SMART Protocol Using Polarized Infrared Cameras

T. Nedwed, Doug Mitchell, W. Konkel, Tom Coolbaugh
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Abstract

Tier II/III SMART protocol for dispersant use requires placing fluorometers in the water and towing them under a slick by boat. To protect the health of SMART teams, boats typically remain at least 2 miles away from slicks during aerial dispersant treatment. After the spray completes, the SMART boats transit into oil slicks. The time between completion of spray and initiation of SMART monitoring can be > 30 minutes. In 30 minutes, dispersed oil plumes will significantly dilute making them difficult to detect based on fluorescence. Further, we identified a separate issue. That is, oil fluoresces primarily because of the aromatic constituents in the oil and many of the aromatics in oil are at least somewhat volatile and water soluble. Modeling found that these aromatics leach from the oil prior to the application of dispersant. So, even if fluorometers were immediately underneath dispersing oils slicks, the loss of aromatics from the oil challenges SMART. The combination of aromatic leaching and rapid plume dilution limits the ability of the Tier II/III SMART protocol to identify fluorescence signals above the recommended five times background. This means that effectively dispersed oil slicks might not be accurately characterized. What is needed is a monitoring technique that can be applied rapidly and targets some other characteristic of the oil. Polarized infrared (IR) cameras can measure both the thermal differences between slicks and water and the difference in emissivity when IR energy is emitted by sheens / slicks relative to water. These cameras can be easily flown on dispersant spray/support planes. They can be used to image oil slicks before, during, and after dispersant spray operations. Effectively dispersed oil slicks will have a significant change in their thermal signature and IR emissivity as the oil transfers from the water surface into the water column. Polarized infrared cameras can be an effective tool for monitoring dispersant operations. They can be deployed continually during slick dispersion providing a longitudinal and synoptic record of the dispersion process. In this paper, we describe modeling to estimate the water-column concentrations of aromatic hydrocarbons (both mono and polycyclic) from plumes after applying dispersants to an oil slick. In addition, we describe testing of a polarized IR camera at the OHMSETT tank during dispersant testing. We use the modeling to identify the need for modifying SMART and the OHMSETT testing to show that polarized IR cameras can meet this need.
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使用偏振红外摄像机的SMART协议
关于分散剂使用的第II/III级SMART协议要求将荧光计放置在水中并用船将其拖到浮油下。为了保护SMART小组的健康,在空中分散剂处理期间,船只通常与浮油保持至少2英里的距离。喷洒完成后,SMART船进入浮油区。从喷淋完成到SMART监控启动的时间可以> 30分钟。在30分钟内,分散的油羽将显著稀释,使它们难以通过荧光检测到。此外,我们还发现了一个单独的问题。也就是说,油发出荧光主要是因为油中的芳香族成分油中的许多芳香族成分至少在一定程度上是挥发性和水溶性的。建模发现,这些芳烃在使用分散剂之前从油中浸出。因此,即使荧光计立即在分散的浮油下面,石油中芳烃的损失也对SMART提出了挑战。芳香浸出和快速羽流稀释的结合限制了Tier II/III SMART协议识别高于推荐5倍背景的荧光信号的能力。这意味着有效分散的浮油可能无法准确表征。我们需要的是一种可以快速应用的监测技术,并针对石油的某些其他特性。偏振红外(IR)相机既可以测量油油和水之间的热差异,也可以测量油油/油油相对于水发出的红外能量时的发射率差异。这些相机可以很容易地在分散剂喷雾/支援飞机上飞行。它们可用于在分散剂喷洒作业之前、期间和之后对浮油进行成像。当石油从水面转移到水柱中时,有效分散的浮油在其热特征和红外发射率方面会发生显著变化。偏振红外摄像机是监测分散剂操作的有效工具。它们可以在光滑扩散过程中连续部署,提供扩散过程的纵向和天气记录。在本文中,我们描述了在将分散剂应用于浮油后,从羽流中估计芳香烃(单环和多环)水柱浓度的模型。此外,我们描述了在分散剂测试期间在OHMSETT储罐上偏振红外相机的测试。我们使用建模来确定修改SMART的必要性,并通过OHMSETT测试来证明偏振红外相机可以满足这一需求。
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