{"id":232,"date":"2018-03-21T10:18:43","date_gmt":"2018-03-21T10:18:43","guid":{"rendered":"https:\/\/www.tce.co.in\/blogs\/?p=232"},"modified":"2021-09-29T12:57:05","modified_gmt":"2021-09-29T12:57:05","slug":"brief-aspects-on-different-mercury-monitoring-techniques","status":"publish","type":"post","link":"https:\/\/www.tataconsultingengineers.com\/blogs\/brief-aspects-on-different-mercury-monitoring-techniques\/","title":{"rendered":"Brief Aspects on Different  Mercury Monitoring  Techniques"},"content":{"rendered":"<p>The recent revision in environmental norms issued by MOEF made it mandatory for thermal power plants and process industries to measure mercury emission in air .Hence it is impervitive that proper understanding of mercury measurements technology and its availability in market is essential for the implementation of mercury measurement mechanism in plant<\/p>\n<p>This paper makes an attempt to bring out the availability technologies and their commercial usage for mercury measurement and monitoring.<\/p>\n<p>Mercury is found \u00a0\u00a0in environment in various distributed &amp; different forms. Elemental mercury vapor is found in atmosphere, while inorganic &amp; organic form of element is found in soil, water, plants &amp; animals.\u00a0\u00a0 Natural sources of mercury are from forest fires, volcanoes and weathering of mercury bearing rocks. However large amount of mercury gets \u00a0\u00a0liberated to atmosphere through various human activities like combustion of\u00a0 fossil fuels , incarnation of solid waste , mining etc ,<\/p>\n<p>A Toxic metal mercury exists in coal. \u00a0\u00a0Mercury is volatized and a portion \u00a0\u00a0\u00a0of volatized mercury is absorbed in unburnt carbon and ash, when coal is combusted.. They are\u00a0 \u00a0captured along with \u00a0\u00a0particulate matter.<\/p>\n<p>So, It is difficult \u00a0\u00a0to predict \u00a0\u00a0and also complicated to characterize the Mercury emissions during coal combustion. \u00a0\u00a0\u00a0In vapor phase volatile mercury is thermodynamically stable \u00a0\u00a0at high combustion temperature and at low temperature major portion of mercury gas absorb into ash and oxidized compounds in flue gas \u00a0and form mercury compound after reacting\u00a0 \u00a0with mercury vapour<\/p>\n<p>During the combustion, the mercury in the coal is liberated \u00a0\u00a0into 3 forms \u2013 particle bound mercury, \u00a0elemental mercury and \u00a0oxidized mercury.<\/p>\n<p>Hence , to control Mercury emission first step is to measure and monitor the mercury emission and thereafter introduce\u00a0\u00a0 mercury control mechanism to reduce the mercury emission. Various methods are used to measure mercury emission.\u00a0 \u00a0These methods are \u00a0divided into offline \u00a0through manual \u00a0\u00a0\u00a0analysis and online analysis.<\/p>\n<p><b>Manual analysis<\/b> \u2013 Wet chemical mercury testing and dry sorbent method.<\/p>\n<p>Dry sorbent methods are very popular \u00a0\u00a0and used for measuring mercury concentrations and speciation. Wet chemical method (Method 20 US Environmental protection agency (USEPA )) is a relatively complex method and also costly . USEPA has developed a mobile mercury monitor toolkit based on \u00a0\u00a0Sorbent trap popularly known as Tool kit in Large TPP. These are now generally used by regulators and the researchers. In sorbent trap sampling system, mercury is collected inside a\u00a0 trap that is filled with a sorbent medium such as iodated\u00a0\u00a0 carbon. The collected sample is analyzed using traditional wet chemical methods or by thermal decomposition\/ direct combustion. This OH method (Ontario Hydro method) is a choice in measuring mercury concentration and speciation.<\/p>\n<p>Methodology for collecting sample<\/p>\n<ul>\n<li>Sampling probe with pair of sorbent traps installed in the stack.<\/li>\n<li>Flue gas is pulled through the sorbent traps which collect mercury from the gas<\/li>\n<li>Each sorbent trap has 2 to 3 sections. 1<sup>st<\/sup> section quantitatively captures mercury and 2<sup>nd<\/sup> section is used for breakthrough calculation and 3<sup>rd<\/sup> section commonly used for compliance reporting since it contains known amount of \u00a0\u00a0mercury.<\/li>\n<li>Each sorbent section is individually emptied into Quartz ladle and analyzed in analyzer. Analysis takes usually around 90 seconds.<\/li>\n<\/ul>\n<p>This\u00a0\u00a0 system \u00a0\u00a0involves \u00a0\u00a0continuous and \u00a0\u00a0repetitive \u00a0\u00a0stack sampling, using paired sorbent traps in subsequent analysis as time integrated samples.\u00a0 This system can be a primary system for compliance monitoring and as back up during CEMS maintenance &amp; verification of performance.<\/p>\n<p><b>ONLINE ANALYSIS <\/b><\/p>\n<p>Online\u00a0\u00a0 CEMS is \u00a0\u00a0\u00a0\u00a0used for real\u00a0 \u00a0time monitoring and analysis.<\/p>\n<p>The popular advanced techniques \u00a0\u00a0used are<\/p>\n<ul>\n<li>Cold vapor atomic absorption spectrometry (CVAAS)<\/li>\n<li>Cold vapor atomic fluorescence spectroscopy (CVAFS)<\/li>\n<\/ul>\n<p>The working principle of above online mercury monitoring is similar to other flue gas monitoring emission systems. Objects to be analyzed are taken by sampler from flue gas .The\u00a0 \u00a0interferential components available in sample gas such as HCI, SO<sub>2<\/sub>, SO<sub>3,<\/sub> andother acidic gases are removed before going to detector<\/p>\n<p><b>Cold Vapor Atomic Absorption Spectrometer (CVAAS<\/b>)<\/p>\n<p>It is widely accepted\u00a0 \u00a0methods \u00a0\u00a0for determining mercury i.e total mercury content. Mercury is reduced to elemental form\u00a0 for by using \u00a0Tin Chloride or Sodium borohydroide \u00a0\u00a0From solution, vapor mercury is purged by air, nitrogen or argon carrier gas.\u00a0 After \u00a0\u00a0it passes through gas liquid separately, it is led into optical path of atomic absorption spectrometer.<\/p>\n<p>These analyzers use a electrode less\u00a0\u00a0 discharge lamp EDL as light source which is driven by high frequency. Extremely narrow band width emission\u00a0\u00a0 lines are generated by lamp which is congruent with mercury atom \u00a0\u00a0absorption lines .<\/p>\n<p>CVAAS is primary technique for analyzing mercury. These \u00a0\u00a0instruments have peristaltic pump \u00a0\u00a0that transports \u00a0\u00a0sample &amp; stannous chloride separately\u00a0 into gas liquid , where pure dry gas (argon) stream\u00a0 is introduced into \u00a0liquid mixture to release mercury vapour\u00a0 . Mercury shall be carried by dry argon gas\u00a0 \u00a0in vapour phase through dryer and into \u00a0atomic absorption optical cell. In absorption cell, the elemental mercury will absorb the light at 253.7 nm in logarithm which is proportion to its actual concentration of the sample.<\/p>\n<p><b>Cold Vapor Atomic Fluorescence Spectroscopy (CVAFS) <\/b><\/p>\n<p>These mercury analysis include sub ppt detection limits and much wider dynamic range can be achieved. CVAFS analyzer \u00a0\u00a0are available with 2 configurations \u2013 one which employs single atomic fluorescence and other which employs gold amalgamation system to pre concentrated mercury. The detection limit for only fluorescence approach \u00a0\u00a0is 0.2 ppt whereas method using pre-concentration approach with fluorescence\u00a0\u00a0 detection is low as 0.02 ppt.<\/p>\n<p>The sample is introduced by peristaltic pump and stannous chloride into gas liquid separator where \u00a0\u00a0pure dry argon \u00a0\u00a0gas stream is \u00a0bubbled through a mixture to release mercury vapor.\u00a0\u00a0 This technique uses unique characteristic of mercury that allows measurement at room temperature.<\/p>\n<p>The mercury is transported in carrier gas through a dryer\u00a0\u00a0 and then to a valve which selects\u00a0\u00a0 between fluorescence &amp; pre concentration approach. In the detector mercury vapor absorbs \u00a0\u00a0254.7 nm and fluorescence at the same wavelength. Fluorescence signal is the measurement at 90 deg to incident beam to minimize scatter from excitation source. The intensity of the fluorescence light is directly proportional to the concentration of mercury.<\/p>\n<p>Typical flow diagram of CVAAS monitor<\/p>\n<p>Courtesy- Sick instruments<\/p>\n<p><a href=\"https:\/\/www.tce.co.in\/blogs\/wp-content\/uploads\/2018\/03\/1asd.png\"><img loading=\"lazy\" decoding=\"async\" class=\"alignnone size-full wp-image-233\" src=\"https:\/\/www.tce.co.in\/blogs\/wp-content\/uploads\/2018\/03\/1asd.png\" alt=\"1asd\" width=\"975\" height=\"458\" srcset=\"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/1asd.png 975w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/1asd-300x141.png 300w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/1asd-768x361.png 768w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/1asd-520x245.png 520w\" sizes=\"auto, (max-width: 975px) 100vw, 975px\" \/><\/a><\/p>\n<p>Courtesy- Sick instruments<\/p>\n<p>The Gas flow path consists of strong bypass stream from which for a sample preparation a \u00a0small partial stream is extracted\u00a0 by a built in gas transfer pump. The 2<sup>nd<\/sup>\u00a0 \u00a0pump extracts the partial stream and sends it to reduction step &amp; amalgamation unit. All the components in contact with gas are heated electrically \u00a0\u00a0to high temperature.<\/p>\n<p>Reduction<\/p>\n<p>Mercury chloride compounds are reduced to elemental mercury by wet chemical reduction process with SnCl<sub>2 <\/sub>solution within reduction vessel. Excess condensate is removed by peristaltic pumps &amp; feed in reductant \u00a0solution. This sampling gas\u00a0\u00a0 is conducted into the gold trap after \u00a0\u00a0processing.<\/p>\n<p>Amalgamation<\/p>\n<p>During this\u00a0 process \u00a0a defined sample gas volume\u00a0 is conducted through gold trap, so \u00a0metallic mercury forms an amalgam with gold. Gold trap is heated electrically and in collection phase they are released and later transported through photometer cell by inert carrier stream of gas. In this amalgamation technique interferences of other flue gas components are avoided \u00a0since analyzer is in contact with mercury &amp; carrier gas<\/p>\n<p>Photometric measurement<\/p>\n<p>Atomic absorption spectrometry is used to measure mercury.\u00a0 Single beam photometer with Hg discharge lamp, photodiode detector, quartz cell &amp; assembly is thermo-stated.\u00a0 So \u00a0high stability measurement is ensured due to baseline correction automatically.<\/p>\n<p><a href=\"https:\/\/www.tce.co.in\/blogs\/wp-content\/uploads\/2018\/03\/2as.png\"><img loading=\"lazy\" decoding=\"async\" class=\"alignnone size-full wp-image-234\" src=\"https:\/\/www.tce.co.in\/blogs\/wp-content\/uploads\/2018\/03\/2as.png\" alt=\"2as\" width=\"808\" height=\"519\" srcset=\"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/2as.png 808w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/2as-300x193.png 300w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/2as-768x493.png 768w\" sizes=\"auto, (max-width: 808px) 100vw, 808px\" \/><\/a><\/p>\n<p><a href=\"https:\/\/www.tce.co.in\/blogs\/wp-content\/uploads\/2018\/03\/3as.png\"><img loading=\"lazy\" decoding=\"async\" class=\"alignnone size-full wp-image-235\" src=\"https:\/\/www.tce.co.in\/blogs\/wp-content\/uploads\/2018\/03\/3as.png\" alt=\"3as\" width=\"812\" height=\"515\" srcset=\"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/3as.png 812w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/3as-300x190.png 300w, https:\/\/www.tataconsultingengineers.com\/blogs\/wp-content\/uploads\/2018\/03\/3as-768x487.png 768w\" sizes=\"auto, (max-width: 812px) 100vw, 812px\" \/><\/a><\/p>\n<p>&nbsp;<\/p>\n<p>For Reference courtesy- Durag<\/p>\n<p>The continuous mercury monitors shall meet these following needs:<\/p>\n<ul>\n<li>The analyzers results indicate mercury emission and healthiness of\u00a0 \u00a0Air pollution control devices (APCD).<\/li>\n<li>The analyzers shall distinguish the various chemical form of mercury<\/li>\n<li>The analyzer result can be used to control feed rate \u00a0of the process responsible for mercury \u00a0emission<\/li>\n<li>The analyzers results can be used to check and ensure compliance to regulatory norms<\/li>\n<\/ul>\n<p>India has already revised to more stringent emissions norms to embark as the road map of improving energy efficiency and reduce emissions. However, it is imperative that following mercury control strategies to be taken in current scenario in Indian context to improve &amp; reduce emissions.<\/p>\n<p>The broad control strategies for controlling mercury emissions<\/p>\n<ul>\n<li>To improve plant efficiency by modernization of plant equipment and coal treatment technologies.<\/li>\n<li>To improve air pollution Equipment like ESP, FGD &amp; SCR.<\/li>\n<li>To install dedicated mercury removal technologies like sorbent injection &amp; multipollutant technologies.<\/li>\n<\/ul>\n<p><b>Conclusion <\/b><\/p>\n<p>As<b> <\/b>could be\u00a0\u00a0 seen, both offline\u00a0\u00a0 and online measurement techniques are available for mercury measurement &amp; monitoring. Application\u00a0\u00a0 for offline and online system would depend upon the extent of mercury emission expected from particular industry, severity of its impact on environmental and prevailing environmental regulations.<\/p>\n","protected":false},"excerpt":{"rendered":"<p>The recent revision in environmental norms issued by MOEF made it mandatory for thermal power plants and process industries to measure mercury emission in air .Hence it is impervitive that proper understanding of mercury&#46;&#46;&#46;<\/p>\n","protected":false},"author":28,"featured_media":743,"comment_status":"open","ping_status":"open","sticky":false,"template":"","format":"standard","meta":{"_acf_changed":false,"footnotes":""},"categories":[2],"tags":[],"ppma_author":[89],"class_list":["post-232","post","type-post","status-publish","format-standard","has-post-thumbnail","hentry","category-technical-papers"],"acf":[],"authors":[{"term_id":89,"user_id":28,"is_guest":0,"slug":"jayprakash","display_name":"K Jayprakash","avatar_url":"https:\/\/secure.gravatar.com\/avatar\/99bdac0ab5b3afe9bcfe57e761b730d07674a67dcb4b6aea6be8ffb408d9a18f?s=96&d=mm&r=g","first_name":"K","last_name":"Jayprakash","user_url":"","description":""}],"_links":{"self":[{"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/posts\/232","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/posts"}],"about":[{"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/users\/28"}],"replies":[{"embeddable":true,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/comments?post=232"}],"version-history":[{"count":2,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/posts\/232\/revisions"}],"predecessor-version":[{"id":742,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/posts\/232\/revisions\/742"}],"wp:featuredmedia":[{"embeddable":true,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/media\/743"}],"wp:attachment":[{"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/media?parent=232"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/categories?post=232"},{"taxonomy":"post_tag","embeddable":true,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/tags?post=232"},{"taxonomy":"author","embeddable":true,"href":"https:\/\/www.tataconsultingengineers.com\/blogs\/wp-json\/wp\/v2\/ppma_author?post=232"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}