中国有色金属学报(英文版)

Apparent activation energy for spontaneous combustion of sulfide concentrates in storage yard

YANG Fu-qiang1, 2, WU Chao1, 2, CUI Yan1, 2, LU Guang1, 2

1. School of Resources and Safety Engineering, Central South University, Changsha 410083, China;

2. National Research Center of Safety Science and Technology for Metal Mines,

Central South University, Changsha 410083, China

Received 17 March 2010; accepted 1 July 2010

Abstract:

In order to evaluate the spontaneous combustion hazard of sulfide concentrates in storage, three different kinds of sulfide concentrates (sulfur-rich sulfide concentrate, iron sulfide concentrate and copper sulfide concentrate) were obtained from a storage yard in Dongguashan Copper Mine, China. The reaction processes at different heating rates of 5, 10, 15, 20, and 25 °C/min in air flow from ambient temperature to 1 000 °C were studied by TG-DTG-DSC analysis. By the peak temperatures of DTG curves, the whole reaction process for each sample was divided into different stages, and the corresponding apparent activation energies were calculated by the Ozawa-Flynn-Wall method. It is found that the reaction process of each sample is considerably complex; the apparent activation energy values change from 36 to 160 kJ/mol in different temperature ranges; sulfur-rich sulfide and iron sulfide concentrates have lower apparent activation energy than copper sulfide concentrate below 150 °C; so they are more inclined to cause spontaneous combustion at ambient temperature.

Key words:

apparent activation energy; sulfide concentrates; spontaneous combustion; thermogravimetry (TG) analysis; differential scanning calorimetry (DSC);

1 Introduction

Sulfide concentrates produced in excess of demand have to be deposited in stockpiles. Spontaneous combustion is a common phenomenon when convenient conditions are available, especially where large quantities of sulfide concentrates are stored for extended periods. During the storage, a major source of SO2 releases, then sulfide concentrates will lose both their economic values and cause environmental problems. In Dongguashan Copper Mine of China, spontaneous combustion of sulfide concentrates in the storage yard occurs frequently[1]. The maximum temperature of sulfide concentrate stockpile surfaces can reach 40 °C in summer, with strong sulfur gas odor. The metallic walls and ceilings have to be replaced frequently resulting from the acid erosion, leading to a large economic loss.

Based on the relevant literatures, reports on dealing with spontaneous combustion of sulfide concentrates were scarce. However, the oxidation of sulfide ores has been studied in detail[2-5] because of their importance in the acid generation in mine waters, mineral processing, and hydrometallurgical systems. Evaluation of the self- ignition hazard, considering the heat properties of sulfide concentrates, requires experimental methods. These experimental methods can be divided into self-heating and temperature-programmed experiments[6]. The self- heating methods[7-9] include adiabatic experiments, the standard wire mesh basket test and the appropriate Frank-Kamenetskii (F-K) analysis, as well as the crossing-point temperature (CPT) method. Differential scanning calorimetry (DSC), thermogravimetric analysis (TG), and differential thermal analysis (DTA) represent the temperature-programmed methods[10]. The main difference[6] is that in self-heating experiments, the temperature—time course is studied at a constant ambient temperature, whereas for the temperature-programmed experiments, a constant heating rate is applied to the sample. Although adiabatic experiments[11-12] can yield the most direct information on the low-temperature oxidation of sulfide concentrates, including such parameters as heats of adsorption and reaction, and activation energies, they are difficult to be performed.

In this study, chemical composition and mineral phase analysis of sulfide concentrates were carried out by precision instruments; the apparent activation energy values for the investigated processes were determined on the basis of TG-DTG-DSC results obtained at different heating rates by the methods of Ozawa-Flynn-Wall.

2 Experimental

2.1 Sample preparation and analysis

Three typical samples (sulfur-rich sulfide concentrate, iron sulfide concentrate, and copper sulfide concentrate) were collected from Dongguashan Copper Mine in China, of which the particle diameter was grinded to less than 0.2 mm.

The samples were analyzed by scanning electron microscopy (SEM), X-ray diffractometry (XRD), and Fourier transform infrared spectrum analysis (FTIR) in details. Table 1 indicates that the sulfur contents of three samples are high, iron sulfide concentrate has the highest iron content, and copper sulfide concentrate has the most copper content. Fig.1 shows that three sulfide concentrates are broken into rough particles or rods by grinding, and the caking of iron sulfide concentrate can be also observed.

XRD measurement was performed on a Riguku D/Max 3041 system to analyze the mineragraphy composition of samples. XRD patterns were recorded with Cu Kα (λ = 0.154 2 nm) radiation and the X-ray tube was operated at 40 kV and 20 mA with time constant of 0.5 s. Step scans were taken over a range of 2θ from 10° to 90° at a speed of 2 (°)/min. The results display that sulfur-rich sulfide concentrate is mainly composed of pyrite (FeS2), pyrrhotite (Fe1-xS), gypsum (CaSO4·2H2O), isocubanite (CuFe2S3), and quartz (SiO2); iron sulfide concentrate mostly contains magnetite (Fe3O4),

Fig.1 SEM images for three samples: (a) Sulfur-rich sulfide concentrate; (b) Iron sulfide concentrate; (c) Copper sulfide concentrate

Table 1 Chemical composition of three sulfide concentrates (mass fraction, %)



pyrrhotite (Fe1-xS), pyrite (FeS2), Ca[B(OH)4]2·2H2O (hexahydroborite), and (CaSO4)·2H2O (gypsum); copper sulfide concentrate contains mainly chalcopyrite (CuFeS2) and zinc sulfide (ZnS).

Each sample was smeared onto a potassium bromide disc and the corresponding absorbance peaks were obtained by the diffuse-reflection mode of FTIR (type NEXUS 670). The wave length scanning range is from 4 000 to 400 cm-1, and number of scans is 32. The results show that FTIR spectra of three samples are extremely similar, with the structure of bisulfide, sulfate, silicon compound, and water structure.

2.2 Test method

Thermogravimetric (TG) and differential scanning calorimetry (DSC) are the most commonly used techniques to follow the course of solid state reactions; the relative sensitivities of the two techniques depend upon the change in mass for the process (processes) (TG) or the enthalpy of the process (processes) (DSC)[13]. Simultaneous TG/DSC instrument Netzsch Model STA449C/3/MFC/G was performed, and synthetic air (20.5% O2 (quality 4.5 g) in N2 (quality 5.0 g)) was used as the purge gas with an air flow rate of 20 mL/min. The samples with mass of about 20 mg were measured at the heating rates of 5, 10, 15, 20, and 25 °C/min respectively, from ambient temperature to1 000 °C.

2.3 Results and discussion

The curves of simultaneous TG-DTG-DSC analysis for the oxidation reaction of the investigated sulfide concentrates in air at different heating rates are exemplarily shown in Fig.2 and Fig.3, which indicate the complexity of each reaction process. At diverse heating rates, the gained curves are different. In general, increasing the heating rate results in higher temperature values for the oxidation and decomposition reaction.

Table 2 shows the maximum peak temperatures detected on the DTG curves from ambient to 800 °C, which depends on the heating rate.

The obvious mass loss (gain), and endothermic (exothermic) peaks can be found from Fig.2 and Fig.3, which show the formation of sulfate, the oxidation of the sulfide, and the decomposition of sulfates. For the oxidation of sulfide minerals under air condition, the direct formation of oxide can be expressed in general as follows[14]:

2MS(s) + 3O2(g) →  2MO(s) + 2SO2(g)                 (1)

The formation of SO2 is highly exothermic, and

Fig.2 TG curves of three sulfide concentrates at different heating rates: (a) Sulfur-rich sulfide concentrate; (b) Iron sulfide concentrate;      (c) Copper sulfide concentrate

Fig.3 DSC-TG-DTG curves of three sulfide concentrates at heating rate of 10 °C/min:     (a) Sulfur-rich sulfide concentrate; (b) Iron sulfide concentrate; (c) Copper sulfide concentrate

Table 2 DTG results for peak temperatures Tm in different reaction stages at various heating rates


corresponding reactions are readily detected as an exothermic peak in the DSC curve (Fig.3). The conversion of sulfide to oxide produces a mass loss coincident with the exothermic event. Formation of sulfate can take place by direct oxidation of the sulfide and sulfation of the oxide with sulfur trioxide. The formation of sulfate is also an exothermic process, but the reaction is relatively slow and takes place over a wide range of temperature, so there are the broad exothermic peaks in Figs.3(a) and (c).

For sulfur-rich sulfide concentrates, pyrite and pyrrhotite are two main sulfide minerals. The moisture of the samples is lost in a temperature range of 100-150 °C, indicated by a mild loss of mass on the TG curve. At

about 520 °C dissociation of pyrite begins, indicated by a loss of mass on the TG curve. A sharp DTG peak shows a fast process. Because this stage takes place in an oxidative atmosphere, sulfur released during dissociation of pyrite is oxidized to SO2. Oxidation of FeS to Fe2O3 is also taking place. A summary of these reactions are as follows[14-15]:

FeS2=FeS+S0                                                  (2)

S2+2O2=2SO2                                                 (3)

4FeS+7O2=2Fe2O3+4SO2                                   (4)

For iron sulfide concentrate, magnetite, pyrrhotite, and pyrite are three primary minerals. As is shown in Fig.3(b), the oxidation reaction of magnetite mineral particles is also highly exothermic, indicated by a mass gain on the TG curve. The corresponding reaction equation is written as follows[16]:

4Fe3O4+O2=6Fe2O3                                          (5)

For copper sulfide concentrates, it can form a protective layer on the surface during oxidation at low heating rates, and access to unreacted surface is greatly hindered and oxidation slows greatly[17]. Under high heating rates, the first exothermic effect on the DSC curve occurs with a loss of mass on the TG curve at about 470 °C. This indicates that during the dissociation, chalcopyrite releases elemental sulphur which is oxidized to SO2. At above 500 °C the oxidation of Cu2S starts, formed by dissociation of chalcopyrite, giving copper sulphates, which corresponds to further increase in mass on the TG curve. A summary of these reaction processes are as follows[18]:

2CuFeS2+O2=Cu2S+2FeS+SO2                            (6)

Cu2S+SO2+3O2=2CuSO4                       (7)

2Cu2S+5O2=2(CuO·CuSO4)                     (8)

CuFeS2+2O2=CuS+FeSO4                                  (9)

CuS+2O2=CuSO4                                           (10)

12FeSO4+3O2=4Fe2(SO4)3+2Fe2O3                      (11)

3 Theoretical analysis

The methods used for analyzing the data obtained from temperature programmed experiments can be classified as differential and integral methods, and the two methods are classified further based on data acquired for one or more heating rates[13]. It is figured out that methods based on the experiments carried out under different heating rates give more reliable results than those based on data from a single heating rate, and that the integral methods are subjected to fewer experimental errors[19].

In this study, the way for determining the apparent activation energy has been performed by Ozawa-Flynn-Wall (OFW) method[13, 19-20], which is attributed to the integral methods. Ozawa has quantified the dependence between the maximum peak temperature and the heating rate in the following equation:

          (12)

where β is the heating rate; Tm is the maximum peak temperature; E is the activation energy; R is the gas constant; A is the pre-exponential; and a is the conversion degree.

By plotting lgβ versus 1/Tm, one can obtain E from the slope of the resulting straight line, regardless of the reaction order of the system. The validity of this equation is based on the assumption that the conversion at the peak maximum is constant for different heating rates[20].

4 Apparent activation energy of sulfide concentrates

In order to determine the kinetic parameters for the oxidation processes of sulfide concentrates in air, experimental results were treated according to Eq.(12). Fig.4 shows the dependencies of lgβ versus 1/Tm, where Tm is the maximum temperature on the DTG curve. The linear regression to the experimental values is excellent. The apparent activation energy in different reaction stages can be obtained from the slope of the regression line. All the results are listed in Table 3. It can be found that the apparent activation energy values vary in different temperature ranges, with 36-160 kJ/mol; sulfur-rich sulfide and iron sulfide concentrates have lower apparent activation energy than copper sulfide concentrate below 150 °C.

Table 3 Apparent activation energy of sulfide concentrates for different reaction processes from ambient temperature to   800 °C

Fig.4 Arrhenius plots for DTG experiments: (a) Sulfur-rich sulfide concentrate; (b) Iron sulfide concentrate; (c) Copper sulfide concentrate

5 Conclusions

1) Three types of representative sulfide concentrates, including sulfur-rich sulfide concentrates, iron sulfide concentrates, and copper sulfide concentrate in a storage from a typical metal mine, were obtained. The chemical compositions and mineral phases of each sample are approved to be complex by XRD, SEM, and FTIR measurements.

2) According to the TG-DTG-DSC curves, the heating rate has a significant effect on the chemical reactions of each sample, influencing not only the amount of residues but also the DTG and DSC peak temperatures. By the Ozawa-Flynn-Wall method, the apparent activation energy values of each kind of sulfide concentrates were calculated. The results show that apparent activation energy of each sample varies in different thermal degradation temperature ranges, with 35-160 kJ/mol from ambient temperature to 800 °C.

3) Below 150 °C, sulfur-rich sulfide and iron sulfide concentrates have lower apparent activation energy value than copper sulfide concentrate, so they are more susceptible to oxidize than copper sulfide concentrate at ambient temperature, and may cause spontaneous combustion.

References

[1] WU Chao, LI Zi-jun. The controlling technology of the spontaneous combustion of sulfide concentrates [R]. Changsha: Central South University, 2008. (in Chinese)

[2] IGARASHI T, HATAYA R, OYAMA T. Estimation of pyrite oxidation rate by sulfate ion discharged from a catchment [J]. Journal of Geochemical Exploration, 2003, 77: 151-165.

[3] DIMITROV R, BOYANOV B. Investigation of the oxidation of metal sulphides and sulphide concentrates [J]. Thermochimi Acta, 1983, 64: 27-37.

[4] JANZEN M P, NICHOLSON R V, SCHARER J M. Pyrrhotite reaction kinetics: Reaction rates for oxidation by oxygen, ferric iron, and for nonoxidative dissolution [J]. Geochimica et Cosmochimica Acta, 2000, 64(9): 1511-1522.

[5] BELZILE N, CHEN Y W, CAI M F, LI Y. A review on pyrrhotite oxidation [J]. Journal of Geochemical Exploration, 2004, 84: 65-76.

[6] MALOW M, KRAUSE U. The apparent activation energy of the exothermic reactions of thermally unstable materials [J]. Journal of Loss Prevention in the Process Industries, 2004, 17: 51-58.

[7] SUJANTI W, ZHANG D K, CHEN X D. Low-temperature oxidation of coal studied using wire-mesh reactors with both steady-state and transient methods [J]. Combustion and Flame, 1999, 117: 646-651.

[8] CHEN X D. On basket heating methods for obtaining exothermic reactivity of solid materials: The extent and impact of the departure of the crossing-point temperature from the oven temperature [J]. Transactions of the Institution of Chemical Engineers B, 1999, 77: 187-192.

[9] JONES J C, CHIZ P S, KOH R, MATTHEW J. Kinetic parameters of oxidation of bituminous coals from heat-release rate measurements [J]. Fuel, 1996, 75(15): 1755-1757.

[10] OZAWA T. Thermal analysis review and prospect [J]. Thermochimica Acta, 2000, 355: 35-42.

[11] REN T X, EDWARDS J S, CLARKE D. Adiabatic oxidation study on the propensity of pulverised coals to spontaneous combustion [J]. Fuel, 1999, 78: 1611-1620

[12] VANCE W E, CHEN X D, SCOT1TM S C. The rate of temperature rise of a subbituminous coal during spontaneous combustion in an adiabatic device: The effect of moisture content and drying methods [J]. Combustion and Flame, 1996, 106: 261-270.

[13] HU Rong-zu, GAO Sheng-li, ZHAO Feng-qi, SHI Qi-zhen, ZHANG Tong-lai, ZHANG Jian-jun. Kinetics of thermal analysis[M]. 2nd ed. Beijing: Science Publishing House, 2001. (in Chinese)

[14] DUNN J G. The oxidation of sulphide minerals [J]. Thermochimica Acta, 1997, 300: 127-139.

[15] WU Chao, MENG Ting-rang. Theory and technology for control of the mine spontaneous combustion of sulfide ores [M]. Beijing: Metallurgical Industry Press, 1995. (in Chinese)

[16] FORSMO S P E. Oxidation of magnetite concentrate powders during storage and drying [J]. Int J Miner Process, 2005, 75: 135-144.

[17] AGNEW C J, WELHAM N J. Oxidation of chalcopyrite by extended milling [J]. Int J Miner Process, 2005, 77: 208-216.

[18] ZIVKOVIC Z D, MITEVSKA N, SAVOVIC V. Kinetics and mechanism of the chalcopyrite-pyrite concentrate oxidation process [J]. Thermochimica Acta, 1996, 282-283: 121-130.

[19] POPESCU C. Integral method to analyze the kinetics of heterogeneous reactions under non-isothermal conditions: A variant on the Ozawa-Flynn-Wall method [J]. Thermochimica Acta, 1996, 285: 309-323.

[20] MIN Fan-fei, ZHANG Ming-xu, CHEN Qing-ru. Non-isothermal kinetics of pyrolysis of three kinds of fresh biomass [J]. Journal of China University of Mining & Technology, 2007, 17(1): 105-111.


矿仓硫精矿自燃的表观活化能

阳富强1, 2, 吴 超 1, 2, 崔 燕 1, 2, 陆 广 1, 2

1.中南大学 资源与安全工程学院,长沙 410083;

2. 中南大学 国家金属矿安全科学技术研究中心,长沙 410083

摘 要:为了判定储存在矿仓内的硫精矿是否存在自燃危险性,从冬瓜山铜矿矿仓采集了不同类型的3种矿样(高硫精矿、硫铁精矿、硫铜精矿)。利用同步TG-DTG-DSC分析技术对3种矿样在升温速率分别为5、10、15、20和 25 °C/min的条件下,在空气气氛中的化学反应过程进行深入研究。利用DTG曲线上的峰值温度,将每种矿样的反应过程划分为不同阶段,基于Ozawa-Flynn-Wall方法求得相应区间的表观活化能。结果表明:每种矿样的反应过程相当复杂,求得的表观活化能随着反应温度区间的不同而发生改变,从室温到800 °C,3种矿样在各个反应阶段的活化能为36~160 kJ/mol;高硫精矿与硫铁精矿在150 °C以下的表观活化能较铜精矿的低,因此在室温条件下高硫精矿与硫铁精矿更容易引发自燃。

关键词:表观活化能;硫精矿;自燃;热重分析;差示扫描量热法

(Edited by YANG Hua)

                     

Foundation item: Project (2006BAK04B03) supported by the National Science and Technology Pillar Program during the 11th Five-Year Plan Period of China; Project (kjdb200902-7) supported by Doctoral Candidate Innovation Research Support Program of Science & Technology Review, China; Project (1960-71131100023) supported by Postgraduate Dissertation Innovation Foundation of Central South University, China; Project (ZKJ2009008) supported by Precious Apparatus Opening Center Foundation of Central South University, China

Corresponding author: YANG Fu-qiang; Tel: +86-13467517626; E-mail: ouyangfq@163.com

DOI: 10.1016/S1003-6326(11)60727-9

[1] WU Chao, LI Zi-jun. The controlling technology of the spontaneous combustion of sulfide concentrates [R]. Changsha: Central South University, 2008. (in Chinese)

[2] IGARASHI T, HATAYA R, OYAMA T. Estimation of pyrite oxidation rate by sulfate ion discharged from a catchment [J]. Journal of Geochemical Exploration, 2003, 77: 151-165.

[3] DIMITROV R, BOYANOV B. Investigation of the oxidation of metal sulphides and sulphide concentrates [J]. Thermochimi Acta, 1983, 64: 27-37.

[4] JANZEN M P, NICHOLSON R V, SCHARER J M. Pyrrhotite reaction kinetics: Reaction rates for oxidation by oxygen, ferric iron, and for nonoxidative dissolution [J]. Geochimica et Cosmochimica Acta, 2000, 64(9): 1511-1522.

[5] BELZILE N, CHEN Y W, CAI M F, LI Y. A review on pyrrhotite oxidation [J]. Journal of Geochemical Exploration, 2004, 84: 65-76.

[6] MALOW M, KRAUSE U. The apparent activation energy of the exothermic reactions of thermally unstable materials [J]. Journal of Loss Prevention in the Process Industries, 2004, 17: 51-58.

[7] SUJANTI W, ZHANG D K, CHEN X D. Low-temperature oxidation of coal studied using wire-mesh reactors with both steady-state and transient methods [J]. Combustion and Flame, 1999, 117: 646-651.

[8] CHEN X D. On basket heating methods for obtaining exothermic reactivity of solid materials: The extent and impact of the departure of the crossing-point temperature from the oven temperature [J]. Transactions of the Institution of Chemical Engineers B, 1999, 77: 187-192.

[9] JONES J C, CHIZ P S, KOH R, MATTHEW J. Kinetic parameters of oxidation of bituminous coals from heat-release rate measurements [J]. Fuel, 1996, 75(15): 1755-1757.

[10] OZAWA T. Thermal analysis review and prospect [J]. Thermochimica Acta, 2000, 355: 35-42.

[11] REN T X, EDWARDS J S, CLARKE D. Adiabatic oxidation study on the propensity of pulverised coals to spontaneous combustion [J]. Fuel, 1999, 78: 1611-1620

[12] VANCE W E, CHEN X D, SCOT1TM S C. The rate of temperature rise of a subbituminous coal during spontaneous combustion in an adiabatic device: The effect of moisture content and drying methods [J]. Combustion and Flame, 1996, 106: 261-270.

[13] HU Rong-zu, GAO Sheng-li, ZHAO Feng-qi, SHI Qi-zhen, ZHANG Tong-lai, ZHANG Jian-jun. Kinetics of thermal analysis[M]. 2nd ed. Beijing: Science Publishing House, 2001. (in Chinese)

[14] DUNN J G. The oxidation of sulphide minerals [J]. Thermochimica Acta, 1997, 300: 127-139.

[15] WU Chao, MENG Ting-rang. Theory and technology for control of the mine spontaneous combustion of sulfide ores [M]. Beijing: Metallurgical Industry Press, 1995. (in Chinese)

[16] FORSMO S P E. Oxidation of magnetite concentrate powders during storage and drying [J]. Int J Miner Process, 2005, 75: 135-144.

[17] AGNEW C J, WELHAM N J. Oxidation of chalcopyrite by extended milling [J]. Int J Miner Process, 2005, 77: 208-216.

[18] ZIVKOVIC Z D, MITEVSKA N, SAVOVIC V. Kinetics and mechanism of the chalcopyrite-pyrite concentrate oxidation process [J]. Thermochimica Acta, 1996, 282-283: 121-130.

[19] POPESCU C. Integral method to analyze the kinetics of heterogeneous reactions under non-isothermal conditions: A variant on the Ozawa-Flynn-Wall method [J]. Thermochimica Acta, 1996, 285: 309-323.

[20] MIN Fan-fei, ZHANG Ming-xu, CHEN Qing-ru. Non-isothermal kinetics of pyrolysis of three kinds of fresh biomass [J]. Journal of China University of Mining & Technology, 2007, 17(1): 105-111.