Ecosystem Injuries from the DeepWater Horizon Blow-out: A Tale of Two Spills Ocean Conservancy – GOMURC Workshop April 2012 Charles H. “Pete” Peterson
Dec 14, 2015
Ecosystem Injuries from the DeepWater Horizon Blow-out:
A Tale of Two Spills
Ocean Conservancy – GOMURC WorkshopApril 2012
Charles H. “Pete” Peterson University of North Carolina at Chapel Hill
DWH Blowout – Two Types of Oil Spills Type I - Familiar Spill
Composite of nearshore oil spillsFate:
Oil rises to the surfaceFloating oil grounds on shores
Effects:Surface organism mortality Intertidal habitats fouledShallow subtidal contaminationSublethal effects induce pop losses
Type II - Deepwater Spill Novel offshore, deep-water
blowout of oil and gasFate:
Extensive fine dispersion of oil & gas via turbulent pressurized injection into cold seawater
Retention in plumes at depthSurfacing and grounding of oilBroad deposition on sea floor
Effects:Surface organism mortality Intertidal habitats fouledBio exposures in water columnWidespread benthic mortalitiesUPINOAA
Type IIType I
well head
dispersant
accumulating oil on sediments
finely dispersed subsurface oil plume
finely dispersed oil/hydrate plume
asphaltines
oil plume
oil slick
1000 m
500 m
200 m
1500 m
1800 m
The Deepwater Horizon Spill
NearshoreEstuaryContinental shelf
Pelagic OceanicNeritic
Epipelagic
Mesopelagic
0 to 200 m
1000 m
4000 m
Bathypelagic
Ph
oti
c A
Ph
oti
c
Benthic
BathyalWind
SheensThick Oil
Dispersant
Turbulent Dispersion
Volatilization
Turbulent Dispersion
Surfacing
Current
Adsorption and Adherence to Particulates
Complex Physics and Chemistry
Oil Spill Oceanography
Legacy of the Exxon Valdez Oil SpillOf all oil spills, EVOS impacts are the most
thoroughly studied in scope, duration, and roles of ecosystem-based interconnectivity of natural resource impacts
Explicit impact studies of EVOS are relevant to the Type I components of DWH (surface and shorelines), but offer only procedural insights to guide impact assessment of DWH Type II components
EVOS helps guide the processes of impact assessment and restoration by example, good and bad
EVOS brings new insights into ecotoxicological mechanisms and processes – new paradigms only slowly incorporated into injury models
Photos: Anchorage Daily News Exxon Valdez Oil Spill = EVOS Deepwater Horizon Spill = DWH
Myths Debunked and Emerging Paradigms Created by EVOS Science
Significant toxicity is not limited to acute exposure to BTEXs, but continues for decades via exposure to buried oil sequestered in biologically accessible, but anoxic reservoirs
Toxicity of chronic exposures to PAHs occurs at ppb concentrations, much lower than the ppm water quality standards (based only on acute exposures to water-soluble fractions from fresh oil)
Clean-up and restoration responses can be more injurious than the oilbenzene, toluene, ethylbenzene, and xylenes = BTEX polycyclic aromatic hydrocarbons
= PAH
Novel Scientific Insights from EVOSSublethal impacts (affecting individual growth,
reproduction, behavior) may have serious effects at the population level and must be incorporated into the injury assessment process
Major physical effects of oil (smothering, fouling of feeding apparatus, etc.) can continue to operate independent of chemical toxicity of the oil
An ecosystem-based approach is critical to account for interactions and indirect effects that ramify through the interaction webs; this coupled with long-term monitoring is the only way to understand some delayed and long-term impacts of the oil spill
Deepwater Horizon TimelineApril 20 – well blow-out and fire @ 21:45 hApril 22 – first surface oil slick detectedMay 1 – surface application of dispersant beganMay 14 – injection of dispersant at well-head beganJuly 15 – oil and gas discharge ended (after 84 d)
Comparative Spill Oil Volumes
DWH: 4.9 million barrels of oil, 14.7 million ft3 of gas 1.8 million gallons of dispersant added
1.07 million gallons at sea surface 0.77 million gallons at the well-head
1.5 to 1.9 x more gas released than oil by mass
8
7
6
5
4
3
2
1
0
Kuwait oil field1991
DWH2010
Ixtoc I1979
Santa Barbara 1969
Exxon1989
4.9
6 to 8
3.5
0.75
0.1
mil
lion
barr
els
of
oil
Natural Resource Injuries from the Type I Portion of the DWH Incident
The “easy” part – long agency (NOAA) experience/skills directly applicable here to surface and shoreline habitat oiling impacts
Potentially trivial compared to novel subsurface ecosystem impacts ?
May form the vast majority of the focus of restoration because:Better capacity to infer injuriesEcosystem values and uses to humans understoodCompensatory restoration is deemed feasiblePolitical pressure for state “wish list” projects
EPA
Press-Register
Type I Injuries: Species Oiled at Sea SurfaceSeabirds found dead in oiled areas in USFWS counts to 12/2011
gulls = 2901 brown pelican = 556 northern gannet = 441 royal tern = 233 black skimmer = 233
Sea turtles – 613 dead (incl. Kemp’s ridleys) in NOAA counts from 4/2010-4/2011
Marine mammals – 452 dolphin strandings in NOAA data base out of 625 total cetacean strandings from 4/2010-1/2012; abnormally high miscarriage rates
Fish –concerns about impacts on early life stages because of dispersed oil in fine droplets is so highly bioavailable and to nearshore demersal fish like killifish in contact with oil
Blue crab and penaeid shrimps – still under study but clearly extensive exposure to oil and dispersants
Floating Sargassum community – high risk and likely injury to habitat provider (plant) and associated fish and wildlife – incl. dead hatchling sea turtles; concern over larval & juvenile bluefin tuna, mahi, cobia, etc.
Reuters
AP
Type I Injuries: Shoreline Habitats Oiled (1053 linear miles)
Coastal marsh – especially margins, where below-ground plant mortality also fostered marsh edge erosion but low total acreage lost
Sandy ocean beaches – coatings of mousse, tarballs, and layers of buried oil at depths in the sand with intense disturbance of clean-up
Seagrass beds – some direct habitat lossOyster reefs – some mortality from smothering plus
possible oyster larval mortality; mass freshwater diversion mortality
Protected mudflats – some loss of benthic invertebrate prey for higher trophic levels
Estuarine muddy bottom and ocean floor – PAH contamination plus persistence of oiled detritus, evident during summer 2011 storms
Type I Injuries: Grounded Oil Effects on Shoreline
SpeciesGround- and low-nesting marsh birds (double jeopardy for
pelicans etc. = feeding at sea + nesting impacts).Fiddler crabs, blue crabs, and marsh nekton, esp. shrimps.Oysters by adult and juvenile mortality, larval losses, and
likely slower growth.Terrapins and marsh mammals.Nekton, including juvenile and resident fishes (killifish), that
use shallow marsh, oyster reef, seagrass habitats.Seaducks, sea turtles, and demersal fishes that eat benthic
invertebrates in shallow estuarine bottom are at risk.
AP
Collateral Injuries: from Response ActionsToxicity from chronic exposure to persistent dispersant -
alone and with oil
Fine-scale chemical dispersal of oil enhanced bio- availability and kept it sub-surface for longer, thereby magnifying impacts to zooplankton, particle feeders
Physical injuries to marsh from boom groundings and vessel groundings while deploying boom
Waterbird mortalities from “booming in” both oil and birds around marsh islands
Habitat and food-web degradation from beach “nourishment”, which kills benthic invertebrates
Oyster mortality from of freshwater diversions
Air pollution and health effects in wildlife and humans from soot creation during at sea burning
AP
Collateral Injuries: from Clean-up EffortsVehicle driving on beaches (especially at night)
destroyed nests, killed nesting birds/chicksBirds and other animals killed during uptake into oil
skimmersConstruction of coastal barrier berms killed benthic food
resources and misguided sea turtles / ground-nesting birds to nest on that rapidly eroding sand
Sea turtle mortalities from intense trawl fishing, perhaps with disabled TEDs, immediately before closures when enforcement attention was diverted
Repeated mortality of benthic invertebrates and consequent loss of prey from demersal surf fishes and shorebirds after beach excavations to remove buried tarballs and oil layers and raking up wrack
U.S. Coast Guard
AP
Injuries: Type II Oil Spill Impacts (Subsurface including Deep Ocean)
By far the hardest aspect of the DWH spill to assess, requiring new research on interdisciplinary oil-spill oceanography
Possibly largest portion of the ecosystem impacts of the hydrocarbon release
Effective restoration depends on scientific advances to understand direct and indirect ecosystem impacts and service losses in meso-pelagic, bentho-pelagic, and deep-bottom communities
Failures by government and industry to conduct necessary science for readiness
NOAA
NOAA
Subsurface Ecosystem Consequences of a Deep-water Blowout
3 broad categories of subsurface impacts from the DWH1. Toxicity of oil and dispersant (includes physical smothering and
fouling) – pelagic particle feeders and all guilds of benthos2. Implications of organic carbon loading (perhaps 0.5-3.0 x annual
production over the spill area) with resultant intense microbial heterotrophic production and CO2 injection into seawater
3. Indirect effects of food web disruption – likely a widespread fracture of the food-chain linkage from particle feeders to higher trophic levels – including (?) species like sperm whales
2 ecological compartments outside familiar scope of NRDA1. pelagic (mostly deep) water column2. deep benthos
Type II Effects of DWH Oil Spill:Glimpses of Pelagic Impacts
Extensive mortality by fouling the feeding and respiratory organs of pelagic particle feeders such as copepods, salps, and appendicularians, thereby fracturing the food chain linkages to higher trophic levels
Massively elevated heterotrophic microbial production and consequent oxygen sags detected in petroleum hydrocarbon plumes trapped at a pycnocline in 800-1,100 m, but oxygen not depleted enough to induce hypoxia
Microbial production has been associated with marine snow and slime that helped aggregate oil droplets with organic particles and induce transport the oil to the deep sea floor
Study of higher trophic levels could integrate impacts to food chains, taking opportunity to use the spill as an oceanographic experiment
The high likelihood of large indirect food-web effects from DWH oil implies that delayed injuries will emerge, detectable only if focused ecosystem-based injury assessments continue over sufficient time
M. Joye
Type II Effects of DWH Oil Spill:Glimpses of Deep Benthos Impacts
Deposition of dark, hydrocarbon-rich sediments mm-cm thick onto sedimentary bottoms appears to have caused widespread mortality of resident soft-bottom benthic invertebrates, perhaps by smothering (Joye)
Some emergent hard-bottom areas exhibit apparent cover by a similar dark material and exhibit mortality of soft corals, sea fans, brittle stars, and other inverts (Fisher)
After the early bloom of heterotrophs, microbial activity now appears grossly suppressed on the sedimentary seafloor
Guiding Principles for GoM Ecosystem Restoration from 2011 Pew Report
Recognizing that past human and natural perturbations have compromised Gulf ecosystem function and resilience
Acknowledging that dramatic environmental change is inevitable and must be integrated into restoration plans
Treating the Gulf as one interconnected network of ecosystems from the shoreline to the deep sea
Realizing that ecosystem productivity, health, and sustainability of the Gulf and human welfare are intrinsically codependent
AP
NCEAS Working Group:Sean Anderson, Gary Cherr, Rich Ambrose, Shelly Anghera, Steve Bay, Michael Blum, Rob Condon, Tom Dean, Monty Graham, Michael Guzy, Stephanie Hampton, Samantha Joye, John Lambrinos, Bruce Mate, Doug Meffert, Sean Powers, Ponisseril Somasundaran, Bob Spies, Caz Taylor, Ron Tjeerdema, Charles Peterson : paper now posted on-line in BioScience May 2012.
Ocean Conservancy Team:Stan Senner, Jeff Short, Chris Haney, Bob Spies, Lisa Suatoni, Paul Kemp, Dennis Kelso, Charles Peterson
Acknowledged Contributors