“Very low levels” of crude oil from the 1989 Exxon Valdez spill in Prince William Sound, Alaska, are a threat to the survival of herring and pink salmon that spawn in the region, according to a study released today by the US National Oceanic and Atmospheric Administration.
The study shows that embryonic salmon and herring exposed to very low levels of crude oil can develop hidden heart defects that compromise their later survival.
That means that the Exxon Valdez spill on March 24, 1989 may have had much greater impacts on spawning fish than previously recognized, according to the study published in Nature’s online journal Scientific ReportsVery low embyronic crude oil exposures cause lasting defects in salmon and herring.
“These juvenile fish on the outside look completely normal, but their hearts are not functioning properly and that translates directly into reduced swimming ability and reduced survival,” said John Incardona, a research toxicologist at NOAA Fisheries’ Northwest Fisheries Science Center (NWFSC) in Seattle. “In terms of impacts to shore-spawning fish, the oil spill likely had a much bigger footprint than anyone realized.”
Previous research has shown that crude oil disrupts the contraction of the fish heart muscle cells. Embryonic fish exposed to trace levels of crude oil grow into juveniles with abnormal hearts and reduced cardiorespiratory function.
“With this very early impact on the heart, you end up with an animal that just can’t pump blood through its body as well, which means it can’t swim as well to capture food, form schools, or migrate,” said Mark Carls, toxicologist at the Alaska Fisheries Science Center. “Crude oil is changing basic physiology, or what makes a fish a fish.”
The research builds on earlier work by the Auke Bay Laboratories, part of NOAA Fisheries’ Alaska Fisheries Science Center, which found much reduced survival of pink salmon exposed as embryos to polycyclic aromatic hydrocarbons (PAH) from crude oil.
“Our findings are changing the picture in terms of assessing the risk and the potential impacts of oil spills,” said Nat Scholz, leader of the NWFSC’s ecotoxicology program and a coauthor of the new study. “We now know the developing fish heart is exquisitely sensitive to crude oil toxicity, and that subtle changes in heart formation can have delayed but important consequences for first-year survival, which in turn determines the long-term abundance of wild fish populations.”
The Exxon Valdez spill was the largest in U.S. history, with extensive oiling of shoreline spawning habitats for Pacific herring and pink salmon, the two most important commercial fish species in Prince William Sound.
Herring larvae sampled in proximity to oil were visibly abnormal, and mortality rates were higher for pink salmon embryos at oil spill sites than unaffected regions.
The herring fishery collapsed three to four years after the spill, when the herring spawned in oiled areas reached reproductive maturity.
The paper notes that the contribution of the spill to the herring population collapse, if any, was never determined and remains controversial.
Other studies, however, tend to confirm the findings, including heart problems for fish exposed to the Gulf of Mexico Deepwater Horizon spill and even fish exposed to naturally occurring oil seeps.
The new findings suggest that the delayed effects of the spill may have been important contributors to the declines.
Scientists from the Northwest Fisheries Science Center and Alaska Fisheries Science Center temporarily exposed embryonic salmon and herring to low levels of crude oil from the North Slope of Alaska and found that both absorbed chemicals at similar concentrations in their tissues. The embryos were then transferred to clean seawater and raised as juvenile fish for seven to eight months.
Few of the exposed embryos were outwardly abnormal in any way. However, closer examination of the fish revealed subtle defects that could reduce their long-term survival.
Juvenile salmon exposed to oil grew more slowly, with those exposed to the highest concentrations growing the slowest. For salmon, early survival in the ocean is strongly influenced by juvenile growth, with smaller fish suffering higher loss to predators.
Scientists used swimming speed as a measure of cardiorespiratory performance and found that fish exposed to the highest concentrations of oil swam the slowest. Slower swimming is an indication of reduced aerobic capacity and cardiac output, and likely makes fish easier targets for predators.
Exposure to oil as embryos altered the structural development of the hearts of juvenile fish, potentially reducing their fitness and swimming ability. Poor swimming and cardiac fitness is also a factor in disease resistance.
Earlier studies on the ecosystem-scale crash of the Prince William Sound herring population several years after the Exxon Valdez spill were based on higher levels of exposure to the oil. The new study shows that that cardiac injury occurs in normal-appearing fish that survive even lower level exposures.
The scientists reviewed data on measured oil concentrations in surface water samples collected in Prince William Sound after the oil spill and during the 1989 herring spawning season. Most of the 233 samples contained less oil than was believed to be toxic to herring at the time, based on visible gross developmental abnormalities. However, nearly all of the samples contained oil at or above concentrations shown in the new study to alter heart development.
If the Exxon Valdez spill impacted heart development among a large majority of fish that were spawned in proximity to oiled shorelines, the subsequent losses of juveniles to delayed mortality would have left fewer adults to join the population. Although not direct proof, this provides a plausible explanation for the collapse of the Prince William Sound herring stock four years later, when fish spawned during the oil spill would have matured.
The study concludes that the impacts of the Exxon Valdez spill on near shore spawning populations of fish are likely to have been considerably underestimated in terms of both the geographic extent of affected habitat and the lingering toxicity of low levels of oil. The findings will likely contribute to more accurate assessments of the impacts of future oil spills, Incardona said. “Now we have a much better idea of what we should be looking for,” he said.
That means, according to the study “that the impacts of the Exxon Valdez oil spill on populations of near shore spawning fish are likely to have been considerably underestimated, in term of both the geographic extent of affected habitats and the lingering toxicity of low levels of residual oil.”
The report calls for more studies of the sensitivity of the developing fish heart since the vulnerability “also has implications for other pollution sources in marine ecosystems, including increasing maritime vessel traffic and expanding land-based urban runoff.”
Scientific studies after the Exxon Valdez spill indicated that the vast majority of species recovered following the spill and that functioning ecosystems, similar to those existing pre-spill, were established.
Species for which recovery is not fully apparent, such as Pacific herring, killer whales, and pigeon guillemots, appear to have been affected by other environmental factors or human influences not associated with the oil spill. Insufficient pre-spill baseline data on these species contributed to difficulties in determining the extent of spill effects.
Based on the evidence, the Panel finds that natural recovery of the aquatic environment after an oil spill is likely to be the primary recovery mechanism, particularly for marine spills. Both freshwater and marine ecosystem recovery is further mitigated where cleanup is possible, effective, and beneficial to the environment.
Natural processes that degrade oil would begin immediately following a spill. Although residual oil could remain buried in sediments for years, the Panel finds that toxicity associated with that oil would decline over time and would not cause widespread, long-term impacts.
Gaby Poirier, BC operations manager for the Rio Tinto Aluminum metals group called it a shining moment as the first ingots from the new modernized potlines were wheeled into the also new Henning Hall at the Kitimat smelter on Tuesday, July 7. Referring to the nearly complete Kitimat Modernization Project (KMP), Poirier said, “It’s now like these ingots, our time to shine. Let’s all shine together and become the best aluminum smelter in the world.”
The Kitimat Modernization Project increases aluminum production capacity by 48 per cent. “I have no doubt that KMP will help secure the future for Rio Tinto in British Columbia as a supplier of high quality, low carbon footprint aluminium for the Pacific Rim customer,” Poirier told employee and guests at the First Metal ceremony. (The company held similar ceremonies later in the week for employees unable to attend the first event).
“As we move to ramp to full production sometime in 2016, the transition is still at an early stage. Now more than ever we have to keep the focus to have a safe, sustainable ramp up. When we reach our full capacity of 420,000 tonnes sooner than you think… we’ will have been here 60 years. We’re aiming for another 60 years now.
“It’s more than a ramp up for us; it’s our journey to be the best aluminium smelter in the world. And yes the best, nothing less. Everything starts with a dream. So today we’ve got about 10 pots started, there are still 374 to go. And all this ramp up will be done to a scheduled drum beat, with a safe and sustainable. So today’s a well-deserved celebration for first hot metal and we are now preparing our first metal shipment but there are still significant challenges among us that we’ll go through together. One team one goal. That’s the only way we’ll be successful by working together.”
The modernized smelter, which was delivered in line with the revised schedule and budget, is powered exclusively by Rio Tinto’s wholly owned hydro power facility [at Kemano] and uses the company’s proprietary AP40 smelting technology which will effectively halve the smelter’s overall emissions, Rio Tinto said in a news release.
Michel Charron, KMP Project Director with Rio Tinto’s Technology Group, told reporters that the project did come in at the revised budget of $4.8 billion up from the original estimate of $3.3 billion, discounting reports in some media that the costs had reached as high as $5.5 billion. ‘”They gave me 4.8 and I finished at 4.8,” Charron said.
Charron compared what’s left to do with someone moving into a new house. “There’s a bit of asphalt to be put in, there’s a bit of construction on the last part of the potline…. there’s three months to finish up everything, the little things, the painting, so we’re going to be doing that.”
As of July 7, KMP employed 1024 people, Charron said. As the construction finishes, he said, “The work force will be going down quite rapidly at the end of July and through August and September,”
The newly constructed Henning Hall cafeteria, meeting hall and change facility, named in honour of Paul Henning, now Vice President of Strategic Projects, was packed as Charron, Poirier, Henning, Phil Newsome, KMP Project Director for Bechtel, Sean O’Driscoll, Unifor 2301 president, Mayor Phil Germuth and Haisla Nation Deputy Chief Councillor Taylor Cross brought in the two ingots which were actually poured on June 29.
“As we focus on getting a brand new and somewhat very complex facility up to speed, I urge you to remember that safety remains our top priority, ” Poirier said. “If we get this right the start-up and ramp up will be right too. And this is the only way we can be successful in delivering that world class project. So now in a few words, it is now the time to show what four generations of aluminum producers can do,” Poirier said.
Poirier then turned to Haisla Nation hereditary chief Sammy Robinson. Robinson and his wife Rose unveiled a totem pole commissioned by Rio Tinto for Henning Hall.
The pole tells the story of a time when there were a lot eagles in the Kitimat region. One young man was told “to listen to your elders, listen to your mother, not to laugh at handicapped people, not to laugh at old people for they are good in their own way,” Robinson said. Another thing that this young man was told was never to pick up anything shiny, but he didn’t listen and tried to capture a fur seal that has shiny fur. Unfortunately, for the young man, at that moment a giant eel was swallowing the fur seal and dragging them both down to the bottom of the sea. The eagles, however, got together and lifted the seal and the young man from sea and he safely returned to the beach.
Taylor Cross, Deputy Chief Counsellor for the Haisla, said “It’s a great feeling that big companies like this are doing their best to protect the environment we all live in. Every last one of us enjoys this beautiful country we live in. Myself I’m on my boat almost every weekend, down the Channel. I want to that to continue that for the rest of my life and for my kids’ lives. I want to pass that knowledge on that I’m getting. This project created employment opportunities for us, contracting opportunities for the Haisla Nation and training that we would have never gotten.
“Our unemployment rate when from about 60 to 65 per cent down to may be five or eight per cent. Every Haisla Nation member who wanted to work was working. It was a great achievement, it gave them skills, training, anything they wanted to be. And getting ready for the next project that’s going to come through Kitimat.” Cross warned that with KMP ending, unemployment among the Haisla will be going up again. The legacy agreement signed between Rio Tinto and the Haisla will ensure that members of the First Nation will continue to be trained and be part of running the smelter. A Haisla joint venture runs catering for the cafeteria.
Paul Henning, who had pushed the modernization project for years was greeted by a sustained round of applause. He opened his talk by saying how he told Sean O’Driscoll about the intent to modernize the plant. “He was the kind of guy like Gabby is striving and thriving and pushing and pulling. Nothing was a barrier, nothing was too high to climb to get this project and this guy said ‘hey just cool it these mega projects can take a decade.’ Well boy did we show him. Boy did we show him Boy did we show him, we did in it nine years,” as the guests laughed.
“Of course we have a wonderful platform. The platform not only being Kemano…the Douglas Channel and of course the site that… we have here in BC. The modernized smelter we know well. It is world class we have adopted the best technology we can apply in this location coupled to the lowest cost energy supply to a smelter anywhere in the world with access to global markets particularly the Asian Pacific Rim
“Sounds like a factor of success to me. If you’re going to build it, you build it right here.
“Even though the economic climate was difficult during the journey we’ve been through, I always felt that I had support at every level. We continued to get funding, even if it at sometimes it was smaller than we wanted. We got funding to keep this project alive. We engaged at different levels the creativity in construction… to help us get over that threshold and that hurdle to allow us to be here today. to be able to celebrate this fantastic milestone.
“I truly believe that KMP is a catalyst for megaprojects in the northwest. I am fortunate to be involved in other projects that are looking to come to Kitimat and they’re going to come to Kitimat because of its location but what I think you’ve also demonstrated as a community that they’re coming to Kitimat because of its people, As a host community you’ve demonstrated that you can live alongside and support three and half thousand construction professionals at any given time,
“I’m delighted that we’re through. I’m delighted that the team has got through before the next wave comes.
“I hope that legacy of the learning is two things, It’s enabled the community to be ready and be better prepared for the next one, also for those companies to learn from some of the opportunities and challenges we’ve been through and overcome.
“It was built in Kitimat BC by Canadians… I think at one point I think we had a hundred international workers. So the [labour agreement] allowed the ebb and flow of workers here form a Canadian base. I think that is also a true success factor.”
“For myself each milestone that we go through is a pinch. My goodness we actually pulled this off. We actually pulled this off. So my challenge, you know have the tools. you know have the equipment. You have the people, I was never worried about the people, smelting is in our DNA, three perhaps four generations of smelter experts in Kitimat. Now is your time to show what the best smelter in the world can do.”
1. Why was the study suddenly released after the province said it was “privileged?”
2. Did the apparently rushed release mean that the study, as far as the public is concerned, is incomplete?
3. While most people in Kitimat believed that the study would be a wide ranging look at all parameters of industrial development in the valley, it was limited to just two factors, sulphur dioxide and nitrogen dioxide.
4. It appears that everyone involved were consulted prior to the release with one key execption, the District of Kitimat. Why?
5. The study appears to have changed in its criterion from the time of the request for proposal and the final release one issue—an oil export terminal, which went from “crude” in the request for proposal to refined in the final report.
While the study is spun has a showing that industrial development in the Kitimat Valley can proceed as long as the environment is properly managed, the gaps and the spin will likely bring doubt to the results. That means that a wider ranging and truly independent study of the air shed is needed so that both residents and industry can then make the proper decisions.
In October 2013, the Ministry of the Environment issues a “request for proposal” to “study potential cumulative effects to environment and human health from existing and proposed industrial facilities in the Kitimat airshed.” to be filed by March 31, 2014.
The Province will fund a $650,000 scientific study to help inform regulatory and policy development for future industrial activity in the Kitimat area. The goal is to ensure the potential impacts from industrial air emissions are clearly understood prior to new projects being approved and in operation.
The Kitimat Airshed Impact Assessment Project will look at the cumulative effects of existing and proposed industrial air emissions in the airshed. These include emissions from: an existing aluminium smelter, three proposed LNG terminals, a proposed oil refinery, a crude-oil export facility, and gas-turbine-powered electrical generation facilities. The study will focus on sulphur dioxide and nitrogen dioxide emissions from these facilities.
The study will assess the impact of emissions through a number of scenarios, including their potential effects on water and soil, as well as on vegetation and human health from direct exposure.
With that news release, it appears that many people assumed that “cumulative effects of existing and proposed industrial air emissions in the air shed,” would include all possible scenarios and contaminants.
The report, when it was released on Friday, covered just the “focus” sulphur dioxide and nitrogen dioxide and no other factors in air quality.
Crude or refined oil export?
As Northwest Coast Energy News noted that the report, as released, doesn’t include any references to the Enbridge Northern Gateway project, even though Northern Gateway is a source of “proposed industrial air emissions in the air shed.” The request for proposal also mentions “a crude-oil export facility” but the report as issued concerns a marine terminal for Black’s refinery
The products will be exported via a marine terminal on the Douglas Channel. Projected volumes include 320,000 barrels per day of diesel fuel, 110,000 barrels per day of gasoline and 60,000 barrels per day of jet fuel.
The map in the main report clearly shows that the study concerned the “Kitimat Clean Refinery Port” not a crude oil export facility—in other words likely Enbridge Northern Gateway.
Kitimat excluded
On October 21, 2013, District of Kitimat Council endorsed a motion by former Councillor Corinne Scott:
“The BC Government has recently announced a budget of $650,000 to study the cumulative effects on the air quality due to the proposed industrial development in the District of Kitimat. It would be beneficial to have a representative from the District of Kitimat as an active participant on the committee to provide input and feedback as the study progresses.”
At the time Chief Adminstrative Officer Ron Poole told council that the minister’s office had called and promised to “involve the District.”
At that meeting, Councillor Mary Murphy reported that member were “vocal” at the Union of BC Municpalities that it was essential that Kitimat be involved. Councillors suggested that the study be wide ranging and include emissions already in the area and residual emissions left over from the closed Eurocan and Methaex operations.
The provincial final air shed report makes no mention at all of the District of Kitimat, Eurocan or Methanex.
In April, 2014, after the March 31, reporting deadine, the District and Council had heard nothing from the province. So in April, District Council passed a motion asking for a report on the status of the study.
Crown Privilege
In June, the province refused to release the report to lawyers involved in a suit against the Environmental Assessment Board which is challenging Rio Tinto Alcans’ permit to increase sulphur dixoide emission in the valley. According to the Globe and Mail, Dennis Doyle, a lawyer with the Ministry of the Attorney General, in the RTA suit, wrote to the Environmental Law Centre in Victoria
In a follow-up letter dated June 12, Mr. Doyle said, “On the matter of the Kitimat Airshed Study I am instructed that this report was prepared to guide development of government policy on industrial development in the Kitimat area and to assist the executive council in its ongoing deliberations. It is not a report that was prepared for the Respondent and played no part of the decision-making process for the permit amendment which is now under appeal.”
The EAB told the province to respond to that question by July 18. Instead there was a hastily called news conference and the report was released. However, a close look at the report shows that it was likely rushed to meet the EAB deadine and was incomplete—rather surprising for a report that was supposed to be complete by March 31.
Rushed report
What evidence is there that the report was rushed out by the Ministry of the Environment? The most compelling indication is that instead of a public-friendly Summary Report with an executive summary and clear conclusions, there was nothing more than a short Power Point presentation.
Most people in Kitimat who follow the energy debate are familiar with the approach of combining a readable summary with technical data. It is most evident in the report of the Enbridge Northern Gateway Joint Review, which issued a relative short summary, Connections along with the long technical report, Considerations.
Let’s take as a prime example, the original report on the Kitimat airshed commissioned by Rio Tinto Alcan. In that case, ESSA Technologies Ltd of Vancouver, the company hired by the RTA Kitimat Modernization Project to study the effects of increased sulphur dioxide emissions in the Kitimat Valley, issued three documents, an easy to understand 37-page summary report, a much longer 456 page Technical Assessment Report and a third 332 page volume of appendices, technical data and tables.
It was the same company, ESSA Technologies, that was retained by the province to do the much larger study of the airshed. However, the only public-friendly information was the 16 page highly simplified Power Point presentation.
The ESSA summary report for RTA shows in plain language, the reasons for its conclusions that the increased sulphur dioxide from KMP on human health “is characterized as moderate, an acceptable impact, but in need of closer scrutiny with moderate monitoring.” That report also outlines the limitations and uncertainties of the study.
There was no similar plain language summary released for the overall provincial air shed study, even though it was produced by the same company and came to similar conclusions. To find any limitations or uncertainties in the provincial air shed study you have to do a computer search for those key words.
So it is apparent that intended audience for the report is not really those who live in Kitimat, where over the past five years there is wide knowledge that a summary release along with a technical report is considered a standard procedure.
Kitimat not consulted
At the Friday news conference, reporters asked Environment Minister Mary Polak several times about the delay in releasing the report, and then why it was suddenly released.
In answer to the initial question, Polak said, “We had always intended to release it.” She refused to comment on the claim of cabinet privilege, saying that was the responsibility of government lawyers at the Ministry of the Attorney General. She said that the government had received the March 31 report “by the end of April and “it went through quite a rigorous and thorough review by different agencies… we are satisfied now that the findings have been given the kind of rigorous overview and we’re pleased with what has resulted from that.”
Polak said the Haisla Nation were consulted before the commissioning of the report.
Asked again about who the BC government consulted during the review period, she replied, “There were a number of other groups involved in technical review, so not just Ministry of Environment, you’ll be aware of Northern Health authority, but Ministry of Natural Gas Development, Health Canada, Environment Canada and also specialist reviewers from the Province of Quebec, the University of Helsinki, UBC, also private consultants. Then we spent some time going over and having a technical review with Gitga’at and Coastal Coastal First Nations. So it was a matter of ensuring that we had done the very best review of the work before the occasion on which we released it.”
Which leaves one big question, why was the Province of Quebec and the University of Helsinki consulted and Kitimat, despite requests, was not?
Not in the report, not my department
The provincial government called for a report on the “cumulative effects of existing and proposed industrial air emissions” and noted it would focus “ focus on sulphur dioxide and nitrogen dioxide emissions from these facilities.” It is clear that the report did not go beyond the narrow focus on those two substances.
At the Vancouver news conference, a reporter asked Polak why green house gases were not included.
She replied, “That’s not what this study was intended to look at. This department deals with pollutants and pollution and protecting our environment from it, whereas GHG [green house gas] emissions are dealt with in our department around climate change and climate action. These particular substances have an immediate impact on human health and vegetative health and the receiving environment generally unlike GHGs which are a more global impacted and of course have an impact on climate change. This study only looked at those pollutants sulphur doixide and nitrogen dioxide
Then a second reporter asked here about particulate matter, to which Polak replied, “Coming from the Fraser Valley I am very aware of the impact of particulate matter. Any industrial development that we permit in British Columbia or receives an environmental assessment certificate, particulate matter and the release of particulate matter is one of the things that gets evaluated as we determine whether or not to grant those permits. Or to put stipulations on those permits in order to ensure a reduction or management of particulate matter. That’s where that’s dealt with and we have some pretty good understanding of how that operates. We also have some modelling from this study.
“The reason this study didn’t report on that because we hadn’t asked them to. We specifically wanted to get at the issue of sulphur disoxide and nitrogen dioxide but please do not take frm that because it’s not in the study, it doesn’t get looked at. It simply gets looked at in a different process. In this case it was the understanding of the Kitimat air shed with respect to sulphur dixoide and nitrogen dioxide that we needed to have a better answers and better information.”
In other words, despite what the original proposal said: “The goal is to ensure the potential impacts from industrial air emissions are clearly understood prior to new projects being approved and in operation,” the provincial government is content to wait until the permit phase to consider particulate matter, rather than include particulate matter in the long term planning for the air shed.
And for green house gases, the same attitude seems to apply, either it’s not her department or it will be dealt with sometime in the future.
What’s going on in the air shed?
Although the provincial government has been able to spin that the air shed report clears the way for more industrial development in the region, the report isn’t much help for long term planning for those both for and against industrial development in the valley.
First one has to wonder just how comprehensive was the study, even when it comes to sulphur dioxide and nitrogen dioxide?
The report for Rio Tinto Alcan for just one substance—sulphur dixoide—from one industry—aluminum smelting–led to a 456 page technical report with 332 pages of appendices.
The provincial technical report adds one more substance, nitrogen dioxide, and adds four LNG facilities, an oil refinery, different export terminals for those industries, and two hydro generating stations plus related shipping, including a passing mention of vehicular and train traffic. The new report is 363 pages, including the appendices. (It should be noted that the air shed report does reference some of the information in the RTA report)
The various studies for the Enbridge Northern Gateway, which often contained material on air emissions, included a much longer list of what in industry jargon are called CPOC “chemicals of potential concern,” including chemicals that might be released in trace amounts from the Northern Gateway terminal, but may be of more concern from LNG projects. Who knows unless those substances are studied?
As was required by the Joint Review Panel, Enbridge also studied potential problems from accidental release of air-borne contaminants from the Northern Gateway project. There is no mention of accidental release in the current air shed study.
Although the increase in truck traffic in Kitimat is clearly visible to people who live in the town, the air shed report also speculates that with LNG and a possible refinery, there will also be a significant increase in rail traffic coming into Kitimat, hauled, of course, by diesel locomotives, which the report says is “expected to be conservatively captured within the background concentration adjustment.”
Can the Valley “handle industrial expansion”
Stakeholders in the region from the District of Kitimat to the Gitga’at First Nation to various environmental groups asked for a comprehensive review of what is going to happen in the Kitimat air shed with industrial expansion.
So the answer to the question can the valley “handle industrial expansion” after the flawed and limited report from the provincial government is not “yes,” but “we don’t know yet.”
It appears that the report is part of Christy Clark’s ongoing campaign that LNG will save the provincial economy.
There are two factors the report ignores.
First the energy companies are going to make their final investment decision on cold hard facts, including their own assessment of the potential problems from the air shed, not spin from the provincial government.
Second, until there is a proper air shed study, the First Nations, including the Haisla in Kitimat, the Gitga’at at Hartley Bay, the Kitselas in Terrace will not have solid evidence to make a decision on the details of the LNG or refinery development on their traditional territory and increased ship traffic along the coast and that will come into immediate conflict with the Supreme Court ruling on the Tsilhqot’in decision and the finding that “Whether a particular use is irreconcilable with the ability of succeeding generations to benefit from the land will be a matter to be determined when the issue arises.”
There is a new Orwellian phrase used by both the federal and provincial government. Every report is “independent” and “science-based,” although all they all tend to support the policy of the commissioning agency.
What the Kitimat Valley, Douglas Channel and the Terrace region need is a truly independent and truly science based and truly comprehensive evaluation of the air shed. At the moment, that doesn’t exist. It should whether it comes from industry or if the local governments can find the budget to fund a proper study or some combination of the two.
That was 25 years ago. The media loves anniversary stories and the Exxon Valdez look-backs and updates are already ramping up—right in the middle of the Kitimat plebiscite on the Northern Gateway pipeline and terminal project.
The hashtag #ExxonValdez25 is beginning to trend, based on a Twitter chat for Monday sponsored by the US National Oceanic and Atmospheric Administration.
The voters of Kitimat who will have to cast their ballots on the Joint Review Panel’s interpretation of the Northern Gateway proposal will find once again that the JRP tilted toward the industry and downplayed the lingering risks from a major tanker disaster—and that means neither the pro nor the anti side can be happy with the events that will be marked on March 24, 2014.
The Exxon Valdez accident is part of the Joint Review Panel findings that the economic benefits of Northern Gateway outweigh the risks. The JRP generally accepted the industry position, taken by both Northern Gateway and by ExxonMobil that Prince William Sound has recovered from the Exxon Valdez incident, something that is fiercely debated and disputed.
One area that is not in dispute is that the Exxon Valez disaster brought laws that forced energy companies to use double-hulled tankers. However, commercials that indicate that Northern Gateway will be using double-hulled tankers because the company respects the BC coast is pushing things a bit far, since those tankers are required by law.
Northern Gateway told the Joint Reivew Panel that
on a worldwide basis, all data sets show a steady reduction in the number
and size of oil spills since the 1970s. This decline has been even more apparent since regulatory changes in 1990 following the Exxon Valdez oil spill, which required a phase-in of double-hulled tankers in the international fleet. No double-hulled tanker has sunk since 1990. There have been five incidents of double-hulled tankers that have had a collision or grounding that penetrated the cargo tanks. Resulting spills ranged from 700 to 2500 tonnes
The Haisla countered by saying:
The Haisla Nation said that, although there have been no major spills since the Exxon Valdez spill in Prince William Sound, there were 111 reported incidents involving tanker traffic in Prince William Sound between 1997 and 2007. The three most common types of incidents were equipment malfunctions, problems with propulsion, steering, or engine function, and very small spills from tankers at berth at the marine terminal. The Haisla Nation said that, in the absence of state-of-the-art prevention systems in Prince William Sound, any one of those incidents could have resulted in major vessel casualties or oil spills.
The herring of Prince William Sound still have not recovered. Neither have killer whales, and legal issues remain unresolved a quarter of a century later. Monday is the 25th anniversary of the disaster, in which the tanker Exxon Valdez ran aground on Bligh Reef and spilled at least 11 million gallons of oil into the pristine waters of the sound.
Prince William Sound today looks spectacular, a stunning landscape of mountainous fjords, blue-green waters and thickly forested islands. Pick up a stone on a rocky beach, maybe dig a little, though, and it is possible to still find pockets of oil.
“I think the big surprise for all of us who have worked on this thing for the last 25 years has been the continued presence of relatively fresh oil,” said Gary Shigenaka, a marine biologist for the National Oceanic and Atmospheric Administration.
The legal dispute over the spill is still ongoing, with the Telegraph’s Joanna Walters noting:
[S]tate senator Berta Gardner is pushing for Alaskan politicians to demand that the US government forces ExxonMobil Corporation to pay up a final $92 million (£57 million), in what has become the longest-running environmental court case in history. The money would primarily be spent on addressing the crippled herring numbers and the oiled beaches.
“There’s still damage from the spill. The oil on the beaches is toxic and hurting wildlife. We can’t just say we’ve done what we can and it’s all over – especially with drilling anticipated offshore in the Arctic Ocean – this is significant for Alaska and people around the world,” she told The Telegraph.
An ExxonMobil spokesman then told The Telegraph, the energy sector’s standard response:
Richard Keil, a senior media relations adviser at ExxonMobil, said: “The overwhelming consensus of peer-reviewed scientific papers is that Prince William Sound has recovered and the ecosystem is healthy and thriving.”
But federal scientists estimate that between 16,000 and 21,000 gallons of oil from the spill lingers on beaches in Prince William Sound and up to 450 miles away, some of it no more biodegraded than it was at the time of the disaster.
Overall, the Exxon Valdez disaster was, as US National Public Radio reported, a spur to science. But NPR’s conclusion is the exact opposite of that from the Northern Gateway Joint Review Panel—at least when it comes to fish embryos.
Twenty-five years of research following the Exxon Valdez disaster has led to some startling conclusions about the persistent effects of spilled oil.
When the tanker leaked millions of gallons of the Alaskan coast, scientists predicted major environmental damage, but they expected those effects to be short lived. Instead, they’ve stretched out for many years.
What researchers learned as they puzzled through the reasons for the delayed recovery fundamentally changed the way scientists view oil spills. One of their most surprising discoveries was that long-lasting components of oil thought to be benign turned out to cause chronic damage to fish hearts when fish were exposed to tiny concentrations of the compounds as embryos.
It seems that some species recovered better than others from the oilspill.
For example, the recovery of the sea otter population has received widespread media coverage, but with widely divergent points of view. The more conservative and pro-industry writers point to the recovery of the otter population, while environmental coverage stresses the quarter century it took for the otter population to rebound.
Although recovery timelines varied widely among species, our work shows that recovery of species vulnerable to long-term effects of oil spills can take decades,” said lead author of the study, Brenda Ballachey, research biologist with the U.S. Geological Survey. “For sea otters, we began to see signs of recovery in the years leading up to 2009, two decades after the spill, and the most recent results from 2011 to 2013 are consistent with recovery
The Joint Review Panel generally accepted Northern Gateway’s and the energy industry’s evidence on the Exxon Valdez incident and concluded
The Panel’s finding regarding ecosystem recovery following a large spill is based on extensive scientific evidence filed by many parties, including information on recovery of the environment from large past spill events such as the Exxon Valdez oil spill. The Panel notes that different parties sometimes referred to the same studies on environmental recovery after oil spills, and drew different conclusions.
In its consideration of natural recovery of the environment, the Panel focused on effects that are more readily measurable such as population level impacts, harvest levels, or established environmental quality criteria such as water and sediment quality criteria.
The Panel finds that the evidence indicates that ecosystems will recover over time after a spill and that the post-spill ecosystem will share functional attributes of the pre-spill one. Postspill ecosystems may not be identical to pre-spill ecosystems. Certain ecosystem components may continue to show effects, and residual oil may remain in some locations. In certain unlikely circumstances, the Panel finds that a localized population or species could potentially be permanently affected by an oil spill.
Scientific studies after the Exxon Valdez spill indicated that the vast majority of species recovered following the spill and that functioning ecosystems, similar to those existing pre-spill, were established.
Species for which recovery is not fully apparent, such as Pacific herring, killer whales, and pigeon guillemots, appear to have been affected by other environmental factors or human influences not associated with the oil spill. Insufficient pre-spill baseline data on these species contributed to difficulties in determining the extent of spill effects.
Based on the evidence, the Panel finds that natural recovery of the aquatic environment after an oil spill is likely to be the primary recovery mechanism, particularly for marine spills. Both freshwater and marine ecosystem recovery is further mitigated where cleanup is possible, effective, and beneficial to the environment.
Natural processes that degrade oil would begin immediately following a spill. Although residual oil could remain buried in sediments for years, the Panel finds that toxicity associated with that oil would decline over time and would not cause widespread, long-term impacts.
The Panel finds that Northern Gateway’s commitment to use human interventions, including available spill response technologies, would mitigate spill impacts to ecosystems and assist in species recovery..
It is clear, however, from the local coverage in Alaska and from the attention of the world’s media that Prince William Sound has not fully recovered from the Exxon Valdez incident (it may yet in who knows how many years). Anger and bitterness still remains among the residents of Alaska, especially since the court cases are dragging on after a quarter century.
Those are the kinds of issues that Kitimat residents will face when they vote in the plebiscite on April 12. Just who do the people of Kitimat believe, those who say the chances for a spill are remote and the environment and the economy will quickly recover? It probably depends on whether or not you consider 25 years quick. Twenty-five years is quick in geological time but it is a third or a half of a human life time.
As for the residents of Kitamaat Village, and probably many people in Kitimat, Haisla Chief Counsellor Ellis Ross summed it up in a Facebook posting on Sunday
If this happens in Kitamaat, all those campaigning for Enbridge will pack up and leave for another coastline to foul. Haisla don’t have much of a choice. We would have to stay and watch the court battles on who should pay what.
Ross is right. Whether it’s Prince William Sound or Douglas Channel, the people who live the region are stuck with the mess while the big companies walk away and the lawyers get rich.
Excerpts from the Northern Gateway Joint Review Panel report relating to the Exxon Valdez disaster.
Northern Gateway told the Joint Reivew Panel that
on a worldwide basis, all data sets show a steady reduction in the number
and size of oil spills since the 1970s. This decline has been even more apparent since regulatory changes in 1990 following the Exxon Valdez oil spill, which required a phase-in of double-hulled tankers in the international fleet. No double-hulled tanker has sunk since 1990. There have been five incidents of double-hulled tankers that have had a collision or grounding that penetrated the cargo tanks. Resulting spills ranged from 700 to 2500 tonnes
The Haisla countered by saying:
The Haisla Nation said that, although there have been no major spills since the Exxon Valdez spill in Prince William Sound, there were 111 reported incidents involving tanker traffic in Prince William Sound between 1997 and 2007. The three most common types of incidents were equipment malfunctions, problems with propulsion, steering, or engine function, and very small spills from tankers at berth at the marine terminal. The Haisla Nation said that, in the absence of state-of-the-art
prevention systems in Prince William Sound, any one of those incidents could have resulted in major vessel casualties or oil spills.
There were disputes about how the Exxon Valdez affected species in the Prince William Sound area:
Northern Gateway said that, although crabs are known to be sensitive to toxic effects, they have been shown to recover within 1 to 2 years following
a spill such as the Exxon Valdez incident. Northern Gateway said that Dungeness crab was a key indicator species in its assessment of spill effects.
Northern Gateway said that potential effects to razor clams are not as well studied. It said that sediment toxicity studies after the Exxon Valdez spill did not suggest significant effects on benthic invertebrates. Following the Exxon Valdez and
Selendang Ayu oil spills in Alaska, food safety closures for species such as mussels, urchins, and crabs were lifted within 1 to 2 years following the
spill.
In response to questioning from the Council of the Haida Nation regarding potential spill effects on herring, Northern Gateway said that herring were a key indicator species in its spill assessment.
Northern Gateway said that the Exxon Valdez spill did not appear to cause population-level effects on Prince William Sound herring.
As did throughout its report, the Joint Review Panel gave great weight to Northern Gateway’s evidence:
Northern Gateway said that potential effects of oil stranded on the shorelines and in the intertidal environment were assessed qualitatively with particular reference to the Exxon Valdez oil spill. It said that the entire intertidal zone along affected
shorelines would likely be oiled, coating rocks, rockweed, and sessile invertebrates. Some of the diluted bitumen could penetrate coarse-grained intertidal substrates, and could subsequently be remobilized by tides and waves. There were
relatively few shoreline areas with potential for long oil residency. Northern Gateway said that the stranded bitumen would not be uniformly distributed, and that heavy oiling would likely be limited to a small proportion of affected shoreline. Northern
Gateway said that, compared to the Exxon Valdez oil spill, the simulation suggested that more dilbit would be distributed along a shorter length of shoreline.
Northern Gateway said that, due to the relatively sheltered conditions in Wright Sound, and in the absence of cleanup, most of the stranded oil would be weathered or dispersed into the marine environment within 3 to 5 years. It said that,
while weathering and dispersal could represent an important secondary source of hydrocarbon contamination of offshore or subtidal sediments, the weathered hydrocarbons themselves would have lower toxicity than fresh dilbit.
Northern Gateway assessed potential effects on key marine receptors including marine water quality, subtidal sediment quality, intertidal sediment
quality, plankton, fish, and a number of bird and mammal species. The company said that acute effects from monocyclic aromatic hydrocarbons such as benzene, toluene, ethylbenzene, and xylene may briefly occur in some areas. Acute effects from polycyclic aromatic hydrocarbons were not likely due to their low water solubility.
Northern Gateway said that chronic adverse effects on the subtidal benthic community were not predicted. After a large spill, consumption advisories for pelagic, bottom-dwelling and anadromous fish, and invertebrates from open
water areas and subtidal sediments would probably be less than 1 year in duration. Northern Gateway said that consumption advisories for intertidal communities and associated invertebrates, such as mussels, could persist for 3 to 5 years or longer in
some sheltered areas.
But dilbit is different from heavy crude
In response to questions from the Haisla Nation and the United Fishermen and Allied
Workers Union, Fisheries and Oceans Canada said that, although it had a great deal of information on conventional oils, the results of research conducted on the biological effects of conventional oil products may not be true for dilbit or unconventional products. Fisheries and Oceans Canada said that it was not in a
position to quantify the magnitude and duration of impacts to marine resources
The United Fishermen and Allied Workers Union said that, because there are so many variables, each spill is a unique event, and some results will be unknowable. It said that a spill the size of the Exxon Valdez incident would affect the entire ecosystem
in the project area, and that recovery to pre-spill conditions would be unlikely to ever occur. It said that a spill the size of the Exxon Valdez oil spill would likely have similar effects in the project area because marine resources in the project area are
similar to those in Prince William Sound. It argued that the cold, sheltered, waters of the Confined Channel Assessment Area would likely experience reduced natural dispersion and biodegradation of oil, leading to heavier oiling and longer recovery
times than seen in Prince William Sound and elsewhere.
The United Fishermen and Allied Workers Union said that patches of buried oil from the Exxon Valdez oil have been found on sand and gravel beaches overlain by boulders and cobbles. It said that effects from a tanker spill associated with the
Enbridge Northern Gateway Project would likely be more severe than the Exxon Valdez oil spill due to the more persistent nature of dilbit and the lack of
natural cleaning action in the sheltered waters of the Confined Channel Assessment Area.
The Gitxaala Nation’s experts said that large historical spill events are not necessarily good indicators of what will happen in the future. They
argued that each spill has unique circumstances and there is still significant uncertainty about the effects of major spills.
The Gitxaala Nation concluded Northern Gateway had failed to adequately consider the potential consequences on ecological values of interest to the Gitxaala.
Gitga’at First Nation said that a spill of dilbit greater than 5,000 cubic metres would result in significant, adverse, long-term, lethal, and sublethal effects
to marine organisms, and that effects would be particularly long-lasting on intertidal species and habitats. It also said that effects from a tanker spill associated with the project would probably be more severe than the Exxon Valdez oil spill, due to
the more persistent nature of dilbit and the lack of natural cleaning action in the sheltered waters
The JRP told how Nothern Gateway looked at the scientific evidence:
The company used a case study approach and reviewed the scientific literature for environments similar to the project area. The review examined 48 spills, including the Exxon Valdez oil spill in 1989, and 155 valued ecosystem components from cold temperate and sub-arctic regions. Northern Gateway said that the scientific evidence is clear that, although oil spills have adverse effects on biophysical and human environments, ecosystems and their components recover with time.
Pacific herring, killer whales, and pink salmon were species that were extensively studied following the Exxon Valdez spill and were discussed by numerous participants in the Panel’s process.
As referred to by the Haisla Nation, Pacific herring are listed as “not recovering” by the Exxon Valdez Oil Spill Trustee Council. The Trustee Council said that, despite numerous studies to understand the effects of oil on herring, the causes constraining population recovery are not well understood.
Northern Gateway said that scientific evidence indicates that a combination of factors, including disease, nutrition, predation, and poor recruitment
appear to have contributed to the continued suppression of herring populations in Prince William Sound.
Northern Gateway said that 20 years of research on herring suggests that the Exxon Valdez oil spill is likely to have initially had localized effects on herring eggs and larvae, without causing effects at the population level. Northern Gateway said
that, even after 20 years, the effects of the spill on herring remain uncertain. It said that there has also been convergence amongst researchers that herring declines in the spill area cannot be connected to the spill.
Northern Gateway said that herring stocks along the entire coast of British
Columbia have been in overall decline for years and that herring were shown to recover within 1 to 2 years following the Nestucca barge spill.
A Gitxaala Nation expert noted the uncertainty in interpreting the decline of herring following the Exxon Valdez oil spill and said that the debate is not likely to ever be settled.
The Living Oceans Society said that the Exxon Valdez Oil Spill Trustee Council reported that some killer whale groups suffered long-term damage from initial exposure to the spill. Northern Gateway’s expert said the research leads him to
conclude that the actual effects on killer whales of the Exxon Valdez spill are unknowable due to numerous confounding factors. He said that the
Exxon Valdez Oil Spill Trustee Council has not definitively said that killer whale mortalities can be attributed to the spill. A Government of Canada
expert said that the weight of evidence suggests that the mortality of killer whales was most likely related to the spill.
Northern Gateway said that mass mortality of marine fish following a spill is rare. In response to questions from the Haisla Nation, Northern Gateway said that fish have the ability to metabolize potentially toxic substances such as polycyclic aromatic hydrocarbons. It said that international experience with oil spills has demonstrated that fin fishery closures tend to be very short in duration.
Northern Gateway said that food safety programs for fin fish conducted following the Exxon Valdez spill and the Selendang Ayu spill in Alaska indicated
that the finfish were not affected by the spill and that the fish were found, through food safety testing programs, to be safe to eat.
The Haisla Nation referred to the Exxon Valdez Oil Spill Trustee Council report that discussed the complexities and uncertainties in the recovery status of pink salmon. It said that, by 1999, pink salmon were listed as recovered and that the
report noted that continuing exposure of embryos to lingering oil is negligible and unlikely to limit populations.
Northern Gateway said that the longterm effect of the spill on pink salmon survival is
best demonstrated by the success of adult returns following the spill. Northern Gateway said that, in the month following the spill, when there was still
free oil throughout Prince William Sound, hundreds of millions of natural and hatchery pink salmon fry migrated through the area. It argued that these fish would arguably be at greatest risk from spill-related effects but that the adult returns 2 years later were one of the highest populations ever. Northern Gateway said that sockeye and pink salmon appear to have been unaffected by the Exxon Valdez spill
over the long term.
In response to questions from the Council of the Haida Nation and the United Fishermen and Allied Workers Union, Northern Gateway said that effects
on species such as seaweed, crabs, and clams have been shown to be relatively short-term, with these species typically recovering within 2 years or less
following a spill, depending on circumstances.
Northern Gateway said that, based on the Exxon Valdez spill, the level of hydrocarbons dissolved or suspended in the water column would be expected
to be substantially lower than those for which potential toxic effects on crabs or fish may occur.
In response to questions from BC Nature and Nature Canada, Northern Gateway said that the Exxon Valdez oil spill indicates which species of birds are most susceptible to oiling. Seabirds are generally vulnerable to oil spills because many species spend large amounts of time at sea. Diving seabirds such as murres are particularly vulnerable to oiling because they spend most of their time on the surface, where oil is found, and tend to raft together. Thus, these species often account for most of the bird mortality associated with oil spills.
More than 30,000 seabird carcasses, of which 74 per cent were murres, were recovered following the Exxon Valdez spill and it was initially estimated
that between 100,000 and 300,000 seabirds were killed. However, detailed surveys of breeding murres in 1991 indicated no overall difference from pre-spill levels confirming rapid recovery of this species.
Northern Gateway said that, although potential toxicological effects from oil spills on
birds have been well documented in laboratory studies, the ultimate measure of recovery potential is how quickly birds return to their natural abundance and reproductive performance. It said that recovery is often difficult to measure due to
significant natural variation in populations and the fact that the baseline is often disputed. It said that this can lead to misinterpretation of results depicting recovery.
At the request of Environment Canada, Northern Gateway filed two reports on the susceptibility of marine birds to oil and the acute and chronic effects of the Exxon Valdez oil spill on marine birds. Northern Gateway said that marine birds are
vulnerable to oil in several ways such as contact, direct or indirect ingestion, and loss of habitat.
It said that many marine bird populations appear to have recovered from the effects of the Exxon Valdez spill, but some species such as harlequin ducks and pigeon guillemots have not recovered, according to the Exxon Valdez Oil Spill Trustee
Council. It said these reports demonstrate that marine birds are susceptible to marine oil spills to varying degrees depending on the species, its life
history and habitat, and circumstances associated with the spill.
Northern Gateway concluded that:
• Marine, freshwater, and terrestrial environments recover from oil spills, with recovery time influenced by the environment, the valued ecosystem components of interest, and other factors such as spill volume and characteristics
of the oil. Depending on the species and circumstances, recovery can be quite rapid or it can range from 2 to 20 years. Other scientific reviews have indicated that recovery of marine environments from oil spills takes 2 to 10 years.
• Different marine ecosystem components recover at different rates. Recovery time can range from days or weeks in the case of water quality, to years or decades for sheltered, soft sediment marshes. Headlands and exposed rocky shores can take 1 to 4 years to recover.
• Little to no oil remained on the shoreline after 3 years for the vast majority of shoreline oiled following the Exxon Valdez spill,
• The Exxon Valdez Oil Spill Trustee Council concluded that, after 20 years, any remaining Exxon Valdez oil in subtidal sediment is no longer a concern, and that subtidal communities are very likely to have recovered.
• Because sheltered habitats have long recovery times, modern spill response gives high priority to preventing oil from entering marshes and other protected shoreline areas.
• Valued ecosystem components with short life spans can recover relatively rapidly, within days to a few years. Recovery is faster when there is an abundant supply of propagules close to the affected area. For example, drifting larvae from
un-oiled marine and freshwater habitats will rapidly repopulate nearby areas affected by a spill.
• Plankton recovery is typically very rapid.
• Seabed organisms such as filter feeders may be subject to acute effects for several years, depending on location, environmental conditions, and degree of oiling.
• Marine fisheries and other human harvesting activities appear to recover within about 2 to 5 years if the resource has recovered and has not been affected by factors other than the oil spill.
• Protracted litigation may delay resumption of fisheries and other harvesting.
• Local community involvement in spill response priorities and mitigation plans can reduce community impacts and speed recovery of
fisheries and harvesting activities.
• A long life span typically means a long recovery time, in the case of bird and mammal populations that can only recover by local reproduction rather
than by immigration from other areas.
• Fast moving rivers and streams tend to recover more quickly than slow flowing watercourses, due to dispersal of oil into the water column by turbulence, which can enhance dissolution, evaporation, and microbial degradation.
• Drinking water and other water uses can be affected by an oil spill for weeks to months. Drinking water advisories are usually issued. Groundwater use may be restricted for periods ranging from a few weeks to 2 years, depending on
the type of use.
• Groundwater can take years to decades to recover if oil reaches it. Groundwater does not appear to have been affected in the case of Enbridge’s Kalamazoo River spill, near Marshall, Michigan.
• Freshwater invertebrates appear to have recovered within 2 years in several cases.
• Freshwater fisheries may recover fully in as little as four years, with signs of partial recovery evident after only a few months. The ban on consumption of fish in the Kalamazoo River was to be lifted approximately two years following
the spill.
• Human activities are affected by factors such as cleanup activities, safety closures and harvesting bans. These typically persist for months to a few years.
• Appropriate cleanup can promote recovery, while inappropriate cleanup techniques can actually increase biophysical recovery time.
Modern spill response procedures carefully consider the most appropriate treatment for the oil type, level of contamination, and habitat type.
The Living Oceans Society noted the following in relation to potential recovery of the marine environment following a spill:
• Physical contamination and smothering are primary mechanisms that adversely affect marine life, particularly intertidal organisms.
• Birds and mammals suffer the greatest acute impact when exposed to oil at or near the water surface.
• Marine communities have variable resiliency to oil spills, from highly tolerant (plankton, kelp beds), to very intolerant (estuaries and sea otters). Impacts to communities and populations are very difficult to measure due
to lack of scientific methods to measure long term,sublethal, and chronic ecological impacts.
• As the return of the marine environment to the precise conditions that preceded the oil spill is unlikely, a measurement of spill recovery can be
based on a comparison of un-oiled sites with oiled sites of similar ecological characteristics.
• The Exxon Valdez oil spill killed many birds and sea otters. Population-level impacts to salmon, sea otters, harbour seals, and sea birds appear to have been low. Wildlife populations had recovered within their natural range of variability after 12 years.
• Intertidal habitats of Prince William Sound have shown surprisingly good recovery. Many shorelines that were heavily oiled and then cleaned appear much as they did before the spill. There is still residual buried oil on some beaches. Some mussel and clam beds have not fully recovered.
• The marine environment recovered with little intervention beyond initial cleaning. Natural flushing by waves and storms can be more effective than human intervention.
• Wildlife rescue and rehabilitation efforts had a marginal beneficial effect on the recovery of bird and mammal populations
• The impacted area of Prince William Sound had shown surprising resiliency and an ability to return to its natural state within the range of natural variability.
• The Exxon Valdez oil spill had significant and long-lasting effects on people and communities.
Questioning experts
The Panel posed a series of questions to experts representing Northern Gateway, federal government participants, and the Gitxaala First Nation regarding the potential recovery of marine ecosystems following a large oil spill.
Northern Gateway said that past marine spills have demonstrated that, over time, the environment will recover to a pre-spill state, and that most species fully recover. It said that species associated with the surface of the water tend to be most susceptible to oil spills, and that cleanup efforts can help direct and
accelerate natural restoration processes.
Federal government experts generally agreed with Northern Gateway’s responses, although they stressed that effects could be felt in areas other than the water surface, such as intertidal and subtidal zones. They said that it is difficult to define
and assess effects and recovery, depending on the species and availability of baseline information.
They said that most species may fully recover over time, and that the time frame for this recovery can be extremely variable depending on species and circumstances.
The Gitxaala Nation’s experts noted the potential for effects on species at the water surface and in intertidal areas, and noted exceptions to the notion that
the marine environment will naturally restore itself.
They said that full recovery can occur, depending on the circumstances, but is not guaranteed. They said that it is difficult to assess spill effects in the absence
of adequate baseline information.
Despite the quarter century of studies on the Exxon Valdez inicident, the paucity of studies prior to the spill mean that arguments will continue over “baseline information.”
Participants told the Panel that a lack of baseline information has often made it difficult to separate spill-related effects from those that were caused by natural variation or other causes not related to a spill.
Northern Gateway acknowledged the need for adequate baseline information. Parties such as Coastal First Nations, Raincoast Conservation Foundation, and the Gitxaala Nation said that Northern Gateway had provided insufficient baseline information to assess future spill-related effects. The Kitsumkalum First Nation asked how
spill-related effects on traditionally harvested foods could be assessed in the absence of baseline information.
The Haisla Nation noted the importance of collecting baseline data in the Kitimat River valley to compare with construction and spill-related impacts. The Haisla Nation submitted a report outlining important considerations for a baseline
monitoring program. One recommendation was that the program should engage stakeholders and be proponent-funded. In response to questions
from Northern Gateway, the Haisla Nation noted that a design along the lines of a before/after control/impact model would be appropriate.
In response to these comments, Northern Gateway noted its commitment to implement a Pipeline Environmental Effects Monitoring Program. Northern Gateway’s
proposed framework for the monitoring program indicates that a number of water column, sediment, and biological indicators would be monitored.
The Raincoast Conservation Foundation said that one of the principal lessons learned from the Exxon Valdez oil spill was the importance of collecting abundance and distribution data for non-commercial species. Because baseline information was
lacking, spill effects on coastal wildlife were difficult to determine. Environment Canada also noted the importance of adequate baseline information to
assess, for example, spill-related effects on marine birds.
Northern Gateway outlined the baseline measurements that it had already conducted as part of its environmental assessment. It also said that is
would implement a Marine Environmental Effects Monitoring Program. Northern Gateway said that the initial baseline data, plus ongoing monitoring,
would create a good baseline for environmental quality and the abundance, distribution, and diversity of marine biota. In the event of an oil spill
it would also help inform decisions about restoration endpoints.
Northern Gateway said that it would provide Aboriginal groups with the opportunity to undertake baseline harvesting studies. In response to questions from the United Fishermen and Allied Workers Union, Northern Gateway said that baseline information gathered through the environmental effects monitoring program would also be relevant to commercial harvest management and for assessing compensation claims in the event of a spill.
The Kitimat Valley Naturalists noted the ecological importance of the Kitimat River estuary.
The Joint Review Panel, in its conclusions and ruling, generally agreed with the energy industry that affects of a major oil spill would be temporary.
The Panel heard evidence and opinion regarding the value that the public and Aboriginal groups place on a healthy natural environment.
The Panel finds that it is not able to quantify how a spill could affect people’s values and perceptions.
The Panel finds that any large spill would have short-term negative effects on people’s values, perceptions and sense of wellbeing.
The Panel is of the view that implementation of appropriate mitigation and compensation following a spill would lessen these effects over time. The
Panel heard that protracted litigation can delay recovery of the human environment.
The Panel heard that appropriate engagement of communities in determining spill response priorities and developing community mitigation plans can also lessen effects on communities. Northern Gateway has committed to the development
of Community Response Plans
The Panel’s finding regarding ecosystem recovery following a large spill is based on extensive scientific evidence filed by many parties, including information on recovery of the environment from large past spill events such as the Exxon Valdez
oil spill. The Panel notes that different parties sometimes referred to the same studies on environmental recovery after oil spills, and drew different conclusions. In its consideration of natural recovery of the environment, the Panel focused
on effects that are more readily measurable such as population level impacts, harvest levels, or established environmental quality criteria such as
water and sediment quality criteria.
The Panel finds that the evidence indicates that ecosystems will recover over time after a spill and that the post-spill ecosystem will share functional attributes of the pre-spill one. Postspill ecosystems may not be identical to pre-spill ecosystems. Certain ecosystem components may continue to show effects, and residual oil
may remain in some locations. In certain unlikely circumstances, the Panel finds that a localized population or species could potentially be permanently affected by an oil spill. Scientific studies after the Exxon Valdez spill indicated that the vast majority of species recovered following the spill and that functioning ecosystems, similar
to those existing pre-spill, were established.
Species for which recovery is not fully apparent, such as Pacific herring, killer whales, and pigeon guillemots, appear to have been affected by other
environmental factors or human influences not associated with the oil spill. Insufficient pre-spill baseline data on these species contributed to
difficulties in determining the extent of spill effects.
Based on the evidence, the Panel finds that natural recovery of the aquatic environment after an oil spill is likely to be the primary recovery
mechanism, particularly for marine spills. Both freshwater and marine ecosystem recovery is further mitigated where cleanup is possible, effective, and beneficial to the environment.
Natural processes that degrade oil would begin immediately following a spill. Although residual oil could remain buried in sediments for years, the Panel finds that toxicity associated with that oil would decline over time and would not cause
widespread, long-term impacts.
The Panel finds that Northern Gateway’s commitment to use human interventions,
including available spill response technologies, would mitigate spill impacts to ecosystems and assist in species recovery. Many parties expressed concerns about potential short-term and long-term spill effects on resources that they use or depend on, such as drinking water, clams, herring, seaweed, and fish. The weight of
evidence indicates that these resources recover relatively rapidly following a large oil spill.
For example, following the Selendang Ayu and Exxon Valdez spills in Alaska, fin fish were found, through food safety testing programs, to be safe to eat. Food safety closures for species such as mussels, urchins, and crabs were lifted within 1 to
2 years following the spills.
The actual time frame for recovery would depend on the circumstances of the spill. Until harvestable resources recover, various measures are typically put in place, such as compensation,harvest restrictions or closures, and provision of
alternative supply.
It is difficult to define recovery of the human environment because people’s perceptions and values are involved. This was made clear to the
Panel through oral statements and oral evidence.
The Panel finds that oil spills would cause disruptions in people’s lives, especially those people who depend on the marine environment for sustenance, commercial activities and other uses. The extent and magnitude of this disruption
would depend on the specific circumstances associated with the spill. The Panel views recovery of the socio-economic environment as the time when immediate impacts and interruption to people’s lives are no longer evident, and the
natural resources upon which people depend are available for use and consumption.
The Panel heard that assessing the potential recovery time of the environment is often complicated by challenges in separating background or unrelated events from spill-related effects. There can be natural variation in species populations,
and other natural and human-induced effects can also make it difficult to determine which impacts are spill-related and which are not.
The Panel notes that Northern Gateway has committed to collect baseline data and gather baseline information on harvest levels and values through initiatives such as its Environmental Effects Monitoring Program, Fisheries Liaison
Committee, and traditional harvest studies. The Panel finds that these commitments go beyond regulatory requirements and are necessary. This information would contribute to assessments of spill effects on resource harvesting values,
post-spill environmental recovery, and loss and liability determinations.
The Panel is of the view that it is not possible to predict a specific time in which overall recovery of the environment may occur. The time for recovery would depend on the type and volume of product spilled, environmental conditions,
the success of oil spill response and cleanup measures, and the extent of exposure of living and non-living components of the environment to the product spilled. Recovery of living and non-living components of the environment would
occur over different time frames ranging from weeks, to years, and in the extreme, decades.
Even within the same environmental component, recovery may occur over different time frames depending on local factors such as geographic location, the amount of oiling, success of cleanup, and amount of natural degradation.
Based on the physical and chemical characteristics described for the diluted bitumen to be shipped and the fate and transport modelling conducted, the Panel finds that stranded oil on shorelines would not be uniformly distributed on
shorelines and that heavy oiling would be limited to specific shoreline areas. The Panel accepts Northern Gateway’s prediction that spilled dilbit could persist longer in sheltered areas, resulting in longer consumption advisories for intertidal
communities and associated invertebrates than in more open areas.
Based on the scientific evidence, the Panel accepts the results of the
chronic risk assessment that predicted no significant risks to marine life due to oil deposition in the subtidal sediments.
For potential terrestrial and marine spills, the Panel does not view reversibility as a reasonable measure against which to predict ecosystem recovery. No ecosystem is static and it is unlikely that an ecosystem will return to exactly the same
state following any natural or human induced disruption. Based on the evidence and the Panel’s technical expertise, it has evaluated whether or not functioning ecosystems are likely to return after a spill. Requiring Northern Gateway to
collect baseline data would provide important information to compare ecosystem functions before and after any potential spill.
The Panel finds that Northern Gateway’s ecological and human health risk assessment models and techniques were conducted using conservative assumptions and state of the art models. Combined with information from past spill events, these assessments provided sufficient information to inform the Panel’s deliberation on
the extent and severity of potential environmental effects. The Panel finds that this knowledge was incorporated in Northern Gateway’s spill prevention strategies and spill preparedness and response planning. Although the ecological risk assessment
models used by Northern Gateway may not replicate all possible environmental conditions or effects, the spill simulations conducted by Northern Gateway provided a useful indication of the potential range of consequences of large oil spills in
complex natural environments.
Oil spills kill fish. That’s well known. Now scientists say they have found out why oil spills kill adult fish. The chemicals in the oil often trigger an irregular heartbeat and cardiac arrest.
A joint study by Stanford University and the US National Atmospheric and Oceanic Administration have discovered that crude oil interferes with fish heart cells. The toxic consequence is a slowed heart rate, reduced cardiac contractility and irregular heartbeats that can lead to cardiac arrest and sudden cardiac death.
The study was published Feb. 14, 2014 in the prestigious international journal Science and unveiled at the convention of the American Association for the Advancement of Science in Chicago.
The study is part of the ongoing Natural Resource Damage Assessment of the April 2010 Deepwater Horizon oil spill in the Gulf of Mexico.
Scientists have known for some time that crude oil is known to be “cardiotoxic” to developing fish. Until now, the mechanisms underlying the harmful effects were unclear.
Exxon Valdez
Studies going back to the Exxon Valdez oil spill in Alaska in 1989 have shown that exposure to crude oil-derived chemicals disrupt cardiac function and impairs development in larval fishes. The studies have described a syndrome of embryonic heart failure, bradycardia (slow heart beat), arrhythmias (irregular heartbeats) and edema in exposed fish embryos.
After the Gulf of Mexico spill, studies began on young fish in the aftermath of the Deepwater Horizon spill. The two science teams wanted to find out how oil specifically impacts heart cells.
Crude oil is a complex mixture of chemicals, some of which are known to be toxic to marine animals.
Past research focused on “polycyclic aromatic hydrocarbons” (PAHs), which can also be found in coal tar, creosote, air pollution and stormwater runoff from land. In the aftermath of an oil spill, the studies show PAHs can persist for many years in marine habitats and cause a variety of adverse environmental effects.
The scientists found that oil interferes with cardiac cell excitability, contraction and relaxation – vital processes for normal beat-to-beat contraction and pacing of the heart.
Low concentrations of crude
The study shows that very low concentrations of crude oil disrupt the specialized ion channel pores – where molecules flow in and out of the heart cells – that control heart rate and contraction in the cardiac muscle cell. This cyclical signalling pathway in cells throughout the heart is what propels blood out of the pump on every beat. The protein components of the signalling pathway are highly conserved in the hearts of most animals, including humans.
The researchers found that oil blocks the potassium channels distributed in heart cell membranes, increasing the time to restart the heart on every beat. This prolongs the normal cardiac action potential, and ultimately slows the heartbeat. The potassium ion channel impacted in the tuna is responsible for restarting the heart muscle cell contraction cycle after every beat, and is highly conserved throughout vertebrates, raising the possibility that animals as diverse as tuna, turtles and dolphins might be affected similarly by crude oil exposure. Oil also resulted in arrhythmias in some ventricular cells.
“The ability of a heart cell to beat depends on its capacity to move essential ions like potassium and calcium into and out of the cells quickly.” said Barbara Block, a professor of marine sciences at Stanford. She said, “We have discovered that crude oil interferes with this vital signalling process essential for our heart cells to function properly.”
Nat Scholz, leader of the Ecotoxicology Program at NOAA’s Northwest Fisheries Science Center in Seattle said.”We’ve known from NOAA research over the past two decades that crude oil is toxic to the developing hearts of fish embryos and larvae, but haven’t understood precisely why.”
Long term problems in fish hearts
He added: “These new findings more clearly define petroleum-derived chemical threats to fish and other species in coastal and ocean habitats, with implications that extend beyond oil spills to other sources of pollution such as land-based urban stormwater runoff.”
The new study also calls attention to a previously under appreciated risk to wildlife and humans, particularly from exposure to cardioactive PAHs that can also exist when there are high levels of air pollution.
“When we see these kinds of acute effects at the cardiac cell level,” Block said, “it is not surprising that chronic exposure to oil from spills such as the Deepwater Horizon can lead to long-term problems in fish hearts.”
The study used captive populations of bluefin and yellowfin tuna at the Tuna Research and Conservation Center, a collaborative facility operated by Stanford and the Monterey Bay Aquarium. That meant the research team was able to directly observe the effects of crude oil samples collected from the Gulf of Mexico on living fish heart cells.
“The protein ion channels we observe in the tuna heart cells are similar to what we would find in any vertebrate heart and provide evidence as to how petroleum products may be negatively impacting cardiac function in a wide variety of animals,” she said. “This raises the possibility that exposure to environmental PAHs in many animals – including humans – could lead to cardiac arrhythmias and bradycardia, or slowing of the heart.”
Tuna spawning
The Deepwater Horizon disaster released over 4 million barrels of crude oil during the peak spawning time for the Atlantic bluefin tuna in the spring of 2010. Electronic tagging and fisheries catch data indicate that Atlantic bluefin spawn in the area where the Deepwater Horizon drilling rig collapsed, raising the possibility that eggs and larvae, which float near the surface waters, were exposed to oil.
The spill occurred in the major spawning ground of the western Atlantic population of bluefin tuna in the Gulf of Mexico. The most recent stock assessment, conducted in 2012, estimated the spawning population of the bluefin tuna to be at only 36 percent of the 1970 baseline population. Additionally, many other pelagic fishes were also likely to have spawned in oiled habitats, including yellowfin tuna, blue marlin and swordfish.
Block and her team bathed isolated cardiac cells from the tuna in low dose crude oil concentrations similar to what fish in early life stages may have encountered in the surface waters where they were spawned after the April 2010 oil spill in the Gulf of Mexico.
They measured the heart cells’ response to record how ions flowed into and out of the heart cells to identify the specific proteins in the excitation-contraction pathway that were affected by crude oil chemical components.
Fabien Brette, a research associate in Block’s lab and lead author on the study said the scientists looked at the function of healthy heart cells in a laboratory dish and then used a microscope to measure how the cells responded when crude oil was introduced.
“The normal sequence and synchronous contraction of the heart requires rapid activation in a coordinated way of the heart cells,” Block said. “Like detectives, we dissected this process using laboratory physiological techniques to ask where oil was impacting this vital mechanism.”
The Haisla Nation response to the federal government’s request for consultation on the Joint Review Panel report on the Northern Gateway lists what the First Nation sees as flaws in the panel’s assessment of the project. (The Haisla filed their first list of flaws in the JRP in a court challenge).
In the response, seen by Northwest Coast Energy News, the Haisla are objecting to both the government’s and the JRP’s attitude toward the idea of consultation as well as some of the specific findings by the panel. The Haisla also fault the JRP process for refusing to take into consideration reports and studies that were released after the evidentiary deadlines.
Overall, the Haisla say
The JRP report is written in a way that prevents an assessment of how or whether the JRP considered Haisla Nation concerns and of how whether the JRP purports to address the Haisla Nation’s concerns. Further the JRP Report is lacking n some of the fundamental justification required to understand how arrived at its recommendations.
So what are the Haisla concerns?
In the document filed with the Canadian Environmental Assessment Agency, the Haisla say:
The proposed project carries with it an inordinate amount of risk to Haisla Nation Territory. The Haisla Nation is being asked to play host to this proposed project, despite the risk the proposed project poses to the land waters and resources relied on by the Haisla Nation for sustenance and cultural heritage. The risk includes a huge risk to Haisla Nation aboriginal rights to trap, hunt and fish, to gather seafood and gather plant materials. It could result in significant damage to the Haisla Nation cultural heritage—its traditional way of life…..
The terminal site is one of the few areas suitable for terminal development in our territory. It is also home to over 800 Haisla Nation Culturally Modified Trees (CMTs). Northern Gateway proposes to irrevocably alter the land, the use of the land and access to this land for the duration of the proposed project, which is anticipated to be at least 80 years. This irrevocable alteration includes the felling of our CMTS….
By seeking to use Haisla Nation aboriginal title land for the proposed project, Northern Gateway will be effectively expropriating the economic value of this land. Northern Gateway is proposing to use Haisla Nation aboriginal title land for a project with no benefit to the Haisla Nation and which is fundamentally at odds with Haisla Nation stewardship principles.
Obstructed clear understanding
The Haisla say that “Canada has failed to adhere is own framework” for the JRP because in the Aboriginal Consultation Framework says “Federal departments will be active participants in the JRP process to ensure the environmental assessment and consultation record, is as accurate and complete as possible.”
The Haisla say “Canada provided limited written evidence to the JRP” and goes on to say that the “federal governments not only failed to provide relevant information but also obstructed a clear understanding of project impacts.”
Among the evidence relevant to Northern Gateway that the federal government was “unable or unwilling to provide” includes:
Natural Resources had expertise on acid rock damage and metal leaching but did not include evidence on that in their evidence
Fisheries and Oceans did not have a mandate to conduct an assessment of the potential toxicological effects of an oil spill.
Environment Canada did not review or provide information on the spills from pipelines.
The federal government witnesses were unable to answer questions about the toxicity of dispersant.
Environment Canada was asked if it had studies of the subsurface currents and the movement of submerged oil. Environment Canada told the JRP did not measure hydrodynamic data but relies on DFO. DFO cold not provide any witnesses to the JRP with expertise on subsurface currents.
In the formal response on the JRP report, Haisla also say:
The JRP has concluded that the risk of a large spill form the pipeline in the Kitimat River Valley is not likely, despite very significant information gaps relating to geohazards, leak detection and spill response.
The JRP has concluded that a large spill would result in significant adverse environmental effects. However, the JRP appears to base a finding that these effects are unlikely to occur on an unreasonable assumptions about how widespread the effects could be or how long they would last. The JRP has not considered the extent to which a localized effect could impact Haisla Nation.
The JRP relies on the concept of “natural recovery” as mitigation of significant adverse effects. The Haisla Nation asked the JRP to compel information from Northern Gateway about the applicability of its evidence to species found in Haisla National Territory. The JRP, however, refused to compel this evidence from Northern Gateway.
The JRP has accepted at face value that Northern Gateway would shut down its pipeline within 13 minutes in the event of a rupture and has failed to consider the effects of a large spill that is not detected with this timeframe through the control centre (or was in the case of Kalamazoo, is detected by the control centre but is systematically mischaracterized and ignored).
As part of the consultation process the Haisla want 22 changes to the JRP report, changes which echo the Haisla Final Written Argument that was filed at the end of the hearings.
It says:
The Panel should find that potential impacts to asserted Haisla Nation aboriginal rights and title from the proposed project are such that project cannot be found to be in the public interest in the absence of meaningful consultation… The current status of engagement and the federal government imposition of a 6-month time limit to complete consultation raise serious concerns that meaningful consultation will not be possible. Therefore the proposed project is not in the public interest.
Among the others are:
The JRP should have determined the significant of adverse effects to rare ecological communities that cannot mitigated.
The JRP should have provided more information to allow a reasonable assessment of the risk of a spill from the pipelines.
The JRP would have considered all factors to contribute to the risk of a spill.
The JRP should have found that Northern Gateway’s assessment of the toxicity of an oil spill because it did not consider the full range of products to be shipped nor did it consider the potential pathways of the effect of a toxic spill, whether from a pipeline, at the marine terminal or in the case of a tanker spill
The evidence had not demonstrated that Northern Gateway’s spill response would be able to mitigate the effects of a spill either at the pipeline, at the Kitimat marine terminal or from a tanker spill.
The JRP did not consider the impact of the Kitimat Marine Terminal on their cultural and archaeological heritage, including culturally modified trees.
Skeena Bulkley Valley MP Nathan Cullen says at least two of the Northern Gateway Joint Review Panel’s 209 conditions may already be outdated.
In a news release January 15, 2013, Cullen said, “The requirement of $950 million in spill insurance was recently called into question as reports surfaced of cleanup costs at the sites of Enbridge’s 2010 Michigan spill surpassing $1.035 billion.”
Cullen is referring to a study by Environment Canada Emergencies Science and Technology,Fisheries and Oceans Canada Centre for Offshore Oil, Gas and Energy Research and Natural Resoures Canada on bitumen that was completed in November and released this week.
The study found
. Like conventional crude oil, both diluted bitumen products floated on saltwater (free of sediment), even after evaporation and exposure to light and mixing with water;
. When fine sediments were suspended in the saltwater, high-energy wave action mixed the sediments with the diluted bitumen, causing the mixture to sink or be dispersed as floating tarballs;
(The use of the term “tarball” in this report follows convention in the literature and refers to the consistency of floating, heavily-weathered oil. It does not describe the chemical composition of the product.)
. Under conditions simulating breaking waves, where chemical dispersants have proven effective with conventional crude oils, a commercial chemical dispersant (Corexit 9500) had quite limited effectiveness in dispersing dilbit;
. Application of fine sediments to floating diluted bitumen was not effective in helping to disperse the products;
. The two diluted bitumen products display some of the same behaviours as conventional petroleum products (i.e. fuel oils and conventional crude oils), but also significant differences, notably for the rate and extent of evaporation.
The Panel acknowledges the variety of opinions from experts regarding the behavior and fate of oil spilled in aquatic environments. These experts generally agreed that the ultimate behavior and fate of the oil would depend on a number of factors, including the volume of oil spilled, the physical and chemical characteristics of the product, and the environmental conditions at the time.
The Panel finds that likely oil behaviour and potential response options can be predicted from knowledge of the type of oil spilled and its physical and chemical characteristics. Details of oil behaviour and response options cannot be specified until the actual circumstances of a spill are known.
The Panel is of the view that, if placed along a spectrum of: tendency to submerge; persistence; and recovery difficulty, dilbit would be on the higher end of the spectrum, similar to other heavy oil products.
The Panel accepts evidence from previous spills showing that, in response to circumstances at the time, the behaviour of heavier oils, including conventional oils and synthetic crudes, can be dynamic. Some oil floats, some sinks, and some is neutrally buoyant and subject to submergence and overwashing.
Although the project would transport different types of oil, the majority of the evidence presented during the hearing process focussed on whether dilbit is likely to sink when spilled in an aquatic environment. In light of this, the Panel has chosen to focus its views on dilbit. The Panel heard that the fate and behaviour of dilbit has not been studied as much as that of other oils.
Although there is some uncertainty regarding the behavior of dilbit spilled in water, the Panel finds that the weight of evidence indicates that dilbit is no more likely to sink to the bottom than other heavier oils with similar physical and chemical properties.
The Panel finds that dilbit is unlikely to sink due to natural weathering processes alone, within the time frame in which initial, on-water response may occur, or in the absence of sediment or other particulate matter interactions. The Panel finds that a dilbit spill is not likely to sink as a continuous layer that coats the seabed or riverbed.
“It hasn’t even been a month since the JRP released their 209 conditions, and it seems like we’re already seeing some of them become obsolete,” Cullen said.
“Throughout the review process, the JRP continually ignored the situation in Michigan as it unfolded before our eyes. They saw the spill caused by Enbridge’s negligence, which was worsened by Enbridge’s incompetence, and how it brought untold damage to the local ecosystem and cost over $1 billion US. But the 209 conditions didn’t reflect what we learned about Enbridge’s history or its culture, or what we’ve learned about diluted bitumen at all.”
The Joint Review process was set up to deliver a positive verdict, according to Cullen, regardless of what the real life case studies in Michigan had already shown. “To say that it won’t cost as much – if not more – to respond to a spill in a remote corner of northwestern BC during winter than it was in Michigan in the middle of July is ridiculous,” Cullen said.
“What’s even more astonishing is that we asked repeatedly for these studies on the behaviour of diluted bitumen in the marine environment to be part of the Joint Review Panel’s assessment. That the government waited until after the JRP had given its conditional yes to release these findings is not only appalling but also highly suspect.
Cullen says there are two key questions that the Harper government now must answer. “What kind of protection is the government providing when it lowballs on the insurance for oil spills? And what kind of oversight is it giving Canadians when the verdict is given before the evidence is released?”
The costs for Enbridge to clean up the 2010 Marshall, Michigan oil spill now far exceeds the maximum estimate that the Joint Review Panel gave for a major spill on the Northern Gateway Pipeline and also exceeds the amount of money the JRP ordered Enbridge to set aside to deal with a spill. Enbridge’s cleanup costs have also now edged past the higher liability amount requested by the Haisla Nation.
According to the US firm Enbridge Energy Partners’ filing with the United States Securities and Exchange Commission, as of September 30, 2013, the cost of cleanup was $1.035 billion US, not including possible additional fines and penalties that might be imposed by US authorities in the future.
In its decision, the Joint Review Panel estimated the cost a major oil spill from the Northern Gateway project would be about $693 million. As part of the 209 conditions, the JRP ordered Enbridge to set aside “financial assurances” totaling $950 million.
Note all costs in this article are for a pipeline breach. The Joint Review Panel had different estimates for a tanker spill and the liability rules for marine traffic are different from pipelines.
In its filing for the third quarter of 2013, with the SEC, Enbridge Energy Partners say that the cost up until September 2013 had “exceed[ed] the limits of our insurance coverage.” The same filing says that Enbridge is in a legal dispute with one its insurers.
Lakehead Line 6B Crude Oil Release
We continue to perform necessary remediation, restoration and monitoring of the areas affected by the Line 6B crude oil release. All the initiatives we are undertaking in the monitoring and restoration phase are intended to restore the crude oil release area to the satisfaction of the appropriate regulatory authorities.
As of September 30, 2013, our total cost estimate for the Line 6B crude oil release is $1,035.0 million, which is an increase of $215.0 million as compared to December 31, 2012. This total estimate is before insurance recoveries and excluding additional fines and penalties which may be imposed by federal, state and local governmental agencies, other than the Pipeline and Hazardous Materials Safety Administration, or PHMSA, civil penalty of $3.7 million, we paid during the third quarter of 2012. On March 14, 2013, we received an order from the EPA, or the Environmental Protection Agency, which we refer to as the Order, that defined the scope which requires additional containment and active recovery of submerged oil relating to the Line 6B crude oil release. We submitted our initial proposed work plan required by the EPA on April 4, 2013, and we resubmitted the workplan on April 23, 2013. The EPA approved the Submerged Oil Recovery and Assessment workplan, or SORA, with modifications on May 8, 2013. We incorporated the modification and submitted an approved SORA on May 13, 2013. The Order states that the work must be completed by December 31, 2013.
The $175.0 million increase in the total cost estimate during the three month period ending March 31, 2013, was attributable to additional work required by the Order. The $40.0 million increase during the three month period ending June 30, 2013 was attributable to further refinement and definition of the additional dredging scope per the Order and associated environmental, permitting, waste removal and other related costs. The actual costs incurred may differ from the foregoing estimate as we complete the work plan with the EPA related to the Order and work with other regulatory agencies to assure that our work plan complies with their requirements. Any such incremental costs will not be recovered under our insurance policies as our costs for the incident at September 30, 2013 exceeded the limits of our insurance coverage.
According to the SEC filing, the breakdown of costs include $2.6 million paid to owners of homes adversely impacted by the spill.
Despite the efforts we have made to ensure the reasonableness of our estimates, changes to the recorded amounts associated with this release are possible as more reliable information becomes available. We continue to have the potential of incurring additional costs in connection with this crude oil release due to variations in any or all of the categories described above, including modified or revised requirements from regulatory agencies in addition to fines and penalties as well as expenditures associated with litigation and settlement of claims.
The material components underlying our total estimated loss for the cleanup, remediation and restoration associated with the Line 6B crude oil release include the following: (in millions)
Response Personnel & Equipment $454
Environmental Consultants $193
Professional, regulatory and other $388
Total $ 1,035
For the nine month periods ended September 30, 2013 and 2012, we made payments of $62.3 million and $120.9 million, respectively, for costs associated with the Line 6B crude oil release. For the nine month period ended September 30, 2013, we recognized a $2.6 million impairment for homes purchased due to the Line 6B crude oil release which is included in the “Environmental costs, net of recoveries” on our consolidated statements of income. As of September 30, 2013 and December 31, 2012, we had a remaining estimated liability of $265.9 million and $115.8 million, respectively.
As for insurance, Enbridge Energy Partners say:
The claims for the crude oil release for Line 6B are covered by the insurance policy that expired on April 30, 2011, which had an aggregate limit of $650.0 million for pollution liability. Based on our remediation spending through September 30, 2013, we have exceeded the limits of coverage under this insurance policy. During the third quarter 2013, we received $42.0 million of insurance recoveries for a claim we filed in connection with the Line 6B crude oil release and recognized as a reduction to environmental cost in the second quarter of 2013. We recognized $170.0 million of insurance recoveries as reductions to “Environmental costs, net of recoveries” in our consolidated statements of income for the three and nine month periods ended September 30, 2012 for the Line 6B crude oil release. As of September 30, 2013, we have recorded total insurance recoveries of $547.0 million for the Line 6B crude oil release, out of the $650.0 million aggregate limit. We expect to record receivables for additional amounts we claim for recovery pursuant to our insurance policies during the period that we deem realization of the claim for recovery to be probable.
In March 2013, we and Enbridge filed a lawsuit against the insurers of our remaining $145.0 million coverage, as one particular insurer is disputing our recovery eligibility for costs related to our claim on the Line 6B crude oil release and the other remaining insurers assert that their payment is predicated on the outcome of our recovery with that insurer. We received a partial recovery payment of $42.0 million from the other remaining insurers and have since amended our lawsuit, such that it now includes only one insurer. While we believe that our claims for the remaining $103.0 million are covered under the policy, there can be no assurance that we will prevail in this lawsuit.
The Joint Review, Enbridge and Michigan
The Joint Review Panel based its finding on the Marshall, Michigan spill on the figure of $767 million from the summer of 2012 –again showing the limitations of the JRP’s evidentiary deadlines since the costs are now much higher.
The JRP quoted Enbridge as saying:
Northern Gateway considered the high costs of the Marshall, Michigan spill, which were at least $252,000 per cubic metre ($40,000 per barrel), to be an outlier or a rare event because the spill occurred in a densely populated area, because the pipeline’s response time was abnormally long, and because there was the prospect of potentially lengthy legal proceedings.
Enbridge assured the JRP that the corporate culture and management changes and equipment upgrades since the Marshall, Michigan spill lowered that chances of a similar event.
The company based its models for the JRP on much smaller spills, including one spill at Lake Wabamun, Alberta from a train not a pipeline (Vol. 2 p 357)
Enbridge’s risk assessment did not “generate an estimate of economic losses caused
by a spill.”
The JRP says Northern Gateway relied on its analysis of literature, and spill events experienced by Enbridge and other liquid hydrocarbon carriers in Alberta and British Columbia. After assessing all of this information, Northern Gateway regarded the high costs of a cleanup as “conservative”–meaning the company expects costs to be lower than its estimates in evidence before the JRP.
In Northern Gateway’s view the most costly pipeline spill incident would be a full-bore oil pipeline rupture, with an estimated cost of $200 million, and an extremely low probability of occurrence.
Haisla evidence
In their evidence, the Haisla (and other First Nations and intervenors) were doubtful about Northern Gateway’s assurances. The Haisla asked that Enbridge have a minimum of $1 billion in liability, an amount Enbridge has now exceeded in Michigan.
Haisla Nation estimated the cost of damage to ecosystem services because of a terrestrial oil spill from Northern Gateway’s pipeline would be in the range of $12,000 to $610 million for a 30-year period.
The Haisla’s cost estimates were based on values for environmental goods and services and probabilities of spills that were independent of Northern Gateway’s parameters for estimating oil spill costs. In contrast to Northern Gateway’s estimated spill frequency and costs, the Haisla predicted that spills would occur more often and placed a higher value on damages to environmental goods and services.
Haisla Nation argued that Northern Gateway overestimated its ability to detect and respond to a spill. In the Haisla’s view this resulted in the cost of a spill and the requisite financial assurances being understated. Haisla cited several factors, including: remote location, limited access, challenging terrain, seasonal conditions, and river flow conditions that would cause the cost of cleaning up a spill in the Kitimat River valley to be significantly greater than the costs associated with Enbridge’s Marshall, Michigan spill.
For these reasons, Haisla proposed that Northern Gateway should be required to obtain a minimum of $1 billion of liability coverage through insurance and financial assurances. Haisla said that Northern Gateway should file annually the report from an independent third party assessing the financial assurances plan. (Vol 2 p359)
In response Northern Gateway said:
Northern Gateway said that Haisla’s findings were based on a number of fundamental methodological flaws and a lack of probability analysis to support the high frequency of occurrence of oil spill events. Northern Gateway argued that Haisla’s estimates of ecosystem service values were inflated because they were based on values from unrelated studies. In Northern Gateway’s view, Haisla relied on high passive use values that were not justified.
JRP ruling
As it has in most of its decision, the JRP accepted Northern Gateway’s evidence, including its explanation of the Marshall, Michigan spill and then went on to base its spill cost estimates not on a pipeline breach but on the 2005 railway spill at Lake Wabumum, near White Sands, Alberta.
The Panel accepts that the cleanup costs for the Marshall, Michigan spill were orders of magnitude higher because of the extended response time. In this application, the Panel accepts Northern Gateway’s commitment to complete the shutdown in no more than 13 minutes after detection. For this reason the Panel did not use the Marshall spill costs in its calculations. The spill volume and the resulting costs are directly dependent on the Northern Gateway’s control room staff and the pipeline control system fully closing the adjacent block valves no longer than 13 minutes from the detection of an alarm event, as well as the amount of oil which would drain out of the pipeline after valve closure due to elevation differences.
The Panel decided on a total unit cost of $138,376 per cubic metre ($22,000 per barrel). This is midway between the unit cost of $88,058 per cubic metre ($14,000) per barrel proposed by Northern Gateway and the unit cost of $188,694 per cubic metre ($30,000 per barrel) for the Lake Wabamun spill. It is about one-half of the Marshall spill’s unit cost. Giving weight to the Lake Wabamun costs recognizes actual costs experienced in a Canadian spill and the greater costs of spills in high consequence areas. In these areas, individuals, populations, property, and the environment would have a high sensitivity to hydrocarbon spills. The deleterious effects of the spill would increase with the spill volume, the extent of the spill, and the difficulty in accessing the spill area for cleanup and remediation.
Using these spill volume and unit cost values in the calculation below, the Panel estimated the total cost of a large spill could be $700 million. Total cost of a spill = 31,500 barrels x $22,000 per barrel = $693 million, or $700 million when rounded up.
(p362)
The Panel based the financial assurances requirements for Northern Gateway on a spill with a total estimated cost of $700 million and directs Northern Gateway to develop a financial assurances plan with a total coverage of $950 million that would include the following components:
i. Ready cash of $100 million to cover the initial costs of a spill;
ii. Core coverage of $600 million that is made up of stand-alone, third party liability insurance and other appropriate financial assurance instruments, and
iii. Financial backstopping via parental, other third party guarantees, or no fault insurance of at least $250 million to cover costs that exceed the payout of components i. and ii.
The financial backstopping would be available to fill the gap if the spill volumes or unit costs were under-estimated or if the payout from the core coverage would be less than 100 per cent.
The Panel noted that:
The evidence indicates that there is some probability that a large oil spill may occur at some time over the life of the project. In these circumstances the Panel must take a careful and precautionary approach because of the high consequences of a large spill. The Panel has decided that Northern Gateway must arrange and maintain sufficient financial assurances to cover potential risks and liabilities related to large oil spills during the operating life of the project.
Northern Gateway committed to investing $500 million in additional facilities and mitigation measures such as thicker wall pipe, more block valves, more in-line inspections, and complementary leak detection systems. This initiative should enhance the safety and reliability of the system and help reduce and mitigate the effects of a spill, but it would not eliminate the risk or costs of spills. This initiative is not a direct substitute for third party liability insurance and does not eliminate the need for liability insurance or any other form of financial assurance to cover the cost of a spill. (p 361)
So the JRP decision comes down to this, if you accept Northern Gateway’s position that pipeline spills are rare and mostly small, then the company has the financial resources to cover the damage. If, however, Northern Gateway is wrong and the costs of a pipeline cleanup exceed the $950 million required by the Joint Review Panel, as has happened in Michigan, then those JRP conditions are already obsolete.
(Northwest Coast Energy News encourages all readers to read the complete JRP report and SEC filing since space and readability does not permit fully quoting from the report)
Enbridge has missed the US Environmental Protection Agency’s deadline to clean up parts of the Marshall, Michigan bitumen spill by December 31, 2013.
Local television news, WOOD-TV says the EPA is now considering “enforcement options.”
The EPA had already granted Enbridge a 10 month extension that the company requested in March, 2013, setting the new December deadline.
In November, Enbridge requested a second extension. The EPA denied that request.
From the EPA letter it appears that, as in previous years, Enbridge is trying to avoid continuing clean up work into the winter. The EPA rejects that position, telling Enbridge it shouldn’t wait until the spring run off could spread the sunken bitumen.
The EPA says that beginning in March, 2013, “Enbridge has successfully removed oil and sediment from two of the three major impoundment areas identified in the order and from several smaller sediment trap locations.”
The letter to Enbridge, from Jeffrey Kimble, Federal On-Scene Coordinator denying the extension is another scathing indictment of Enbridge’s attitude toward the public and the cleanup, citing Enbridge failing to prepare “adequate contingency plans,” by failing to recognize the “serious opposition” the dredging plans.
Although the EPA had told Enbridge to consider alternative plans—and Enbridge claimed it did that—the EPA found the Enbridge’s own logs showed the company didn’t start considering alternatives until it was obvious that Comstock Township would reject their dredging plans.
The EPA letter also reveals that once again Enbridge is reluctant to do further cleanup work during the Michigan winter. The EPA rejects that stance, saying that “Removal of oiled sediments prior to the spring thaw will lessen the potential oiled sediment transport in the spring to Morrow Lake via increased river velocities from rain and ice melt.”
Although we recognize that the work required by the Order is unlikely to be completed by December 31, 2013, U.S. EPA believes that had Enbridge taken appropriate steps earlier as requested, it would not require an extension now. In particular, U.S. EPA believes that Enbridge has continuously failed to prepare adequate contingency plans for a project of this nature. For example, U.S. EPA acknowledges that failure to obtain a site plan approval for use of the CCP property for a dredge pad was a setback in the timely completion of the work in the Delta.
However, Enbridge failed to prepare any contingency plans recognizing the possibility of such an occurrence. Enbridge has known since at least the middle of July 2013 that there was serious opposition to its proposed use of the CCP property. When it became clear in August 2013 that opposition to the site use might delay the project, U.S. EPA directed Enbridge to “conduct a more detailed review of your options in short order.”
Although your letter claims that Enbridge “has considered such alternatives,” your logs indicate that Enbridge did not hold initial discussions with the majority of these property owners until long after the final decision to abandon plans for use of the CCP property. These contact logs do not demonstrate that Enbridge fully explored and reviewed alternative options in a timely manner so as to avoid delay in completion of the work. Although Enbridge claims that use of identified alternative properties would be denied by Comstock Township, Enbridge did not present any site plans to the Township for approval (other than use of the county park for staging of frac tanks). To the extent that any of Enbridge’s contingency plans include the use of land for dredge pads, U.S. EPA believes that Enbridge should begin multiple submissions for property use until one is accepted….
Enbridge claims that it cannot install winter containment in the Delta to prevent the potential migration of sediments to the lake. To support that claim, Enbridge has attached a letter from STS directing Enbridge to remove anchors and associated soft containment during winter monthsas these structures could damage STS’s turbines. However, none of the correspondence provided by Enbridge discusses the use of more secure containment methods, such as metal sheet piling, which may not pose the same risks as soft containment structures. Enbridge should consider using sheet piling to construct cells which would both allow winter work and contain the sediment during that work. Enbridge should therefore try to obtain access from STS for this specific work, and for other appropriate work, for the winter timeframe. Use of sheet pile cells would allow continued operations during the winter, especially in the southern zone of the Delta outside of the main river channel. Removal of oiled sediments prior to the spring thaw will lessen the potential oiled sediment transport in the spring to Morrow Lake via increased river
velocities from rain and ice melt.
Finally, U.S. EPA is unwilling to allow Enbridge to wait until after the likely spring high
velocity river flush to reinstall the E-4 containment structures. U.S. EPA has reviewed Enbridge’s modeling, which Enbridge claims supports its requested timeline, and has found it incomplete. The model has not incorporated, and does not match, field observation of flow velocities and water levels and their potential to impact upstream critical structures if containment is in place. Moreover, U.S. EPA completely disagrees with Enbridge’s assertion that there is no evidence of migration of submerged oil during high flow events. The results of three years of poling and sheen tracking demonstrate that Line 6B oil is mobile during periods of
high flow. Now that Enbridge has a five year permit from MDEQ for the E-4 containment system, U.S. EPA reiterates that this containment must be in place immediately upon thawconditions in the spring….
Although Enbridge’s proposed two phase approach may have components that can be incorporated into a final plan, it should not be considered the approved way forward. U.S. EPA believes that pausing the work cycle until new poling can be done in June or July of 2014 could again result in a wasted construction season in the Delta. Enbridge should consider and utilize a combination of techniques in the plan. For example, several dredge pad sites have been identified by Enbridge. Enbridge should obtain approval for one of these sites, or a combination of smaller sites, so as to support hydraulic dredging in conjunction with the current approved
approach and any potential dry excavation techniques. Enbridge should also consider other winter work techniques, such as cell build out and dewatering in the Delta via sheet piling.
As always, U.S. EPA will continue to work with Enbridge to develop adequate plans and complete the work required by the Order. However, nothing in this letter excuses any noncompliance with the Order nor does it serve as the granting of any extension to any deadline in the Order. U.S. EPA reserves all its rights to pursue an enforcement action for any noncompliance with the Order.
The EPA letter also calls into question the ruling of the Joint Review Panel on the Enbridge Northern Gateway. The JRP accepts, without question, Enbridge’s assurances that the company has changed its attitude and policies since the long delay in 2010 in detecting the pipeline rupture in Marshall, Michigan.
The JRP, on the other hand, accepts, without question, Enbridge’s assurances that it has expertise in winter oil recovery from a pipeline spill.
Parties questioned Northern Gateway about locating and recovering oil under ice. Northern Gateway said that Enbridge conducts emergency exercises in winter and that Northern Gateway would learn from those experiences.
Northern Gateway outlined a number of oil detection techniques including visual assessment (at ice cracks and along the banks), drills, probes, aircraft, sniffer dogs, and trajectory modelling. It said that, once located, oil would be recovered by cutting slots into the ice and using booms, skimmers, and pump systems to capture oil travelling under the ice surface.
The company said that oil stranded under ice or along banks would be recovered as the ice started to melt and break up. It discussed examples of winter oil recovery operations during Enbridge’s Marshall, Michigan incident, and said that operational recovery decisions would be made by the Unified Command according to the circumstances.
Northern Gateway said that equipment caches would be pre-positioned at strategic locations, such as the west portal of the Hoult tunnel. It said that decisions regarding the location or use of pre-positioned equipment caches would be made during detailed design and planning, based on a number of considerations including, but not limited to, probability of a spill, access, site security,
environmental sensitivities, and potential for oil recovery at the response site.
(vol 2 page 153)
In its ruling, the Joint Review Panel said
The Panel finds that Northern Gateway’s extensive evidence regarding oil spill modelling, prevention, planning, and response was adequately tested during the proceeding, and was credible and sufficient for this stage in the regulatory process.
Parties such as the Province of British Columbia, Gitxaala Nation, Haisla Nation, and Coalition argued that Northern Gateway had not provided enough information to inform the Panel about proposed emergency preparedness and response planning. The Panel does not share this view.
Northern Gateway and other parties have provided sufficient information to inform the Panel’s views and requirements regarding malfunctions, accidents, and emergency preparedness and response planning at this stage of the regulatory process.
Many parties said that Northern Gateway had not demonstrated that its spill response would be “effective.” Various parties had differing views as to what an effective spill response would entail.
The Panel is of the view that an effective response would include stopping or containing the source of the spill, reducing harm to the natural and socio-economic environment to the greatest extent possible through timely response actions, and appropriate follow-up and monitoring and long-term cleanup. Based on the evidence, in the Panel’s view, adequate preparation and planning can lead to an effective response, but the ultimate success of the response would not be fully known
until the time of the spill event due to the many factors which could inhibit the effectiveness of the response. The Panel finds that Northern Gateway is being proactive in its planning and preparation for effective spill response….
The Panel is of the view that an effective response does not guarantee recovery of all spilled oil, and that that no such guarantee could be provided, particularly in the event of a large terrestrial, freshwater, or marine spill.
The oil spill preparedness and response commitments made by Northern Gateway cannot ensure recovery of the majority of oil from a large spill. Recovery of the majority of spilled oil may be possible under some conditions, but experience indicates that oil recovery may be very low due to factors such as weather conditions, difficult access, and sub-optimal response time, particularly for large marine spills. …
To verify compliance with Northern Gateway’s commitments regarding emergency preparedness and response, and to demonstrate that Northern Gateway has developed appropriate site-specific emergency preparedness and response measures, the Panel requires Northern Gateway to demonstrate
that it is able to appropriately respond to an emergency for each 10-kilometre-long segment of the pipeline.
The Panel notes the concerns of intervenors regarding Northern Gateway’s ability to respond efficiently and effectively to incidents in remote areas, and its plan to consider this during detailed design and planning. The Panel finds that Northern Gateway’s commitment to respond immediately to all spills and to incorporate response time targets within its spill response planning is sufficient to
address these concerns. Northern Gateway said that its emergency response plans would incorporate a target of 6 to 12 hours for internal resources to arrive at the site of a spill. It also said that it would target a response time of 2 to 4 hours at certain river control points.
The Panel agrees with Northern Gateway and several intervenors that access to remote areas for emergency response and severe environmental conditions pose substantial challenges. The Panel notes that the company has committed to develop detailed access management plans and to evaluate contingencies where timely ground or air access is not available due to weather, snow, or other logistic
or safety issues.
Despite the EPA letter (which admittedly was released long after the JRP evidentiary deadline) that shows that Enbridge did not consult the people of Comstock Township, Michigan, the JRP says
The Panel accepts Northern Gateway’s commitment to consult with communities, Aboriginal groups, and regulatory authorities. The objective of this consultation is to refine its emergency preparedness and response procedures by gaining local knowledge of the challenges that would be present in different locations at different times of the year
(Vol 2 p 165-167)