wetland reclamation in the green zone of alberta · wetland reclamation in the green zone of...
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Wetland Reclamation in the Green Zone of Alberta
Dr. Markus N. Thormann, P.Biol., R.P.Bio., PWS, QWAES
Senior Wetland and Aquatic Ecologist
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2 19-Oct-12
Overview
Physical setting
Background
– Wetland classes
– Peatland vs. wetland
Challenges
– Geotechnical and engineering
– Soil quality
– Water quality and quantity
– Plant communities
Wetland reclamation success stories
Conclusions
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Oil Sands and Peatlands of Alberta
Alberta •17.3% of the landscape is covered by wetlands. • Mostly peatlands (bogs – 4.9%; fens – 11.4%), with few marshes and swamps (1%).
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Wetlands in the Oil Sands – Area Perspective
Alberta peatland area
~ 10,300,000 ha (Vitt et al. 1996)
Oil Sands peatland area
~ 304,000 ha (Rooney et al. 2012)
~ 3% of total peatland
area in Alberta
Surface mining peatland
area ~ 28,000 ha (Rooney et al. 2012)
~ 0.3% of total peatland
area in Alberta
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Canadian Wetland Classification System
Wetlands
Organic wetlands (peatlands)
Mineral wetlands
Swamps Bogs Marshes Shallow open water Fens Swamps Marshes
Class – 5 classes, e.g. bog Form – 49 forms, 71 sub-forms, e.g. palsa bog Type – many, e.g. black spruce bog
National Wetlands Working Group. 1997. The Canadian Wetland Classification System, 2nd Edition. Warner, B.G. and C.D.A. Rubec (eds.). Wetlands Research Centre, University of Waterloo, Waterloo, Ontario. 68 pp.
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Wetland Classes
Bog
Shallow water wetland Marsh Swamp
Fen
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Reclamation
Reclamation – reconstructing a disturbed site to be
habitable by similar organisms present before the
disturbance in approximately the same composition and
density.
Requires considerable expertise in varying disciplines,
including:
– hydrogeologists, hydrologists, vegetation ecologists, wildlife
ecologists, engineers, designers, geophysicist, etc.
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Peat Harvesting vs. Oil Sands Developments
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Challenges – Geotechnical and Engineering
Composite tails (CT) – mixture of fine tails, gypsum, sand,
and water; hydraulically placed on site (i.e. needs to drain)
Mature fine tails (MFT) – mixture of silt, clay, hydrocarbons,
and water; very fluid (very long settling times); not
permitted in closed landscape
Trafficability challenges in In-Pit features
Physical dimension challenges
– some In-Pit lakes are >1,000 ha in size
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Challenges – Geotechnical and Engineering
Physical dimension challenges – pouring CT and tailings
sand in desired locations and into desired landforms
Containment challenges
– need dams
Sequential closure of mine
– hydrologic connectivity
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Challenges – “Soil” Characteristics
CT covered by tailings sand covered by cover soil
Tailings sand thickness at least 2 m over CT
Cover soil thickness in wetlands at least 0.2 m
Various approaches to establish
plant communities in wetlands
using soil
– 100% cover with donor wetland soil
– Donor wetland soil “islands”
– 100% cover with a peat/mineral soil
mix (salvaged, stored)
Planting/seeding with wetland plants
Natural re-vegetation
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Challenges – Water Quality
Water quality managed by careful design of landforms
Elevated areas (hummocks) facilitate flushing of tailings
sand and CT with PPT and groundwater
Primary issues around salinity, hydrocarbons, and some
metals (e.g. B, Cr, Ni, Se, Zn, and others)
Salt-crusting likely at hummock
toes and in lowlands, including
wetlands
Concentration of undesirable
compounds in some areas
– Managed via biodegradation,
flushing, plant uptake, etc.
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Challenges – Water Quality
Surface water quality managed by landform design, i.e.
hummock dimensions (i.e. primarily height and slopes)
Need separation of groundwater
from surface water in uplands
– Results in poorer water quality in
wetlands
Wetland
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Challenges – Plant Communities
Salinity likely greatest challenge for plant communities
– Na+, SO42-, Cl-, etc.
– EC = 2,000 µS/cm and up
In Wetlands, need to focus on salt-tolerant plant species
Abundant research in area
Many emergent wetland
plants tolerant of elevated
salinities
Shrubs and trees less
tolerant
May take years/decades
to achieve good ground
cover, e.g. bryophytes
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Potential Solutions to Reclamation Challenges
Flushing
– Underdrains, pumping fresh water into landscape, steeper
slopes
Plant communities
– Salt-tolerant species, design for salt-tolerant communities,
harvesting of salt-tolerant plants
Rooting substrata
– Increased soil cover to increase rooting depths, remove salts
from sands, independent sand sources (not linked to
operations), freshwater as transport medium for sands
Landscape stability
– Geotextiles/geogrid, even surface rather than topographic
variability, “straight” drainage pathways
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Oil Sands Region Wetland Reclamation
As of Dec. 31, 2010:
Certified reclaimed ~ 104 ha
Permanently reclaimed ~ 4,900 ha
Temporary reclaimed ~ 780 ha
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Wetland Reclamation Success Stories
Syncrude – Bills Lake
Suncor wetland
Suncor – Crane Lake
Syncrude - Gateway Hill
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Sandhill Fen
One of two “peatland” reclamation projects in the oil
sands region
Landscape designed as a 10-year research facility
– 10-m tailings sand cap over MFT
– Clay separating tailing sand from “fen”
– Several tailings sand hummocks
– 15.5 ha central “fen”, peat islands
throughout “fen”
– Freshwater supply
– Results will be used to design future
“peatlands”
Syncrude
Sandhill Fen
(57 ha)
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Conclusions
Peatland reclamation cannot be done (trajectory only)!
Wetland reclamation can be done!
Primary challenges in wetland reclamation are related to
soil and water quality and suitable plants; also geotechnical
and engineering constraints
Industry is (and has been for many years) actively engaged
in wetland reclamation research
Several success stories around wetland reclamation
Two pilot “peatland” reclamation projects are underway