Category: remediation

Kitimat Votes: 25th anniversary of Exxon Valdez disaster looms over Northern Gateway plebiscite

On March 24, 1989, the tanker Exxon Valdez plowed into Bligh Reef in Alaska’s Prince William Sound,  spilling 260,000 to 750,000 barrels or 41,000 to 119,000 cubic metres of crude oil.

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.

 

Related: What the Joint Review Panel said about the Exxon Valdez disaster

A local daily newspaper, The Anchorage Daily News sums it all up:

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.

Britain’s Sunday Telegraph headlined: Exxon Valdez – 25 years after the Alaska oil spill, the court battle continues

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.

The Sunday Telegraph chronicles which species have recovered in Exxon Valdez: Animal populations in Prince William Sound, Alaska

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.

Why The Exxon Valdez Spill Was A Eureka Moment For Science

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.

(NPR also reports on the The Lingering Legacy Of The Exxon Valdez Oil Spill)

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.

Scientific American online and other media outlets reported 25 Years after Exxon Valdez Spill, Sea Otters Recovered in Alaska’s Prince William Sound quoting a report from the U.S. Geological Survey that said that spill killed 40 percent of the 6,500 sea otters living in the sound and more in 1990 and 1991.USGS reported that the main sea otter population in the sound was 4,277 in 2013.

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.

 

Anniversary stories (as of March 23, 2000 PT)

Alaska Media

Valdez Star
First Associated Press story on Exxon Valdez Oil Spill reprinted

KTUU

Exxon Valdez Oil Spill 25th Anniversary: Alaskans Remember

Alaska Dispatch

Exxon Valdez oil lingers on Prince William Sound beaches; experts debate whether to clean it up

While Alaska’s Prince William Sound is safer, questions linger about preventing oil spills

Recalling the shock and sadness of Exxon Valdez spill 25 years ago

How the Exxon Valdez spill gave birth to modern oil spill prevention plans

Seward City News
25 years later Exxon Valdez memories still stink

Bristol Bay Times
Exxon lesson: Prevention, RCACs the key to avoiding future disaster

Anchorage Daily News
Red Light to Starboard: Recalling the Exxon Valdez Disaster

Exxon Valdez photogallery

25 years later, oil spilled from Exxon Valdez still clings to lives, Alaska habitat

 

World Media
Al Jazeera
The legacy of Exxon Valdez spill
The tanker ran aground 25 years, but the accident continues to harm the environment and human health

Vancouver Sun
Opinion: Oil spills — the 10 lessons we must learn Reality check: Next incident would ruin coastal economy

Seattle Times

Promises broken by the Exxon Valdez oil spill, 25 years later

SFGate

25 years since the Exxon Valdez spill

CNN
After 25 years, Exxon Valdez oil spill hasn’t ended

Kitmat Votes: What the Joint Review Panel said about the Exxon Valdez disaster

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.

Clio Bay reclamation postponed as new contractor takes over at KM LNG

Marine clay sign Robin Rowland photo
Sign explaining marine clay at the Chevron/ KMLNG Open House, in Kitimat, March 13, 2014. (Robin Rowland/Northwest Coast Energy News)

Studies on the Clio Bay reclamation project have been postponed until the fall while the new prime contractor takes over the Kitimat LNG project.

A spokesperson for Chevron said at the Kitimat LNG open house on Wednesday now that Irving , Texas-based Fluor Corp, in partnership with a joint-venture partner, Japan’s JGC Corp. has won the engineering, procurement and construction contract for the KM LNG project, it will take some time for the new company to be briefed on the Clio Bay project and then begin working with Stantec the environmental contractor on the project. That means that the reclamation project itself will now not likely proceed until spring of 2015.

In community meetings last fall, Chevron had said it expected the preliminary studies to be completed in January or February.

KM LNG, a partnership between Chevron and Apache Corp, took over the Riverlodge Recreation Centre for three days from February 2 to 4, to brief employees and contractors on the transition from KBR Inc., the original prime contractor which lost the bidding for the second stage of the contract to Flour.

KM LNG organized the open house mainly to show what is happening at the old Eurocan site, which is being converted to a work camp for the project.

The Clio Bay project, however, had a prominent place among the panels on display at Riverlodge. In the panels, Chevron says that up to 40 per cent of the Clio Bay bottom is covered with wood debris, at some points, as much as 10 metres deep, meaning a degraded habitat for dungeness crab and eel grass.

As was announced in the fall, Chevron, in partnership with the Haisla Nation, plan to take marine clay from Bish Cove and use it to cover the wood debris to create a new sea bottom. One panel said: “The new layer of marine clay is expected to be colonized by eel grass and by species such as worms, crustaceans, small fish and other sea life that will encourage a more plentiful, healthy ecosystem replacing the degraded ecosystem created by the decomposing wood debris that now covers the ocean floor.”

Chevron sees the project as an example that others could follow. Another panel notes: “Project proponents around the world are moving away from the old practice of dredging and disposing of marine clay. The Clio Bay restoration project would see marine clay used wisely to deliver benefits to the environment, community and culture.”

Work continues on the remediation of the old Eurocan mill site. Chevron and Apache are, in effect, spending millions of dollars to clean up the mess left behind when West Fraser abandoned the mill.

The company has to demolish the old mill and remediate contaminated areas. One of the big challenges is dealing with the old landfill site, which Chevron says has to be brought up to 21st century environmental standards. That includes adding an impermeable lining to the landfill and upgrading the leachate treatment systems.

Cleaning up the mess left by Eurocan will take about five years, according to one of the panels at the Open House. Chevron says that job will improve the environment, where they plan to build a work camp both in the short term and in the long term as work continues.

 

Ottawa’s Northern Gateway consultation with First Nations limited to three simple questions and 45 days: documents

The federal government’s main consultation with First Nations on the Northern Gateway Joint Review Panel report is limited to just three simple questions that had to be answered within 45 days, according to documents seen by Northwest Coast Energy News.

Joint Review Panel cover
Cover of Volume 1 of the Joint Review Panel ruling on Northern Gateway

That despite the fact that the first volume of the JRP report “Connections” is 76 pages and the second volume “Considerations” is 418 pages including the 209 recommendations and appendices and came after two years of hearings and tens of thousands of pages of evidence.

On Dec. 6 and again on Dec. 16, 2013, just prior to the release of the Joint Review Panel report, Brett Maracle, Crown Consultation Coordinator at the Canadian Environmental Assessment Agency for the Northern Gateway project wrote to the First Nations potentially affected by Northern Gateway, saying their response had to be filed within 45 days of the release of the JRP. Since the report was released on December 19, 2013, that made the initial deadline January 31, 2014.

The letter also told the First Nations that if they wanted their positions included in the “Crown Consultation Report” that would be part of the package on Northern Gateway presented to the federal cabinet, that position had to be limited to just two to three pages “given the number of groups involved” with a final deadline of April 16, 2014.

Maracle’s letters used the term Phase IV to define the post JRP consultations, implying there were three earlier stages of consultation, something many First Nations have disputed, especially since the Harper government had earlier maintained that the JRP itself was the constitutionally mandated consultation.

The cabinet has until June 19, 2014, 180 days after the release of the report to approve the issuing of the federal permits for the Northern Gateway project. Consultation with First Nations on projects such as the Northern Gateway is required by the Constitution and has been upheld by the Supreme Court of Canada.

The three questions outlined in the letter were:

  • Does the Report appropriately character the concerns you raised during the JRP process?
  • Do the recommendations and conditions in the Panel Report address some/all of your concerns?
  • Are there any “outstanding” concerns that are not addressed in the Panel Report? If so, do you have recommendations (i.e proposed accommodation measures) how to address them?

Consultation on implementation

The third question appears to confirm what most political observers have said, approval of the Northern Gateway by the Harper cabinet is a a forgone conclusion, since Maracle speaks of “accommodation measures.” When the JRP approved the Northern Gateway project, the panel said that Enbridge’s proposed “mitigation” measures in case of a spill were adequate, something environmental groups and First Nations are now disputing in court.

It appears from the correspondence seen by Northwest Coast Energy News, that the federal government will only consider further specific consultations with First Nations after the approval of the Northern Gateway and only then on the implementation and construction process, rather than consulting on the project as a whole.

The Haisla have filed a document in response to the JRP that notes that

The Haisla Nation needs to understand Canada’s views of the role that future federal decisions might play for the proposed project. In its December 12, 2013 to Mr. Maracle, the Haisla Nation asked the federal government to provide a comprehensive list of the regulatory permits which would be issued the the federal government decision-makers in Haisla Nation Territory in the event the proposed project is approved and describe the consultation process that would occur prior to decisions being on those regulatory permits, within 45 days of the issuance of the JRP Report.

Mr. Maracle’s January 29, 2014 [reply] suggests that the only future federal decisions on the proposed project which may entail consultation are specific watercourse crossing and fish habitat destruction permits issued by Fisheries and Oceans Canada.

Whole-of-government

One of the problems reaching back to long before the Joint Review Panel hearings began is that the Harper government policy was what they called a “whole-of-government” approach in its consultations with First Nations, saying: “The Crown is open to discussing how consultation with the framework provided will be carried out.”

In their repose, the Haisla say the federal government never defined how the “whole-of-government” approach to First Nations was going to work and noted:

What Canada should have realized is that it has a very real obligation to consult with the Haisla Nation at the deepest end of the consultation spectrum that cannot be pigeon-holed into a one size fits all approach.

Further, the term whole-of-government is misleading, as this approach actually prohibits the majority of government from engaging in consultation.

The Haisla then say: “Documents we have obtained under an Access to Information Request clearly indicate individual departments were asked not to communicate directly with the Haisla Nation.”

The response goes on to say:

Further questions at federal government witnesses during the JRP process confirmed that federal departments had not met with the Haisla Nation since the commencement of the JRP process. While these witnesses were reluctant to confirm that they had been prohibited from meeting with us, they repeatedly referred to the “whole-of-government” approach to consultation as their reason for not meeting.

Canada’s “whole-of-government” approach clearly limited engagement to a strict process with no opportunity for real engagement.

Earliest stages

The Haisla are telling the Harper government:

It is clear that the Haisla Nation that we are the very earliest stages of consultation with Canada about the proposed project….It is clear to the Haisla Nation that the 45-day period within which Canada has unilaterally determined face-to-face meetings with all the Aboriginal groups potentially affected by the proposed project will occur is not an adequate amount of time to complete a meaningful consultation process.

 

Related

Haisla ask cabinet to postpone Northern Gateway decision to allow for adequate consultation with First Nations

Haisla consultation reply outlines flaws in Northern Gateway Joint Review report

Haisla response lists evidence rejected by Northern Gateway Joint Review

Haisla consultation reply outlines flaws in Northern Gateway Joint Review report

Haisla NationThe 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.

Related

Ottawa’s Northern Gateway consultation with First Nations limited to three simple questions and 45 days: documents

Haisla ask cabinet to postpone Northern Gateway decision to allow for adequate consultation with First Nations

Haisla response lists evidence rejected by Northern Gateway Joint Review

Haisla response lists evidence rejected by Northern Gateway Joint Review

Members of the Joint Review panel make notes at Kitamaat Village (Robin Rowland)
Members of the Northern Gateway Joint Review Panel, left to right, Kenneth Bateman, chair Sheila Leggett and Hans Matthews make notes at the June 25, 2012 hearings at the Haisla Recreation Centre, Kitamaat Village. A map of Douglas Channel can be seen behind the panel. (Robin Rowland/Northwest Coast Energy News)

The Haisla Nation in their response to the Crown on the Northern Gateway Joint Review Panel details four studies, three Canadian and one American that were released after the Joint Review evidentiary deadline had passed, evidence that the Haisla say should be considered in any consideration of the Northern Gateway pipeline, terminal and tanker project. (The American report from the National Oceanic And Atmospheric Administration was released after the JRP final report)

JRP chair Sheila Leggett’s constant citing of rules of procedure and her stubborn refusal to consider new evidence and studies in a dynamic situation that was changing rapidly was one of the reasons that many people in the northwest said the JRP had lost credibility.

The Haisla say: “It is incumbent upon Canada to consider and discuss the information in these reports as part of a meaningful consultation process…” and then lists “key findings” that have potential impacts on aboriginal rights and title:

The West Coast Spill response for the government of British Columbia which found:

  • Most oil spilled into the marine environment cannot be cleaned up
  • There is a disconnect between planning and actual repose capability
  • Canada’s spill response is “far from world class.”

The Transport Canada Ship Oil Spill Preparedness and Response study:

  • Douglas Channel will go from low risk to high risk for pills if the project goes ahead
  • The study recommends preparation for a “true worst case discharge” rather than “the credible worst case discharge” as proposed by Northern Gateway
  • Canada needed a much more rigorous regulatory regime covering tankers.

The joint federal government technical report on the properties of bitumen from the Canadian Oil Sands:

  • There are uncertainties on how diluted bitumen would behave in a marine environment.
  • Northern Gateway did not provide adequate information about sediment levels to allow for proper study of interaction with diluted bitumen
  • Dispersant may not be effective.
  • Weathered diluted bitumen would “reach densities at which it will sink freshwater without mechanical or physical assistance.”

The US National Oceanic And Atmospheric Administration report on Transporting Alberta Oil sands:

  • Diluted bitumen has “significant differences from conventional crudes.’ (The JRP used conventional crude as a benchmark in its findings)
  • The physical properties of diluted bitumen “fluctuate based on a number of factors.
  • Pipeline operators may not have detailed information related to products in the pipeline at the time of a spill
  • There is a lack of experimental data on the weathering behaviour of oil sands product which limits the ability of spill response organizations “to understand and predict the behaviour and fate of oil sands products in freshwater, estuarine and saltwater environments.”

 
Related

Ottawa’s Northern Gateway consultation with First Nations limited to three simple questions and 45 days: documents

Haisla ask cabinet to postpone Northern Gateway decision to allow for adequate consultation with First Nations

Haisla consultation reply outlines flaws in Northern Gateway Joint Review report

 

Two JRP conditions are already outdated, Cullen says

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.”

The $1.035 billion figure was contained in Enbridge’s American arm, Enbridge Energy Partners, latest filing for the third quarter over 2013 with the US Securities and Exchange Commission.
Cullen went to say that, “The JRP’s order for Enbridge to carry out new research on the behaviour of diluted in bitumen in a marine environment has been questioned following the publication of an Environment Canada study confirming that diluted bitumen will sink in saltwater in high waves and where sediment is present.”

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.

Read the report:Properties, Composition and Marine Spill Behaviour, Fate and Transport of Two Diluted Bitumen Products from the Canadian Oil Sands (pdf)
The Joint Review Panel found that dilbit was “ no more likely to sink to the bottom than other
heavier oils”

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?”

 

Enbridge’s Michigan cleanup costs now exceed JRP pipeline conditions for Gateway, SEC filing shows

NTSB staff examine ruptured pipe
US National Transportation Safety Board staff examine a ruptured pipe from the Enbridge oil spill in August, 2010. The photo was released by the NTSB May 21, 2012. (NTSB)

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.

In its SEC filing, Enbridge says:

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 misses deadline to clean up Michigan’s Morrow Lake; EPA cites reluctance to do winter cleanup

EPA map of Kalamazoo River
EPA map of river closures and dredging operations on the Kalamazoo River during 2013. (EPA)

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 area that Enbridge failed to clean up is known as the Morrow Lake and Morrow Lake Delta. The cleanup in that area was delayed when the Comstock Township planning commission unanimously  denied Enbridge a permit for “dredge pad” after fierce public opposition

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)

EPA letter to Enbridge denying deadline extension  (pdf)

How Gateway’s plans to dredge Douglas Channel show the limitations of the JRP mandate and ruling

(First in series of reports on how the Joint Review Panel report will affect the Kitimat region)

JRP map of blasting on Douglas Channel
Joint Review map of Northern Gateway plans for dredging and blasting on Douglas Channel (JRP)

 

If there is a significant flaw in the Joint Review Panel report on Northern Gateway, it can be found in the panel’s analysis of Enbridge Northern Gateway’s plans to blast and dredge at the proposed Kitimat terminal site.

While the Joint Review Panel does consider what it calls “cumulative effects,” the panel plays down those effects and offers no specifics about interaction between the Northern Gateway project and the two liquified natural gas projects, the KM LNG project at Bish Cove and the BC LNG floating terminal at the old log dump.

It appears the JRP considered the legacy effects of the Rio Tinto Alcan smelter and other Kitimat industries while not taking into consideration future development.

The dredging and blasting planned by Northern Gateway, as Enbridge said in its evidence,  appears to have only a minimal effect on Douglas Channel.

A glance at the map in the Joint Review ruling shows that that the dredging and blasting site is directly opposite Clio Bay, where Chevron, in partnership with the Haisla Nation, plan a remediation project using marine clay from the Bish Cove construction site to cap decades of sunken and rotting logs.

The Clio Bay project was not part of the evidence before the Joint Review Panel, the plans for the project were not formulated until well after the time for evidence before the JRP closed. But those deadlines show one area where the rules of evidence and procedure fail the people of northwestern BC.

The JRP is a snapshot in time and changes in the dynamics of the industrial development in the Kitimat Arm are not really considered beyond the terms of reference for the JRP.

It appears from the report that Enbridge plans to simply allow sediment from the blasting and dredging to float down Douglas Channel, dispersed by the currents and the outflow from the Kitimat River.

Northern Gateway said that dredging and blasting for marine terminal construction would result in a sediment plume that would extend over an area of 70,000 square metres for the duration of blasting activities.

Approximately 400 square metres of the assessed area of the marine terminal is expected to receive more than 1 centimetre of sediment deposition due to dredging. Outside of this area, typical sediment deposition levels alongshore where sediment is widely dispersed (a band approximately 4 kilometres long and 400 metres wide) are very low; in the range of 0.001 to 0.1 centimetres. Dredging and blasting activities are expected to occur over a period of approximately 18 weeks.

Northern Gateway expected most of the sediment plume created by construction activities to be minor in relation to natural background levels.

Northern Gateway would use bubble curtains to reduce pressure and acoustic effects of blasting, and silt curtains to reduce the effect of sedimentation from dredging. It said that bubble curtains are used extensively for other activities, such as pile driving, to reduce the effect of high pressure pulses that can cause injury to fish.

It added that bubble curtains have been tested extensively with blasts, and literature shows they are effective.

Northern Gateway said that physical effects from suspended sediment on marine fish and invertebrates could include abrasion and clogging of filtration mechanisms, which can interfere with ingestion and respiration. In extreme cases, effects could include smothering, burial, and mortality to fish and invertebrates. Direct chemical-related effects of suspended sediment on organisms, including reduced growth and survival, can also occur as a result of the uptake of contaminants
re-suspended by project construction activities, such as dredging and blasting, and as a result ofstorm events, tides, and currents.

The Haisla Nation and Raincoast Conservation objected to Northern Gateway’s figures, noting

Northern Gateway’s sediment and circulation model and its evidence related to contaminated sediment re-suspension at the terminal site. Both parties said that the sediment model was applied for the spring, when the increase in total suspended solids would be negligible compared to background values. In the event of delays, blasting and dredging would likely occur at other times of the year when effects would likely be higher, and these scenarios were not modelled.

The panel’s assessment of the area to be blasted found few species:

Species diversity within Kitimat Arm’s rocky intertidal community is generally low. Barnacles, mussels, periwinkles, and limpets can be found on rocky substrate. Sea urchins, moon snails, sea anemones, sea stars, and sea cucumbers are in shallow subtidal areas. Sandy areas are inhabited by commercially-harvested bivalves such as butter clams and cockles.

Northern Gateway told the JRP that it would “offset” any damage to Douglas Channel caused by the blasting and dredging

Northern Gateway said that construction, operations, and decommissioning of the marine terminal would result in both permanent and temporary alteration of marine fish habitat. Dredging and blasting, and installing physical structures in the water column for the marine terminal would permanently alter marine fish habitat. Based on the current terminal design, in-water site preparation would result in the physical alteration of approximately 1.6 hectares of subtidal marine habitat and 0.38 hectares of intertidal marine habitat. Northern Gateway expected approximately 353 square metres of subtidal marine habitat and 29 square metres of intertidal habitat to be permanently lost.This habitat would be compensated for by marine habitat offsets.

The project’s in-water vertical structures that would support the mooring and berthing structures could create new habitat, offsetting potential adverse effects. The structures may act as artificial reefs, providing marine fish habitat, food, and protection from predation. Although organisms currently inhabiting the work area would be killed, the exposed bedrock would be available for colonization as soon as the physical works are completed.

In its finding on marine sediment, the panel, as it does throughout the ruling, believes that the disruption to the environment caused by previous and ongoing human activity, means that the Northern Gateway Kitimat terminal won’t make that much difference.

Sediment quality in the marine environment is important because sediment provides habitat for benthic aquatic organisms. Northern Gateway’s baseline data for the area immediately surrounding the marine terminal indicated some contamination of water, sediments, and benthic organisms from previous industrial activity. Industrial activities in the Kitimat area have released contaminants through air emissions and effluent discharges since the 1960s. Sources of contaminants to Kitimat Arm
include effluent from a municipal wastewater treatment plant, the Alcan smelter, Methanex Corporation’s methanol plant, and the Eurocan pulpmill, as well as storm water runoff from these operations and the municipality.

Area is largely controlled by natural outflow from the Kitimat River with suspended sediment levels being highest during peak river runoff (May to July, and October) and lowest during winter. Storm events, tides, and currents can also suspend sediments. Levels of total suspended solids fluctuate seasonally and in response to climatic variations, but are generally highest during the summer.

Commercial and recreational vessels currently operating in the area may increase suspended solids by creating water turbulence that disturbs sediments. Given the current sediment contamination levels and the limited area over which sedimentation from construction activities would be expected to disperse, the Panel finds that the risk posed by disturbed contaminated sediment is low. Northern Gateway has committed to monitoring during construction to verify the predicted effects on sediment and water quality for both contaminants and total suspended solids..

The dredging and blasting section of the Joint Review Report is small when compared to the much more extensive sections on pipeline construction and tanker traffic, and the possible effects of a catastrophic oil spill.

Although minor, the marine sediment section exposes the question that was never asked, given the disruptions from years of log dumping at Clio Bay and Minette Bay and the decades of  developments at the mouth of the Kitimat River, and future development from LNG, when do cumulative effects begin to overwhelm? How much is enough? How much is too much? If every project continues to be viewed in isolation, what will be left when every project is up and running?