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Open Cell Monitoring, a Follow-up After Reformulation

机译:开放式电池监测,重新制定后的后续行动

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A paper entitled "Spray Polyurethane Foam Monitoring and Re-Occupancy of High Pressure Open Cell Applications to New Residential Constructions" was presented at the 2014 CPI Conference in Dallas, Texas where industrial hygiene air monitoring was conducted during the application of open cell spray polyurethane foam (SPF) in residential homes. The results of the study indicated residual amine catalyst was found 24 hours after application at concentrations above any recommended occupational exposure limit (OEL) for the catalyst. In a follow-up study presented in this paper, the open cell formulation was modified to replace the emissive catalyst with a non-emissive or reactive catalyst. Components measured during application included the new non-emissive catalyst, MDI and flame retardant. Additional monitoring for MDI, flame retardant, and amine catalyst was also conducted during trimming of the overspray foam (two hours after application) and twenty four hours after application in the homes. Validated air sampling and analytical methods were followed for these studies. In the previous paper, the amine catalyst results were verified through work at the BASF Research and Training Center in Houston, TX under controlled conditions during the trimming of freshly sprayed foam as well as foam aged one day to one week following application without ventilation. The ventilation was not used to simulate worst case scenario and ensure that any emission was captured by our monitoring method. BDMAEE (Bis-(2-Dimethylaminoethyl) ether) catalyst concentrations exceeded recommended OELs during trimming activities in the absence of mechanical ventilation. Though it is industry best practice for workers to consider a combination of engineering controls including, but not limited to, mechanical ventilation, the previous study was designed as a worst-case scenario therefore, under controlled study environment, mechanical ventilation was omitted. Following the controlled laboratory study, the SPF system was reformulated using non-emissive catalysts. In this follow up study, after reformulation of the catalyst package, the half-pound open cell SPF formulation, was applied at the BASF Research and Training Center in Houston, in a large warehouse and in a residential home under construction. To simulate worst-case scenario and to ensure capture of emissions no mechanical ventilation was used during the study. Natural ventilation, through open windows and doors typical of new residential construction applications, was utilized. Airborne concentrations of MDI, flame retardant, amine catalyst, and total VOCs were evaluated during and after application of SPF. At the BASF Research and Training Center, using the same study protocol of cutting and trimming of foam, resulted in the non-emissive amine catalyst concentrations below analytical detection limits. Industrial Hygiene monitoring (SPF application in a large open building) of the amine catalysts were also below detection limits for the applicator, 15 feet and 30 feet from the application. MDI and TCPP were also extremely low. Also, SPF application in a new home under construction, personal samples resulted in amine catalysts below detection limits. TCPP and aldehydes were also extremely low. There have been suggestions that formaldehyde may be generated during the polyurethane reaction of spray foam. The results clearly do not show this. All were at background concentrations.
机译:在2014年CPI会议上在达拉斯的2014年CPI会议上举行了“喷雾聚氨酯泡沫监测和高压开放电池应用再占用高压开放式电池应用再占用”德克萨斯州达拉斯,德克萨斯州达拉斯在德克萨斯州的开放式电池喷雾聚氨酯泡沫中进行了工业卫生空气监测(SPF)在住宅家中。研究表明,在催化剂的任何推荐职业暴露极限(七)以上施用后24小时发现残留的胺催化剂。在本文提出的后续研究中,改性开放电池制剂以用非发光或反应催化剂代替发光催化剂。施用期间测量的组分包括新的非发光催化剂,MDI和阻燃剂。还在将过喷泡沫(施用后2小时)和在众所周性施用后的24小时内进行MDI,阻燃剂和胺催化剂的额外监测。遵循验证的空气抽样和分析方法进行这些研究。在前一篇文章中,胺催化剂结果通过在休斯顿的巴斯夫研究和培训中心工作,在德克萨斯州的基础上的工作,该条件下,在微喷涂的泡沫和泡沫,在没有通风的情况下施加一天的一天至一周后的泡沫。通风不用于模拟最坏情况的情况,并确保我们的监测方法捕获了任何排放。 BDMAEE(二甲基氨基乙基)醚)催化剂浓度在没有机械通气的情况下在修剪活动期间超过推荐的卷曲。虽然工人的行业最佳实践,以考虑工程控制的组合,包括但不限于机械通风,之前的研究被设计为最糟糕的情况,因此,在受控的研究环境下,省略了机械通风。在受控实验室研究之后,使用非发光催化剂重新重整SPF系统。在这种后续研究中,在催化剂包重构后,半磅开放式电池SPF制剂在休斯顿的巴斯夫研究和培训中心应用,在一个大型仓库和居住家庭建设中。为了模拟最坏情况的情况,并确保在研究期间没有使用机械通风的排放捕获。利用自然通风,通过开放的窗户和典型的新住宅施工应用。在施用SPF期间和之后,评估MDI,阻燃剂,胺催化剂和总VOC的空中浓度。在巴斯夫研究和培训中心,采用相同的切割协议和泡沫的修剪方案,导致非发光胺催化剂浓度低于分析检测限。胺催化剂的工业卫生监测(在大型开放式建筑物中的SPF施用)也低于涂抹器,15英尺和30英尺的检测限。 MDI和TCPP也非常低。此外,SPF应用在施工的新家中,个人样品导致胺催化剂低于检测限。 TCPP和醛也极低。已经建议可以在喷雾泡沫的聚氨酯反应过程中产生甲醛。结果显然不显示这一点。一切都在背景浓度。

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