TW201021899A - Bromine chloride compositions for removing mercury from emissions produced during fuel combustion - Google Patents

Bromine chloride compositions for removing mercury from emissions produced during fuel combustion Download PDF

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TW201021899A
TW201021899A TW98132251A TW98132251A TW201021899A TW 201021899 A TW201021899 A TW 201021899A TW 98132251 A TW98132251 A TW 98132251A TW 98132251 A TW98132251 A TW 98132251A TW 201021899 A TW201021899 A TW 201021899A
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Taiwan
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bromine
composition
chlorine
source
absorbent
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TW98132251A
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Chinese (zh)
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Christopher J Nalepa
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Albemarle Corp
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

Compositions, and processes utilizing such compositions, are provided for reducing mercury emissions during flel combustion. Such compositions comprise a sorbent, a bromine source, and a chlorine source. Cuch compositions exhibit improved thermal stability as compared to that of the sorbent by itself.

Description

201021899 六、發明說明: 【發明所屬之技術領域】 本發明係有關用於自燃料燃燒期間所產生的排放物中 移除汞之氯化溴組成物。 【先前技術】 在200 5年,EPA頒布了清淨空氣汞管制條例(Ciean Air Mercury Rule)以限制及降低燃煤電廠的汞排放。此項條例 ,結合了 EPA的清淨空氣州際條例(cAIR)或其它法規,可 ❹ 能需要在2010年開始大幅降低美國境內燃煤電廠的汞排 放。 世界各處蘊藏了大量的煤礦資源,其具有滿足世界在 一段長時間內之能源需求的潛力。美國具有大量的低硫煤 礦資源,例如在懷俄明和蒙大拿的粉河盆地煤,但是此種 煤礦無論是元素或氧化形式皆含有不可忽略數量的汞。因 此,爲了使燃煤電廠能利用此種煤礦資源而不會造成大量 φ 的汞排放,必須要有某種形態的汞排放調節技術。 美國能源部依據許多硏究提出資訊並指出:以低量的 溴來處理煤燃料可降低煤燃料燃燒期間的汞排放量。 在世界許多區域所產生的鹵水中含有大量的溴鹽,如 溴化鈉。可以用氯處理使得溴化物氧化成溴,而自此種鹵 水中回收溴。將溴化物電解轉化成溴的方法亦爲已知;但 是電解轉化是上述方法的一種昂貴替代選項。亦有記載用 氧或空氣混合物來將溴化物催化氧化成溴;但是目前還沒 201021899 有成功的、經濟的商業運轉。 已知要自氣體流出物中去除有害氣體成分可藉由在流 出物中均勻地分散吸附劑微粒以接觸和捕捉飛行中的目標 氣體成分,接著再藉由靜電集塵器(ESP)、織物過濾器(FF) 或濕式洗滌器以機械方式自流出物氣體中去除帶有被吸附 物的吸收劑。非常有效的吸收劑爲粉狀活性碳(PAC)。使用 的PAC可以是曾經或未曾改質。改質PACs可藉由改進吸 附效率來改善目標有害物質的捕捉。在US 4,427,630、US w 5,1 79,05 8、US6,5 1 4,907、US 6,953,494、US 200 1 /00023 87 、US 2006/0051270 和 US 2007/0234902 中曾舉例說明 PAC 改質。 PACs和其它吸收劑的熱穩定性可能是有問題的;例如 ’當PAC被用於處理溫或熱的氣體流出物或者是當被大量 包裝或收集時,PAC可能會因爲未減緩的氧化反應而導致 自燃’並且可導致悶燒或燃燒。可能遭遇大量PAC的情況 φ 包括:當包裝PAC時,例如以超大型包裝袋包裝,或者是 當在FF單元中被製成濾餅或者是在與ESP結合的儲倉或 是進料斗中被收集時。自燃可能會因爲PAC變微熱或變熱 而惡化’其可能在處理燃煤鍋爐流出物時發生。如果在氧 化位置未能隔絕氧氣(空氣)或者是如果該位置沒有被冷卻 ’來自初始氧化反應的熱量可以傳送,直到PAC悶燒或點 燃爲止。這樣的點燃作用可能會相當悲慘。公用設施工廠 對於流出物管線中的自燃(例如悶燒或燃燒)非常敏感,其 201021899 可能會造成工廠停機並且對於消費者具有廣泛的影響。 有鑑於上述情況’若有新的方法能使煤和其它燃料儲 備的汞排放降至最低,將會有商業上的優勢。除此之外, 較爲有利的是使PACs和其它吸收劑具有改良的熱穩定性 〇 【發明內容】 本發明可滿足上述需求’其係提供用於降低煤和其它 可燃燃料燃燒期間所產生燃燒氣流之汞排放的組成物及方 ® 法。本發明之組成物包含溴源、氯源及可吸附溴和氯的吸 收劑。本發明亦提供此種組成物和方法,其中該組成物與 本身所含之吸收劑相比具有改善的熱穩定性。在本文和申 請專利範圍中所謂的”降低汞排放”乙詞係指藉由任何機制 (例如吸附或吸收)自排放物中去除汞的任何量,而使得燃 料在燃燒時排放至大氣中的汞量比沒有使用本發明之駔成 物和/或方法之排放量要少。本發明之吸收劑組成物可以 φ 添加至可燃燃料燃燒所產生的燃燒氣流中。除此之外,本 發明之吸收劑組成物可以在燃燒之前和/或燃燒期間添加 (結合)至燃料中。除此之外,本發明意欲在燃燒之前和/ 或燃燒期間將本發明之吸收劑組成物添加至燃料及燃燒氣 體中。此種吸收劑組成物包含溴源、氯源及可吸附溴和氯 的吸收劑。 本發明之方法可包括:將包含溴源、氯源及可吸附溴 和氯的吸收劑之組成物添加至一或多種可燃燃料在燃燒期 201021899 間所產生的燃燒氣流中;由此降低來自燃燒氣流的汞排放 。在此方法中,溴源可包括溴或HBr,氣源可包括氯或HC1 ’溴源和/或氯源可包括氯化溴。同樣在此方法中,吸收 劑可包括含碳基質、活性碳、木材衍生的活性碳或是椰子 殻衍生的活性碳。同時,燃燒氣流可衍生自煤的燃燒或是 另一種基質。在本發明之方法中,組成物具有的PIO至少 比只有吸收劑的PIO要高約10度C。 本發明之方法可包括:在可燃燃料燃燒之前和/或期 間,將包含溴源、氯源及可吸附溴和氯的吸收劑之組成物 添加至可燃燃料中;燃燒可燃燃料;產生燃燒氣流;由此 降低來自燃燒氣流的汞排放。在此方法中,可燃燃料可包 含煤或是另一種基質。同樣的,吸收劑可包括含碳基質、 活性碳、木材衍生的活性碳或是椰子殼衍生的活性碳。在 此方法中,組成物具有的PIO至少比只有吸收劑的PIO要 高約10度C。 Φ 本發明之方法可包括:在可燃燃料燃燒之前和/或期 間,將包含氯化溴及可吸附溴和氯的吸收劑之組成物添加 至可燃燃料中;燃燒可燃燃料;產生燃燒氣流;由此降低 來自燃燒氣流的汞排放。 本發明亦提供了能降低來自燃燒氣流的汞排放之組成 物,此組成物包含溴源、氯源及可吸附溴的吸收劑。在此 組成物中,溴源可包括溴或HBr’氯源可包括氣或HC1, 或者是溴源和/或氯源可包括氯化溴。此組成物也可包括 201021899 氯化溴。在本發明之組成物中,吸收劑可包括含碳基質、 活性碳、木材衍生的活性碳或是椰子殻衍生的活性碳。本 發明之組成物具有的PIO至少比只有吸收劑的PIO要高約 10 度 c 〇 本發明可藉由參考圖(第1圖)而得到更佳的理解,本 發明之吸收劑組成物可以固體形態(例如粉末或顆粒形式) 或者是液體形態添加或結合可燃燃料和/或燃燒氣流中。 吸收劑組成物可以被添加至溫度爲約150度C至約400度 ❹ c的燃燒氣流中。舉例而言,在ESPs(靜電集塵器)的冷側, 可以將吸收劑組成物注入約150度C至約200度C的燃燒 氣流中。或者是’在ESPs(靜電集塵器)的熱側,可以將吸 收劑組成物注入約300度C至約400度C的燃燒氣流中。 【實施方式】 吸收劑 適合用於本發明之可吸附溴的吸收劑包括,例如,活 φ 性碳、活性炭、活性焦炭、碳黑、粉煤、活性焦、來自燃 燒方法的未燃燒或部分燃燒碳、高嶺土或其它黏土、沸石 、氧化鋁和其它含碳基質。木材衍生的PACs特別適合用 於本發明,包括那些衍生自木質材料者,如鋸木屑、木片 或其它微粒狀木材產品。椰子殻衍生的PACs也很適合用 於本發明。對於習於本技術領域者而言,亦將會知道或可 能會知道其它適合的吸收劑,並且具有本專利申請書所教 示的優勢。 201021899 溴/氯源 適合用於本發明之溴源包括Br2和溴先質,例如HBr 。NaBr和KBr並不適合用於本發明。在一方面,本發明的 溴源不包括NaBr和KBr,並且可視爲非-鈉或鉀衍生的溴 源。在本文中,當NaBr和KBr及/或所謂非-鈉或鉀衍生 的溴源被排除在外時,係指沒有NaBr、KBr、鈉或鉀被刻 意加入。適合的氯源包括Cl2和氯先質,例如HC1。除此之 外,適合用於Br2和/或Cl2的來源包括同時包含溴和氯先 質的化合物,例如氯化溴或溴化氯。對於習於本技術領域 者而言,亦將會知道或可能會知道其它適合的溴源和/或 氯源,並且具有本專利申請書所教示的優勢。本發明所使 用之組成物可包括氯化溴、溴源和氯源。本發明所使用之 組成物可包括氯化溴、溴和氯。 吸收劑組成物 有數種程序可用來將溴和氯倂入如活性碳之吸收劑中 。在其中一個這樣的程序中,參照第1圖,將所需重要的 活性碳8置入管柱10中,其係位於加熱/冷卻套管11之 中。粗的燒結玻璃(圖中未顯示)支撐著管柱1〇中的活性碳 8。將活栓12打開並且關閉活栓14,以使得整個系統7抽 真空至壓力爲5毫米汞柱。經由加熱套11將管柱10加熱 至95度C,並且維持在95度C達一小時,以去除水份。 接著讓管柱10冷卻至室溫並且關閉活栓12。此時活性碳8 被適度的乾燥及脫氣。將所需數量的氯化溴19放入圓底燒 201021899 瓶20中。氯化溴的沸點爲4度C,所以燒瓶20被冷卻至4 度C以下。停止冷卻並且打開活栓1 4以將氯化溴1 9引進 管柱10中的活性碳8之上。讓冷卻水流進冷卻套管11’ 以去除在製程中所產生的吸附熱。吸附通常會在數個小時 內達到完全,其係由所產生批料的多寡來決定。藉由打開 活栓12且在室溫下將空氣或氮氣流通過管柱1〇和/或選 擇性地經由加熱套管11加熱至150度C的方式來去除過量 的氯化溴。現在將經氯化溴處理的活性碳8轉移到適合的 ❹ 容器中(未顯示於圖中)並且混合備用。對於習於本技術領 域者而言,亦將會知道或可能會知道其它適合用來將溴和 氯倂入如活性碳之吸收劑中的程序,並且具有本專利申請 書所教示的優勢。 熱穩定性 物質之熱穩定性可以經由初始能量釋放的溫度,亦稱 爲物質的初始氧化點(P10)來評定。在本專利申請書(包括 _ 申請專利範圍)中,本發明之組成物和/或吸收劑的PIO係 被定義爲:以DSC測得之熱流爲10 W/g時的溫度,並基 準線已被校正成在100度C下爲零。本發明之組成物與此 組成物中所使用的吸收劑相比,其具有改善的熱穩定性, 該組成物具有的PIO至少比只有吸收劑的PIO要高約10 度C。本發明之組成物所具有的PIO至少比只有吸收劑的 PIO要高約10度C至約94度C,或約10度C至約90度C ,或約10度C至約50度C,或約20度C至約80度C。 201021899 可燃燃料 本發明之方法和吸收劑組成物適合用於降低由任何含 有汞之可燃燃料燃燒所造成之燃燒氣流中的汞排放。此種 可燃燃料包括煤、天然氣、固態或流體之廢料和其它物質 0 實施例 以下實施例係用來說明本發明之原理。應了解本發明 並非偈限於此處所舉例的任何一個特定實施實例,無論是 ® 在這些實施例或是本專利申請書的其餘部分。 在以下的實施例中,我們係以氯化溴來處理木材衍生 的活性碳(熱活化木材)樣品。這種樣品的性能係與僅僅經 過元素溴、元素氯、溴化鈉或溴化鉀處理之類似活性碳樣 品做比較。使用的溴化鈉或溴化鉀可取自商業產品。性能 測試包括DSC (其係量測活性碳的熱性質),以及在某些 例子中,還包括汞捕捉的實驗室測試。 φ 實施例1 比較實施例 以DSC-TGA來分析這些實施例中所使用木材衍生之 PAC(粉狀活性碳)(以熱活化方法來製備)。初始會g量釋放 (PIO)的點爲267度C。201021899 VI. Description of the Invention: [Technical Field to Which the Invention Is Ascribed] The present invention relates to a bromine chloride composition for removing mercury from emissions generated during combustion of a fuel. [Prior Art] In 2005, EPA issued the Ciean Air Mercury Rule to limit and reduce mercury emissions from coal-fired power plants. This regulation, combined with the EPA's Clean Air Interstate Regulations (cAIR) or other regulations, may require a significant reduction in mercury emissions from coal-fired power plants in the United States in 2010. There are a large number of coal resources around the world that have the potential to meet the world's energy needs for a long time. The United States has a large number of low-sulfur coal resources, such as coal in the Powder River Basin in Wyoming and Montana, but such coal mines contain a non-negligible amount of mercury, whether in elemental or oxidized form. Therefore, in order for coal-fired power plants to use such coal resources without causing a large amount of mercury emissions, there must be some form of mercury emission regulation technology. The US Department of Energy has provided information based on many studies and pointed out that treating coal fuel with low amounts of bromine can reduce mercury emissions during combustion of coal fuels. The brine produced in many parts of the world contains large amounts of bromine salts, such as sodium bromide. The bromine can be recovered from such brine by treatment with chlorine to oxidize the bromide to bromine. A method of electrolytically converting bromide to bromine is also known; however, electrolytic conversion is an expensive alternative to the above process. It has also been reported that oxygen or a mixture of air is used to catalyze the oxidation of bromide to bromine; however, there is currently no successful economical commercial operation of 201021899. It is known that the removal of harmful gas components from the gas effluent can be achieved by uniformly dispersing the sorbent particles in the effluent to contact and capture the target gas component in flight, followed by electrostatic precipitator (ESP), fabric filtration. The (FF) or wet scrubber mechanically removes the absorbent with adsorbate from the effluent gas. A very effective absorbent is powdered activated carbon (PAC). The PAC used may or may not have been modified. Modified PACs can improve the capture of target hazardous substances by improving the adsorption efficiency. PAC modification is exemplified in US 4,427,630, US w 5,1 79,05 8, US 6,5 1 4,907, US 6,953,494, US 200 1 /00023 87, US 2006/0051270, and US 2007/0234902. The thermal stability of PACs and other absorbents can be problematic; for example, 'When PAC is used to treat warm or hot gas effluents or when packaged or collected in large quantities, PAC may be due to unmitigated oxidation reactions. Causes spontaneous combustion' and can cause smoldering or burning. Cases in which a large number of PACs may be encountered φ include: when packaging a PAC, for example in an oversized package, or when being made into a filter cake in an FF unit or being collected in a storage bin or feed hopper combined with ESP Time. Spontaneous combustion may be exacerbated by the fact that the PAC becomes slightly hot or hot. It may occur when processing coal-fired boiler effluents. If oxygen (air) is not isolated at the oxidation site or if the location is not cooled, the heat from the initial oxidation reaction can be transferred until the PAC is smoldered or ignited. Such ignition can be quite tragic. Utility plants are very sensitive to spontaneous combustion (such as smoldering or burning) in the effluent line, and its 201021899 may cause plant downtime and have a wide-ranging impact on consumers. In view of the above, there will be a commercial advantage if there are new ways to minimize mercury emissions from coal and other fuel storage. In addition, it is advantageous to have improved thermal stability of PACs and other absorbents. [Invention] The present invention satisfies the above needs. It is provided for reducing combustion during combustion of coal and other combustible fuels. Composition and method of mercury emissions from airflow. The composition of the present invention comprises a bromine source, a chlorine source, and an adsorbent capable of adsorbing bromine and chlorine. The present invention also provides such compositions and methods wherein the composition has improved thermal stability compared to the absorbents contained therein. The term "reduce mercury emissions" as used herein and in the scope of the patent application refers to any amount of mercury removed from the effluent by any mechanism (eg, adsorption or absorption) that causes the fuel to be released into the atmosphere upon combustion. The amount is less than that of the composition and/or method without the use of the present invention. The absorbent composition of the present invention can be added to the combustion gas stream produced by the combustion of combustible fuel. In addition to this, the absorbent composition of the present invention may be added (combined) to the fuel before and/or during combustion. In addition to this, the present invention is intended to add the absorbent composition of the present invention to fuel and combustion gases prior to and/or during combustion. Such an absorbent composition comprises a bromine source, a chlorine source, and an absorbent capable of adsorbing bromine and chlorine. The method of the present invention may comprise: adding a composition comprising a bromine source, a chlorine source, and an adsorbent capable of adsorbing bromine and chlorine to a combustion gas stream produced by one or more combustible fuels during a combustion period of 201021899; thereby reducing combustion from Mercury emissions from airflow. In this method, the bromine source may comprise bromine or HBr, the gas source may comprise chlorine or an HC1 'bromo source and/or the chlorine source may comprise bromine chloride. Also in this method, the absorbent may include a carbonaceous substrate, activated carbon, wood derived activated carbon or coconut shell derived activated carbon. At the same time, the combustion gas stream can be derived from the combustion of coal or another matrix. In the process of the present invention, the composition has a PIO that is at least about 10 degrees C higher than the PIO of only the absorbent. The method of the present invention may comprise: adding a composition comprising a bromine source, a chlorine source, and an adsorbent capable of adsorbing bromine and chlorine to the combustible fuel before and/or during combustion of the combustible fuel; combusting the combustible fuel; generating a combustion gas stream; This reduces mercury emissions from the combustion gas stream. In this method, the combustible fuel may comprise coal or another substrate. Similarly, the absorbent may include a carbonaceous substrate, activated carbon, wood derived activated carbon, or coconut shell derived activated carbon. In this method, the composition has a PIO that is at least about 10 degrees C higher than the PIO of only the absorbent. Φ The method of the present invention may comprise: adding a composition comprising bromine chloride and an adsorbent capable of adsorbing bromine and chlorine to the combustible fuel before and/or during combustion of the combustible fuel; burning the combustible fuel; generating a combustion gas stream; This reduces mercury emissions from the combustion gas stream. The present invention also provides a composition capable of reducing mercury emissions from a combustion gas stream comprising a bromine source, a chlorine source, and an adsorbent capable of adsorbing bromine. In this composition, the bromine source may include bromine or HBr'. The chlorine source may include gas or HCl, or the bromine source and/or the chlorine source may include bromine chloride. This composition may also include 201021899 bromine chloride. In the composition of the present invention, the absorbent may include a carbonaceous substrate, activated carbon, wood derived activated carbon or coconut shell derived activated carbon. The composition of the present invention has a PIO which is at least about 10 degrees higher than the PIO of the absorbent only. The present invention can be better understood by referring to the figure (Fig. 1), and the absorbent composition of the present invention can be solid. The form (eg, in the form of a powder or granules) or a liquid form is added or combined with the combustible fuel and/or combustion gas stream. The absorbent composition can be added to a combustion gas stream having a temperature of from about 150 degrees C to about 400 degrees ❹ c. For example, on the cold side of ESPs (electrostatic precipitators), the absorbent composition can be injected into a combustion gas stream from about 150 degrees C to about 200 degrees C. Alternatively, the absorbent composition can be injected into the combustion gas stream from about 300 degrees C to about 400 degrees C on the hot side of the ESPs (electrostatic precipitator). [Embodiment] Absorbent Suitable bromine-absorbing absorbents of the present invention include, for example, activated carbon, activated carbon, activated coke, carbon black, pulverized coal, activated coke, unburned or partially burned from a combustion process. Carbon, kaolin or other clays, zeolites, aluminas and other carbonaceous substrates. Wood derived PACs are particularly suitable for use in the present invention, including those derived from wood materials such as sawdust, wood chips or other particulate wood products. Coconut shell derived PACs are also well suited for use in the present invention. Other suitable absorbents will also be known or may be known to those skilled in the art and have the advantages as taught by the present patent application. 201021899 Bromine/Chlorine Sources Bromine sources suitable for use in the present invention include Br2 and bromine precursors such as HBr. NaBr and KBr are not suitable for use in the present invention. In one aspect, the bromine source of the present invention does not include NaBr and KBr and can be considered a non-sodium or potassium derived bromine source. Herein, when NaBr and KBr and/or a so-called non-sodium or potassium-derived bromine source are excluded, it means that no NaBr, KBr, sodium or potassium is intentionally added. Suitable chlorine sources include Cl2 and chlorine precursors such as HCl. In addition, sources suitable for use in Br2 and/or Cl2 include compounds containing both bromine and chlorine precursors, such as bromine chloride or chlorine bromide. Other suitable sources of bromine and/or chlorine will also be known or may be known to those skilled in the art and have the advantages taught by the present application. The composition used in the present invention may include a bromine chloride, a bromine source, and a chlorine source. The composition used in the present invention may include bromine chloride, bromine and chlorine. Absorbent Compositions There are several procedures for the incorporation of bromine and chlorine into an absorbent such as activated carbon. In one of such procedures, referring to Fig. 1, the desired important activated carbon 8 is placed in the column 10, which is located in the heating/cooling jacket 11. The coarse sintered glass (not shown) supports the activated carbon 8 in the column 1 . The stopcock 12 is opened and the stopcock 14 is closed so that the entire system 7 is evacuated to a pressure of 5 mm Hg. The column 10 was heated to 95 ° C via a heating mantle 11 and maintained at 95 ° C for one hour to remove moisture. The column 10 is then allowed to cool to room temperature and the stopcock 12 is closed. At this time, the activated carbon 8 is moderately dried and degassed. Place the required amount of bromine chloride 19 in a round bottom burnt 201021899 bottle 20. The boiling point of the bromine chloride is 4 degrees C, so the flask 20 is cooled to 4 degrees C or less. The cooling is stopped and the stopcock 14 is opened to introduce bromine chloride 19 onto the activated carbon 8 in the column 10. Cooling water is allowed to flow into the cooling jacket 11' to remove the heat of adsorption generated in the process. Adsorption usually reaches full within a few hours, depending on the amount of batch produced. Excess bromine chloride is removed by opening the stopcock 12 and passing a stream of air or nitrogen through the column 1 at room temperature and/or optionally heating to 150 degrees C via the heating jacket 11. The bromine chloride treated activated carbon 8 is now transferred to a suitable helium vessel (not shown) and mixed for later use. Other procedures suitable for the incorporation of bromine and chlorine into absorbents such as activated carbon will also be known or may be known to those skilled in the art and have the advantages taught by the present patent application. Thermal stability The thermal stability of a substance can be assessed by the temperature at which the initial energy is released, also known as the initial oxidation point (P10) of the substance. In the present patent application (including the scope of the patent application), the PIO system of the composition and/or absorbent of the present invention is defined as the temperature at which the heat flow measured by DSC is 10 W/g, and the reference line has been Corrected to be zero at 100 degrees C. The composition of the present invention has improved thermal stability compared to the absorbent used in this composition, and the composition has a PIO of at least about 10 degrees C higher than that of the absorbent only. The composition of the present invention has a PIO that is at least about 10 degrees C to about 94 degrees C higher than the PIO of the absorbent, or from about 10 degrees C to about 90 degrees C, or from about 10 degrees C to about 50 degrees C. Or about 20 degrees C to about 80 degrees C. 201021899 Flammable Fuel The process and absorbent composition of the present invention are suitable for use in reducing mercury emissions from combustion gases resulting from the combustion of any combustible fuel containing mercury. Such combustible fuels include coal, natural gas, solid or fluid waste and other materials. 0 EXAMPLES The following examples are illustrative of the principles of the invention. It is to be understood that the invention is not limited to any specific embodiment exemplified herein, either in the embodiments or the remainder of the application. In the following examples, we treated wood-derived activated carbon (heat activated wood) samples with bromine chloride. The performance of this sample is compared to a similar activated carbon sample treated with only elemental bromine, elemental chlorine, sodium bromide or potassium bromide. The sodium bromide or potassium bromide used can be taken from commercial products. Performance tests include DSC (which measures the thermal properties of activated carbon) and, in some cases, laboratory tests for mercury capture. φ Example 1 Comparative Example Wood-derived PAC (powdered activated carbon) used in these examples (prepared by a heat activation method) was analyzed by DSC-TGA. The point at which the initial amount of g release (PIO) is 267 degrees C.

實施例2 比較實施例 以溴處理PAC 依照US 6 95 3 494中所揭露的方法將實施例1的Pac 予以溴化。元素分析結果指出,PAC的溴含量爲5重量% 。DSC的分析指出P10爲3 64度C。 -10- 201021899EXAMPLE 2 Comparative Example Treatment of PAC with bromine The Pac of Example 1 was brominated according to the method disclosed in US 6,95 3 494. Elemental analysis indicated that the PAC had a bromine content of 5% by weight. The DSC analysis indicated that P10 was 3 64 degrees C. -10- 201021899

實施例3 比較實施例 以氯處理PAC 以已知數量的氣態元素氯(0.53克)來處理實施例1的 PAC(9.5克)。元素分析結果指出,PAC的氯含量爲6重量 %。DSC的分析指出PIO爲356度C。Example 3 Comparative Example Treatment of PAC with Chlorine The PAC of Example 1 (9.5 g) was treated with a known amount of gaseous elemental chlorine (0.53 g). Elemental analysis indicated that the chlorine content of PAC was 6% by weight. The DSC analysis indicated that the PIO was 356 degrees C.

實施例4 以氯化溴處理PAC 以已知數量的氯化溴來處理實施例1的PAC(9.6克) ,氯化溴係藉由將溴(0.36克)與氯(0.15克)結合而產生。 元素分析結果指出,PAC的氯化溴含量爲6重量%。DSC 的分析指出PIO爲361度C。Example 4 Treatment of PAC with bromine chloride The PAC of Example 1 (9.6 g) was treated with a known amount of bromine chloride, which was produced by combining bromine (0.36 g) with chlorine (0.15 g). . Elemental analysis indicated that the chlorinated bromine content of PAC was 6% by weight. The DSC analysis indicated that the PIO was 361 degrees C.

實施例5 比較實施例 以溴化鈉處理PAC 以已知數量的溴化鉀來處理實施例1的PAC。實驗分 析結果指出,PAC的溴化物含量爲5重量%。DSC的分析 指出PIO爲27 5度C。Example 5 Comparative Example Treatment of PAC with Sodium Bromate The PAC of Example 1 was treated with a known amount of potassium bromide. The results of the experimental analysis indicated that the bromide content of PAC was 5% by weight. The DSC analysis indicated that the PIO was 27 5 degrees C.

實施例6 比較實施例 以溴化鉀處理PAC 以已知數量的溴化鉀來處理實施例1的PAC。實驗分 φ 析結果指出,PAC的溴化物含量爲5重量%。DSC的分析 指出PIO爲270度C。 實施例1-4的汞捕捉數據 以下數據指出,與未經處理之PAC和只經過氯處理之 PAC相比,經氯化溴處理之PAC提供了非常良好的汞捕捉 能力。這些數據係利用US 6953494中描述的汞捕捉裝置所 取得。 201021899 PAC _ 汞捕捉量,(%,平均値) 實 施 例 1(比 較 用 ) 46 實 施 例 2(比 較 用 ) 72 實 施 例 3(比 較 用 ) 41 實 施 例 4 65 如 這 些 實施 例 中 所示1 >令人驚訝的發現,包含溴源、 氯源及可吸附溴和氯的吸收劑之本發明組成物,其具有的 w PIO不只是高於吸收劑本身的PIO,甚至於與包含吸收劑和 溴源(亦即未出現可測量數量的氯)之組成物的PIO —樣高 。同時,本發明之組成物和方法的汞排放降低能力非常良 好,雖然並沒有像基本上由吸收劑和溴所構成的組成物(亦 即沒有可測量出的氯或其它鹵素)一樣好。這是相當令人驚 訝的結果,因爲氯本身會減少吸收劑的汞排放降低能力。 有鑑於氯比顯地比溴要來的便宜,所以本發明在商業上特 Φ 別有利。 本發明特別有利之處在於:可以接受比溴還要便宜氯 的使用,以及將木材衍生之活性碳用於汞捕捉。 應了解的是,在本專利申請書及其專利申請範圍中任 何一處以化學名稱或化學式表示之反應物和成分,無論爲 單數或複數,係被視爲以化學名稱或化學型態(例如另一種 反應物、溶劑…等)所表示之另一種物質結合或進行接觸之 前的存在狀態。其與所得之混合物或溶液中所發生的化學 -12- •201021899 改變、轉換和/或反應無關(如果有的話),如同這樣的 改變、轉換和/或反應就是將所指定的組分依照本發明揭 露之條件放在一起的自然結果。因此’反應物和成分被視 爲有關於進行所需之化學反應而匯集在一起的組分,或者 是用來形成用於進行所需反應之組合而匯集在一起的組分 。因此,即使在下文的申請專利範圍中可能以現在式(“包 含”,”是”等等)提到物質、成分和/或組分,其所謂的物質 、成分和/或組分係指它依照本發明首次與一或多種其它 e 物質、成分和/或組分接觸、結合、摻混或混合之前所存 在的時間點。無論是何種轉換,如果有的話,其在原位發 生的反應係以申請專利範圍所意圖涵蓋的方式來進行。因 此,事實上,物質、成分或組分雖然可能會在接觸、結合 、摻混或混合的操作(如果係依照本發明揭露內容及習於 此技術之化學家一般知識之應用來進行)過程中經由化學 反應或轉換而喪失其原始的性質,但是這對於本發明揭露 φ 內容及其申請專利範圍的正確了解及其真義和物質的正確 評價來說並不重要。如同習於本技術領域者所熟悉的,本 文中所用的”結合”乙詞係指被”結合”的成分互相被置入一 個容器中,例如,燃燒室、管線等。同樣的,成分的”組合 ”係指己被一起置入此種容器中的成分。 雖然本發明已用一或多個較佳實施實例來描述,但應 了解也可以有其它的變化,而不會背離以下專利申請範圍 中所提出本發明之範疇。 -13- 201021899 【圖式簡單說明】 第1圖說明可用來將溴和氯倂入吸收劑(如活性碳)之 程序。 【主要元件符號說明】 7 系統 8 活性碳 10 管柱 11 加熱/冷卻套管Example 6 Comparative Example Treatment of PAC with Potassium Bromide The PAC of Example 1 was treated with a known amount of potassium bromide. The experimental results of φ analysis indicated that the bromide content of PAC was 5% by weight. The DSC analysis indicated that the PIO was 270 degrees C. Mercury Capture Data for Examples 1-4 The following data indicates that chlorinated bromine treated PAC provides very good mercury capture capacity compared to untreated PAC and only chlorine treated PAC. These data were obtained using the mercury capture device described in US 6,953,494. 201021899 PAC _ Mercury capture amount, (%, average 値) Example 1 (for comparison) 46 Example 2 (for comparison) 72 Example 3 (for comparison) 41 Example 4 65 As shown in these examples 1 &gt Surprisingly, it has been found that a composition of the invention comprising a bromine source, a chlorine source and an absorbent capable of adsorbing bromine and chlorine has a w PIO which is not only higher than the PIO of the absorbent itself, but even with the absorbent and The PIO of the composition of the bromine source (ie, no measurable amount of chlorine) is high. At the same time, the mercury emission reduction ability of the compositions and methods of the present invention is very good, although it is not as good as a composition consisting essentially of an absorbent and bromine (i.e., no measurable chlorine or other halogen). This is quite a surprising result, as chlorine itself reduces the mercury emission reduction capacity of the absorbent. In view of the fact that the chlorine ratio is significantly lower than that of bromine, the present invention is commercially advantageous. The invention is particularly advantageous in that it permits the use of chlorine which is less expensive than bromine and the use of wood-derived activated carbon for mercury capture. It should be understood that the reactants and ingredients, whether singular or plural, in any one of the scope of the present patent application and the scope of the patent application, whether in the singular or plural, are considered to have a chemical name or a chemical form (eg another The presence of another substance, such as a reactant, solvent, etc., in combination with or prior to contact. It is irrelevant, if any, to the chemical, -12-201021899 change, conversion, and/or reaction that occurs in the resulting mixture or solution, as such changes, transformations, and/or reactions are performed in accordance with the specified components. The natural consequences of putting together the conditions disclosed herein. Thus, the reactants and components are considered to be components that are brought together to carry out the desired chemical reaction, or components that are used to form a combination for performing the desired reaction. Therefore, even though the substance, ingredients and/or components may be referred to in the present formula ("include", "is", etc.) in the scope of the claims below, the so-called substance, ingredient and/or component refers to it. The point in time prior to the first contact, binding, blending or mixing with one or more other e-substance, ingredients and/or components in accordance with the present invention. Regardless of the conversion, if any, the reaction occurring in situ is carried out in the manner contemplated by the scope of the patent application. Thus, in fact, a substance, component or component may be in the process of contacting, bonding, blending or mixing, if carried out in accordance with the disclosure of the present invention and the application of the general knowledge of the chemist of the art. It loses its original properties via chemical reaction or conversion, but this is not important for the correct understanding of the φ content and the scope of its patent application and its correct evaluation of the true meaning and substance. As is well known to those skilled in the art, the term "incorporated" as used herein means that the components "combined" are placed in a container, such as a combustion chamber, a pipeline, or the like. Similarly, a "combination" of ingredients refers to ingredients that have been placed together in such a container. Although the present invention has been described in terms of one or more preferred embodiments, it should be understood that other modifications may be made without departing from the scope of the invention as set forth in the appended claims. -13- 201021899 [Simple description of the diagram] Figure 1 illustrates the procedure that can be used to decompose bromine and chlorine into an absorbent such as activated carbon. [Main component symbol description] 7 System 8 Activated carbon 10 Pipe column 11 Heating/cooling casing

12 活栓 14 活栓 19 氯化溴 20 圓底燒瓶 參 -14-12 Stopcock 14 Stopcock 19 Bromine chloride 20 Round bottom flask Reference -14-

Claims (1)

.201021899 七、申請專利範圍: 1. 一種方法,其包括: -將包含溴源、氯源及可吸附溴和氯的吸收劑之組成物 添加至一或多種可燃燃料在燃燒期間所產生的燃燒氣 流中; -由此降低來自燃燒氣流的汞排放。 2. 如申請專利範圍第1項之方法,其中溴源包括溴或HBr e 3. 如申請專利範圍第1項之方法,其中氯源包括氯或HCl 〇 4. 如申請專利範圍第1項之方法,其中溴源和/或氯源包 括氯化溴。 5. 如申請專利範圍第1項之方法,其中組成物亦包括氯化 溴。 6. 如申請專利範圍第1項之方法,其中吸收劑包括含碳基 ❹ 質。 7 .如申請專利範圍第1項之方法,其中吸收劑包括活性碳 〇 8. 如申請專利範圍第1項之方法,其中吸收劑包括木材衍 生的活性碳或是椰子殼衍生的活性碳。 9. 如申請專利範圍第1項之方法,其中燃燒氣流係衍生自 煤的燃燒。 〃 10. 如申請專利範圍第1項之方法,其中組成物具有的PIO -15- 201021899 至少比只有吸收劑的PIO要高約10度C。 11.一種方法,其包括: 在可燃燃料燃燒之前和/或期間,將包含溴源、氯源 及可吸附溴和氯的吸收劑之組成物添加至可燃燃料 中; -燃燒可燃燃料; -產生燃燒氣流; -由此降低來自燃燒氣流的汞排放。 —12.如申請專利範圍第11項之方法,其中可燃燃料包括煤 〇 13. 如申請專利範圍第11項之方法,其中吸收劑包括含碳 基質。 14. 如申請專利範圍第Π項之方法,其中吸收劑包括活性 碳。 15. 如申請專利範圍第Π項之方法,其中吸收劑包括木材 ©衍生的活性碳或是椰子殼衍生的活性碳。 16.如申請專利範圍第11項之方法,其中組成物具有的pio 至少比只有吸收劑的PI0要高約10度C» 1 7.如申請專利範圍第1 1項之方法,其中溴源包括溴或HBr 〇 18·如申請專利範圍第11項之方法,其中氯源包括氯或HC1 〇 19.如申請專利範圍第Π項之方法,其中溴源和/或氯源 -16- 201021899 包括氯化溴。 20. 如申請專利範圍第11項之方法,其中組成物亦包括氯 化溴。 21. —種方法,其包括: -在可燃燃料燃燒之前和/或期間,將包含氯化溴及可 吸附溴和氯的吸收劑之組成物添加至可燃燃料中; -燃燒可燃燃料; -產生燃燒氣流; -由此降低來自燃燒氣流的汞排放。 22. —種組成物,其能降低來自燃燒氣流的汞排放,此組成 物包含溴源、氯源及可吸附溴的吸收劑。 23. 如申請專利範圍第22項之組成物,其中溴源包括溴或 HBr。 24. 如申請專利範圍第22項之組成物’其中氯源包括氯或 HC1。 0 25.如申請專利範圍第22項之組成物’其中溴源和/或氯 源包括氯化溴。 2 6 .如申請專利範圍第2 2項之組成物’其中組成物亦包括 氯化溴。 27.如申請專利範圍第22項之組成物’其中吸收劑包括含 碳基質。 2 8 .如申請專利範圍第2 2項之組成物’其中吸收劑包括活 性碳。 -17- 201021899 2 9 .如申請專利範圍第2 2項之組成物,其中吸收劑包括木 材衍生的活性碳或是椰子殻衍生的活性碳。 30.如申請專利範圍第22項之組成物,其中組成物具有的 PIO至少比只有吸收劑的PIO要高約10度C。.201021899 VII. Scope of Application: 1. A method comprising: - adding a composition comprising a bromine source, a chlorine source and an absorbent capable of adsorbing bromine and chlorine to the combustion of one or more combustible fuels during combustion In the gas stream; - thereby reducing mercury emissions from the combustion gas stream. 2. The method of claim 1, wherein the bromine source comprises bromine or HBr e 3. The method of claim 1 wherein the chlorine source comprises chlorine or HCl 〇 4. as claimed in claim 1 A method wherein the bromine source and/or chlorine source comprises bromine chloride. 5. The method of claim 1, wherein the composition also includes bromine chloride. 6. The method of claim 1, wherein the absorbent comprises a carbon-containing ruthenium. 7. The method of claim 1, wherein the absorbent comprises activated carbon. 8. The method of claim 1, wherein the absorbent comprises wood-derived activated carbon or coconut shell-derived activated carbon. 9. The method of claim 1, wherein the combustion gas stream is derived from combustion of coal. 〃 10. The method of claim 1, wherein the composition has a PIO -15-201021899 that is at least about 10 degrees C higher than the PIO of the absorbent only. 11. A method comprising: adding a composition comprising a bromine source, a chlorine source, and an adsorbent capable of adsorbing bromine and chlorine to a combustible fuel before and/or during combustion of the combustible fuel; - burning a combustible fuel; Combustion gas flow; - thereby reducing mercury emissions from the combustion gas stream. The method of claim 11, wherein the combustible fuel comprises coal hydrazine. 13. The method of claim 11, wherein the absorbent comprises a carbonaceous substrate. 14. The method of claim 2, wherein the absorbent comprises activated carbon. 15. The method of claim 2, wherein the absorbent comprises wood © derived activated carbon or coconut shell derived activated carbon. 16. The method of claim 11, wherein the composition has a pio of at least about 10 degrees C»1 than the PI0 of the absorbent only. 7. The method of claim 11, wherein the bromine source comprises Bromine or HBr 〇18. The method of claim 11, wherein the chlorine source comprises chlorine or HC1 〇 19. The method of claim IA, wherein the bromine source and/or the chlorine source-16-201021899 comprises chlorine Bromine. 20. The method of claim 11, wherein the composition also includes bromine chloride. 21. A method comprising: - adding a composition comprising bromine chloride and an adsorbent capable of adsorbing bromine and chlorine to a combustible fuel before and/or during combustion of the combustible fuel; - burning a combustible fuel; - producing Combustion gas flow; - thereby reducing mercury emissions from the combustion gas stream. 22. A composition that reduces mercury emissions from a combustion gas stream comprising a source of bromine, a source of chlorine, and an adsorbent capable of adsorbing bromine. 23. The composition of claim 22, wherein the bromine source comprises bromine or HBr. 24. The composition of claim 22, wherein the chlorine source comprises chlorine or HCl. 0 25. The composition of claim 22, wherein the bromine source and/or chlorine source comprises bromine chloride. 2 6. The composition of claim 22, wherein the composition also includes bromine chloride. 27. The composition of claim 22, wherein the absorbent comprises a carbonaceous substrate. 2 8. The composition of claim 22, wherein the absorbent comprises activated carbon. -17- 201021899 2 9. The composition of claim 22, wherein the absorbent comprises wood-derived activated carbon or coconut shell-derived activated carbon. 30. The composition of claim 22, wherein the composition has a PIO that is at least about 10 degrees C higher than the PIO of the absorbent only. -18--18-
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