Oil Spill Response Capability Building in China and Her Road Map

2014 ◽  
Vol 2014 (1) ◽  
pp. 837-846
Author(s):  
Jin Xiang Cheng ◽  
Chun Chang Zhang ◽  
Hong Lei Xu ◽  
Shou Dong Wang

ABSTRACT In recent decades, China's strong economic development has brought higher risk of oil spill at sea from ships, oil exploration and land. Accordingly, China government has enacted some new laws and policies such as the compulsory requirements on certain ships calling Chinese ports enter into a preparedness and response contract with a pre-approved response organization, up to now, there are already 137 private oil spill response organizations along the coastline. Also, the port operators are required to invest on oil spill response equipments depending on the result of risk assessment. At the same time, the central government has invested more 20 stockpiles along the sea port and Yangzi River. Nowadays, the amount of clean-up equipments has reached to a historical high level, and the total investment in recent three years is near ten times more than those ten years ago. Therefore, scientific evaluation of the risk and its spatial distribution of oil spill, and development of the reasonable and effective oil spill response capability planning, are the major demands for marine environmental risk management in China. To solve the issues above, a model with oil spill risk evaluation and multi-objective response resources layout is proposed for multi–sources risk. Hopefully, the model will be used to develop the national plan for National Contingency Plan for oil spill capability building in China.

1995 ◽  
Vol 1995 (1) ◽  
pp. 513-522 ◽  
Author(s):  
Carlos Villoria ◽  
Elia Gomez ◽  
Nelson García Tavel

ABSTRACT In November 1993, the first drill of the Venezuelan national oil spill contingency plan (VNCP) was carried out to evaluate both the response capability of the plan to cope with an emergency and the effectiveness of the regional response organization to manage the given scenario. During four days of intensive work, 800 participants, evaluators, and controllers of the drill made decisions and took actions to mobilize resources and pollution countermeasure equipment for cleanup operations. To measure the effectiveness of the response actions, 23 oil spill response processes were evaluated based on flow charts or decision trees designed for each process. In summary, the drill covered all areas related to response actions in the case of an oil spill (alert, notification, evaluation, decision-making, mobilization, field response, and postmortem), evaluating the ability of the VNCP to cope with a major emergency and identifying weaknesses in order to improve the response capability.


1993 ◽  
Vol 1993 (1) ◽  
pp. 39-43
Author(s):  
Sakae Shirai

ABSTRACT With the large oil spill that occurred in 1971 as an impetus, Japan's Maritime Pollution and Disaster Prevention Law was amended in 1973 and subsequently in 1976. The amendments required owners of vessels and petroleum facilities to retain designated quantities of oil boom, sorbent, dispersant, and other items to minimize impact from spills. A large oil spill caused by a ruptured crude oil storage tank in 1974 led to the enactment of additional legislation: the Petroleum Complex Disaster Prevention Law. Under this, petroleum facilities are required to maintain designated quantities of oil boom, oil boom deploying vessels, skimming boats, and the like. These legislative measures, together with voluntary efforts, have contributed to a sound buildup of the nation's oil spill response force. However, the response capability including stockpiled materials and equipment has been designed primarily to cope with incidents in closed waters such as inland seas, bays, and ports, and hence not for a oil spill in open seas as large as that from the Exxon Valdez. As one of the measures under the 1990 International Convention for Oil Spill Preparedness, Response and Cooperation, the Government of Japan has entrusted the Petroleum Association of Japan with an oil spill response capability reinforcement project to cope with a large oil spill should one occur in Japanese waters or nearby seas. Under the scheme, during the 5 year period beginning in 1991, the Petroleum Association of Japan is scheduled to build up, using subsidies from the government, stockpiles of cleanup equipment and materials and to augment the existing response capability.


1997 ◽  
Vol 1997 (1) ◽  
pp. 439-442
Author(s):  
Todd Mitchell

ABSTRACT This paper presents a discussion of oil spill equipment selection from a practical standpoint. The specification of effective oil spill equipment is often a difficult task because of the wide array of commercially produced goods available to the end user. In addition, in various countries there exists little or no framework legislation that quantifies the equipment component in practical terms. This paper attests to the usefulness of the new Canada Shipping Act guidelines for the purposes of planning the equipment requirements for a predetermined potential spill quantity. Through the elaboration of a case history, it presents the development of an integrated 2500-ton oil spill response capability. Since response organizations under the new Canada Shipping Act regime are in effect commercial ventures rather than simply oil spill cooperatives, innovative and cost-effective solutions are necessary to maintain capital costs at a minimum. Although the equipment in the case history was commissioned directly as a response to the new Canadian standards, the important planning principles can be applied to any geographical region.


1977 ◽  
Vol 1977 (1) ◽  
pp. 309-311
Author(s):  
L. A. Schultz

ABSTRACT The increased interest in, and development of, arctic petroleum resources has increased correspondingly the potential for oil spills in cold regions. A recently completed survey of cold regions oil spill mitigation technology included a cursory determination of the applicability of presently available means to the problems of detection, containment, recovery, temporary storage, and disposal of oil spilled in cold regions. For purposes of the study, cold regions were characterized by the existence of low temperatures and the presence of ice in its many forms. The evaluations were based upon the experience of the authors in conducting other cold regions laboratory and field programs, and the experiences of others in cold regions as reported in the technical literature. This survey revealed that, while a very limited degree of oil spill response capability is available for use in cold regions based upon using the techniques and equipment currently employed in warmer climates, a great deal of development work must be undertaken before a total cold regions oil spill response capability will be available. Current technology falls far short of the desired capability in all functional areas including remote sensing, containment, recovery, temporary storage, and disposal.


Oceanography ◽  
2021 ◽  
Vol 34 (1) ◽  
pp. 228-239
Author(s):  
Charles Wilson ◽  
◽  
Michael Feldman ◽  
Michael Carron ◽  
Nilde Dannreuther ◽  
...  

Following the Deepwater Horizon explosion and oil spill in 2010, the Gulf of Mexico Research Initiative (GoMRI) was established to improve society’s ability to understand, respond to, and mitigate the impacts of petroleum pollution and related stressors of the marine and coastal ecosystems. This article provides a high-level overview of the major outcomes of the scientific work undertaken by GoMRI. This initiative contributed to significant knowledge advances across the physical, chemical, geological, and biological oceanographic research fields, as well as in related technology, socioeconomics, human health, and oil spill response measures. For each of these fields, this paper outlines key advances and discoveries made by GoMRI scientists (along with a few surprises), synthesizing their efforts in order to highlight lessons learned, future research needs, remaining gaps, and suggestions for the next generation of scientists.


1999 ◽  
Vol 71 (1) ◽  
pp. 103-111 ◽  
Author(s):  
F. R. Engelhardt

Introduction: Remote sensing is useful in several modes of oil spill control, including large area surveillance, site specific monitoring and tactical assistance in emergencies. Remote sensing is able to provide essential information to enhance strategic and tactical decision-making, potentially reducing incidence of spills by providing a deterrent factor, decreasing response costs by facilitating rapid oil recovery and ultimately minimising impact. Marine oil spills can be separated into two categories of relevance to the type of remote sensing technology which might be used to detect and respond to the incident. A first category is non-accidental discharges, which can include incidental losses from vessels due to hull or equipment leaks, as well as oil discharged intentionally during deballasting and tank-cleaning activities. While these non-accidental discharges tend to be small in themselves, they are frequent and contribute much more to the overall introduction of oil to the marine environment than accidental spills, and are of increasing international regulatory concern. Accidental spills are much less frequent, but typically involves much larger releases of oil. Such oil spills are high profile events for which rapid and effective emergency response is needed to contain and recover the spilled oil. In many countries, an appropriate and effective response capability is required by law, such as demanded by the Oil Pollution Act of 1990 in the US, as well as by recent amendments to the Canada Shipping Act in Canada. There is a growing recognition that using remote sensing, especially airborne, to aid cleanup response efforts can mitigate the effects of oil on the environment, as well as reduce cleanup costs. Airborne remote sensing sensing in the support of spill response operations has a mixed level of interest by spill responders when viewed globally. In the US, for instance, airborne remote has had varying degrees of success in meeting operational expectations, and thus is not yet fully integrated into national, regional and area response plans and operations. By comparison, the record of successful use in the UK, for instance, is such that remote sensing support is contracted by the UK Coast Guard on a stand-by basis and used routinely when a significant spill occurs. As another example, airborne remote sensing technologies are now being adopted by the Australian Maritime Safety Authority to support its spill response actions. Low altitude aircraft have proven to be the most effective tactical method for obtaining information about spills and assisting in spill response. Combined with accurate oil drift computer model forecasting, these two methods were the primary strategic tools used for environmental response planning during the IXTOC-1 and Arabian Gulf spills, although less useful for guiding tactical operations (Pavia and Payton, 1983; Cekirge et al., 1992). Conversely, essential tactical support was provided by aerial remote sensing for the application of dispersants, a major spill response in the Sea Empress spill in Southwest Wales (Harris, 1997; Lunel et al., 1997). Currently, the use of imaging satellites for spill response is restricted because of limited spatial resolution, slow revisit times and often long delays in receipt of processed image data. The topic of oil spill monitoring by imaging satellites has been reviewed by Bern (1993a,b). There are significant advances being made, however, to increase resolution and coverage, as well as in the speed of image product delivery. Sensing oil on water by satellites appears best suited for routine surveillance purposes. There are synergisms in protecting the environment and property from oil spills which can be achieved by an integrated approach which draws on the remote sensing advantages of airborne and satellite imaging technology. There are many potential users of such remote sensing information, in government and private sector organisations. Government authorities use such information in surveillance, for example in the North and Baltic Seas, detecting spills when they occur and for identification of the spiller, which could be a vessel discharging illegally. Many government organisations also maintain an organised oil spill response capability, which would be supported by remote sensing information in oil spill response operations. The private sector includes the primary oil industry operating globally, and oil transporters, which carry responsibility and potential liability in the event of a spill. Other potential users are oil spill response organisations which might offer a sub-contracted remote sensing capability to their clients. Other private sector groups include the insurers for the shipping industry, who are directly and immediately interested in keeping both the costs of the response and oil spill impact damage as low as possible. The news media is a additional potential user, interested in quality graphical representation of the oil spill, as is true for any disaster event.


1995 ◽  
Vol 1995 (1) ◽  
pp. 801-805
Author(s):  
Jonathan K. Waldron

ABSTRACT The Oil Pollution Act of 1990 (OPA 90) promoted a coordinated industry and government enhancement of response resources to combat oil spills effectively in the United States. However, the United States remains vulnerable to oil spills near the borders it shares with Canada, Mexico, and various nations in the Caribbean due to legal and administrative impediments associated with cross-boundary spill response activities. This paper explores cross-boundary related issues that could hinder a response and the relationship and roles of industry and government with regard to such issues, and provides recommendations to enhance improved cooperation between government and industry to facilitate response activities. The international structure that currently exists—globally, regionally, and bilaterally—provides a basic framework that promotes cooperation between nations to respond harmoniously to spills threatening the shores of neighboring countries. However, the existing agreements and understandings only provide a basic umbrella. They require planning and implementation of details and commitment to take the specific actions required to implement these agreements and understandings fully. As a result, the enhanced private response capability that now exists in the United States may not be available in a spill involving cross-boundary operations. Neighboring nations must take action to facilitate cross-boundary activities by responders by providing responder-immunity protection similar to that provided under OPA 90 and by removing potential impediments to response activities: laws and other requirements relating to matters such as customs, immigration, and safety training.


2011 ◽  
Vol 2011 (1) ◽  
pp. abs105 ◽  
Author(s):  
Peter Velez ◽  
Hanne Greiff Johnsen ◽  
Alexis Steen ◽  
Yvette Osikilo

ABSTRACT Industrial and commercial activities in Arctic and sub-Arctic regions, including oil exploration, have increased in recent years. The 2008 circumpolar analysis by the US Geological Survey highlighted the large quantities of undiscovered oil and gas (O&G) estimated to be present. Governments of Arctic coastal states require industry to ensure a high level of environmental protection while operating in these areas. There are unique considerations which must be addressed such as: prolonged periods of darkness and daylight, cold temperatures, environmental sensitivities, indigenous peoples and their culture, distant infrastructure and remoteness, presence of seasonal/dynamic sea ice offshore, and a generally higher cost of doing business. Oil spill response (OSR) in the ice-free season can be comparable to the response in others parts of the world, with the exception of lower temperatures and extended daylight hours. The latter is a distinct advantage for OSR operations. Prevention of spills remains a top priority for industry. To address spills, if prevention is unsuccessful, the O&G industry has made significant progress over the last decades on addressing the technical challenges of operating in the Arctic. The O&G industry has also performed work to evaluate and validate OSR response measures under Arctic conditions. Oil spill response is a demanding task in any environment, but responding to spills in Arctic regions can present different challenges, especially with presence of sea ice, than to spills found in more temperate regions and opportunities exist to improve upon this existing capability. Some response techniques have been modified or specially developed for use in the Arctic. The O&G industry will undertake a joint industry research program to further address the challenges of Arctic Oil Spill Response. This paper describes the background, planning, and scope for this Joint Industry Program (JIP).


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