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Recent Diatom Changes in the Lake of the Woods (Ontario): A Case Study for a Hemispheric-Scale Pattern of Ecological Change
Kathleen Rühland, A.M. Paterson, J.P. Smol
NOTE: Presentation slides are annotated: place cursor over commeNOTE: Presentation slides are annotated: place cursor over comment bubble to toggle on or offnt bubble to toggle on or off
-95°
-95°
-90°
-90°
-85°
-85°
-80°
-80°
-75°
-75°
45° 45°
50° 50°
55° 55°
Manitoba
Ontario
Minnesota
-96º
-96º
-95º
-95º
-94º
-94º
-93º
-93º
49º 49º
50º 50º
0 510
km
OntarioManitoba
Minnesota
Kenora
Lake of the Woods, Ontario, Canada
Big Traverse Bay
Kenora
Modified from Robertson & McCracken 2003
Lake of the Woods, Ontario, Canada
• Main direction of flow is south from the Rainy River to the northern outlet, the Winnipeg River
• Steep gradient in total phosphorus generally follows this direction of flow
August 31st
July 18th
June 19th
Development of an Algal Bloom - 2003
(Terra MODIS images – G. McCullough, U. of Winnipeg)
“The islands were numerous and crowded, the water shoal and foul, frequently with a green scum of vegetable matter”
- Major Joseph Delafield, July 30th, 1823
“…the water became tinged with green, derived from aminute vegetable growth”
- S. J. Dawson, Summer 1857
“…deposits of green vegetable matter” in the lake’s bays during the summer.
- objection to a proposal to use LOW to supply clean water to Winnipeg 1883
Some Important Lake Management Questions:
1) What is the ‘natural’ or baseline condition of the lake?
2) Has the water quality changed since pre-development (or pre-industrial) times?
3) If so, when did these changes occur?
4) What is the direction and magnitude of this change?
5) What are the possible reasons for this change?
Location of sampling sites for sediment cores
Modified from Robertson & McCracken 2003
PP1PP1
Whitefish BayWhitefish Bay
Kenora
BigstoneBigstone BayBay
The Instrumental Record
Historical Lake Ice Records
1960 1970 1980 1990 2000 2010180
190
200
210
220
230
240
250
260y = 0.6556x + 203.64
Year AD
# ic
e-fr
ee d
ays
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Whitefish Bay Diatom ProfileWhitefish Bay Diatom ProfileReference siteReference site
10 10 10 30 10 10 20 10 10 30 10 30 50 10 20 10 30 50 10 20 10 10 20 10 10 10
% Relative Abundance
20011999199719951993199119881986198319791974
19651970
19601956195219481944194019321926191919111889
Syned
radeli
catis
sima
Fragila
riacro
tonensis
Cyclotel
laste
lligera
/pseudoste
lligera
Cyclotel
labodan
icava
r. lem
anica
Fragila
riaca
pucina va
r. rumpen
s
Asterio
nella form
osa
Cycloste
phanos tholifo
rmis
Stephan
odiscus minutulus
Stephan
odiscus med
ius
Cyclotel
laoce
llata
Aulacose
iraisl
andica
Aulacose
iraam
bigua
Benthic
Fragila
riasp
ecies
Tabell
aria flo
cculosa
str. IV
12 18 24
1980 – present
µg/L
DI-TP
1980
10 30 10 30 5010 30
Rühland et al. in prep
Cyclotel
la
Cyclotel
laco
mensis
comen
sisco
mplex
complex
Aulacose
ira
Aulacose
irasu
barctic
a
subarc
tica
PCA axis 1
-1.5 -1.0 -0.5 0.0 0.5 1.0 1.5 2.0
PCA
axi
s 2
-3
-2
-1
0
1
2
3
1884
2002
1980
Whitefish Bay (reference site)
Summary of Diatom Trends: principal components analysis (PCA)
Rühland et al. in prep
Kenora 100-year Temperature Record
1900 1920 1940 1960 1980 20001.0
1.5
2.0
2.5
3.0
3.5
4.0
Mea
n A
nnua
l Tem
pera
ture
(ºC
)
Year AD
-96º -95º -94º -93º
49º
50º
KenoraKenora
Minnesota
Ontario
Manito
ba
1960 1970 1980 1990 2000 2010180
190
200
210
220
230
240
250
260y = 0.6556x + 203.64
Year AD
# ic
e-fr
ee d
ays
Whitefish Bay Ice Cover Record
• Ice-free period increased by 27.7 days since 1964
• Corresponds to increased temperatures
1960 1970 1980 1990 2000 2010180
190
200
210
220
230
240
250
260
1
2
3
4
5
6
# ic
e-fr
ee d
ays
Year AD
Temperature (ºC
)
R = 0.77
# Ice-free DaysAnnual Temperature
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Whitefish Bay (reference site)
Taxon-specific shifts: a closer look at Whitefish Bay
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
1900 1920 1940 1960 1980 2000 20201.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
0
10
20
30
40
50Annual TemperatureCyclotella spp
Whitefish Bay: Taxon-Specific RelationshipsKenora Temperature Record
1900 1920 1940 1960 1980 2000 20201.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
10
20
30
40
50
60Annual TemperatureAulacoseira spp
Year AD
R = 0.73
R = - 0.65
Ann
ual T
empe
ratu
re (º
C)
Relative A
bundance (%)
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Whitefish Bay Ice-out Record
Whitefish Bay: Taxon-Specific Relationships
1970 1980 1990 2000118
120
122
124
126
128
130
132
134
0
10
20
30
40
50Ice-out DayCyclotella spp
1970 1980 1990 2000118
120
122
124
126
128
130
132
134
10
20
30
40
50
60Ice-Out DayAulacoseira spp
Ice-
Out
Day
of Y
ear
Relative A
bundance (%)
Year AD
R = - 0.76
R = 0.77
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Taxon-Specific Shifts: ELA Nitrogen Data
% Cyclotella spp. vs TIN (3 year mean) from 1974-2004
Year (AD)1970 1975 1980 1985 1990 1995 2000 2005
TIN
(mg·
m-2 ·
yr-1 )
250
300
350
400
450
500
550
600
% R
elative Abundance
0
10
20
30
40
50
ELA TINCyclotella spp (%)
R = 0.28p=0.20
Year (AD)1970 1975 1980 1985 1990 1995 2000 2005
250
300
350
400
450
500
550
600
10
15
20
25
30
35
40
45
50
ELA TINAulacoseira spp (% )
R = -0.28p=0.20
TIN
(mg·
m-2 ·
yr-1 )
% R
elative Abundance
% Aulacoseira spp. vs TIN (3 year mean) from 1974-2004
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Diatom trends in the Lake of the Woods
Substantial change in last few decadesSubstantial change in last few decades
Impact site: PP-1Reference site: Whitefish Bay
PCA trajectories - ecological threshold passed?
Timing of changes consistent between sites
Diatom trends in the Lake of the Woods
Possible mechanismsPossible mechanisms ((Whitefish BayWhitefish Bay))
Strong relationship to increased temperature
Strong relationship to decreased ice cover
TemperatureTemperature
Inorganic nitrogen deposition (ELA)Inorganic nitrogen deposition (ELA)
strong +ve correlation to increased % Cyclotella spp
Weak correlation to Cyclotella trends
Taxon-specific trends in the Lake of the Woods
strong -ve correlation to decreased % Aulacoseira spp.
IceIce--out day of yearout day of yearstrongly correlated to increase % Cyclotella species
strongly correlated to decrease % Aulacoseira species
Weak correlation to Aulacoseira trends
Physical, chemical & biological changesPhysical, chemical & biological changesDecrease in ice cover duration
Thermal stratificationThermal stratification
Deeper subsurface habitats - nutrients
Planktonic Cyclotella species increase
Longer growing season
Light properties – more stable
Reduction in water column mixing (turbulence)
Warming and diatom changes
Heavier Aulacoseira species decrease
HemisphericHemispheric--scale trendscale trend
Decrease in DI-TP
SpeciesSpecies--specific shiftsspecific shifts
Further reading : Raubitschek et al. 1999 JOPL: Forsström et al. 2005 Polar Biol; Fahnenstiel & Glime 1983 Int Rev Hydrobiol
Cyclotella stelligera/pseudostelligera
Cyclotella comensis/gordonensis
Cyclotella comensis
Cyclotella gordonensis
Planktonic Cyclotella stelligera & C. comensis
From the Lake of the Woods Diatom Taxonomy Workshop: View a pdf of this booklet on our website under Research and Diatoms
Synthesis of Cyclotella/Aulacoseira/Fragilaria trend
1) How many profiles contain Cyclotella species?
2) How many record an increase? A decrease?
3) What do these lakes have in common?
4) Do these profiles show concurrent decreases in Aulacoseira species and/or Fragilaria species?
5) What is the geographic extent of this trend?
6) What are the most plausible mechanisms
• Whitefish Bay = case study
Criteria for Cyclotella compilation
1) Established chronology for last ca. 200 years (i.e. 210Pb dating)
2) At least 2% relative abundance of Cyclotella in at least one interval
3) Increase in Cyclotella = 5% or greater compared to background levels
Results of Cyclotella compilation
• Detailed Cores:• 170 lakes contained Cyclotella deposited within last ca. 200 years
• 14% of these did not have established chronology
• Remaining 147 lakes met first two criteria• 89 lakes (61%) of these showed an increase >5%
- Unimpacted sites• 29% showed a decrease
- 98% of these from eutrophic/acidic lakes• 10% showed no change
• Top-Bottom:• 146 lakes
• 120 recorded increases in Cyclotella from pre-industrial times
Geographic extent of Cyclotella species increases
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Subarctic FinlandSorvari et al. 2002Subarctic Canada
Rühland et al. 2003
Great Slave L. N.W.TStoermer et al. 1990
Eastern GreenlandCremer et al. 2001
High Arctic CanadaPerren et al. 2003
SwedenBigler & Hall 2003
Geographic extent of Cyclotella species increases
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Subarctic CanadaRühland et al. 2003
Yukon CanadaKarst-Riddoch et al. 2002
Great Slave L. N.W.TStoermer et al. 1990
Subarctic FinlandSorvari et al. 2002
Eastern GreenlandCremer et al. 2001
Spanish PyreneesCatalan et al. 2002
High Arctic CanadaPerren et al. 2003
SwedenBigler & Hall 2003
Geographic extent of Cyclotella species increases
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Subarctic CanadaRühland et al. 2003
Yukon CanadaKarst-Riddoch et al. 2002
Great Slave L. N.W.TStoermer et al. 1990
Subarctic FinlandSorvari et al. 2002
SwedenBigler & Hall 2003
High Arctic CanadaPerren et al. 2003
Spanish PyreneesCatalan et al. 2002
NB CanadaHarris et al. 2006
SW ONWerner et al. 2005
SE ONForrest et al. 2002
ELA NW ONEnache et al. unpubl.
Northern Hemisphere-Scale Trend
BC CanadaReavie et al. 2005, 2006; Laird et al. 2001
Eastern GreenlandCremer et al. 2001
NS CanadaGinn et al. in press
Geographic extent of Cyclotella species increases
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Comparison in the timing of Cyclotella increases
Year AD
Cyc
lote
llare
lativ
e ab
unda
nce
(%)
0
10
20
30
40
50
60 Whitefish Bay Emmett LakeWolfe LakeFairy Lake Indian LakeBig Rideau Lake
1630 1680 1730 1780 1830 1880 1930 1980
05
101520253035404550
Slipper LakeLake SaanajarviLake TK20Lake TK54Lake BirgervatnetLake CF-11
A
B
AD
187
0
AD
197
0
Circumpolar lakes
Temperate lakes
0 10 20 30 40 50 60 70
0
10
20
30
40
50
60
70
0 20 40 60 80 100
0
20
40
60
80
100
0 10 20 30 40 50 60 70
0
10
20
30
40
50
60
70
0 10 20 30 40 50 600
10
20
30
40
50
60
AA
0 20 40 60 80 100
0
20
40
60
80
100
0 20 40 60 80
0
20
40
60
80
P<0.010 P<0.012
P<0.003 P<0.011
P<0.001P<0.001
1:11:1
1:1 1:1
1:11:1
Climatic Warming and Taxon-specific Shifts
Pre-industrial Sedimentary Diatoms
Mod
ern
Sedi
men
tary
Dia
tom
s
South-western OntarioSouth-central OntarioSouth-eastern Ontario
BB
CC DD
EE FF
% C
yclo
tella
spp
% C
yclo
tella
spp
% C
yclo
tella
spp
% A
ulac
osei
rasp
p%
Aul
acos
eira
spp
% F
ragi
laria
spp
Cyclotella
Fragilaria/Aulacoseira
1.1. NWT-Nunavut (n=40)Rühland et al. 2003 AAAR
2.2. New Brunswick (n=16)Harris et al. 2006 CanJBot
3.3. Ontario Combined (n=91)Hall & Smol 1996 CanJFishAquat Sci
Reavie et al. 2002 Hydrobiol
Werner 2003 PhD thesis
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Climatic Warming and increases in Cyclotella species
Subarctic CanadaRühland et al. 2003
Yukon CanadaKarst-Riddoch et al. 2002
Great Slave L. N.W.TStoermer et al. 1990
Subarctic FinlandSorvari et al. 2002
SwedenBigler & Hall 2003
High Arctic CanadaPerren et al. 2003
Spanish PyreneesCatalan et al. 2002
NB CanadaHarris et al. 2006
SW ONWerner et al. 2005
SE ONForrest et al. 2002
ELA NW ONEnache et al. unpubl.
Northern Hemisphere-Scale Trend
BC CanadaReavie et al. 2005, 2006; Laird et al. 2001
Eastern GreenlandCremer et al. 2001
NS CanadaGinn et al. in press
Rühland, Paterson & Smol: Global Change Biology (2008) 14, doi: 10.1111/j.1365-2486.2008.01670.x
Summary of Results: Lake of the Woods
• Greatest change in diatom composition over last ca. 20-30 yrs
• Changes consistent with climate records
• Taxon-specific shifts correlated to increase in temperature
• Taxon-specific shifts correlated to decrease in length of ice cover
• Taxon-specific shifts not related to nitrogen deposition
• Climatically-induced limnological changes = 1º mechanism
• Climate must be included in lake management strategies
• LOW fits into global pattern of recent taxon-specific diatom shifts
Acknowledgements
• Bev Clark (MOE, Dorset)
• Mike Stainton (DFO, MB)
• Sergi Pla (formerly at PEARL)
• Tom Mosindy & Gavin Olson (MNR Kenora)
• Ron Ingram (MOE, Dorset)
• Joy Ramstack (St. Croix Watershed Research Station, MN)
• Mark Edlund (St. Croix Watershed Research Station, MN)
• Euan Reavie (Natural Resources Research Institute, Ely MN)
• Nolan Baratono (Minnesota Pollution Control Agency)