8.2 Canopy Forming Seaweeds Flashcards

1
Q

what are canopy forming seaweeds?

A
  • Kelps, fucoids and other complex, erect mainly brown macroalgae that produce relatively large biogenic habitats
  • They include some of the largest marine algae, with thallus divided into basal part, stem and frond.
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2
Q

life cycle of fucoids (Facales)

A
  • fucoids are diploid
  • life cycle is a diploid monogenetic cycle
  • reproduction through gametes
  • gametes produced by meiosis
  • gametes carried by antheridia and oogones (found within apical male and female conceptacles)
  • fertilization in water
  • new diploid plants will be generated again from the zygote
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3
Q

life cycle of kelps (Laminariales)

A
  • haplodiplont cycle
  • alternation of two morphologically distinct phases:
    1) diploid sporophyte (macroscopic)
    2) haploid gametophyte (microscopic)
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4
Q

Distribution of canopy forming seaweeds
(facts and map)

A
  • widespread on shallow hard substrata
  • in temperate and polar coastal ecosystems
  • main genera along coasts of north-west Europe: Laminaria and Fucus
  • main genera in Mediterranean Sea: Cystoseira and Sargassum
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5
Q

facts about canopy forming FOUNDATION species

A
  • they modify light, flow, sedimentation and nutrients
  • they buffer erosion
  • they are nursery areas
  • highly productive
  • habitat for diverse assemblages
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6
Q

human usage

A
  • food
  • cosmetics
  • fertilizer
  • stabilizers and emulsifiers
  • medicines
  • thalassotherapy
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7
Q

estimated value of canopy habitats

A
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8
Q

these systems (canopy forming seaweeds) are___ ?

A
  • naturally dynamic
  • resilient
  • have a generally rapid recovery from disturbances (ms to a few years)

they are influenced by
- dispersal
- biotic interactions (competition with understory species, herbivores)
- habitat characteristics

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9
Q

retraction of canopies
where?

A

(Rückgang)
documented widespread range retractions and declines since 1900’s in
- Europe (examples of Sweden and Mediterranean Sea were shown in slides)
- North and South America
- Japan
- Korea
- South Africa
- Australia
- New Zealand
- Alaska

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10
Q

what are canopies replaced by?

A
  • turfs
  • ephemeral algae
  • mussels
  • barrens
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11
Q

what are algal turfs?

A
  • they are loosely to densely aggregated thalli
  • < 15cm tall
  • composed of more or 1 species
  • often associated with sediments (sediment-trapping morphology)
  • covering large areas
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12
Q

global map of canopy-shifts to turf

A
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13
Q

where are losses particularly severe?

A
  • in urban areas
  • e.g. Italy:
  • 13 sites around Italy
  • 40% of losses of C. compress explained by urban-related indicatorsw
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14
Q

what are canopy-losses accelerated by?

A
  • climatic changes
  • drives shifts in species compositions (e.g. Laminaria along
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15
Q
A
  • Shift from canopy to less complex systems is globally happening
  • Functional consequence?
  • here: example of temperate seaweeds
  • System shifty in many different ways
  • lost and replaced by b, c, d
    b) function don’t change too much
    most similar to system befor
    novel system with similar function
    c) d) different system , diff. species and functions
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16
Q

multiple stressors that drive changes in kelp forests

A
  • pollution
  • fishing
  • harvesting
  • invasions
  • herbivory
  • warming
  • others
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17
Q

conceptual models of canopy shifts

A

most likely drivers of loss here:
- decreased water quality through sedimentation
- cascading effects from overfishing (as Orcas/Alaska example)
- regression of macroalgal canopies –> turfs, ephemeral algae, mussel or barrens

-2 main types of alternatives: turfs and urchin
- in the conceptual model, two pressures are always there: x + y aches
- Low water quality from canopy to turf
In one case its barren (urchin), in other one turf, different, but in both we lose

18
Q

cascading effects of predator removal

A
19
Q

graph showing temporal trends in kelp forests where otters (predators) and sea urchins are present (Alaska)

A
  • arrows indicate the timing of change in major community-changing forcing functions
  • width of arrowheads indicates magnitude of the forcing function’s impact
20
Q

graph showing temporal trends in kelp forests and sea urchins (Gulf of Maine)

A

Urchin dominant-> loss of kelp -> fishing urchin –> kelp comes back

21
Q

Northern California - trophic cascade (fishery, urchin, kelp, barrens)

A
  • Strongly dominated by fishery
  • Start of fishing urchins: kelp came back
22
Q

graph showing temporal trends in kelp forests and sea urchins (Nova Scotia, Canada)

A
  • Extremely fluctuating system
23
Q

Southern California - Trophic Cascade

A
24
Q

graph showing temporal trends in kelp forests and sea urchins (California)

A
  • When top control removed, other factors come in to control
  • Strongly dominated by el nino
25
Q

water quality is declining, why?

A
  • Oceans long regarded as a dumping ground for humans
  • Changes are more difficult to see and so are easy to ignore
26
Q

changes to water quality can include ___ ?

A
  • increased nutrient loads
  • enhanced sedimentation rates
  • turbidity
  • reduced light penetration (needed
    for photosynthesis)
  • increased temperatures
  • altered salinity regimes
  • harmful algal blooms
  • toxins, herbicides and heavy metal
    pollutants
27
Q

what is one of the main drivers of the loss of canopy forming algae and their turf-replacement?

A

enhanced sedimentation

28
Q

what happens when sediments interact with other types of pollution?

A
  • other types like nutrients or acidification
  • greater negative effects than alone
29
Q

examples of recovery from barrens

A

1)
- in southeast Alaska
- kelp beds recovered after reestablishment of sea otters
- due to local protection

2)
- over-fishing in a Reserve, New Zealand
- declared unproductive when sea urchins und unproductive barrens habitat was dominating (1997)
- by 2003 , large predaory fish and lobsters had returned, urchin populations had declined, and lush kelp forests returned
- But: this community change was recent and highlighted a time-lag effect of protection

30
Q

loss of canopy forming algae in the mediterranean sea due to ___ ?

A
  • date mussel fishery
31
Q

recovery from barren to canopy can be difficult, why?

A
  • Many habitats have not recovered yet as the empty holes enhance sea urchins recruitment
32
Q

why are turfs so stable?

A

Sedimentation mediates interactions between canopies and turfs via direct and indirect effects:
- Turfs accumulate sediments and can trap large amounts
- Accumulation of sediments deters grazers: Herbivores are generally sparse in areas with high sediment loads
- Accumulation of sediments inhibits the recruitment of erect algae that compete for space with turf: Sediment virtually precludes settlement, and reduces survival of germlings by >50%

33
Q

feedback mechanisms that pave the shifts between canopies and turfs

A
  • pulse sedimentation events (e.g. beach nourishment) remove canopy algae
  • sediment no longer removed by canopies accumulates
  • accumulation of sediments favours development of turfs which further bound and stabilize sediments
  • algal turfs replace and prevent re-establishment of productive canopy forests
34
Q

the shift from kelp forest to turf can be accelerated by ___ ?
name some negative effects on kelps

A

1) climatic stressors as heat
- that can delay the population recovery (germlings survival higher under low temperatures)
- ocean warming can increase herbivorous fish pressure

2) increased storminess
-storms may destroy recruitment which was consistent

3) other stressors such as herbivores

4) increased substratum instability

5) water quality/ sediment accumulation

–> Meta-analysis shows, that ultimate effect on seaweed is driven by combination of many factors (e.g. overfishing, water quality…)

35
Q

synergistic

A

Synergistic: resulting effect is greater than the sum of independent effects (greater effect)

36
Q

prevalence of synergistic interactions between nutrients and other global stressors leads to ___ ?

A
  • Synergistic interactions between nutrient
    enrichment and the presence of competitors, low light, and increasing temperature, leading to amplified negative effects on canopy- forming algae.
  • Synergistic interactions between nutrient enrichment and increasing CO2 and temperature leading to amplified positive effects on mat-forming algae.

—-> Nutrients are major player in issues of our system: if you can improve that factor, it has a major effect and improvement because it acts synergistic with so many others

37
Q

can the management of local stressors remediate for the impact of global stressors?

A
  • Systems were stressed before (local stressors)
  • “now” climate change comes on top (global stressor)
  • global stressor will not change but can situation be improved if local stressors are improved?
38
Q

experiment: can the management of local stressors improve the resilience of Marine Canopy Algae to global stressors?

A
  • yes
  • different climatic scenarios and management scenarios were tested in an experiment
  • Cystoseira doesn’t recruit when there is sediment (NM = no management)
  • Ranking: sediment removal, because it has a high effect on recruitment
  • Also Nutrients
  • is is a matter of HOW to manage climate change factors, because systems can (!)
  • Connectivity as very important gradient (be aware when managing)
39
Q

can canopies actively be restored where natural recovery is low? give examples

A
  • If you just protect they will hardly recover
    –> active restoration needed

example 1
- crayweed restoration (Sydney, 2014)
- First: driver removed but seaweeds didn’t come back
- then: Decided for active restoration
- big and worldwide success

example 2
- Kang et al. 2008 at east and south coasts of Korea
- In 2003 restoration using a combination of transplants of adults on artificial reefs
- In 2005 complete recovery of macroalgal community structure and trophic food webs

40
Q

what are the most common approaches to restore canopy forming seaweeds

A
  • adult-plant transplantation on either natural or artificial substrata
  • transplantation of juveniles either collected or intercepted in the field by using artificial panels or cultured indoor
  • seeding of germling in the field (generally associated with creation of artificial habitats)
  • use of “fertile mesh-bags” packed with fertile, adult plants suspended over rocky substrata or artificial reefs during the reproductive season
  • Enhancement of natural recruitment e.g. by using chemical fiber fabrics
41
Q

what are challenges in reforestation of canopy forming seaweeds

A
  • biotic disturbance
  • scientific challenges (e.g. herbivory very high at urban sites as compared to nearby rocky reefs)
  • practical challenges (e.g. identifying cost-effective tools to protect reforestation efforts)
  • economic challenges (–> expensive)
  • conceptual challenges (–> what do you want to/ decide to restore in the end?
    Restoration doesn’t put exactly back what used to be there before
    Going back to what used to be ther?
    Saving functions? /services?)
42
Q

what can buffer the impact of global stressors?

A

coordinated remediation of local stressors (e.g. water quality) - at least temporarily