固定相：高聚物
規(guī)格2m*3mm，2m*4mm，2m*1/8
粒度：60-80目
型號(hào)：GDX-104，GDX-502

總烴柱

固定相：硅烷化玻璃微球

應(yīng)用：HJ 604-2017 環(huán)境空氣 總烴、甲烷和非甲烷總烴的測(cè)定 直接進(jìn)樣-氣相色譜法

浩瀚色譜（山東）應(yīng)用技術(shù)開(kāi)發(fā)有限公司對(duì)典型企業(yè)固定污染源非甲烷總烴在線(xiàn)監(jiān)測(cè)系統(tǒng)開(kāi)展比對(duì)監(jiān)測(cè),通過(guò)對(duì)比分析自動(dòng)監(jiān)測(cè)系統(tǒng)與手工方法監(jiān)測(cè)數(shù)據(jù)的相關(guān)性;通過(guò)性能指標(biāo)測(cè)試、方法比對(duì)等獲取系統(tǒng)的性能指標(biāo)、檢測(cè)結(jié)果等方面的基礎(chǔ)數(shù)據(jù)。測(cè)試結(jié)果表明實(shí)際樣品比對(duì)過(guò)程中采用不同的采樣分析儀器,監(jiān)測(cè)結(jié)果差距較大,相對(duì)誤差在1.23%～108.1%,便攜式分析儀結(jié)果相對(duì)誤差較小,實(shí)驗(yàn)室分析結(jié)果相對(duì)誤差較大。系統(tǒng)線(xiàn)性誤差與量程漂移可以滿(mǎn)足現(xiàn)階段管理要求,并根據(jù)測(cè)試結(jié)果為在線(xiàn)監(jiān)測(cè)系統(tǒng)運(yùn)行管理提出建議。


固定污染源非甲烷總烴在線(xiàn)監(jiān)測(cè)系統(tǒng) 測(cè)試譜圖：



Fixed pollution source non-methane total hydrocarbon online monitoring system
Non-methane total hydrocarbons online monitoring system for fixed pollution sources Details:

Methane column
Stationary phase: polymer
Specification 2m*3mm, 2m*4mm, 2m*1/8
Granularity: 60-80 mesh
Model: GDX-104, GDX-502


Total hydrocarbon column

Stationary phase: silanized glass microspheres

Particle size: 80-60 mesh
Specifications: 2m*4mm, 2m*3mm, 2m*1/8 (Agilent, Shimadzu)
Model: HH-NMHC-2
Application: HJ 604-2017 Ambient air Determination of total hydrocarbons, methane and non-methane total hydrocarbons Direct injection-gas chromatography

National Standard HJ/T 38-2017 Fixed Pollution Source Exhaust Gas Determination of Non-Methane Total Hydrocarbons Gas Chromatography


Haohan Chromatography (Shandong) Applied Technology Development Co., Ltd. carried out comparative monitoring of the non-methane total hydrocarbon online monitoring system of fixed pollution sources of typical enterprises, and analyzed the correlation between automatic monitoring system and manual method monitoring data; passed performance index testing and method comparison Obtain basic data such as system performance indicators and test results. The test results show that different sampling and analysis instruments are used in the actual sample comparison process, and the monitoring results have a large gap, with a relative error of 1.23% to 108.1%. The portable analyzer results have relatively small relative errors, and the laboratory analysis results have relatively large relative errors. The linear error and range drift of the system can meet the management requirements at this stage, and suggestions for the operation and management of the online monitoring system are put forward based on the test results.


Fixed pollution source non-methane total hydrocarbon online monitoring system test spectrum: