealing off the district or mine may then become inevitable.The majority of fires can be extinguished quickly if prompt action is taken. This underlines the importance of fire detection systems, training, a well-designed firefighting system and the ready availability of fully operational firefighting equipment. Fire extinguishers of an appropriate type should be available on vehicles and on the upstream side of all zones of increased fire hazard. These include storage areas and fixed locations ofequipment such as electrical or compressor stations and conveyor gearheads. Neither water nor foam should be used where electricity is involved until it is certain that the power has been switched off. Fire extinguishers that employ carbon dioxide or dry powders are suitable for electrical fires or those involving flammable liquids.Deluge and sprinkler systems can be very effective in areas of fixed equipment, stores and over conveyors. These should be activated by thermal sensors rather than smoke or gas detectors in order to ensure that they are operated only when open combustion occurs in the near vicinity.Except where electricity or flammable liquids are involved, water is the most common medium of firefighting. When applied to a burning surface, water helps to remove two sides of the fire triangle. The latent heat of the water as it vapourises and the subsequent thermal capacity of the water vapour assist in removing heat from the burning material. Furthermore, the displacement of air by water vapour and the liquid coating on cooler surfaces help to isolate oxygen from the fire.⑶ Methods of Dust ControlThe three major control methods used to reduce airborne dust in tunnels and underground mines: ventilation, water, and dust collectors.Ventilation air reduces dust through both dilution and displacement. The dilution mechanism operates when workers are surrounded by a dust cloud and additional air serves to reduce the dust concentration by diluting the cloud. The displacement mechanism operates when workers are upwind of dust sources and the air velocity is high enough to reliably keep the dust downwind.① Dilution Ventilation. The basic principle behind dilution ventilation is to provide more air and dilute the dust. Most of the time the dust is reduced roughly in proportion to the increase in airflow, but not always. The cost of and technical barriers to increased airflow can be substantial, particularly where air already moves through ventilation ductwork or shafts at velocities of 3,000 ft/min or more.②Displacement Ventilation. The basic principle behind displacement ventilation is to use the airflow in a way that confines the dust source and keeps it away from workers by putting dust downwind of the workers. Every tunnel or mine passage with an airflow direction that puts dust downwind of workers uses displacement ventilation. In mines, continuous miner faces or tunnel boring machines on exhaust ventilation use displacement ventilation. Enclosure of a dust source, such as a conveyor belt transfer point, along with extraction of dusty air from the enclosure, is another example of displacement ventilation. Displacement ventilation can be hard to implement. However, if done well, it is the most effective dust control technique available, and it is worth considerable effort to get it right. The difficulty is that when workers are near a dust source, say, 10 to 20 ft from the source, keeping them upwind requires a substantial air velocity, typically between 60 and 150 ft/min. There is not always enough air available to achieve these velocities.③ Water sprays. The role of water sprays in mining is a dual one: wetting of the broken material being transported and,airborne capture. Of the two, wetting of the broken material is far more effective.Adequate wetting is extremely important for dust control. The vast majorityof dust particles created during breakage are not released into the air, but stay attached to the surface of the broken material. Wetting this broken material ensures that the dust particles stay attached. As a result, adding more water can usually (but not always) be counted on to reduce dust. For example, coal mine operators have been able to reduce the dust from higher longwall production levels by raising the shearer water flow rate to an average of 100gpm. Compared to the amount of coal mined, on a weight basis, this 100gpm is equivalent to 1.9% added moisture from the shearer alone. Unfortunately, excessive moisture levels can also result in a host of materials handling problems, operational headaches, and product quality issues, so an upper limit on water use is sometimes reached rather quickly. As a result, an alternative to simply adding more water is to ensure that the broken material is being wetted uniformly.⑷ Mine DrainageWater invades almost every mine in the form of :direct precipitation (rain and snow), surface runoff, underground percolation. Flows of water have an important effect on the cost and progress of many mining operations and present life and property hazards in some cases.Means of Mine-water Control(Mine Drainage):As shafts and other mine openings extend below the water table, water is likely to be encountered and to seep into the openings to an extent depending upon the area of rock surface exposed, the hydrostatic pressure, and other factors. In order to continue mining operations, it is therefore necessary to lower the ground water level in the vicinity of the mine by artificial means to keep the workings free of water as well as preventing the flow of surfacewater into the (surface or underground) mine. This operation is known as mine drainage.Means of mine drainage are limited by circumstances and objectives. The following types of mine-water control can be used singly or more effectively in combination:① Locate shafts or excavations in best ground and protect from direct water inflow from surfaces.② Divert or drain water at or near surface.③Reduce permeability of rock mass by grouting with special types of cement, bentonite and liquid chemical grouts (water sealing).④ Case or cement exploration drill holes.⑤Drill pilot holes in advance of work wherever there may be sudden influents at rates potentially inconvenient.⑥Dewater bedrock at depth by pumping through dewatering wells or from an accessible place in the mine.。
矿井通风煤矿瓦斯利用论文中英文资料对照外文翻译文献综述
中英文资料对照外文翻译文献综述附录A:Status of worldwide coal mine methaneemissions and useUnderground coal mines worldwide liberate an estimated 29–41×109 m3 of methane annually, of which less than 2.3×109 m3 are used as fuel. The remaining methane is emitted to the atmosphere, representing the loss of a valuable energy resource. Methane is also a major greenhouse gas and is thus detrimental to the environment when vented to the atmosphere. Coal mine methane recovery and use represents a cost-effective means of significantly reducing methane emissions from coal mining, while increasing mine safety and improving mine economics.The world’s ten largest coal producers are responsible for 90% of global methane emissions associated with the coal fuel cycle. China is the largest emitter of coal mine methane, followed by the Commonwealth of Independent States, or CIS particularly Russia, Ukraine and Kazakhstan, the United States, Poland, Germany, South Africa, the United Kingdom, Australia, India and the Czech Republic. Most of these countries use a portion of the methane that is liberated from their coal mines, but the utilization rate tends to be low and some countries use none at all. Coal mine methane is currently used for a variety of purposes. Methane is used for heating and cooking at many mine facilities and nearby residences. It is also used to fuel boilers, to generate electricity, directly heat air for mine ventilation systems andfor coal drying. Several mines in the United States sell high-quality mine gas to natural gas distributors. There are several barriers to decreasing methane emissions by increasing coal mine methane use. Many of the same barriers are common to a number of the subject countries. Technical barriers include low-permeability coals; variable or low gas quality, variations in gas supply an demand and lack of infrastructure.Economic and institutional barriers include lack of information pertinent to development of the resource, lack of capital and low natural gas prices. A possible option for encouraging coal mine methane recovery and use would be international adoption of a traceable permit system for methane emissions.1 IntroductionIn recent years, coalbed methane has gained attention as a saleable natural gas resource. Methane can be extracted either from coal seams which will never undergo mining, or it can be produced as a part of the coal mining process. This paper focuses on methane which is produced in conjunction with coal mining operations(coal mine methane). According to the United States Environmental Protection Agency (USEPA, 1994a), underground coal mines liberate an estimated 29 to 41×109 m 3of methane annually, of which less than 2.3×109 m3 are used as fuel. The remaining methane is vented to the atmosphere, representing the loss of a valuable energy resource. This paper examines the potential for recovering and using the methane which is currently being emitted from coal mines.There are three primary reasons for recovering coal mine methane. The first reason is to increase mine safety. Worldwide, there have beenthousands of recorded fatalities from underground mine explosions in which methane was a contributing factor. Using methane drainage systems, mines can reduce the methane concentration in their ventilation air, ultimately reducing ventilation requirements.The second reason is to improve mine economics. By reducing emissions and preventing explosions and outbursts, methane drainage systems can cost effectively reduce the amount of time that the coal mine must curtail production. Moreover, recovered methane can be used either as fuel at the mine site or sold to other users.The third reason for coalbed methane recovery and use is that it benefits the global and local environment. Methane is a major greenhouse gas and is second in global impact only to carbon dioxide; methane thus is detrimental to the environment if vented to the atmosphere. Although the amount of carbon dioxide accumulating in the atmosphere each year is orders of magnitude larger than that of methane, each additional gram of methane released to the atmosphere is as much as 22 times more effective in potentially warming the Earth’s surface over a 100-year period than each additional gram of carbon dioxide (USEPA, 1994a) . Compared with other greenhouse gases, methane has a relatively short atmospheric lifetime. The lifetime of methane (defined as its atmospheric content divided by its rate of removal) is approximately 10 years. Due to its short lifetime, stabilizing methane emissions can have a dramatic impact on decreasing the buildup of greenhouse gases in the atmosphere.Coal mine methane recovery and use represent a cost-effectivemeans of significantly reducing methane emissions from coal mines. Methane, moreover, is a remarkably clean fuel. Methane combustion produces no sulfur dioxide or particulates and only half the amount of carbon dioxide that is associated with coal combustion on an energy equivalent basis.Because of the environmental impact of coal mine methane emissions, the USEPA, the Int ernational Energy Agency’s Coal Advisory Board (CIAB), and others have investigated methane emissions from coal mining worldwide. The USEPA (1994a) estimates that the coal fuel cycle (which includes coal mining, post-mining coal transportation and handling, and coal combustion) emits 35 to 59×109 m3 of methane to the atmosphere annually. Table 1 shows methane emissions from the world’s ten largest coal producers, which are responsible for 90% of global methane emissions associated with the coal fuel cycle. Underground coal mining is the primary source of these emissions, accounting for 70 to 95% of total emissions.There are many opportunities for decreasing coal mine methane emissions by increasing recovery of this abundant fuel. Section 2 examines the status of methane recovery and use in key countries worldwide.2 Coal mine methane recovery and use in selected countries2.1 ChinaThe Peoples Republic of China (China) produces about 1.2×109 raw tons of hard coal annually (EIA, 1996). In 1990, coal mining activities in China emitted an estimated 14 to 24×109 m3 (10 to 16×106 ton) ofmethane to the atmosphere, contributing one-third of the world’s total from this source. Not only is China the largest coal producer in the world; it is unique in that underground mines produce over 95% of the nation’s coal. Because of the great depth and high rank of China’s coals, underground coal mines have higher methane emissions than surface mines.There are currently 108 Coal Mining Administrations (CMAs) in China, which manage more than 650 mines. These state-owned mines are responsible for most of China’s methane emissions, but there are numerous gassy local, township, and private mines that cumulatively produce over one-half of China’s coal. However, these non-states owned mines are not gassy (International Energy Agency or IEA, 1994).2.1.1 Methane recovery and use in ChinaChina has a long history of coal mine methane drainage, and the volume of methane drained has increased markedly during the past decade. Nationwide, coal mine methane drainage at state-run mines nearly doubled in 14 years, increasing from 294×106 m3 in 1980 to more than 561×106 m3 in 1994 .However, this is still less than 11% of the total methane liberated annually. Approximately 131 state-owned mines currently have methane drainage systems. Less than one-half of these mines are set up to distribute and use recovered methane. China’s state-run coal mining administrations use about 70% of the methane they drain (USEPA, 1996a).Most of the methane recovered from Chinese mines is used forheating and cooking at mine facilities and nearby residences. Methane is also used for industrial purposes, in the glass and plastics industries, and as a feedstock for the production of carbon black (an amorphous form of ca rbon used in pigments and printer’s ink). Methane is also being used, to a lesser extent, for power generation. In 1990, the Laohutai Mine at the Fushun Coal Mining Administration built a 1200 kW methane-fired power station, the first in China.Several barriers currently prevent China from developing economic methane recovery from coal mining to its full potential. Critical barriers include the lack of an appropriate policy framework, limited capital for project investments and equipment, the need for additional information and experience with technologies and the lack of a widespread pipeline network. Artificially regulated low gas prices and difficulty with repatriation of profits, create barriers to foreign investment in joint ventures for production of domestic energy resources (USEPA, 1993).2.1.2 The future of methane development in China Recognizing the need for a unified effort in advancing coalbed methane development, China’s highest governing body, the State Council, established the China United Coalbed Methane Company (China CBM) in May 1996. As a single, trans-sectoral agency, China CBM is responsible for developing the coalbed methane industry by commercializing the exploration, development, marketing, transportation and utilization of coalbed methane. The State Council has also granted China CBM exclusive rights to undertake theexploration, development and production of coalbed methane in coopera- tion with foreign partners (China Energy Report, 1996). More than 20 coalbed methane projects are underway or planned in China, and at least half of them are taking place at active mining areas. Some of the projects are state-sponsored, while others involve joint ventures with foreign companies. The future of the coalbed methane industry in China appears bright. The government recognizes coalbed methane’s potential for meeting the nation’s burgeoning energy needs and is generally supportive of efforts to develop this resource. With deregulation of energy prices, increased capital investment in pipeline infrastructure, and ongoing research efforts, China can likely overcome its remaining barriers to widespread coalbed methane use. 2.2 Russia, Ukraine and KazakhstanIn 1994, Russia produced more than 169×106 ton of hard coal; Kazakhstan produced nearly 104×106 ton and Ukraine more than 90×106 ton. The coal mining regions of these republics liberate approximately 5.3×109 m3 of methane annually, of which less than 3% is utilized. This amount represents about 20% of world methane emissions from underground coal mining.The energy sectors of these Republics are at a turning point. The coal mining industry, in particular, is undergoing restructuring, a process which includes decreasing or eliminating subsidies, and closing many of the most unprofitable mines. The industry is being compelled to become more efficient in order to increase profitability. Mining regions are also seeking to mitigate environmental problemsresulting from producing and using coal. Thus, there is an impetus to utilize more natural gas and decrease dependency on low grade coal. Increasing recovery and use of coalbed methane is a potential means of improving mine safety and profitability while meeting the regions’ energy and environmental goals.There are five coal basins in the Commonwealth of Independent States where hard coal is mined and which have the potential for coalbed methane development.They are: (1) the Donetsk Basin (Donbass) , located in southeastern Ukraine and western Russia, (2) the Kuznetsk Basin Kuzbass , located in western Siberia (south-central Russia) , (3)the L’vov-Volyn Basin, located in western Ukraine, which is the southeastern extension of Poland’s Lublin Basin, (4)the Pechora Basin, located in northern Russia and (5) the Karaganda Coal Basin, located in Kazakhstan.Of the five basins, the Donetsk and Kuznetsk Basins appear to have the largest near-term potential for coalbed methane development (USEPA, 1994b). Both of these regions are heavily industrialized and present many opportunities for coalbed methane use.2.2.1 Options for methane use in the CIS2.2.1.1 Heating mine facilities. Currently, most mines use coal-fired boilers to produce steam heat for drying coal, heating mine facilities and heating ventilation air. In some cases, mine boilers also supply thermal energy to the surrounding communities. Boilers can be retrofitted to co-fire methane with coal, a relatively simple and low-cost procedure. More than 20 mines in the Donetsk and PechoraBasins use methane to fuel boilers and several mines also use it for directly heating air for the mines’ ventilation systems and for coal drying (Serov, 1995; Saprykin et al., 1995).2.2.1.2. Use in furnaces in the metallurgical industry. Another viable market for methane use is the metallurgical industry. For example, the city of Novokuznetsk, in the southern portion of the Kuznetsk Basin, contains numerous gassy mines and is one of the biggest centers of metallurgy in Russia. The region’s metallurgical industry consumes about 54 PJ of natural gas annually, which is equivalent to about1.4×109 m3 of methane (USEPA, 1996b) .2.2.1.3. Power generation at mine facilities. Most mines purchase electricity from the power grid. Co-firing coalbed methane with coal to generate electricity on-site may be a more economical option for these mines. Coalbed methane can be used, independently of or in conjunction with coal, to generate electricity using boilers, gas turbines and thermal combustion engines (USEPA, 1994b).2.2.1.4. Use as a motor vehicle fuel. The Donetskugol Coal Production Association in Ukraine is draining methane in advance of mining using surface boreholes. The recovered methane is compressed on-site and used as fuel for the Association’s vehicle fleet. The refueling station, which has been operating for more than three years, produces about 1,000 m3 of compressed gas per day. Based on estimated gas reserves it is expected to operate for a total of eight years ( Pudak, 1995 ).While many mines in the CIS are utilizing their methane resources,the majority are not. Certain barriers must be overcome before recovery and use of coal mine methane becomes widespread. These barriers and their potential solutions are discussed in greater detail in Section 3 of this paper.2.3 The United StatesThere are five major coal producing regions in the United States from which hard coal is mined and which have the potential for coalbed methane development. They are: (1)the Appalachian Basin, located in Pennsylvania, Ohio, West Virginia, eastern Kentucky and Tennessee, (2)the Warrior Basin, located in Alabama, (3)the Illinois Basin, located in Illinois, Indiana and western Kentucky, (4)the Southwestern region, including the Uinta, Piceance, Green River and San Juan Basins located in Colorado, Utah and New Mexico and (5)the Western Interior region, including the Arkoma Basin of Oklahoma and Arkansas.In 1994, an estimated 4.2×109 m3 of methane were liberated by underground mining in these regions, of which less than 0.7×109 m3 were used(USEPA, unpublished data).Currently in the United States, at least 17 mines in six states (Alabama, Colorado,Ohio, Pennsylvania, Virginia and West Virginia)recover methane for profit, primarily through sale to gas distributors. In 1995, the total methane recovered from these mines, including vertical wells draining methane in advance of mining, exceeded 1×109 m3.By maximizing the amount of gas recovered via drainage systems, these mines have greatly reduced their ventilationcosts, improved safety conditions for miners and have collected and sold large quantities of high-quality gas. Following is a brief description of selected coal mine methane recovery activities in the United States.2.3.1 Warrior basin: AlabamaSix of the seventeen US mines with commercial methane recovery systems are located in the Warrior Basin of Alabama. Today, energy companies recover methane from the Warrior Basin by horizontal wells, gob wells(in areas being mined )and vertical wells(in both mined and unmined areas). Most of this gas is sold to regional natural gas distributors, although there is some on-site mine use. In 1995, four mines operated by Jim Walter Resources produced more than 380×106 m3 of methane for pipeline sale and USX’s Oak Grove Mine recovered an estimated 117×106 m3 of methane for use.2.3.2 Appalachian regionEight mines in Virginia and West Virginia have developed successful methane recovery and use projects. The Consol mines in Virginia are the most well-documented examples. Consol produces gas from a combination of vertical wells that are hydraulically stimulated, horizontal boreholes and gob wells drilled over longwall panels. In 1995, Consol produced approximately 688×106 m3 of saleable methane from three mines. Methane recovery efficiency at these mines is higher than 60%.2.3.3 Southwestern regionThe Soldier Canyon Mine in Utah recovered about 10.9×106 m3 ofmethane for sale annually until early 1994, when production was curtailed and gas sales ended due to low market prices.2.3.4 SummaryWhile methane recovery has been economically implemented at the above-described mines, safety and high coal productivity remain the impetus for their degasification efforts. Methane drainage at many gassy mines in the United States is limited or nonexistent. Section 3 of this paper discusses potential avenues for increasing methane recovery and use in the United States and other countries.2.4 GermanyGermany produced nearly 54 million tons of hard coal in 1995, all from underground mines (Schiffer, 1995). Of this total, 43 million tons were mined from the Ruhr Basin in northwestern Germany (Von Sperber et al., 1996)and most of the remainder was mined from the Saar Basin in southwestern Germany. Until recently, hard coal mining was heavily subsidized in Germany, and the industry’s future is in question (Schiffer, 1995). Even mines that are closed, however, can continue to liberate methane for long periods of time. An estimated 1.8×109 m3 of methane are liberated annually from underground mining activities in Germany, of which 520×106 m3, or 30%, are drained(63 IEA, 1994). About 371×106 m, or 71% of all drained methane is used, primarily for heating or power generation. Government officials suggest that as much as 45% of the methane emitted from coal mining activities could be drained and used in a variety of applications. The primary barrier to increased methanerecovery is low methane concentrations in the gas mixture.Safety regulations in Germany prohibit any utilization if the methane content is less than 25%. If the average recovery efficiency at German mines is to be increased, it will be necessary to adopt practices that will recover methane in a more concentrated form.3 Barriers to decreasing coal mine methane emissionsThere are several barriers to decreasing methane emissions by increasing coal mine methane use. Some are technical, such as low coal permeability, while others are Institutional, such as low gas prices. In a few cases, certain barriers are country orregion specific, but most cases, many of the same barriers exist in a number of countries. This section discusses obstacles to increased coal mine methane use, and potential ways to overcome these obstacles.3.1 Technical issues3.1.1 Low-permeability coalsCoal seams that exhibit low permeability pose special problems for developingsuccessful methane drainage and recovery systems. Methane desorbs and flows through natural pores and fractures until the gas reaches the mine face or borehole. Stimulation technology that enhances the flow of gases from the seam into a recovery system has been successfully used in the past several years. Early efforts to modify fracturing techniques for application in coal seams were largely unsuccessful (IEA, 1994). The current practice of hydraulic stimulation in coals, however, minimizes roof damage while achievingextensive fracturing. Under ideal conditions, 60 to 70% of the methane contained in the coal seam can be removed using vertical degasification wells drilled more than 10 years in advance of mining. These efforts have been successful in the United States and other industrialized countries. Transfer of this technology to other countries can help increase coal mine methane recovery.3.2 Economic and institutional issuesIn addition to the technical obstacles described above, there are a variety of other issues that have prevented coal mine methane recovery from becoming more widespread.These issues include lack of information, lack of capital, low natural gas prices and risks associated with foreign investment. Some issues are explored below.The key strategy for overcoming informational barriers in the United States has been to develop outreach programs. Outreach programs work well when companies are shown that they can profit while at the same time reducing emissions or improving mine safety. Examples of outreach prog rams include the USEPA’s Coalbed Methane Outreach Program, which is conducted in the United States, and the Coalbed Methane Clearinghouses in Poland, China and Russia. These institutions distribute information and link together interested parties, provide technical training, and in some cases perform pre-feasibility assessments for specific projects.3.2.1 Lack of informationIn the United States and other countries, one of the problems thathas slowed coal mine methane project development is that some coal mine operators do not have adequate information regarding coal mine methane projects. While much has been published on the subject, methane recovery is still seen as a relatively new concept to many coal operators. A related constraint is that some coal operators simply do not have the time or resources to investigate the potential to develop a profitable project at their own coal mine.3.2.2 Lack of capitalEven when a pre-feasibility assessment has demonstrated that the economics of a coal mine methane project are attractive, a lack of financing may prevent projects from taking place. Coal companies often do not have surplus capital available to invest in coalbed methane recovery and use projects because available capital must be invested in their primary business of coal production. Additionally, some lending organizations may be unfamiliar with the relatively new concept of coal mine methane recovery and use, and project developers may thus be unable to secure the necessary up-front financing needed to cover the large capital investments required for such projects.3.2.3 Low natural gas pricesIn some countries natural gas prices are held at artificially low rates. Even in countries whose gas prices are at market levels, prices may be low due to low demand. In such cases, special types of incentives to encourage coal mine methane recovery could be implemented. For example, legislation could be enacted requiring local distributioncompanies to purchase recovered coal mine methane if it is sold at a competitive price. China has recently established preferential policies for projects which involve gas recovery and use from coal mines. The government has also passed a law exempting coalbed methane producers from royalties and land occupation fees for production of up to 2×109 m3 of methane per year.4 ConclusionsAs discussed above, coal mines worldwide emit large volumes of methane, much of which could be recovered and used as fuel. In many instances, countries whose mines emit large quantities of methane are in critical need of a domestic energy source, particularly one which is clean-burning. In countries whose economies are in transition, such as China, the former Soviet Union and the Eastern European nations, coal mine methane recovery offers economic benefits as a new industry that can help provide jobs for displaced coal miners or other workers. In countries whose economies are established, such as the United States, the United Kingdom and Australia, coal mine methane recovery may help increase the profit margin of mining enterprises.The reduction of methane emissions can have a significant global impact, but incentives are needed to encourage more widespread recovery of coal mine methane. An incentive program offered on an international level would probably be the most effective means of stimulating development of the coal mine methane industry. Of the various options for international-level incentives, a system of tradeable permits for methane emissions would likely be the most cost effective.Due to various technical, economic and institutional barriers, it will never be possible to completely eliminate emissions of methane from coal mines. However, a worldwide coal mine methane utilization rate of 25% may be realizable, particularly if an international incentive program is implemented. This would reduce the estimated emissions of coal mine methane to the atmosphere by 7 to 10×109 m3 annually, substantially reducing greenhouse gas emissions and curtailing the waste of a valuable energy source.附录B全球煤矿瓦斯涌出及利用现状全球煤矿每年释放瓦斯29~41×109m3,其中少于2.3×109m3的瓦斯用作燃料,其余的被直接排放到大气中,这是能源的一种浪费。
英译汉(提高矿井中的瓦斯排放)
矿井中瓦斯抽排的改进D. J. BLACK and N. I. AZIZABSTRACTEffective gas management is vital to the success of the longwall mining in the Bulli seam, in the Southern Coalfield, SydneyBasin, NSW, Australia. The evolution of gas drainage methods and practices are discussed with respect to gas type, gas drainage lead time and prevailing geological conditions. Both underground to inseam drilling and surface to inseam drilling techniques are described at both pre and post-drainage conditions. Post-drainage of gas from longwall is discussed for its effectiveness, practicability and efficiency. The long term benefit of the method selected is examined with respect to gas capture efficiency. An alternative method of surface based goaf drainage, using medium radius drilling technology to drill horizontal boreholes above and/or below the production seam into the partial caving zone prior to longwall goaf formation is proposed.摘要:瓦斯的有效管理对于能否成功的在澳大利亚布利煤层、南部煤田、悉尼盆地、新南威尔地区进行长壁开采有至关重要的作用。
煤矿安全专业外文文献(中英文对照)
附录 A关于煤矿安全监控系统技术的研究Zhi Chang,Zhangeng Sun & Junbao GuSchool of Mechanical and Electronic Engineering, Tianjin Polytechnic UniversityTianjin 300160,China前言:无线射频的新的发展和运用使得RFID(射频识别)技术的应用越来越广泛。
同时结合矿山与RFID技术的特点,我们建立了一个地下的安全完整的、实时灵活的监测系统。
这套系统能在发生危险时自动报警并且提高搜索和救援的效率。
该系统可以管理危害气体的浓度、规划工人的安排、进出巷道通过工作的访问控制、巷道人员的分布和工人的资料,实现地下管理的信息化和可视化,提高矿业生产管理水平和矿井安全生产水平。
关键词:射频识别,安全监控系统,电子标签,读写器煤矿事故往往发生在中国近几年,除了矿业主的安全和法律意识薄弱,滞后的安全机构和采矿的人员和设备的不完善管理人员是重要原因.通过分析近期内一些十分严重的事故,一般存在以下常见问题:(1)地面人员和地下人员之间的信息沟通不及时;(2)地面人员不能动态地掌握井下人员的分布和操作情况,并且不能掌握地下人员的确切位置;(3)一旦煤矿事故发生,救援效率低,效果较差。
因此,准确、迅速实施煤矿安全监控职能非常重要和紧迫,有效管理矿工,并确保救援高效率的运作。
文章中提出的煤炭采矿人员和车辆安全监测系统可以跟踪、监视和定位在矿井实时的有害气体,人员和车辆以及提供有关网络的矿井巷道,个人的定位,车辆的位置,危险区域的动态信息和地面人员相应线索。
如果发生意外,该系统还可以查询有关人员的分配,人员数量,人员撤离路线,以提供从事故救援监视计算机科学依据.同时,管理人员可以利用系统的日常考勤功能实施矿工考勤管理。
一、RFID技术简介射频识别是一种非接触式自动识别技术进行排序,可以自动识别的无线电频率信号的目标,迅速跟踪货物和交换数据。
采矿外文翻译---在煤矿主井通风设备中与安全有关的控制系统的用途
英文原文THE USE OF SAFETY RELATED CONTROL SYSTEMS IN PRIMARY MINE VENTILATION RECIRCULATIONSYNOPSISThis paper describes a ventilation problem at a large underground coal Proposals were made to provide additional limitation of conventional solutions is ventilation quantity to the inbye workings discussed,along with the proposed solution by recirculating part of the return air using an underground recirculation fan in back into the intake at a point some 6km the primary mine ventilation the was to be achieved Foreseeable potential hazards associated by a recirculation fan of sufficient rating to overcome the pressure difference between with the proposals are identified.The paper describes the need for emergency shutdown of the recirculation fan and the use of a programmable electronic system (PES) to monitor and automatically initiate a shutdown in the event of predetermined criteria being system had to be designed to ensure the stoppage of the fan on early detection of adverse conditions, but unnecessary interruption of the ventilation system when conditions were satisfactory had to be selection and assessment of the programmable electronics (PE) and the selection and location of suitable transducers to continuously monitor various parameters is use of a transducer 'voting system' controlled by the PE to take account of reliability and replacement of transducers is also described.VENTILATION PROBLEMLarge quantities of air have to be circulated through the underground workings of coal mines to dilute mine gases, prevent accumulations of mine gases, dilute dust concentrations, and provide reasonable working environments in terms of temperature and resistance to ventilation in mine airways increases as the working places advance away from the TO maintain or increase the quantity may involve increasing the surface fan capacity, installing or uprating main underground fans (booster fans), minimising leakage paths between intake and return airways, providing additional airway capacity, or sinking extra shafts or boreholes.LIMITATION OF COVENTI0NAL SOLUTIONSAt one coal mine where the undersea workings had extended over lokm from the shafts,large surface and underground booster fans had already been installed, and leakage paths provision of additional airway capacity would take many years to complete and by itself would be unlikely to provide a satisfactory feasibility ofsinking a shaft offshore was considered,but was not pursued due to cost, technical problems, and security.PROPOSED SOLUTION AND IDENTIFICATION OF ASSOCIATED HAZARDSProposals were made to provide additional ventilation quantity to the inbye workings by recirculating part of the return air back into the intake at a point some 6km from the was to be achieved by a recirculation fan of sufficient rating to overcome the pressure difference between UK the return and intake Mining Regulations prohibit recirculation in mine ventilation , selective exemptions have been granted by the Health and Safety Executive (HSE) to allow the successful use of recirculation techniques in the ventilation of drivages 15 any exemption is for over considered the health, and safety of those employed at the mine should not be compromised in any will Only grant an exemption subject to clearly or defined conditions designed to maintain improve the level of health and safety of the workers.Partial recirculation of air does not result in a build up of contaminant concentration of a contaminant gas in any ventilated region of a mine is given by the rate at which the contaminant gas enters the region divided by the flow of fresh air into the does not depend on any recirculation that may be taking place [Leach and Slack.19691.The most serious foreseeable hazards identified were the possible recirculation into the intake air of smoke and products of combustion or high concentrations of flammable gas (methane) [Mitche11,19891.The products of combustion resulting from an outbreak of fire, if recirculated,would prevent escape from the workings through uncontaminated against these hazards was to be based on early detection of adverse trends, stopping the recirculation fan and reverting to conventional the recirculation fan would also have to be initiated in the event of excessive recirculation factor, fan vibration, and operation of the fire control apparatus at the fan , overcurrent, earth leakage, and pilot circuit electrical fault protection would need tobe the recirculation fan would result in a ventilation short circuit leakage path being opened between intake and to ensure this path was closed off had to be provided.THE NEED FOR AUTOMATIC SHUTDOWNThe need to stop the recirculation fan automatically in response to adverse considered necessary due to indications was the quantity and complexity of the environmental and associated data involved.This decision was taken prior to the design was clear that automatic control would need to be provided by a microprocessor based system capable of handling andprocessing data from numerous on lengthy data transmission lines to the surface control room was to be avoided and this ruled out the use of the surface computer to effect automatic PE were to be installed in an underground substation near the automatic system would not provide for any discretion being exercised by the surface control room operator,and would not be liable to operator error.DEVELOPMENT OF 'VOTING SYSTEM' TO INITIATE AUTOMATIC SHUTDOWNMethane and carbon monoxide levels in the return air would need to be continuously recirculation of return air into the intake would need to be prevented by automatically stopping the fan at predetermined intake of the recirculation circuit would additionally need to be monitored for carbon monoxide, and the fan automatically stopped at a predetermined level [see Fig 1]Single environmental monitors were not satisfactory since a failure or erroneous indication might lead to interruption of ventilation when conditions were satisfactory,or in the event of an erroneous indication,permit continued operation in adverse single monitor would also require the fan to be stopped for monitor replacement.In a system using twin environmental monitors,although maintained in a healthy state,the failure of a single monitor would result in the fan then being controlled from the remaining monitor.The use of three control environmental monitors was considered in which a failure or adverse indication from any two would initiate a ,for the fan to continue running would require a healthy indication from at least two 'voting system' was considered to be the most appropriate single monitor failure would not stop the fan and the system would permit replacement of a monitor without interrupting ventilation.The three sets of three monitors (two sets for carbon monoxide, and one for methane) would continuously supply data to the data would also be continuously transmitted to the surface environmental computer for information and display on thecontrol room VDU.The PE would process data from the sets of environmental monitors and from other would be programmed to interrupt the pilot circuit of the recirculation fan and initiate a trip in response to predetermined EPROM chip programmed in a non volatile memory contained the logic for the safety related and automatic shutdown of the instructions in the EPROM could be changed only by the manufacturer thus overcoming the need for security of access by non competent people.SYSTW DESCRIPTION1.FIREDAMPThe Sieger BM3 methane monitor was selected as the control monitor to supply data to the programmable electronics on methane instrument operates over a range of 0 - 3% with an accuracy of +/- 0.1% (from zero to 1.25%).It is powered from a with a built in rechargeable battery permitting up to 30 hours operation independent of the external power set of three BM3s were installed to monitor the methane content in the return air of the recirculation methane content in the main return airways was typically 0.5% with occasional peaks up to 0.7%.An automatic stop level of 0.8% was set initially, this being considered operationally practical, and took account of transient increases which might be experienced on stopping the recirculation fan.(b) CARBON MONOXIDEMonitoring of carbon monoxide was considered the most reliable means of detecting the products of combustion from an outbreak of SiegerBCOl carbon monoxide monitor was selected to supply data continuously to the instrument has three operating ranges up to 1000ppm,the appropriate range for this duty being 0 - 5Oppm.The BCOl has a similar battery back up to the BM3.The automatic stop levels were selected with due regard to operational carbon monoxide production from diesel exhausts and shotfiring level of 5Oppm was established for the set of three control monitors in the main return airway and a level of 25ppm in the intake of the recirculation circuit.(C) RECIRCULATION FACTORThe recirculation exemption specified a maximum of 37% of the return air to be recirculated back into the intake, this proportion being known as the recirculation loss of control of the quantity recirculated in certain circumstances could lead to increased methane or carbon monoxide levels,protection was provided the arrangements previously described.$owever systems have been designed and installed to stop the recirculation fan in the event of loss of recirculation factor system used air pressure transducers to monitor the pressure difference across the recirculation fan and associated booster fan and initiate a stoppage of the recirculation fan through the programmable electronics on either fan exceeding + or - 15% of the preset normal operating second system was installed using Sieger BAS velocity monitors to compute the air quantity in the main return and the air quantity programmable electronics continuously compare the data and initiate a trip in the event of excess recirculation factor.4.VENTILATION SHORT CIRCUIT PROTECTIONStopping the recirculation fan would result in a ventilation short circuit leakage path being opened between the main intake and return the safety features of the recirculation system were based on automatic shutdown, the closing of anti- reversal doors to prevent short circuiting also had to be designed for automatic flaps were provided at the outlet side of the fan were opened by the pressure generated at the recirculation fan and closed by pressure difference when the fan , centre or side hinged steel doors were installed as back-up anti- reversal doors to the inlet or outlet closure was assisted by positions of both sets of anti-reversal doors were monitored at the surface control room and the operation checked as part of the routine testing procedure.(e)OTHER PROTECTIONA fire control water curtain was installed at the outlet side of the recirculation was activated by a fusible link in a tensioned the wire causes the gravity operated supply valve to of the valve also opens an electrical contact resulting in an automatic stop of the monitorinqecruiDment is Drovided - fin to seise and at the recirculation indicate any developing mechanical lower vibration level gives alarm fan is automatically stopped on reaching the higher vibration level.(f)OTHER CONTINUOUS lloNITORINGComprehensive continuous environmental monitoring was provided throughout the mine in addition to those sensors dedicated to the control of the recirculation was provided by various strategically placed monitors to underground outstations, which in turn relayed information to the surface HINOS (Mine Operating System) computer via a data highway to provide records, and a display in the control monitored include firedamp levels, carbon monoxide levels and air quantities at face workings and auxiliary ventilated recirculation fan monitoring data was transmitted to the surface via the same data highway.A totally separate carbon monoxide monitoring system was installed in the main conveyor roadways with transducers at lkm system, known as the J Jones PDT 300 Envirosystem, had a separate data transmission highway operating on a constant current was connected to the surface control room where it received its power supply and displayed information on a equipment was also installed to continuously monitor the operation of the mine firedamp drainagesystem.THE PROGRAMMABLE ELECTRONIC SYSTEMThe complexity of the recirculating fan monitoring and control system necessitated the use of PE which when connected to the input/output transducers and linked by a data highway to the surface of the mine, forms a was decided that the PE would need to comprise two first would be a microprocessor located at the fan site some6km from the mine shaft and the second would be the existing surface MINOS computer with its twin DEC PDP 11/73 mini- former would be a Transmittion Ltd General Purpose Monitoring and Control Unit (GPMC) type would be configured as an intelligent station with various input and output devices and would operate essentially in a "Control" latter would display information in the surface control room and operate essentially in a "Monitoring" mode.This arrangement has the advantage that the safety related control functions are dealt with locally, are independent of the surface computer and the information transmitted via the data highway is kept to a underground PE would in addition to any other safety assessments, need to be of a type Certified by HSE(M) as suitable for use in a potentially explosive atmosphere.CERTIFICATION OF PROGRAMMABLE ELECTRONICSAs with other electrical equipment used at the underground fan site the PE needed to be certified as suitable for use in a potentially explosive requirement is well known to manufacturers and users of Group I Certified Electrical Equipment (ie that used in mines susceptible to firedamp).The HSE(M) certification is in two parts, a "pit worthiness assessment" and the issue of a certificate of compliance with the appropriate standard [HSE Electrical Equipment Certification Guide 1982].Historically, this involvement by the Mines Inspectorate in the electrical certification process has ensured that before equipment arrives for installation at the workplace all three of the following requirements are met:i) compliance with appropriate statutory requirements.(eg It has the necessary electrical protection and guarding required by mining law):ii) compliance with the relevant British or Harmonised European Standards relating to protection against ignition of flammable gas:iii) compatibility with accepted UK mining industry practice.where the intended equipment purchaser is British Coal HSE liaises with British Coal's HQ electrical engineering staff who simultaneously carry out assessment under their "Electrical Acceptance Scheme".This avoids misunderstandings and helps manufacturers to design equipment to suit the requirements of both the industry and the legislation.In the case of the recirculating fan PES, the Mines Inspectorate performed the pit worthiness assessment, British Coal performed the acceptance assessment and HSE(M) Buxton certified the apparatus as complying with BS 1259:1958 as an Intrinsically Safe System comprising intrinsically safe non IS (power) circuits were contained within flameproof enclosures certified to BS 4683:1971 with an interface from the PES to the power circuit via a hardwired pilot analogue signals from the measuring instruments,such as the methanometers,were designed to comply with BS 5754:1980 and the overall quality control of the manufactured products was checked by British Coal to be in accordance with BS 5750:1987.Having dealt with the flammable gas ignition risk,the legal requirements and some of the safety related aspects of the hardware,there remained a need to assess the system as a whole.ASSESSMENT OF TEE PESi) The surface minos computerThe British Coal HINOS computer has operated in over 160 separate installations throughout the DEC PDP hardware is used in millions of other computers.AS British Coal write and have control over their own MINOS software, there is vast experience with both the hardware and the experience, coupled with the fact that the data transmission system would also be constructed to BS 6556:1985 system,indicated that detailed safety assessment of this part of the PES would be unnecessary.ii) 输入输出设备The input and output devicesThe main problem which arose in the assessment of the input/output transducers,was that of attempting to reduce the risk of failures to the unsafe mode by "Common Cause Failure' (CCF).For example, while several types of methane monitor were available on the market all but a few operated using a "hot pellistor in a Wheatstone bridge".These are susceptible to head poisoning and calibration drift when used continuously in methane concentrations of about 1% in this situation doubling or triplication of devices had only marginal effect on there was a need to introduce manual checks with regular recalibration intervals, to provide a back-up arrangement to reduce the risk of simultaneous failure of detector heads.iii) The intelligent outstationThis was the part of the PES in which the assessment required most attention because the available equipment was to comprise a single microprocessor with no diversity of hardware or software.In an attempt to perform a logical reliability assessment it was agreed that certain criteria be avoid duplication of effort some examinations would be performed by HSE, some by British Coal, and some jointly.The first of these assessments could be loosely described as "Assessing the software life cycle" to establish software assessment was based on the IEE's "Guidelines for the documentation of software in industrial computer systems'.This comprised:- examination of the concept and specification documents produced by British Coal Area and Mine Staff in consultationwith the local HM Inspectorate: - examination of the design documents tosee if they set out a logical sequence of events and contained the safety checks specified by the mining engineers: - examination of the programme listing tosee if its structure was in well definedmodular packages using establishedroutines, and containing watchdog routines,time-outs etc.(ie checks which can beperformed by an assessor even if he hasonly a very limited knowledge of theprogramme language);- examination of the manufacturer's maintenance manuals and operator's instructions to see if they are well written and can be understood, even by a layman: - building up the PES system on the mine surface to test all inputs/outputs to the satisfaction of interested parties:- installation and commissioning underground at the fan site,- assessing the maintenance and repair procedures, especially the procedure for controlling modifications to the programmeand identifying the particular version in the EPROM.[NCB Mining Dept - 'Computer based Monitoring and Control Systems'] The final assessment considered how the intelligent outstation fitted into the installation as an use of transducer digital outputs (flashingcontacts) instead of analogue outputs to initiate safety critical circuits (eg the trip circuit), were looked at to see if it was considered that the system was was based on the fact that the disadvantage created by the lack of diversity in the outstation microprocessorand its software was overcome by the above assessment in conjunction with the alternative and diverse systems of:- the independent fire/carbon monoxide monitoring system:- the B-hourly visual examination of the fan required by statute:- the fact that other parts of the mine are continually monitored eg by Mine Deputies and environmental monitoring systems.The first recirculation fan and Control system was installed in July 1986 before HSE's PES documents had been review of the installation since then has indicatedto HSE that the total configuration of the system satisfies the basic principle in the PES documents because the overall system does not depend upon one safety critical PES.TESTING OF MONITORS AND AUTOMATIC SHUTDOWN SYSTEMA detailed procedure for calibration, testing and maintenance of the monitors, the PE, the data transmission and associated equipment is specified in rules drawn up and implemented by the mine Manager [Robinson and Harrison 19871.The procedure includes systematic on-site testing of the accuracy of monitors,comparing the readings with hand held instruments of known accuracy, and replacing these as for each set of three 'voting' monitors,should the spread of readings exceed 0.2% in respect of methane or loppm in respect of carbon monoxide, then each monitor is checked immediately for accuracy and replaced as necessary.Automatic shutdown of the recirculation fan in response to excess methane or carbon monoxide levels requires two out of three monitors in one of the controlling sets to exceed the trip also depends on the receipt of this data at the outstation,the correct interpretation of the data by the PE, the appropriate output to interrupt the pilot circuit, the operation of the pilot circuit breaker and the operation of the fan switchgear [see Fig 21.The testing procedure includes monthly tests at each of the three sets of control sample of air containing 2-3% methane is introduced into two of the three BM3s and an air sample containing 50-75ppm carbon monoxide into two of the three BCOls of each tests actually stop the fan and are arranged to ensure that all combinations of two from three monitors in each set are tested every 90 also tests the automatic operation of the anti-reversal is also carried out in the event of the printed circuit card containing the EPROM being date all such tests have had positive results.CONCLUSIONThe safety related PES of the recirculation fan has worked satisfactorily for over three years, providing additional ventilation quantity and improved environmental conditions in the, undersea workings of a large coal associated comprehensive environmental monitoring system has enhanced the level of testing procedures described have given a high confidence level that in the event of excess concentrations of methane or carbon monoxide safety related systems will function as designed.中文译文在煤矿主井通风设备中与安全有关的控制系统的用途摘要本文描述了一个大型地下煤矿的通风问题,并对常规解决方案的限制进行了讨论,同时提出在煤矿主井中使用地下对流风扇的解决方案。
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中英文对照外文翻译文附录A:Status of worldwide coal mine methaneemissions and useUnderground coal mines worldwide liberate an estimated 29–41×109 m3 of methane annually, of which less than 2.3×109 m3 are used as fuel. The remaining methane is emitted to the atmosphere, representing the loss of a valuable energy resource. Methane is also a major greenhouse gas and is thus detrimental to the environment when vented to the atmosphere. Coal mine methane recovery and use represents a cost-effective means of significantly reducing methane emissions from coal mining, while increasing mine safety and improving mine economics.The world’s ten largest coal producers are responsible for 90% of global methane emissions associated with the coal fuel cycle. China is the largest emitter of coal mine methane, followed by the Commonwealth of Independent States, or CIS particularly Russia, Ukraine and Kazakhstan, the United States, Poland, Germany, South Africa, the United Kingdom, Australia, India and the Czech Republic. Most of these countries use a portion of the methane that is liberated from their coal mines, but the utilization rate tends to be low and some countries use none at all. Coal mine methane is currently used for a variety of purposes. Methane is used for heating and cooking at many mine facilities and nearby residences. It is also used to fuel boilers, to generate electricity, directly heat air for mine ventilation systems andfor coal drying. Several mines in the United States sell high-quality mine gas to natural gas distributors. There are several barriers to decreasing methane emissions by increasing coal mine methane use. Many of the same barriers are common to a number of the subject countries. Technical barriers include low-permeability coals; variable or low gas quality, variations in gas supply an demand and lack of infrastructure.Economic and institutional barriers include lack of information pertinent to development of the resource, lack of capital and low natural gas prices. A possible option for encouraging coal mine methane recovery and use would be international adoption of a traceable permit system for methane emissions.1 IntroductionIn recent years, coalbed methane has gained attention as a saleable natural gas resource. Methane can be extracted either from coal seams which will never undergo mining, or it can be produced as a part of the coal mining process. This paper focuses on methane which is produced in conjunction with coal mining operations(coal mine methane). According to the United States Environmental Protection Agency (USEPA, 1994a), underground coal mines liberate an estimated 29 to 41×109 m 3of methane annually, of which less than 2.3×109 m3 are used as fuel. The remaining methane is vented to the atmosphere, representing the loss of a valuable energy resource. This paper examines the potential for recovering and using the methane which is currently being emitted from coal mines.There are three primary reasons for recovering coal mine methane. The first reason is to increase mine safety. Worldwide, there have beenthousands of recorded fatalities from underground mine explosions in which methane was a contributing factor. Using methane drainage systems, mines can reduce the methane concentration in their ventilation air, ultimately reducing ventilation requirements.The second reason is to improve mine economics. By reducing emissions and preventing explosions and outbursts, methane drainage systems can cost effectively reduce the amount of time that the coal mine must curtail production. Moreover, recovered methane can be used either as fuel at the mine site or sold to other users.The third reason for coalbed methane recovery and use is that it benefits the global and local environment. Methane is a major greenhouse gas and is second in global impact only to carbon dioxide; methane thus is detrimental to the environment if vented to the atmosphere. Although the amount of carbon dioxide accumulating in the atmosphere each year is orders of magnitude larger than that of methane, each additional gram of methane released to the atmosphere is as much as 22 times more effective in potentially warming the Earth’s surface over a 100-year period than each additional gram of carbon dioxide (USEPA, 1994a) . Compared with other greenhouse gases, methane has a relatively short atmospheric lifetime. The lifetime of methane (defined as its atmospheric content divided by its rate of removal) is approximately 10 years. Due to its short lifetime, stabilizing methane emissions can have a dramatic impact on decreasing the buildup of greenhouse gases in the atmosphere.Coal mine methane recovery and use represent a cost-effectivemeans of significantly reducing methane emissions from coal mines. Methane, moreover, is a remarkably clean fuel. Methane combustion produces no sulfur dioxide or particulates and only half the amount of carbon dioxide that is associated with coal combustion on an energy equivalent basis.Because of the environmental impact of coal mine methane emissions, the USEPA, the Internat ional Energy Agency’s Coal Advisory Board (CIAB), and others have investigated methane emissions from coal mining worldwide. The USEPA (1994a) estimates that the coal fuel cycle (which includes coal mining, post-mining coal transportation and handling, and coal combustion) emits 35 to 59×109 m3 of methane to the atmosphere annually. Table 1 shows methane emissions from the world’s ten largest coal producers, which are responsible for 90% of global methane emissions associated with the coal fuel cycle. Underground coal mining is the primary source of these emissions, accounting for 70 to 95% of total emissions.There are many opportunities for decreasing coal mine methane emissions by increasing recovery of this abundant fuel. Section 2 examines the status of methane recovery and use in key countries worldwide.2 Coal mine methane recovery and use in selected countries2.1 ChinaThe Peoples Republic of China (China) produces about 1.2×109 raw tons of hard coal annually (EIA, 1996). In 1990, coal mining activities in China emitted an estimated 14 to 24×109 m3 (10 to 16×106 ton) ofmethane to the atmosphere, contributing one-third of the world’s total from this source. Not only is China the largest coal producer in the world; it is unique in that underground mines produce over 95% of the nation’s coal. Because of the great depth and high rank of China’s coals, underground coal mines have higher methane emissions than surface mines.There are currently 108 Coal Mining Administrations (CMAs) in China, which manage more than 650 mines. These state-owned mines are responsible for most of China’s methane emissions, but there are numerous gassy local, township, and private mines that cumulatively produce over one-half of China’s coal. However, these non-states owned mines are not gassy (International Energy Agency or IEA, 1994).2.1.1 Methane recovery and use in ChinaChina has a long history of coal mine methane drainage, and the volume of methane drained has increased markedly during the past decade. Nationwide, coal mine methane drainage at state-run mines nearly doubled in 14 years, increasing from 294×106 m3 in 1980 to more than 561×106 m3 in 1994 .However, this is still less than 11% of the total methane liberated annually. Approximately 131 state-owned mines currently have methane drainage systems. Less than one-half of these mines are set up to distribute and use recovered methane. China’s state-run coal mining administrations use about 70% of the methane they drain (USEPA, 1996a).Most of the methane recovered from Chinese mines is used forheating and cooking at mine facilities and nearby residences. Methane is also used for industrial purposes, in the glass and plastics industries, and as a feedstock for the production of carbon black (an amorphous form of carbon used in pigments and printer’s ink). Methane is also being used, to a lesser extent, for power generation. In 1990, the Laohutai Mine at the Fushun Coal Mining Administration built a 1200 kW methane-fired power station, the first in China.Several barriers currently prevent China from developing economic methane recovery from coal mining to its full potential. Critical barriers include the lack of an appropriate policy framework, limited capital for project investments and equipment, the need for additional information and experience with technologies and the lack of a widespread pipeline network. Artificially regulated low gas prices and difficulty with repatriation of profits, create barriers to foreign investment in joint ventures for production of domestic energy resources (USEPA, 1993).2.1.2 The future of methane development in China Recognizing the need for a unified effort in advancing coalbed methane development, China’s highest governing body, the State Council, established the China United Coalbed Methane Company (China CBM) in May 1996. As a single, trans-sectoral agency, China CBM is responsible for developing the coalbed methane industry by commercializing the exploration, development, marketing, transportation and utilization of coalbed methane. The State Council has also granted China CBM exclusive rights to undertake theexploration, development and production of coalbed methane in coopera- tion with foreign partners (China Energy Report, 1996). More than 20 coalbed methane projects are underway or planned in China, and at least half of them are taking place at active mining areas. Some of the projects are state-sponsored, while others involve joint ventures with foreign companies. The future of the coalbed methane industry in China appears bright. The government recognizes coalbed methane’s potential for meeting the nation’s burgeoning energy needs and is generally supportive of efforts to develop this resource. With deregulation of energy prices, increased capital investment in pipeline infrastructure, and ongoing research efforts, China can likely overcome its remaining barriers to widespread coalbed methane use. 2.2 Russia, Ukraine and KazakhstanIn 1994, Russia produced more than 169×106 ton of hard coal; Kazakhstan produced nearly 104×106 ton and Ukraine more than 90×106 ton. The coal mining regions of these republics liberate approximately 5.3×109 m3 of methane annually, of which less than 3% is utilized. This amount represents about 20% of world methane emissions from underground coal mining.The energy sectors of these Republics are at a turning point. The coal mining industry, in particular, is undergoing restructuring, a process which includes decreasing or eliminating subsidies, and closing many of the most unprofitable mines. The industry is being compelled to become more efficient in order to increase profitability. Mining regions are also seeking to mitigate environmental problemsresulting from producing and using coal. Thus, there is an impetus to utilize more natural gas and decrease dependency on low grade coal. Increasing recovery and use of coalbed methane is a potential means of improving mine safety and profitability while meeting the regions’ energy and environmental goals.There are five coal basins in the Commonwealth of Independent States where hard coal is mined and which have the potential for coalbed methane development.They are: (1) the Donetsk Basin (Donbass) , located in southeastern Ukraine and western Russia, (2) the Kuznetsk Basin Kuzbass , located in western Siberia (south-central Russia) , (3)the L’vov-Volyn Basin, located in western Ukraine, which is the southeastern extension of Poland’s Lublin Basin, (4)the Pechora Basin, located in northern Russia and (5) the Karaganda Coal Basin, located in Kazakhstan.Of the five basins, the Donetsk and Kuznetsk Basins appear to have the largest near-term potential for coalbed methane development (USEPA, 1994b). Both of these regions are heavily industrialized and present many opportunities for coalbed methane use.2.2.1 Options for methane use in the CIS2.2.1.1 Heating mine facilities. Currently, most mines use coal-fired boilers to produce steam heat for drying coal, heating mine facilities and heating ventilation air. In some cases, mine boilers also supply thermal energy to the surrounding communities. Boilers can be retrofitted to co-fire methane with coal, a relatively simple and low-cost procedure. More than 20 mines in the Donetsk and PechoraBasins use methane to fuel boilers and several mines also use it for direc tly heating air for the mines’ ventilation systems and for coal drying (Serov, 1995; Saprykin et al., 1995).2.2.1.2. Use in furnaces in the metallurgical industry. Another viable market for methane use is the metallurgical industry. For example, the city of Novokuznetsk, in the southern portion of the Kuznetsk Basin, contains numerous gassy mines and is one of the biggest centers of metallurgy in Russia. The region’s metallurgical industry consumes about 54 PJ of natural gas annually, which is equivalent to about1.4×109 m3 of methane (USEPA, 1996b) .2.2.1.3. Power generation at mine facilities. Most mines purchase electricity from the power grid. Co-firing coalbed methane with coal to generate electricity on-site may be a more economical option for these mines. Coalbed methane can be used, independently of or in conjunction with coal, to generate electricity using boilers, gas turbines and thermal combustion engines (USEPA, 1994b).2.2.1.4. Use as a motor vehicle fuel. The Donetskugol Coal Production Association in Ukraine is draining methane in advance of mining using surface boreholes. The recovered methane is compressed on-site and used as fuel for the Association’s vehicle fleet. The refueling station, which has been operating for more than three years, produces about 1,000 m3 of compressed gas per day. Based on estimated gas reserves it is expected to operate for a total of eight years ( Pudak, 1995 ).While many mines in the CIS are utilizing their methane resources,the majority are not. Certain barriers must be overcome before recovery and use of coal mine methane becomes widespread. These barriers and their potential solutions are discussed in greater detail in Section 3 of this paper.2.3 The United StatesThere are five major coal producing regions in the United States from which hard coal is mined and which have the potential for coalbed methane development. They are: (1)the Appalachian Basin, located in Pennsylvania, Ohio, West Virginia, eastern Kentucky and Tennessee, (2)the Warrior Basin, located in Alabama, (3)the Illinois Basin, located in Illinois, Indiana and western Kentucky, (4)the Southwestern region, including the Uinta, Piceance, Green River and San Juan Basins located in Colorado, Utah and New Mexico and (5)the Western Interior region, including the Arkoma Basin of Oklahoma and Arkansas.In 1994, an estimated 4.2×109 m3 of methane were liberated by underground mining in these regions, of which less than 0.7×109 m3 were used(USEPA, unpublished data).Currently in the United States, at least 17 mines in six states (Alabama, Colorado,Ohio, Pennsylvania, Virginia and West Virginia)recover methane for profit, primarily through sale to gas distributors. In 1995, the total methane recovered from these mines, including vertical wells draining methane in advance of mining, exceeded 1×109 m3.By maximizing the amount of gas recovered via drainage systems, these mines have greatly reduced their ventilationcosts, improved safety conditions for miners and have collected and sold large quantities of high-quality gas. Following is a brief description of selected coal mine methane recovery activities in the United States.2.3.1 Warrior basin: AlabamaSix of the seventeen US mines with commercial methane recovery systems are located in the Warrior Basin of Alabama. Today, energy companies recover methane from the Warrior Basin by horizontal wells, gob wells(in areas being mined )and vertical wells(in both mined and unmined areas). Most of this gas is sold to regional natural gas distributors, although there is some on-site mine use. In 1995, four mines operated by Jim Walter Resources produced more than 380×106 m3 of methane for pipeline sale and USX’s Oak Grove Mine recovered an estimated 117×106 m3 of methane for use.2.3.2 Appalachian regionEight mines in Virginia and West Virginia have developed successful methane recovery and use projects. The Consol mines in Virginia are the most well-documented examples. Consol produces gas from a combination of vertical wells that are hydraulically stimulated, horizontal boreholes and gob wells drilled over longwall panels. In 1995, Consol produced approximately 688×106 m3 of saleable methane from three mines. Methane recovery efficiency at these mines is higher than 60%.2.3.3 Southwestern regionThe Soldier Canyon Mine in Utah recovered about 10.9×106 m3 ofmethane for sale annually until early 1994, when production was curtailed and gas sales ended due to low market prices.2.3.4 SummaryWhile methane recovery has been economically implemented at the above-described mines, safety and high coal productivity remain the impetus for their degasification efforts. Methane drainage at many gassy mines in the United States is limited or nonexistent. Section 3 of this paper discusses potential avenues for increasing methane recovery and use in the United States and other countries.2.4 GermanyGermany produced nearly 54 million tons of hard coal in 1995, all from underground mines (Schiffer, 1995). Of this total, 43 million tons were mined from the Ruhr Basin in northwestern Germany (Von Sperber et al., 1996)and most of the remainder was mined from the Saar Basin in southwestern Germany. Until recently, hard coal mining was heavily subsidized in Germany, and the industry’s future is in question (Schiffer, 1995). Even mines that are closed, however, can continue to liberate methane for long periods of time. An estimated 1.8×109 m3 of methane are liberated annually from underground mining activities in Germany, of which 520×106 m3, or 30%, are drained(63 IEA, 1994). About 371×106 m, or 71% of all drained methane is used, primarily for heating or power generation. Government officials suggest that as much as 45% of the methane emitted from coal mining activities could be drained and used in a variety of applications. The primary barrier to increased methanerecovery is low methane concentrations in the gas mixture.Safety regulations in Germany prohibit any utilization if the methane content is less than 25%. If the average recovery efficiency at German mines is to be increased, it will be necessary to adopt practices that will recover methane in a more concentrated form.3 Barriers to decreasing coal mine methane emissionsThere are several barriers to decreasing methane emissions by increasing coal mine methane use. Some are technical, such as low coal permeability, while others are Institutional, such as low gas prices. In a few cases, certain barriers are country orregion specific, but most cases, many of the same barriers exist in a number of countries. This section discusses obstacles to increased coal mine methane use, and potential ways to overcome these obstacles.3.1 Technical issues3.1.1 Low-permeability coalsCoal seams that exhibit low permeability pose special problems for developingsuccessful methane drainage and recovery systems. Methane desorbs and flows through natural pores and fractures until the gas reaches the mine face or borehole. Stimulation technology that enhances the flow of gases from the seam into a recovery system has been successfully used in the past several years. Early efforts to modify fracturing techniques for application in coal seams were largely unsuccessful (IEA, 1994). The current practice of hydraulic stimulation in coals, however, minimizes roof damage while achievingextensive fracturing. Under ideal conditions, 60 to 70% of the methane contained in the coal seam can be removed using vertical degasification wells drilled more than 10 years in advance of mining. These efforts have been successful in the United States and other industrialized countries. Transfer of this technology to other countries can help increase coal mine methane recovery.3.2 Economic and institutional issuesIn addition to the technical obstacles described above, there are a variety of other issues that have prevented coal mine methane recovery from becoming more widespread.These issues include lack of information, lack of capital, low natural gas prices and risks associated with foreign investment. Some issues are explored below.The key strategy for overcoming informational barriers in the United States has been to develop outreach programs. Outreach programs work well when companies are shown that they can profit while at the same time reducing emissions or improving mine safety. Examples of outreach programs include the USEPA’s Coalbed Methane Outreach Program, which is conducted in the United States, and the Coalbed Methane Clearinghouses in Poland, China and Russia. These institutions distribute information and link together interested parties, provide technical training, and in some cases perform pre-feasibility assessments for specific projects.3.2.1 Lack of informationIn the United States and other countries, one of the problems thathas slowed coal mine methane project development is that some coal mine operators do not have adequate information regarding coal mine methane projects. While much has been published on the subject, methane recovery is still seen as a relatively new concept to many coal operators. A related constraint is that some coal operators simply do not have the time or resources to investigate the potential to develop a profitable project at their own coal mine.3.2.2 Lack of capitalEven when a pre-feasibility assessment has demonstrated that the economics of a coal mine methane project are attractive, a lack of financing may prevent projects from taking place. Coal companies often do not have surplus capital available to invest in coalbed methane recovery and use projects because available capital must be invested in their primary business of coal production. Additionally, some lending organizations may be unfamiliar with the relatively new concept of coal mine methane recovery and use, and project developers may thus be unable to secure the necessary up-front financing needed to cover the large capital investments required for such projects.3.2.3 Low natural gas pricesIn some countries natural gas prices are held at artificially low rates. Even in countries whose gas prices are at market levels, prices may be low due to low demand. In such cases, special types of incentives to encourage coal mine methane recovery could be implemented. For example, legislation could be enacted requiring local distributioncompanies to purchase recovered coal mine methane if it is sold at a competitive price. China has recently established preferential policies for projects which involve gas recovery and use from coal mines. The government has also passed a law exempting coalbed methane producers from royalties and land occupation fees for production of up to 2×109 m3 of methane per year.4 ConclusionsAs discussed above, coal mines worldwide emit large volumes of methane, much of which could be recovered and used as fuel. In many instances, countries whose mines emit large quantities of methane are in critical need of a domestic energy source, particularly one which is clean-burning. In countries whose economies are in transition, such as China, the former Soviet Union and the Eastern European nations, coal mine methane recovery offers economic benefits as a new industry that can help provide jobs for displaced coal miners or other workers. In countries whose economies are established, such as the United States, the United Kingdom and Australia, coal mine methane recovery may help increase the profit margin of mining enterprises.The reduction of methane emissions can have a significant global impact, but incentives are needed to encourage more widespread recovery of coal mine methane. An incentive program offered on an international level would probably be the most effective means of stimulating development of the coal mine methane industry. Of the various options for international-level incentives, a system of tradeable permits for methane emissions would likely be the most cost effective.Due to various technical, economic and institutional barriers, it will never be possible to completely eliminate emissions of methane from coal mines. However, a worldwide coal mine methane utilization rate of 25% may be realizable, particularly if an international incentive program is implemented. This would reduce the estimated emissions of coal mine methane to the atmosphere by 7 to 10×109 m3 annually, substantially reducing greenhouse gas emissions and curtailing the waste of a valuable energy source.附录B全球煤矿瓦斯涌出及利用现状全球煤矿每年释放瓦斯29~41×109m3,其中少于2.3×109m3的瓦斯用作燃料,其余的被直接排放到大气中,这是能源的一种浪费。