石油泄漏-原位修复
地下水石油污染的原位修复技术

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水污染 原位 修 复技术 的 国内外研 究热 点。
关键 词 : 下水 ; 地 石油 烃 ; 原位 修复
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微生物在环境修复中的应用

微生物在环境修复中的应用微生物在环境修复中起着重要的作用。
它们可以通过降解和转化污染物质来改善环境质量。
此外,微生物也可以作为生物控制的一种手段来清理环境污染。
本文将从微生物修复的原理、方法和应用案例三个方面来详细介绍微生物在环境修复中的应用。
第一部分:微生物修复的原理微生物修复是利用微生物的生理代谢和生态作用来降解和转化环境中的污染物质。
微生物在修复过程中主要通过生物降解、生物转化和生物吸附等途径来达到修复的效果。
1. 生物降解微生物通过分泌特定的酶来降解有机污染物质。
酶可以将有机化合物分解成更简单的物质,如二氧化碳、水和无机盐等。
这个过程可以有效地减少环境中有机污染物质的浓度,从而改善环境质量。
2. 生物转化微生物可以将某些污染物质转化成无毒或低毒的物质。
例如,一些细菌可以将重金属污染物质转化成相对无毒的形态,从而减轻对环境的危害。
3. 生物吸附微生物表面的菌丝可以通过物理或化学作用与污染物质之间形成吸附作用。
微生物的吸附作用可以将污染物质从环境中吸附出来,从而达到修复环境的目的。
第二部分:微生物修复的方法微生物修复可以采用不同的方法来实施,具体方法选择的依据包括修复对象、环境条件、微生物特性等因素。
以下是一些常见的微生物修复方法:1. 原位修复法原位修复法是指直接在受污染的土壤或水体中添加适当的微生物来修复环境。
这种方法操作简单,成本较低,适用于一些对环境要求不高的修复工程。
2. 生物固相法生物固相法是将适宜的微生物和修复介质混合,制成固态生物修复剂,然后将修复剂添加到受污染区域。
修复剂中的微生物可以通过代谢活动和生态作用来修复环境。
这种方法适用于一些受污染区域土壤较深的修复工程。
3. 土壤堆肥法土壤堆肥法是指将受污染的土壤与适宜的堆肥材料混合,在适宜的温度和湿度条件下进行堆肥处理。
在堆肥的过程中,微生物可以通过分解和转化来降解污染物质,从而达到修复土壤的目的。
第三部分:微生物修复的应用案例微生物修复在实际工程中得到了广泛的应用。
原油输送管道泄露不停产补焊技术

原油输送管道泄露不停产补焊技术摘要:油田地面建设,油井与计量站FLOWLINE、计量站与联合站TRUNKLINE、联合站与处理装置之间的PIPELINE,具有生产连续性的特点。
如果发生泄露,必须及时堵漏,否则不仅浪费能源、污染环境,还影响到输油管道的正常运行、被迫停产,甚至造成火灾、爆炸等灾难性事故。
因此,在原油不停输的状态下对输油管道进行带压补漏是一门科学性强、要求极高的技术工作。
本文提出的补焊技术改变了传统意义上的停工后修补的方法,在线带压焊接技术补漏,不仅能达到补漏的效果,还能够降低经济损失、降低环境污染。
因此,研究在线带压焊接补漏技术尤为重要。
本文结合国外两起输油管道不停输焊接补漏技术,在这里探讨两种输油管道带压不停输状态下的焊接补漏技术。
关键词:原油输送管道泄露带压不停输焊接补漏技术油田地面建设中,油井与计量站FLOWLINE、计量站与联合站TRUNKLINE、联合站与处理装置之间的PIPELINE,具有生产连续性的特点。
如果发生泄露,必须及时堵漏,否则不仅浪费能源、污染环境,还影响到输油管道的正常运行、被迫停产,甚至造成火灾、爆炸等灾难性事故。
因此,在原油不停输的状态下对输油管道进行带压补漏是一门科学性强、要求极高的技术工作。
1.管道泄漏点焊接补漏的处理原则油井输油管道内的介质大多是高温高压、易燃易爆、有毒有害的原油,在不影响正常生产,恢复管道正常工作状态下,需要选择合理的施工堵漏方法,同时在确保安全的前提下,必须确保管道补漏的焊接质量符合标准。
为了解决在输油过程中焊接可能出现的技术问题,焊接过程应当按照编制的焊接工艺规程严格执行,管道补漏位置在现场安装焊接之后应在图纸上标注编号和准确位置,专业质量工程师对焊缝外观进行检查,对焊接角缝按照相关规范进行无损检测(磁粉MT或着色PT),确保补焊焊缝的质量。
1.管道泄漏点补焊技术经过本文作者在工作实践中的实际操作和经验总结,根据泄漏点的状况补焊技术有如下两种补焊方法。
石油污染区域的微生物修复技术及其应用

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油污染地下水原位生物修复试验研究

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生物修复技术

生物修复技术作为一项有效的环保处理技术被应用始于上世纪70年代初。
由于其具有设备简单、操作方便、经济可靠的特点,生物修复技术在全球范围内得到了迅猛的发展并被广泛应用于石油、化工、制药、矿山等行业的污染处理,成为土壤和地下水污染处理的首选技术。
作为一种新兴的环保技术,生物修复技术具有广泛的市场发展前景。
举例来说,在美国大约有750000个各种地下储罐,一半以上为石油或汽油灌,其中有超过300000个存在泄漏现象,并以每年30000左右的速度递增。
生物修复技术被证明是目前处理此类污染的最经济和有效的环保技术。
关于生物修复技术在处理含油泥沙(主要产生于油田、炼油厂和石油泄漏)的应用,国外进行了大量的研究和实践。
逐渐形成了一套较为成熟和可靠的工艺,并取得了不错的处理效果。
总的来讲,这些工艺可分为异位生物修复和原位生物修复两种。
其中异位生物修复主要包括composting(堆肥)和landfarming工艺,而原位生物修复主要包括Bioventing(生物通风)和soil vapor extraction (土壤气抽吸)工艺。
作为一项较为复杂的环保技术,生物修复牵涉环保、生物、水文、地质等多个学科。
因此,影响生物修复处理效果的因素也很多,大致包括生物种类及活性、污染物种类及浓度、土壤条件(土质、湿度、pH等)、营养成分、充氧状态以及温度等。
所以,一个有效的工程方案在选择合适的工艺的基础上,还必须监测和控制适当的影响因素,才能达到最佳的处理效果。
影响因素的参数确定和优化必须采用试验与实践相结合的方法来获得。
一、异位生物修复工艺1、Composting(堆肥)堆肥工艺就是将污染的土壤与一定量的填料混合后垒成土堆,土壤中的微生物在适当的条件下进行新陈代谢的同时将污染物降解并去除。
填料的作用是改善土壤结构,提高空隙率,增加充氧效果,并提供适合微生物生长的温床。
填料主要有稻草、木屑、鸡粪、牛粪、或活性污泥等。
添加比例应视土壤结构和污染物的种类和浓度而定,通常为5%~40%不等。
石油污染修复技术及案例分析

石油污染修复技术及案例分析石油污染是当今世界所面临的一个严重环境问题。
由于石油及其衍生品的广泛使用,石油泄漏的事故时有发生,不仅给自然环境带来巨大的破坏,同时也对人类的健康和生存环境构成威胁。
为了解决石油污染所带来的问题,许多石油污染修复技术不断涌现并得到了广泛的应用。
本文将探讨一些主要的石油污染修复技术及其相关案例分析。
一、物理方法物理方法是石油污染修复的常见手段之一。
该方法通过物理手段将污染物与底泥或水分离,从而实现石油污染的修复。
物理方法包括吸附、分散、机械分离和气泡浮选等。
吸附法是常用的物理方法之一,利用吸附剂将石油污染物从水或土壤中吸附出来。
例如,使用活性炭、沸石和生物质炭等材料进行吸附可以有效去除水中的石油污染物。
分散法是通过添加分散剂将石油污染物分散成微小颗粒,使其更容易与水分离。
这种方法常用于水体中的石油污染修复。
机械分离法是通过使用机械设备将石油污染物与水或土壤分离。
例如,使用离心机可以将水中的石油分离出来。
气泡浮选法是通过注入气泡来促使污染物浮起。
这种方法广泛用于处理含有大量石油的水体。
案例分析:2005年,美国墨西哥湾发生了历史上最严重的石油泄漏事故之一——BP公司的地平线号石油钻井平台爆炸。
这起事故导致了大量的石油泄漏,对海洋生态系统产生了巨大影响。
为了修复石油污染,当时采取了物理方法中的气泡浮选法。
利用气泡浮选法,石油污染物可以从水中分离出来,并最终被收集起来。
这一修复技术被采用后,效果显著地减少了石油对海洋环境的破坏,并有效保护了世界上最重要的生态系统之一。
二、化学方法化学方法是另一种常用的石油污染修复技术。
该方法通过添加化学品改变石油污染物的性质,并使其变得更容易移除。
化学方法包括氧化、还原、酸洗和中和等。
氧化法是利用氧化剂将污染物氧化成较易分离的物质,从而实现污染物的修复。
例如,使用过氧化氢、高锰酸钾等氧化剂可以对石油污染物进行有效分解。
还原法是通过添加还原剂还原石油污染物,使其变成不溶于水的物质。
石油烃污染土壤微生物修复技术、菌剂的筛选研制及案例分析

为混合颗粒状粉剂,具有调理土壤环境,提高土壤渗透性、增加氧气传输 等作用,同时还具有很好的持水能力,有利于微生物生长,提高污染物降 解率。
油泥生物处理调质营养素
为白色粉剂,能有效改善土壤质地,为微生物提供营养物质,促进微生物 快速繁殖,增强降解活性,提高污染物降解速度。
六、微生物菌剂的生产
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40
30
20
10
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示范现场土壤中石油烃含量的变化
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修复后
五、石油污染土壤微生物修复技术
2、异位修复技术---堆体技术
根据多种生物堆体的生物学过程特性, 将其与微生物包埋/脱附增溶(IMT/SER)等强化工艺 相组合,建立了不同类型的生物堆体强化修复系统,并获得了完整的工艺参数。
土壤中主要石油污染物残留量测试 (GC-FID、UV、IR、重量法) 土壤中微生物群落变化 (PCR、DGGE); 修复植物生物量变化。
CK F-7 FL-7 FH-7 F-24 FL-24 FH-24
FH-24 FL-24 F-24 FH-7 FL-7 F-7
修复后微生物群落谱带条数 增加了3-4倍
溶
(Rhodococcus erythropolis);25%铜绿假单孢杆菌 (Pseudomonas aeruginosa);25% acinetobacter)。
构建适宜反应的微环境
促进污染物的脱附传质
企业标准
《石油污染土壤处理用微生物修复菌剂》 (Q/0500DJH001-2015)
五、石油污染土壤微生物修复技术
菌剂添加量对修复效果的影响
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I N-SITU B URNING A D ECISION-MAKERÕS G UIDE TO I N-SITU B URNINGR EGULATORY A NALYSIS AND S CIENTIFIC A FFAIIRSP UBLICATOIN N UMBER4740A PRIL2005In-situ BurningA Decsion-maker’s Guide to In-situ Burning Regulatory Analysis and Scientific AffairsPUBLICATION NUMBER 4740APRIL 2005I N-SITU B URNINGA D ECISION-MAKER’S G UIDE TO I N-SITUB URNING Regulatory and Scientific Affairs DepartmentAPI PUBLICATION 4740PREPARED UNDER CONTRACT BY:J. M ICHELR ESEARCH P LANNING, I NC.C OLUMBIA, S OUTH C AROLINAANDD. S CHOLZ, S.R. W ARREN J R., AND A.H. W ALKER,S CIENTIFIC A ND E NVIRONMENTAL A SSOCIATES, I NC.C APE C HARLES, V IRGINIAPhotograph CreditsBrunswick Naval Air Station, Brunswick, MaineStephen Lehmann, Office of Response and Restoration, National Oceanic and Atmospheric Administration, Boston, MassachusettsChiltipin Creek, TexasBeau Hardegree, Center for Coastal Studies, Texas A&M University at Corpus Christi, TexasUSFWS, Ecological Services Station, Corpus Christi, TexasExxon Valdez Test Burn, Prince William Sound, AlaskaAlan A. Allen, Spiltec, Inc., Woodenville, WashingtonMosquito Bay, LouisianaJacqueline Michel, Research Planning, Inc., Columbia, South CarolinaJohn Kern, Office of Response and Restoration, National Oceanic and Atmospheric Administration, St.Petersburg, FloridaWarren Lorenz, Louisiana Oil Spill Coordination Office, Baton Rouge, LouisianaNewfoundland Offshore Burn ExperimentMerv Fingas, Environment Canada, Ottawa, Ontario, CanadaRefugio County, TexasBuzz Martin, Texas General Land Office, Austin, TexasFOREWORDAPI publications necessarily address problems of a general nature, with respect to particular circumstances, local, state, and federal laws and regulations should be reviewed.API is not undertaking to meet the duties of employers, manufacturers, or suppliers to warn and properly train and equip their employees, and others exposed, concerning health and safety risks and precautions, nor undertaking their obligations under local, state, or federal laws.Nothing contained in any API publication is to be construed as granting any right, by implication or otherwise, for the manufacture, sale or use of any method, apparatus, or product covered by letters patent. Neither should anything contained in the publication be construed as insuring anyone against liability for infringement of letters patent.API publications may be used by anyone desiring to do so. Every effort has been made by the Institute to assure the accuracy and reliability of the data contained in them; however, the Institute makes no representation, warranty, or guarantee in connection with this publication and hereby expressly disclaims any liability or responsibility for loss or damage resulting from its use or for the violationAll rights reserved. No part of this work may be reproduced, stored in a retrieval system,or transmitted by any means, electronic, mechanical, photocopying, recording, orotherwise, without prior written permission from the publisher. Contact the Publisher,API Publishing Services, 1220 L Street, N.W., Washington, D.C. 20005.Copyright © 2005 American Petroleum InstituteTABLE OF CONTENTSPhotograph Credits (ii)Foreword (iii)Overview (viii)Section I. Introduction (1)Purpose of This Booklet (1)Section II. Oil Chemistry Review (4)What is Oil? (4)Behavior and Weathering Effects (5)How Does Burning Change the Oil? (8)Section III. In-situ Burning (9)What is It? (9)Ignition Sources (9)How is In-situ Burning Conducted? (10)On Water (10)Oil Thickness Requirements (10)Equipment Requirements (11)Operational Guidelines (11)Health and Safety (12)On Land (12)Oil Thickness Requirements (13)Equipment Requirements (13)Operational Guidelines (13)Health and Safety (14)Why You Use In-situ Burning? (14)How Does Weathering of Oil Affect Potential ISB Issues? (15)Section IV. When to Consider In-situ Burning (16)When to Consider In-situ Burning on Water (16)What are the Optimal Site Conditions For Considering Use Of In-situ Burning on Water? (18)When to Consider In-situ Burning on Land (20)What Are The Optimal Site Conditions For Considering Use Of In-situ Burning On Land? (21)Additional Considerations (23)Impacts to Plants from the High Temperatures Present During In-situ Burning (23)Burning in High Organic Soils (24)Potential Effects of the Fire on Overhead or Adjacent Structures (24)Public Notification and Air Quality Approvals (25)Section V. Operational Issues for In-Situ Burning (25)Equipment and Experience Needed for Conducting In-situ Burning (25)On Water (26)On Land (26)Pre-burn Planning (27)Monitoring (29)Pre-burn Monitoring (29)Monitoring during the Burn (30)SMART (30)Immediate Post-burn Monitoring (31)Post-burn Data Gathering (32)Required Authority (33)Section VI. In-situ Burning Health and Safety Concerns (33)OSHA Requirements for ISB Personnel (33)ISB Safety Plans (35)Section VII. In-situ Burning Case Histories and Lessons Learned (36)Case Studies of In-situ Burning on Land (37)Case Study No. 1 Ñ Refugio County, Texas (37)Case Study No. 2 Ñ Brunswick Naval Air Station, Brunswick, Maine (38)Case Study No. 3 Ñ Chiltipin Creek, Texas (39)Case Study No. 4 Ñ Mosquito Bay, Louisiana (40)Case Studies of In-situ Burning on Water (41)Case Study No. 5ÑExxon Valdez Test Burn, Prince William Sound, Alaska (42)Case Study No. 6 Ð Newfoundland Offshore Burn Experiment,Newfoundland, Canada (42)Lessons Learned from Prescribed Burning (43)Lessons Learned from ISB on Land (44)Future Efforts (45)On Land (45)On Water (46)List of Acronyms (48)Generic ISB Checklist for Oil Spill Response (50)References Cited & Further Reading (54)List of Contacts for Additional Information (58)TABLE OF CONTENTS, CONT.Acknowledgements (59)LIST OF FIGURESFigure 1. Crude Oil Composition (4)Figure 2. Generic Fractional Distillation in the Crude Oil Refining Process (6)Figure 3. Oil combustion by-products (8)Figure 4. An example of a hand-held igniter. [Image from FOSS Environmental at] (9)Figure 5. A Helitorch (9)Figure 6. Typical minimum oil slick thickness range (2 Ð 5 mm) required for ignition (10)a. Steel construction boom (11)b. Fire-resistant fabric boom (11)c. Water cooling system boom (11)Figure 7. Oil collection on water (11)Figure 8. Burn residue recovery on water and on land (12)Figure 9. Example of firebreaks (13)Figure 10. Oil in Ice Interactions (17)Figure 11. In-situ Burn Pre-approval Status for the Coastal States of the U.S (34)Figure 12. Example of PM-10 inhalation (35)Figure 13. Refugio County, TX burn (37)Figure 14. Refugio County, TX after the burn (37)Figure 15. Oil/residue re-maining after the burn, Refugio County, TX (37)Figure 16. Brunswick Naval Air Station burn (38)Figure 17. The site of the Brunswick Naval Air Station Burn, 4 to 5 months later (38)Figure 18. The Mosquito Bay, LA burn (39)Figure 19. Chiltipin Creek 2 years after the initial burn (39)Figure 20. The Exxon Valdez Test burn. (Figure not available.) (40)Figure 21. The Mosquito Bay, LA burn, 13 months later (41)Figure 22. Images from the NOBE experimental offshore burn (43)LIST OF TABLESTable 1.Equipment that might be needed for in-situ burning operationson land and on water (25)OVERVIEW·The American Petroleum Institute (API) commissioned the preparation of two booklets to help bridge the gaps in the understanding of in-situ burning (ISB) use, effectiveness, and effects.·This booklet (second of two) focuses on the operational ISB considerations and issues associated with in-situ burning both on land and on water.·This series was developed as a training tool or planning tool for in-situ burning. It is NOT an operations manual.·Crude oil is a complex mixture of thousands of different compounds, composed primarily of carbon, hydrogen, sulfur, nitrogen, and oxygen. Hydrocarbons (composed solely of carbon and hydrogen atoms in various combinations) are the most abundant compounds found in crude oils.·In-situ burning involves controlled burning of oil that has spilled from a vessel or a facility, including pipelines.·For an in-situ burn on water to ignite and sustain, the spilled oil must be approximately 1/10 of an inch or 2Ð3 millimeters in thicknessÑso containment in some form is necessary to limit spreading.·On water, spilled oil is contained within a boom or naturally, such as in ice, and ignited using an ignition source. On land, the oil may need to be contained by physical means (such as dikes), but the spilled oil will collect in natural depressions or low-lying areas where it can be contained and ignited.·When conducted properly, in-situ burning significantly reduces the amount of spilled oil (on the water or on land surface), thereby, preventing that oil from remaining in the environment or moving and affecting other resources and habitats.·In-situ burning offers a practical method to remove large quantities of oil from the land or water surface very quickly, however there are many limiting factors that should be taken into account before a burn is conducted. Physical limitations such as wind speed, wave height, thickness of the oil, oil type, how weathered the oil is, and how emulsified the oil is can limit the feasibility of ISB. Other factors to consider are human exposure to smoke, monitoring requirements, accessibility to the impacted site, and recovery of burned/unburned product and residue.·As oil weathers, it loses its more volatile components. Emulsification may also occur when water mixes with the oil. Either of these processes make it more difficult to ignite the oil as well as sustain the burn. Optimal oil conditions for burning are less than 30% loss by evaporation and less than 25% water content.·Equipment needed to conduct in-situ burning may consist of:·Ignition systems Ð Helitorch component system, gelled fuel, hand held igniter·Fire Booms Ð fabric booms, metal booms, air bubble and water spray systems, and other boom concepts·Firefighting/control equipment· A burn plan will be required. This plan should address human health and safety issues, burn methods, monitoring plans, termination conditions, and post-burn cleanup and restoration.Attempts should be made to remove all remaining burn residue from the environment.·Monitoring an in-situ burn is essential for success and learning more about its effectiveness and effects. Monitoring can include air quality measures as well as maintaining a constant watch on the fire and smoke plume, condition of the boom, and the speed and positions of the towing vessels, if in open water.·In the United States, the Special Monitoring of Applied Response Technologies (SMART) was developed to provide monitoring guidance for the collection and reporting of real-timeinformation on in-situ burning and dispersant use. SMART allows responders to effectively determine potential human health exposures during a burn so that impacts to the public are minimized or eliminated. SMART allows decision-makers to determine when to stop a burn to ensure limited population impacts. SMART is not intended to determine worker health and safety exposure limits.·In the United States, before an in-situ burn can take place (on land or on water), approval must be received from the appropriate state and federal agencies. The approval process varies from state to state or region to region. In some areas of the United States, regional planning efforts have developed pre-approval zones for in-situ burning.·Human health concerns (for both responders and the public) are addressed in monitoring plans.Responders are equipped with protective clothing and masks, as needed. The primary concern for public safety is that of air quality.·The smoke from a burn contains particles that have been found to be harmful to humans. The smoke plume reaching receptor populations should not exceed the average federal and/or state air quality standards in public areas; otherwise the burn should not be allowed or should be terminated.·Also included in the booklet are case studies from various locations with different environments, oil types, and situations. Lessons learned have been developed from theseresponses, which highlight advantages and disadvantages of in-situ burning.Section I.Introductionou are in the midst of a large oil spill and itÕs your first month on the job. Approximately 20,000 gallons of a medium-weight crude oil has been discharged into the environment. Earlier you were asked by the Unified Command (UC) to identify options to remove this oil that will also minimize the potential impacts to the environment (see boxes on pages 2 and 3). Based on the circumstances, you recommended that burning the oil in place, in-situ burning (ISB), would provide the greatest value in terms of removing the threat of liquid oil to resources at risk in and on the ground and water.Now, the On-scene Coordinator (OSC) needs additional information. You have been asked to provide more information on in-situ burning including the operational issues and concerns associated with conducting an ISB, worker and public health issues, and monitoring. Your research will help the OSC verify the appropriateness of this removal method for the incident-specific spill conditions and determine if the requirements for an in-situ burn are achievable within the recommended window of opportunity.As always, the OSC wants the information as soon as possible. You have had basic oil spill response training, and you have heard of ISB, but this is the first time you have been involved in an ISB response. During your training, you remember that there were several guidance documents that have been developed to assist responders in understanding the concept of ISB. Purpose of This BookletThis scenario is fictitious but the circumstances are possible. ISB is a response option that has been used less frequently than countermeasures like booms and skimmers or contaminated soil removal. Consequently, familiarity with the pros and cons of this option is limited. There are ISB ÒexpertsÓ in the United States and internationally, but the intentional practice of this response tool remains relatively limited for both on water and on land situations.This booklet is the second in series that was developed as a reference document for oil spill response decision-makers. It provides the reader with a comprehensive, concise, yet clear summary of the operational requirements and limitations for ISB, and allows decision-makers to better understand the function of in-situburning and the tradeoffs facing decision-makers in usingAn In-situ Burn. Unified Command (UC) is responsible for all aspects of the response, including developing incident objectives and managing all incident o p e r a t i o n s(refer to information box on Page 3 for more information).Actual UC makeup for a specific incident will be determined on a case-by-case basis taking into account:1.specifics of the incident;2.determinations outlined inexisting response plans; or 3.decisions reached duringthe initial meeting of theUC.The makeup of the UC may change as an incident progres-ses, in order to account for changes in the situation. The UC is a team effort, but to be effective, the number of personnel should be kept as small as possible.Ythis technology when responding to an oil spill on land or onwater.The first booklet, ÒThe Fate of Burned OilÓ (API Publication No.4735), was prepared to provide an accurate summary of the fateand effects of burned oil on water and on land, as well as in the air.Throughout both booklets, the first time a new technical term isused, it will appear in an ALL CAPS format; this signifies that amore detailed explanation or definition is present in the right or leftmargin near where the word(s) is first used within the main text.For More Information…The American Petroleum Institute commissioned the development of the booklet, ÒFate of Spilled Oil in Marine Waters: Where Does it Go? What Does It Do? How Do Dispersants Affect it? An Information Booklet for Decision-makersÓ (API Publ. 4691).This booklet provides a more detailed summary on oil chemistry and is recommended reading. This booklet is available from API Publications at .A Team Effort…The Incident Command System, Unified Command, Incident Commanders,On-scene Coordinators, and Responsible PartiesDuring a response to an oil spill, in many cases there are several federal agencies as well as state and local agencies from the affected area that become involved with the response efforts. The Incident Command System (ICS) is a response tool that has been almost universally adopted by state and federal agencies as the method of rapidly organizing a coordinated response to an incident, such as an oil spill. If all agencies involved in the incident are using the same categories to address critical needs to manage their agency, the cooperative effort of all the agencies will increase dramatically.The Unified Command structure is a necessary tool within the ICS for managing multi-jurisdictional responses to oil spills or hazardous substance releases. When planned for and practiced, ICS/UC is viewed as the most effective response management system to address discharges or releases. The ICS/UC is an integrated and flexible structure that emphasizes cooperation and coordination in local, state, and federal responses to complex multi-jurisdictional, multi-agency incidents.Within the ICS/UC, there is a requirement for a single individual, or Incident Commander (IC) to be the final decision-maker for the efforts of the response. The UC is a structure that brings together the ÒIncident CommandersÓ of all major organizations involved (federal, state, local, and Responsible Party groups) in the incident in order to coordinate an effective response while at the same time carrying out their own jurisdictional responsibilities. These ÒIncident CommandersÓ are typically referred to as On-scene Coordinators (OSC)Ñthose individuals who have the pre-designated legal authority to make decisions for their agency during an incident, including the access and disbursement of funds to address their agencyÕs response needs. There may be Federal On-scene Coordinators (FOSCs) from EPA and the U.S. Coast Guard; the affected State(s)Õ On-scene Coordinators (SOSCs); and Local OSCs representing their local jurisdictions. The UC links the organizations responding to the incident and provides a forum for these entities to make consensus decisions. Under the UC, the various jurisdictions and/or agencies and non-government responders may blend together throughout the operation to create an integrated response team.The UC is responsible for overall management of the incident. The UC directs incident activities, including development and implementation of overall objectives and strategies, and approves ordering and releasing of resources. Members of the UC work together to develop a common set of incident objectives and strategies, share information, maximize the use of available resources, and enhance the efficiency of the individual response organizations.Unified Command speaks to the issue that all of the major players in an incident need to get together to share information, resources, and responsibility for the smooth delivery of effective service. But, as in all events, there can only be one boss, one Òshot caller,Ó directing the focus of the group, and setting the groupÕs goals. This whole system of ÒwhoÕs in commandÓ and Unified Command only works if all agencies are aware of each otherÕs primary needs.For more information on ICS and the Unified Command, access the National Response TeamÕs ÒIncident Command System/Unified Command Technical Assistance Document,Ó available from:/production/nrt/home.nsf/resources/Publications1/$File/ICS_UC_Technical_Assistance_Document.pdf.Hydrocarbons are definedas chemical compoundscomposed solely of carbonand hydrogen that come invarious lengths andstructures.Trace Metals in oil consistprimarily of Nickel, Iron,Vanadium, Copper, andArsenic.Asphaltenes and Waxesare components in the oil thatare considered relatively inertand resistant to mostweathering processes.Figure 1. Crude Oil Com-position Section II. Oil Chemistry ReviewWhat is Oil?Oil is not one Òthing;Ó it is a complex and highly variable mixture of compounds. Even oil extracted from the same well may change in component mixtures over time (Lewis and Aurand, 1997). Crude oil, the unprocessed oil that is recovered from the ground, is composed primarily of HYDROCARBONS , and to a smaller extent compounds containing TRACE METALS (Figure 1).Hydrocarbons (including ASPHALTENES and WAXES ) are the most abundant compounds in crude oils (NRC, 2003). In general,there are three groups of hydrocarbons in every oil:· Light-weight components (low molecular weight)·contain 1 Ð 10 carbon atoms in each molecule (C1 to C10);·are simple in molecular structure;· evaporate and dissolve rapidly (hours) and leave little or no residue ;· many of these components (e.g., benzene) are thought to be readily absorbed by animals through the skin or throughinhalation; and· are potentially flammable and readily inhaled by people,and so are of concern for human health and safety.· Medium-weight components (medium molecular weight)· are composed of 11 Ð 22 carbon atoms (C11 Ð C22);· are more complex molecules than light-weight;· evaporate or dissolve more slowly, over several days, with some residue remaining;· are sometimes regarded as a greater concern than the light-weight components since they persist in the environmentlonger and therefore present a longer term risk of exposure(NRC, 2003); and· are not as bioavailable as lower-weight components, so are less likely to affect animals.· Heavy-weight components (high molecular weight)· made up of 23 or more carbon atoms ( ³ C23);·undergo little to no evaporation or dissolution; and·can cause chronic (long-term) effects via smothering or coating, or as residue in the water column and sediments(NRC, or 2003).Crude oils are composed of various combinations of the three hydrocarbon categories. When comparing crude oils, the relative concentration of the larger molecular compounds within the oil affects PERSISTENCE; oils with greater concentrations of medium- and heavy-weight components will typically result in increased persistence. Oils composed primarily of the lightweight components are usually considered NON-PERSISTENT. REFINED PRODUCTS are typically composed of a narrow range of processed components, usually containing the lighter-weight components (e.g., gasoline, condensates, and diesel-like products). Low API GRAVITY oil products are primarily composed of heavy-weight components sometimes mixed with a blending agent (No. 2 fuel oil is a common blending agent) in the development of these heavy refined oils. (See Figure 2 on next page for more information on the oil refinery process.) There are also several naturally occurring crude oils that are considered low API gravity oil products (NRC, 1999).Behavior and Weathering EffectsWhen oil is spilled at sea or on land, it is subject to different transport and weathering processes (more information on weathering of oil is available from Scholz et al., 1999; NRC, 2003). Of the eight major weathering and behavior processes, the following can directly influence slick ignition and burning: Advection: Advection or drifting only occurs for spills on water.It is the process of surface slicks being transported awayfrom the site of a spill by water currents. Advection isusually a combination of residual current movement andwind-induced surface movements. Other causes ofmovement may occur from tidal currents, river outflows,and longshore currents. The advection process influencesthe location of slicks and thus determines whether the oilcan be burned from a safe distance from the spill source orfrom land where people, property or other resources can beat risk. Advection can move the oil away from land,sensitive resources, or population centers; it can also movethe oil toward these resources of concern.Persistence is a means of defining how crude and refined oil products may remain in the environment. Persistent oils may not be completely removed from an affected environment as a result of weathering proces-ses or clean-up operations. An oil that is considered Non-persistent is a refined product that w i l l b e completely removed from affected environments through natural weathering processes. They are largely composed of light-weight components. Examples in-clude gasoline, No. 2 fuel oil and diesel.Refined Products include petrochemical products de-veloped in various refinery processes, like gasoline, die-sel, bunker fuel oils, etc. For more information on the refi-nery process, see the next page.API Gravity (°API) is a scale for measuring fluid specific gravities based on an inverse relationship with specific gravity (SG). This scale was primarily de-veloped to expand the scale for specific gravity so that larger values are used. An oil with a low specific gravity (e.g., gasoline; SG = 0.73) will have a high API gravity (API = 62).API gravity = (141.5/SG at 60¼F) Ð 131.5More on Refining Oils…Crude oils contain hundreds of different types of hydrocarbons and other components mixed together. Crude oil composition can vary widely from well to well in the same region. There are often noticeable differences between crude oils that are recovered at different times from within the same well.In the refining process, oils are separated into various hydrocarbon components, also known as fractions or cuts, based on the number of carbon atoms in each molecule. By heating the crude oil and letting it vaporize, the distillation process (also known as fractional distillation) allows the collection and retrieval of the different hydrocarbon molecules based on their vaporization temperatures.Newer distillation techniques (catalytic cracking) allow a refinery to process the crude oils into the various fractions, but it also allows the breaking of longer chains into shorter ones. This technique allows a refinery to produce a specific product (e.g., gasoline versus diesel fuel), based on demand for the product. The oil remaining after distillation is called the residual or residuum. Refineries must treat the fractions that they produce to remove impurities. Then, using the various fractions collected, they often combine the processed and unprocessed crude oils to create the desired product. For example, the combination of residual oils and diesel fuel are often used to create Number 6 fuel oil for power plants or bunker fuels.Figure 2. Generic Fractional Distillation in the Crude Oil Refining Process.。