Aquatic Ecology final Flashcards

(324 cards)

1
Q

Aquaculture impacts

A
escapement
waste discharge
fish health
water quality
coastal activities
global feedfish populations 
marine foodwebs
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2
Q

Captured/farmed fishery products flow chart

A

aquatic production (PP)– capture fisheries (discarded bycatch, human consumption)- fish meal - aquaculture (livestock) -human consumption (terrestrial agriculture)

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3
Q

Captured/farmed fishery products flow chart, negative feedbacks

A
  • feedbacks on PP

capture fisheries, fish meal, aquaculture

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4
Q

Captured/farmed fishery products flow chart, aquaculture negative feedback

A

waste, habitat modification, pollution, impacts on population/food web dynamics, escaping feral species

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5
Q

PP proportion division from capture fisheries

A

approximately:
1/4 bycatch (waste)
1/4 fish meal
1/2 human consumption (straight)

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6
Q

PP proportion division from fish meal

A

1/6 Aquaculture
2/6 (1/3) livestock
3/6 (1/2) human consumption

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7
Q

changes in total capture

A

increased substantially

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8
Q

human consumption from aquaculture & capture fisheries, 1997

A

~95 million metric tonnes (worldwide)

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9
Q

environment issues from aquaculture

A

discharge degrades water quality
alter/degrade natural habitat
pressure from multi-uses on water system

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10
Q

Biological issues with aquaculture

A

over-exploitation of organisms - food web consequences
chemical use (health concern)
introduction/transmission diseases, parasites, aliens
contamination

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11
Q

production quantity and value vs. year

A

exponential increase
huge increase since 1980’s
2004 quantity: ~60million tonnes
2004 value: $70 billion US

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12
Q

aquaculture production, china/asia/rest of world

A

China by far the hugest proportion and largest increase (50million tonne increase in 30yr), Asia ~20million tonne increase in 30 yrs, rest of world increased less than 10million tonne (an IS less than 10)

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13
Q

world population 1950-2002

A

2.56billion –6.23billion

now ~7billion

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14
Q

consumption per capita, 1950-2002

A

~doubled since 1950 (10-22kg per person/per year)

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15
Q

changes in marine fish catch, 1950-2002

A

~20million tonnes – 80/90million tonnes

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16
Q

Utilization of fish, 2000’s

A
40% fresh
30% non-food (feed)
18% frozen
7% cured
8% canned
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17
Q

Changes in utilization of fish since 1960’s

A

increase in fresh fish- better transportation, maintenance

increase in frozen fish

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18
Q

Canada’s Atlantic cod

A

1980-1990 catch was ~500,000 tonnes, 1995 drops off to nothing, overexploited to population collapse, still can not recover b/c niche space taken over

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19
Q

human fish consumption as a percent of total animal protein

A

worldwide 16%
N America 6.6%
Africa 21%
Far East 28% (Asia, healthier, cheaper, less fresh water needed)

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20
Q

World farm salmon production, 1980-2003

A

BC, Norway, Chile, UK all increase in production

Norway MAJOR increase

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21
Q

Changes in world farm salmon production, 1996-2002

A

Chile +235%
Norway +71% (but highest total value)
Scotland +89%
BC +96% (but lowest total value)

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22
Q

Changes in wild salmon, US + Canada, 1988-2002

A

chinook, chum, coho, sockeye- all decrease in production roughly 30%, decrease in at-vessel price/lb ~70%
pink production +11%

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23
Q

Changes in farmed Atlantic Salmon, US + Canada, 1988-2002

A

production: +895,000%
price: -61%

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24
Q

mariculture

A

cultivation of marine organisms for food and other products in the open ocean

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25
aquaculture by environment (2004)
Brackish 6% Freshwater 43% mariculture 51%
26
what is grown in aquaculture
very diverse: crustaceans (shrimp, crab), finishes (carps, tilapia), filter feeders (mussels, oysters, scallops..), aquatic plants, carnivorous fish (salmon, bass, bream)
27
World aquaculture production by volume, by country/continent, 2004 (the main players)
China 70% Rest of Asia 22% Other 9% w/i Other: W Europe 3.5%, Latin America 2%, NA 1.27%
28
World aquaculture production by value, by country/continent, 2004 (the main players)
China 51% Rest of Asia 29% Other 20% w/i other: WE 8%, LA 7.5%, NA 1.86%
29
fastest growing food producing industry
aquaculture
30
problem of rapidly increasing aquaculture
demand for feed ingredients increasing rapidly, supply limited
31
feed used in BC, 2000
65 million kg | to produce 49million kg farmed fish
32
what happens to feed
20% deposited as feces unused feed deposited as solid excretory release of dissolved material
33
chemical components of aquaculture feed
45-65% is Carbon 6-10% is N, 1-2% is P total system loading unknown
34
whats so important about increased N, P
two most important nutrients responsible fro eutrophication
35
Estimated loading to BCs coastal water from aquaculture
7.1 million kg of C 1.3 million kg of N 236,000kg P all per year may not be significant for entire system, but definitely important in enclosed bays
36
how salmon are unlike other 'farm' animals
carnivorous, feed is 45% fishmeal, 25% fish oil
37
cost of producing farm fish
2.8kg wild fish = 1kg farm fish | area required to produce the feed = 40-50,000X production area
38
Amount of PP being used for aquaculture
European industry - ~90% of North Seas's PP | BC - 7.8million ha of ocean (278X area of all terrestrial BC horticulture)
39
what's underneath a fish farm???
black sediment - highly organic material, reductive, lacking oxygen
40
taxa richness vs [sulfide] (µM)
negative linear | appears well correlated, but also a pretty wide spread in the data
41
whats happening with the sulfide
increased Cord -- increased sulfide accumulation-- kill benthic inverts.
42
rockfish near farms
found to have higher Hg content closer to fish farms
43
why rockfish?
not very migratory, good proxy for local condition
44
why higher Hg near fish farms?
oxygen reduction due to C loading = anoxic sediment-- Hg methylated and converted to usable form (methyl mercury)-- accumulates in tissues-- produces neurological effects
45
levels of contaminants in farm produced, store bought, wild salmon
farmed & most of store bought ~ equal in all of the contaminants/carcinogens tested (PCB, dioxin, toxaphene, dieldrin), wild lower some store bought appears to be wild but more is farmed
46
fish utilization and supply (excluding China), trend
1950-2002 population linear increasing food supply non changing
47
changes in fishmeal use, 1988-2002
1988: Poultry 59%, aquaculture 10%, pigs 20% 2002: poultry 22%, aquaculture 46%, pigs 25%
48
what are poultry being fed now
bluegreen algae (more deeply coloured yolk, carotenoids)
49
fish oil use
1990: edible 76%, aquaculture 16%, industrial 8% 2002: edible 14%, aquaculture 81%, industrial 5%
50
Other sources of fish feed
by-catch fish processing by-products plant products livestock by-products
51
Canada salmon feed
lowest fishmeal and oil inclusion rate
52
SA fish feed
41% of all fish used in feed, including: Anchoret, Chilean jack mackerel, South American pilchard very important low trophic level fishes!!
53
top marine capture, 2002
``` anchoveta (9.7mt) pollock (2.7mt) tuna (2.0mt) capelin (2.0mt) herring (1.9mt) ```
54
changes in salmon fishmeal/fish oil use
fishmeal +185% | fish oil +577%
55
changes in carp fishmeal/fish oil use
fishmeal 750% | oil 70%
56
changes in crustacean fishmeal/oil use
fishmeal 1363% increase | fish oil 2660% increase!
57
overexploited species for fish feed
Peruvian anchovy- 6.2mt harvested 2003, recovering, overfished Chilean jack mackerel- 1.7mt harvest 2003, fully fished, overfished up to 11 species in this list are fully fished, unsustainable!
58
SA harvest of feed fish
1960-70's exploit anchoveta-- collapse-- SA pilchard takes over niche-- exploit them-- collapse-- chilean jack mackerel moves in..
59
natural cause of population decline in fish species
El Niño- huge decrease 1998
60
capture-reduction
how much is caught relative to time vessel spends out (? maybe) .. lowest in El Niño yrs
61
larger scale effects of harvesting fish feed
taking ~85% of sea predators food; seabirds, marine mammals
62
Effects of farming on wild salmon health
smolts travelling to ocean pass by fish farms, pick up significant infections rates; many farm fish have sea lice (infestation from low diversity, close quarters)
63
forage fish
prey fish/bait fish, small pelagic fish preyed on by larger predators for food
64
areas of application for stable isotopes
``` paleoclimate reconstruction (O2) paleolimnology terrestrial aquatic linkages food web ecology migratory studies individual feeding behaviour ```
65
paleolimnology, stable isotopes
historic patterns of productivity, mostly C, N
66
terrestrial aquatic linkages, stable isotopes
terrestrial--> aquatic (lake management) | marine derived nutrients (salmon)--> terrestrial
67
food web ecology, stable isotopes
contaminant transfer, ecology
68
migratory studies, stable isotopes
birds, fish, zooplankton, mammals, C how much time in open/coastal ocean algae isotope ratio highly variable in open/coastal
69
individual feeding behaviour, stable isotope
niche shift, omnivore, trophic position within single population ex. stickleback - some neutral all the time, some pelagic all the time, all related to evolution, studiable by isotopes
70
∂13C ratios
C fractionates during photosynthesis, little-no fractionation up food chain determine what food sources are based on ∂13C ratio
71
∂13C determination of food source possible with following conditions
large isotopic separation (btw food sources) over time food signatures are stable two/few food sources
72
examples of ∂13C determination of food source
middle of lake - very highly negative | close to littoral zone (terrestrial C) - less negative
73
∂15N in food web ecology
tells trophic level, fractionated throughout trophic levels
74
trophic enrichment of ∂15N
2.92+/- 0.8 ‰
75
typical ∂15N signatures
algae 4-8‰ invertebrates 8-16‰ forage fish 10-14‰ predatory fish 10-18‰
76
typical ∂13C signatures
off-shore -28‰ (depleted) | near-shore -14‰
77
why is ∂15N fractionated up trophic level
preferential excretion of 14N
78
high ∂15N
heavy | more positive
79
atmospheric N2 ∂15N
0‰ | hasn't been fractionated by organisms
80
enriched in ∂13C
heavy less negative ∂13C never positive
81
depleted in ∂13C
light more negative ∂13C never positive
82
inorganic fertilizer ∂15N
0‰ | made from captured atmospheric N
83
fractionation
in a chemical reaction one isotope proceeds at a quicker rate than the other due to a slight difference in mass (lighter synthesized faster/easier, more efficient)
84
two types of fractionation
animals- body tissue | algae
85
animal tissue fractionation
14N is preferentially released so 15N increases relative to its food source
86
algae fractionation
photosynthetic enzyme can process 12C molecules quicker than 13C, utilize it preferentially based on size
87
algae photosynthetic enzyme that processes carbon molecule
RUBISCO
88
isotopic composition in foodweb
sediment: ~-30, towards terrestrial inverts: ~-33, ~50/50 terrestrial/planktonic piscivorous fish: ~-28/-30 pretty close to terrestrial
89
littoral zone
near shore area where sunlight penetrates all the way to the sediment and allows aquatic plants (macrophytes) to grow
90
Loch Ness Zooplankton, temporal shift in C signature reflecting food source
winter- low PP, most C is detrital, POM (less - ∂13C), zoop signature matches POM summer- higher PP, signature drops to mirror to algae ∂13C (more - )
91
reconstruct historic salmon runs with ∂15N
sedimentary ∂15N correlated to number of spawners 250,000spawners ~ 6‰ 1mill spawners ~ 8.5‰
92
∂15N sediment signature change in 1900
dramatically drops off, commercial fishing
93
significantly different ∂15N signatures along the river
higher ∂15N signature in root feeders, omnivores, detritivores, predators.. BELOW falls (input of high ∂15N source, salmon)
94
Class 1 lake
lack preferred lake trout prey, pelagic forage fish, causing lake trout to feed on zooplankton and zoobenthos
95
class 2 lake
contain at least one species of pelagic forage fish, resulting in piscivory
96
class 3 lake
pelagic forage fish and glacis-marine relict invertebrate predator Myis relicta - elevates lake trout to fifth trophic level
97
measuring trophic level by ∂15N ratio
gut contents digestibility highly variable assumptions made
98
pelagic
Any water in a sea or lake that is neither close to the bottom nor near the shore
99
pelagic zooplankton signatures
variable! needs to be established as a baseline | study found differences in calanoid copepods, Daphnia, Holopedium
100
lake to lake isotope signatures
highly variable depending on inputs (human, animal, fertilizer, salmon)
101
PCB (ng/g wet mass) vs trophic position
liner increasing class 1 at low end class 2 in middle class 3 at top end (most trophic positions) appears to be due to increased % lipid with increased trophic level
102
PCBs and lipids
lipophilic contaminants, accumulate in fat (lipophilicity) | unnatural, remain in bodies
103
∂15N trophic position vs. dietary trophic position
highly correlated = N good measure of trophic position
104
Hg (µg/g) vs. Lake class
``` higher in higher class higher if smelt present in each individual class ```
105
∂15N vs ∂13C, Arctic Lake System, Lake Trout
LT top predator - highest ∂15N, ~middle of ∂13C spread- consumes pelagic and littoral fish
106
Log Hg (µg/g wet weight) vs. ∂13C
decreasing terrestrial source has lower level of Hg if LT feed more on nearshore/benthic than offshore/pelagic they will have lower Hg
107
Hg consumption guideline
0.5µg/g | one meal per week (non pregnant adults)
108
[Hg] (µg/g) vs. ∂15N (‰) in Ontario, Quebec lakes
all Class 2 and 3 fish are above consumption guideline level of Hg sport fishing species, widely consumed
109
US Hg blood levels
300,000-600,000 children/yr cord blood Hg level > 5.8µg/L, a level associated with loss of IQ
110
cost of methyl mercury toxicity
lost productivity (lower IQ) $8.7bill/yr
111
Daphnia spp. ∂15N (‰) vs levels of land-use (low, high)
low land use (Sooke lake) - 0-5‰ | high land use (Shawnigan lake) - 6-13‰
112
Sooke lake
our drinking water | fully protected
113
Shawnigan lake
developed lots of septic highly enriched in ∂15N
114
Caffeine (ng/L) vs. ∂15N in Mussel Tissue
linear positive caffeine from septic contamination robust indicator of fecal contamination
115
Caffeine (ng/L) vs. Shoreline Development (lots/km^2), Shawnigan lake
linear positive | denser housing = more septic = fecal input = more caffeine
116
∂15N (‰) vs. year, Sooke Lake and Shawnigan lake sediment cores
Shawn. has increased from ~1-3 as a result of human development Sooke- has some spikes from building new dams/raising the dam- inundating land
117
EBS
Eastern Bering Sea
118
EBS 2002-2005
large-scale warming event | followed by 2yrs cooling event (2006-07)
119
EBS sampling
zooplankton from 186 stations each year 13,000 fish 600 zooplankton
120
change in abundance of juvenile salmon and forage fish
increase in warm years decrease in cold years in salmon, juveniles, forage fish
121
EBS zooplankton ∂15N
must be determined for baseline | higher in N EBS- upwelling? predatory?
122
Juvenile Sockeye Salmon ∂15N, EBS
warm years- up to 2 levels above zoop. = piscivory | cool years- remain small, stay near shore, can't grow enough to move up food chain
123
Juvenile Pink Salmon Trophic position above zooplankton, EBS
pink salmon normally zooplanktivorous.. | in wam years- up to 2 levels above zoop., piscivorous
124
Juvenile Chum Salmon trophic position above zooplankton, EBS
chum usually feed on jellies | warm event- up to 2levels above zoop., piscivorous
125
Signatures in northern Bering Sea
warm year- less negative ∂13C, near terrestrial loading (from Yukon river) cool year- more negative ∂13C, pelagic source not really a pattern in ∂15N
126
Signatures in Southern Bering sea
Warm- higher ∂15N, higher trophic position, trophic enrichment Cool- lower ∂15N, lower trophic position
127
sediment ∂15N profiles from NH lakes
26 profiles, almost all show drop in ∂15N since 1900 = depleted N signature from fertilizer use! recall (fertilizer is from atmospheric N2)
128
global fresh water
3% | 99.7% of that 3% is unavailable (glaciers, deep aquifers)
129
Where is our available water
80% is in 20 large lakes | 95% is in 145 lakes
130
water demand per person
1400-1800m^3/person/year | 1.4-1.8million L
131
unequal distribution of water
little water in some parts of China, France, unglaciated US | abundant in Canada, Scandinavia, NZ, Russia
132
Water required for some crops
``` 70L for 1 apple 50L for 1 orange 140L for 1 cup coffee 2300L per kg rice 15,500L per kg beef ```
133
water exchange times, lakes basin
days - centuries | balance of inflow, precipitation, evaporation
134
water balance affected by
dams, diversions
135
Aral Sea
1.3million km^2 watershed before 1960, 4th largest lake in world 67,000km^2 Kazakhstan and Uzbekistan
136
Aral Sea, 1920s
water diversion for agriculture (especially cotton), storage for hydroelectric power
137
Aral Sea ppt
historically- 10ppt | Now- 34ppt (Ocean salinity!)
138
Aral Sea, since 1960s
85% volume lost (42,000km^2 lost) 65% SA lost lakeside towns now 100-150km away former lake area dry, saline
139
Affects of Aral Sea changes
all fish species gone 60,000 fishing jobs lost massive ecological change- species extinctions local climate substantially changed
140
Aral sea historic harvest
48,000T/yr | largest fish processing plant in USSR
141
Aral Sea 2000's
``` area 24,000 volume 175 salinity 65-70 separated in to two lakes in 1993 2010, only 1 lake left ```
142
Economic Consequences of Aral Sea loss
fishing, agriculture, cost of water rights
143
Health Consequences of Aral sea loss
``` highest child mortality in former USSR life expectancy decrease 64-51yrs (in ~60yrs) highest world rate of esophageal cancer widespread DNA damage birth abnormalities 5X EU, infertility ```
144
What's causing the health consequences, Aral Sea
large volume of agricultural chemicals, waste | carcinogenic salt/chemicals transported by wind
145
Pesticide use in Aral sea area
72kg/ha | compared with US- 1.6kg/ha
146
Valiant Dam Italy
265m concrete arch dam, steep walled mountain valley built in 1960 limestone/clay layers = slides as reservoir filled
147
Vainont Dam, 1963
debris slide displaced 30x10^6 m^3 water over dam (1/4 of contents) 2500 deaths downstream
148
China, S-->N water diversion
un-uniform water distribution divert water from major S rivers to industrial in low water N 3X cost of Three Gorges 3 separate routes
149
Three Gorges Dam, China
once largest in world | flood control, diversion of water to N, hydro power, transportation
150
Three Gorges Dam problems
loss of agriculture, historical sites | changes to climate, public health, soil stability
151
Dam changes to soil
when water bodies are made, soils release heavy metals they have been holding into water
152
Colorado River, 1928
water treaty 7 states get 19km^3 Mexico 1.8km^3
153
Colorado River, 1930's
major water diversion to LA
154
Colorado River, 1935
Hoover Dam
155
Colorado River, 1960's
Glen Canyon Dam [salt] exceeds 1.5g/L ruins Mexico agriculture (collapse)
156
Response to Glen Canyon Dam - Mexican agriculture collapse
Yuma (Arizona) desalination plant | $1B/yr
157
Ground Water
``` give stability to ground over draining creates space in ground sinkage drawdown water table subsidence ```
158
Mexico City
built on a lakebed, elevation 2240m | Initially water flowed in and had to be diverted out
159
Changes in Mexico City
rapid growth (more than 20million) Had to pump in water but had very poor infrastructure (holes in pipes) subsidence 1m/yr buildings tilting, roads, pipes moving
160
Canadian water
Great lakes: 240,000km^2 20+% of world FW 85% of NA water 45mill people in watershed (15mill Canada)
161
Canadian water export
policy unclear (provincial vs. federal) NAFTA may require selling water to US potential profit, damage degradation loss
162
Unclear water policy
freshwater is provincial jurisdiction | who can use water is federal - dept transportation, dept fisheries, dept fish&oceans
163
NAWAPA
``` North America Water and Power Alliance potential water diversion: Rocky Mt trench -- Texas from Mackenzie river valley 240 dams nuclear power to pump it ```
164
GRAND Canal dam
Great Recycling and Northern Development channel | potentially divert from James Bay -- Great lakes
165
Dam/Diversion problems and education
``` political economical public education important International co-operation conservation water re-use ```
166
Dam impacts, land inundation
mobilizes DOC & Hg to food web Hg accumulation in fish neuro-degenerative symptoms loading to ocean (of water) is decreasing, may increase ocean salinity
167
MPA, IUCN definition
Any area of intertidal or subtotal domain, together with it's overlying water and associated flora, fauna, historical and cultural features, which has been reserved by law or other effective means to protect part or all of the enclose environment.
168
MPAs attempt to
protect sensitive habitat conserve biodiv. shelter vulnerable/endangered species boost fisheries catch
169
IUCN
international union for conservation of nature
170
MPA coverage, now
less than 1% of worlds oceans
171
Newfoundland Cod, historically
fished from small dories, land lines | spawning ground far offshore (unreachable)- natural protection, refuge
172
dories
small, shallow-draft boat, 5 -7m, usually lightweight with high sides, flat bottom and sharp bows
173
Fishing technology
no natural fish refuges very long range & time targeting capability
174
Traditional fishery protection laws
species specific | i.e. Atlantic Cod
175
MPA, allowable
no ocean dumping or dredging no exploration for or development of non-renewables fishing/extraction permitted
176
fully protected MPA
"No-take zones" "Areas of the ocean completely protected from all extractive and destructive activities" no fishing, removal, dumping, dredging
177
Coverage of 'no-take' zones
less than 0.1% of the worlds ocean
178
Accidental MPA
Cape Canaveral | US gov't creates security zone around Cape C. satellite launch zone
179
MPA benefits
``` Increase/Enhance: fish abundance fish size/age reproductive output species diversity habitat complexity fishery yields in adjacent grounds overall biomass increase ```
180
"Fishing the Edge"
fishing boats sitting right on edge of MPA
181
Importance of letting fish grow big
reproductive output large fish = higher reproductive output 23"in vermilion can produce 17X more young than 14"
182
Sustaining Sea Otter, kelp forest
protects fish abundance, mussel growth, other inverts and crustaceans, changes to predatory sea bird resources
183
Fish Abundance, sea otter presence
~5X higher w/ S.O. present
184
Mussel Growth, sea otter
~2X w/ s.o. present
185
Gull diet, sea otter
Diet is 90% fish w/ s.o. present | 90% macro inverts. without sea otter
186
Bald Eagle diet, sea otter
s. o. present: diet is fish, mammals, birds ~ equal | s. o. absent: ~70% of diet is seabirds
187
control sea urchin populations
sea otter predatory fish species spiny lobsters
188
urchin/kelp feedback
lack of predation-- urchin population boom-- urchins feed on kelp holdfast-- kelp wash away in tide-- habitat is lost
189
Anacapa Island MPA
California - predatory fish, lobsters regaining populations- increased urchin predation- sustainable kelp forest
190
Idealized MPA
``` Equilibrium state: maximized species diversity many linkages in food web redundancy stability ```
191
Ecological redundancy
organisms having several food sources
192
"Spillover effect"
= export of adult fish out of MPA | high fish density within MPA - leave protected area (no physical boundary)
193
MPA size determination
dependent on species to be protected too large detracts from fishery too small ineffective
194
Sizes of MPAs
not self-sustaining moderately self-sustaining completely self-sustaining
195
MPA not self-sustaining
most species lost high periphery : area unsustainable small effect on recruitment and commercial fishing too much loss out of reserve to be effective
196
MPA moderately self-sustaining
``` some species lost adequate periph:area some individuals retained significant source of recruits to fished area some reduction of fishing grounds good balance of benefits for all ```
197
MPA completely self-sustaining
``` all species retained low perish:area small spillover little recruitment outside reserve severe reduction to fishing ground little export ```
198
Where should MPAs be?
vulnerable habitats important habitat species rich habitat spawning grounds
199
MPA and migratory species
doesn't really protect migratory species, better for stationary species (ex. rock cod) DOES increase salmon prey though
200
MPA vulnerability
currents flow through, pollutants can flow through | MPAs necessary but not adequate
201
Lake Victoria
``` SA 69500km^2 depth Zm = 39m several invasives: Nile Perch, water Hyacinth overfishing (gillnets) massive loss of endemics loss of Oreochromis fishery ```
202
Lake Victoria native population
``` 300 Cichlid fish most diverse cichlid population 2/3 gone highest vertebrate extinction rate Oreochromis sp. (algal feeder) - major protein source ```
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Management troubles of Lake Victoria
shared by 3 countries that don't get along | Uganda, Kenya, Tanzania
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Water hyacinth
mostly near shore environment- highly mixed/dynamic water bodies, sheltered small basins clog up waterway
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Major aquatic plants (invasive)
``` Hydrilla (US) Elodea (Europe) Eurasian milfoil (NA) Purple loosestrife (NA) Canary Reed Grass (NA) take over shallow transparent water bodies huge economic losses ```
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Invasive plant management
Herbicides Mechanical harvesting biological control
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Invasive plant management, biological control
introduce something else that will prey on it (kind of like how coopers hawk controls European starlings)
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Invasive plant management, mechanical harvesting
bulldozers!
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Nile Perch
large piscivorous fish introduced in 1960 for British sport fishing up to 300lbs
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Lessons of Lake Victoria
introduction of one species changed entire trophic dynamics of one of the largest lakes in the world
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% of total catch vs year (Lake Victoria)
haplochromines (cichlid) majority of prey catch until ~'74 1974-1980 majority is haplo. and omena after 1980 majority is Nile perch and omena
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Omena
anchovy-like minnow
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Standing stock estimates, Lake Victoria | Kg/ha vs year
Native - ~60 in 1970's down to ~0 in 80's, 90's Introduced- ~30 in 80's --> ~70 in 90's almost entirely introduced species
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Oxygen in Lake victoria | O2 (mg/L) vs Month
surface ~10 all year bottom: less than 5 all year, anoxic in winter, highest in summer loss of haplochromines (algal readers) changed oxygen structure bottom up control
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Eastern Bullfrog
widely introduced for aquaculture (restaurants) Europe, Asia, Japan replace/consume prey of/ infect native amphibians
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spread of Eastern Bullfrog
California 1905 Burnaby 1940 Elk Lake 1960's
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Eastern Bullfrog diet
omnivores | insects, fish, ducklings, rodents
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Invasive Zooplankton
Daphnia lumholtzii (Europe-NA) Bythotrepes (NA) Cercopagus (black sea-baltic) Mysis relicta (Ghost shrimp, glacial relict)
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Success of invasive species
distinct features that give them the advantage | ex. sharp spine, anti predator mechanisms, larger T/resource/habitat ranges
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Mysis relicta foodweb changes
introduced to Flathead river-lake ecosystem to increase kokanee population. Only feed at night, competition for kokanee's resources.. decreases kok. pop., lake trout, bears, eagles, copepods, cladocerans (water flea)
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Invasive filter feeders
``` Zebra, Quagga mussels introduced from ship ballast from E Europe, 1988 few predators (dicks, 1 fish) widespread through Mississippi major financial impact larvae continue to spread with boats ```
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Why are so many eggs released in St. Lawrence seaway
ships have to release ballast to rise in canal
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Effects of increased mussles
clog water pipes, make great lakes more oligotrophic, affect fish productivity
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Origin of foreign fish
mostly from: | South America, Asia, Africa, Central America
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Laurentian Great Lakes
``` most important NA water source SA 244,000km^2 V 23,000km^3 21% worlds water 84% NA water 1/3 of Canadian Population ```
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Great Lakes fish introductions
1600's Carp 1930's Lamprey, alewife 1960's Pacific Salmon Rainbow smelt, reffe, goby (ballast water), zebra mussels
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Lamprey, alewife introduction great leaks
1930's upper lakes via Welland canal loss of lake trout, whitefish alewife - zooplanktiverous--> anoxia
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Welland Canal
waterways connecting Atlantic ocean to great lakes
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Pacific Salmon introduction to great lakes
1960's chinook, coho introduced to deal with alewife (biological control) salmon spawn upstream, don't go to ocean, very contaminated
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VI fish introductions
Sunfish Rainbow Trout Small Mouth Bass Yellow Perch
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Other introduced species
``` Asian carp/Grass carp Cormorants Bang Nutria Didymospenia ```
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Asian Carp, Grass carp
introduced to control aquatic plants, took over | biological control
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Cormorants
Lake Ontario efficient gobies consumer (invasive fish) fewer sport fish
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Bangia
filamentous algae forming extensive growth
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Nutria
'river rat' -kinda looks beaver/marmot like very efficient foragers cause enormous damage from SA
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Didymospenia
filamentous diatom choking river beds decrease use of rivers as spawning grounds
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Caulerpa taxifolia
mediterranean 1984 first discovered 1990 1ha authorities informed (in writing) 1994 declared major threat 1500Ha 1998 UN law to battle invader 4600Ha 1999 covers 97% of suitable surfaces France, Monaco, Italy
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Invasive cats
``` feral populations, one of worst invasive mammalian predators direct predation competition hybridization disease transmission ecologic process alteration behavioural change ```
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Google Earth/GIS
can be used to study introduction/coverage of invasive w/ time google earth found to be 84% accurate at detection
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fate of invasives, possible outcomes
Transport-- introduction -- success (fail) --spread (fast/slow) -- impact (nuisance/non-nuisance)
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dysentry
infection of the intestines resulting in severe diarrhea with the presence of blood and mucus in the feces
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Water contamination
millions die worldwide/yr | rural/slums- high dysentry
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amount of people in rural communities without access to safe water
77% | safe is in don't die from it
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children under 5 that die from diarrhea in rural/slum communities, due to unsafe water
35/1000
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Women and school, rural/slum communities
40% complete 3years | intense effort to collect water
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Water contamination, Canada
many sick, 7 dead in Walkerton, Not | ~1000 small communities on boil water advisories (all the time)
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Water quality parameters of concern
pathogenic bacterie/protozoans (intestine disease) excessive nutrients/algae (neuro/hepato toxins, carcinogenic byproducts) harmful chemicals
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anthropogenic harmful chemicals in drinking water
pesticides, herbicides, metals, antibiotics, pharma-care products chemical/biological/microbial waste from agriculture, livestock, industry, households
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why larger communities at lower risk of water contamination
adequate resources expertise operator training and treatment money able to own and control entire watershed
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example of dharma-care water contaminant, St. Lawrence Seaway
endocrine disrupters causing fish to not develop sex
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Siem Reap River (cambodia), water contamination
throw waste into same small waterbody that is used for drinking
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Bangladesh water crisis
well water becoming contaminated with arsenic from contaminated groundwater = ulcers, amputations, gangrene, carcinoma, pigmentation issues
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Bangladesh water contamination, solution?
develop ponds to harvest rain water and use slow sand filters to clean water to entire village
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BC water utilities
3500 registered systems over 90% unfiltered, only chlorination most small, rural systems most have no control over environment/source quality higher rate of enteric illness than rest of Canada
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Canada boil water advisories
over 1000 communities | higher for aboriginal communities
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enteric illness in BC, Ontario/Quesbec, Praries, Atlantic | rater per 100,000 vs time
All have decreased by ~50/100,000 from 1987-97 BC ~50/100,000 more than O/Q/P BC ~100/100,000 more than Atlantic
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distance from water treatment plant
the further away you are the more at risk you are, may need second treatment
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economic returns from the biosphere
protecting/sustaining the environment lowers health costs
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Land-use activities
``` agriculture farming waste disposal pesticides/herbicides harvesting residential/industrial activities ```
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Land-use activities cause loading of
``` pathogens nutrients metals/organics humic compounds pharmaceuticals ```
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Surface/ground water protection and management must
Develop strategies to reduce loading understand transport and fat of microbes and chemicals Enhance community knowledge and understanding
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Effects on/of water for public health
land-use activities loading quality of source quality of output (tap)
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Affect quality of source water
``` pathogens algae toxins TOC/DOC taste/odour chemicals (drugs) ```
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Natural process affecting water quality
small vs larger grazer system recall: large fish = large grazers = smaller microorganisms (bacteria/algae/pathogens) which also = better water quality! (another problem of fishing down the food web?)
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processes that affect surface water quality
``` wildlife recreation forestry livestock drylands farming mining industrial urbanization climate ```
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Wildlife and surface water quality
beaver, otter, rabbit, ungulates, waterfowl | Protistan parasites
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Recreation and water quality
boating, ATVs, hiking, camping, pets, cottages, skiing | sediments, pathogens, hydrocarbons, herbicides
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Forestry and surface water quality
roads, clear cutting, camps, storage areas, stream crossings, slash burning microbes, turbidity, organic loading
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livestock operations and surface water quality
clearing, manure, feedlot, recreation, soil erosion | microbes, nutrients, turbidity
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drylands farming and surface water quality
clearing, pest/weed management, soil erosion | pesticide, herbicide, turbidity, salt
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mining and surface water quality
clearing, roads, waste rock, tailings, dust, living/operations turbidity, metals, acid mine drainage
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Industrial practices on surface water quality
wastewater effluent, contaminated sites, roads | turbidity, chemicals
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Urbanization and surface water quality
sewage, water extraction, roads, pets, clearing | nutrients, chemicals, turbidity, pathogens
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surface water quality is a measure of
parasites, bacteria, viruses, turbidity, nutrients, algal toxins, pH, hardness, alkalinity, natural organics, metals, hydrocarbons, chemicals
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water treatments
``` no treatment filtration sedimentation flocculation chlorination chloramination ozonation UV irrdiation ```
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contamination in water distribution system (after treatment)
intrusion regrowth permeation leaching
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Intrusion, contamination in water distribution system
``` Pressure drop faulty pipes/gaskets cross-connections unprotected tanks contaminated soil/groundwater ```
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regrowth, contamination in distribution system
distance from treatment plant nutrient availability regrowth conditions (biofilm) regrowth in tanks/pipes
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Permeation, contamination in distribution system
organic compounds plastic pipes elastomers
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leaching, contamination in distribution system
piping material corrosion pipe lines tank lines/seals
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flocculation
rocess wherein colloids come out of suspension in the form of floc or flake; either spontaneously or due to the addition of a clarifying agent
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airborne ammonia
72% of the variability in airborne ammonia explained by expansion of swine population 1988-1998: 0.1 - 0.4ppm
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N:P ratios based on source
``` highest: runoff of unfertilized field forest runoff rainfall manure seepage sewage ```
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controls on algal biomass and blooms
nutrients seasonality of nutrient input physical properties of receiving system structure of the foodweb
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% Total phytoplankton biomass vs. Lot TP (µg/L)
with an increase in TP shift to dominance of cyanobacteria (blue/green algae blooms)
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Mycrostin concentration (µg/L)
linearly increasing with TP, Toxigenic biomass, and TN | -increase # of algae = increase # of toxin producing algae
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major sources of P
septic, sewage, storm water, fertilizers
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biomagnification of BMAA example
cyanobacteria-- cycad-- flying foxes -- Chamorro people | neuro-degenerative & hepato-degenerative disease
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concentrations of BMAA biomagnified
cyano. 0.3µg/g cycad 37µg/g flying fox 3556µg/g x10^2 per "trophic level"
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Coagulation/flocculation
removes colloidal particles by adding coagulants
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sedimentation
Floc settles down to the bottom
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disinfection
kill bacteria and other organisms
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filtration
remove particles through filters
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disinfection byproducts
formed during treatment and disinfection
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water treatment steps
source water--coagulation/flocculation-- sedimentation--filtration-- disinfection-- storage
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Victoria water treatment
only disinfection (UV)
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Increasing disinfection
increases disinfection byproducts, carcinogenic
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Risk vs. Disinfection Level
Microbial curve is decreasing DBPs curve is increasing trade-off.. ideally in lower level of both risks
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some DBPs
``` disinfection by-products Chloroform Chloroacetic acid Chloro... Formaldehyde Acetone Acetic acid Benzoic acid ```
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DBPs produced by
1. Chlorine (produces almost all, strongest disinfectant) | Ozone, ClO2, Chloramines
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Disinfection by-products and birth weight
∆Birth weight (g) vs Concentration (µg/L) | THM, chloroform - decrease function
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THM
trihalomethane (chloroform)
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∂13C as a tracer for water condition
less negative ∂13C (lighter?) -- disturbed watershed | more negative -- pristine water source
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Caffeine
fecal bacteria enriched with caffeine, linear increasing (ng/L) Mussel Tissue- high caffeine rates for high ∂15N
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Ibuprofen (ng/L) vs. Caffeine (ng/L)
lakes all in the low left corner, ocean outfall very high in both
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molecular fingerprinting
take DNA profile of E. coli and compare to animals- tell which animal produced the e.coli gut bacteria specific to animal can tell where specific contaminant came from
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Shawnigan Lake facts
extensive development since 1900, more since 1970 forest harvesting septic inputs changes in fisheries from alien species
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Sooke Lake facts
protected since 1900 raised three time (1910, 1970, 2002) Introduction of Leech river water through Deception in 1988
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chloramination
treatment of drinking water with a chloramine disinfectant. Both chlorine and small amounts of ammonia are added to the water one at a time which react together to form chloramine
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main nutrient linked to algal blooms and toxins
phosphorous
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Lake sediments
preserve past records - can be used to see watershed changes and water quality - sinking of plankton biomass
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molecular fingerprinting
take DNA profile of E. coli and compare to animals- tell which animal produced the e.coli gut bacteria specific to animal can tell where specific contaminant came from
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Shawnigan Lake facts
extensive development since 1900, more since 1970 forest harvesting septic inputs changes in fisheries from alien species
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HPLC
High Performance Liquid Chromatography
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chloramination
treatment of drinking water with a chloramine disinfectant. Both chlorine and small amounts of ammonia are added to the water one at a time which react together to form chloramine
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main nutrient linked to algal blooms and toxins
phosphorous
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Lake sediments
preserve past records - can be used to see watershed changes and water quality - sinking of plankton biomass
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sediment core procedure
select study area and sampling site-- take sediment cores-- section sediment core-- data analysis-- analyze data
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sediment core data analysis
Pigment detection and quantification using HPLC
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HPLC
High Performance Liquid Chromatography
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Total algal biomass (mg/g organic matter) vs. year, Sooke and Shawnigan lake sediment cores
Sooke lake relatively straight | Shawnigan 3-10X higher biomass than Sooke, large spikes
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carotenoid pigment vs. year, Sooke and Shawnigan lake sediment cores
Shawnigan higher than sooke | Sooke watershed protection sustained excellent water quality over 100yrs
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Zeaxanthin pigment (bluegreen algae mg/g) vs. year, Sooke and Shawnigan lake sediment cores
Sooke pretty close to 0 over most of range, almost entirely less than 0.01 Shawn.- all over 0.01, up to 0.04
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∂15N vs. year, Sooke and Shawnigan lake sediment cores
~equal until 1920's both have increased Shawnigan higher from human/animal loading