Pollution Flashcards

1
Q

What can ecological light pollution include

A

Ambient light (eg sky glow)

Direct illuminance from the source (eg street lights)

(astronomical light pollution can reduce number of visible stars, tall lighted structures can be collision hazard)

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2
Q

potential ecological impacts of light pollution

A

Behaviour- sleep, orientation, foraging, mating

Physiological- stress, metabolism

Reproductive/fitness of pops- survival, nesting success, recruitment, phenology

Interactions- completion, predation, pollination, dispersal, herbivory

Community structure and ecosystem function- diversity, productivity

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3
Q

impacts vary among organisms and light sources

A

Artificial lights emit a variety of wavelengths

LEDs have a broad wavelength spectrum, with a particularly big peak at the lower wavelength- this is how they affect a broad range of organisms. The short peak wavelength of white light LEDs coincides with sensitivity of melatonin response and invertebrate behaviours to light

eg spiders affected by relatively low intensity of light

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4
Q

Light pollution and behaviour

A

Disorientation results from ambient illumination (light incidence on objects in an environment)

Attraction/repulsion in response to light sources themselves resulting from how bright they are

Foraging, expansion of foraging time- the nighttime niche

Territoial singing in birds- the night time niche

Eg sea turtles- hatchlings particularly effected b abroad wavelengths of light so can become disorientated. Could be light bouncing off water or actual light itself. Would normally go toward starlight off water but urban lights are much brighter so they get confused.

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5
Q

Effect of light on marine plankton

A

Both direct and indirect ski glow can increase depths of coastal marine invertebrate activity. Sea plankton are sensitive to small changes in short wavelength light bc this time of light goes furthest into the water. They show sensitivities by movement. Light affects depths at which behaviours are triggered- implications for community and ecosystem dynamics

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6
Q

Pollination and light

A

Night lights can have varying effects on moth pollination with effects on community networks. Effects can spill over into unlit regions. eg the lit region may have an increase in moth abundance. Other effects:

Concentration effect- moth had higher abundances in lit, strong interactions incr, weaker lost

Ecological trap- moths attracted up to light, some weaker interactions lost (between plant and bug), may have decreased flower visiting activity

Disruption effect- moth behaviour disrupted around light (decr flower visiting activity)

Preferential disruption effect- behaviour of a subset of moth spp disrupted ( eg larger spp), decreased flower visiting activity by some spp

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7
Q

Dispersal and light

A

Light might repel important seed dispersers in tropical systems eg fruit bats in costa rica. Lit/dark choice experiments clearly show preference for the dark. Bats feed on epiphytes, light might repel this bat from fulfilling its dispersal role and could work with other bat spp

In wild pops, fruit were harvested from a greater percentage of unlit piper plants than lit.

After sunset, fruit was harvested >3 hours in lit, compared to 90mins in unlit. Lower foraging frequency and longer delay may impact on forest successional dynamics in heavily lit, unfragmented areas.

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8
Q

Effect of light at night on plants - phenology

A

Using light data from satellite images and controlled for urban heat island effects and background temperatures. Looked at bud burst. Compared four different spp that opened at different times.

In brighter areas bb advanced by 7.5 days. Stronger effects for later budding spp. Even more pronounced when excluding large urban areas

Light may also affect growth and reproduction, top down effects of predators and herbivores on plants and bottom up effects on herbivores and invertebrates, effects varying with light colour

Number of inflorescences lower with lighting on greater birds foot trefoil. Consistent effect of lighting with herbivores present. Aphid abundance lower with amber lighting in August only. Limited evidence of bottom up effects. Aphids prefer to feed on inflorescences, so if less reproduction for plants the they’ll be affected- experiment type kevin gaston boxes in field?

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9
Q

Mitigating the effects of light pollution

A

Buffer zones to reduce light levels in core protected areas. Ambient light may still be an issue. We would limit artificial lighting and urban development - could be around national parks.

Light reduction and shielding- focussed light sources downward pointing, hooded lights. Conflict of interests (safety) could turn off for periods of time. Even focussed light sources can disorientate/attract/repel at a local scale

Technological solutions eg make light have longer wavelength. In turtle areas could make light shredder. Seen evidence of huge reduction in disoriented hatchlings.

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10
Q

Challenges to understanding the effects of light

A

Confounding factors- european robins in urban areas might sing at night. This was initially thought to be a shift to the ‘nighttime niche’ bc higher levels of light. But evidence suggests the shift may be due to noise pollution. Birds sing at night so they can be heard (sound interferes with communication). Can see correlation with noise and signing so this is thought to be more likely. Fitness benefit to shifting to night

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11
Q

Sound pollution in PA

A

Researchers found that 63 percent of all U.S. protected lands are exposed to manmade noise that is at least as twice as loud as ambient sounds from natural sources like wind

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12
Q

Potential ecological effects of sound

A

Behaviour - sleep, foraging, mating (communication)

Physiology - stress, metabolism,

Reproduction/fitness of the pop - survival, nesting success

Interactions- competition, predation, pollination

Community structure and ecosystem function - ?

A lot of the work focusses on individual animals, a lot less on community structure and impacts

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13
Q

Sources of sound pollution

A

Intentional (aquatic)

  • seismic exploration (prospecting for prescence of oil, vessels emit high pressure sound that is absorbed into seabed)
  • harassment devices- eg in fisheries, might want to repel predators of fish using sound devices

Unintentional

  • industry eg pile deriving to create foundations and mining, oil wells, compression of gases out of terrestrial gas wells
  • transport
  • construction
  • forestry and mining
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14
Q

How can sounds manifest below water

A

As pressure (sound waves) or as particle movement

Animals hear either or both forms

Can be short wave (0-8KHz)
Or long wave (90-200KHz)

This coincides with hearing freq and communication freq in multiple taxa. Noise pollution in most cases leads to some sort of response. Almost all cases for invertebrates

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15
Q

sound and behaviour and reproduction of birds

A

Gas extraction sites either with or without gas compressors

Measured

  1. survival
  2. predation (particularly by brood predator spp)
  3. number of nest predators

Found

  1. survival lower in control (no noise)
  2. Greater predation in control,
  3. Higher rate of nest predators in control sites

Noise repels predator species. Another study found nesting species richness lower in noisy sites. Different spp composition at sites,

spp present in noisy and quiet had higher nesting success in noisy

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16
Q

Wider community effects of noise pollution

A

Artificial flower (with sugar and water) visitation and pollination by hummingbirds. Noisy sites had higher number of hummingbirds visits.Pollen transfer high within and between patches.

Pine seed predators (mice) seen at more feeding stations with seeds in noisy sites. Seed disperser (western scrub jay) avoids noisy sites completely. so may have more seed predation of important trees–> may lose dispersal services of jay. Mous predators locate and hunt using sound. Cant do when nose. Evidence of lower pine recruitment at noisy sites

17
Q

What are possible proximate, ultimate, and ecological effects of noisy pollution

A

POP

18
Q

Stress responses of sound pollution

A

Play back experiment measuring opercular beat rate (gill covers) in Eu Seabass.

Faster beat = more stress

Naive fish (never experienced sound, newly developed) or noise experienced

Heard: pile driving, ambient noise, passing shifts

Naive and experienced fish showed greatest response to pile-driving, then ships. Found responses reduced after time –> could become desensitised. Read paper

19
Q

Pile driving and seismic blasts

A

Certain types of sound pollution will lead to less responses. Not entirely clear why they are being desensitised. Both noises incr operculum rate compared to ambient. Hearing pile driving reduces reaction to pile driving and seismic.

But for seismic, only seismic is reduced response

20
Q

Mitigation of noise pollution

A

US wilderness areas have lower levels of noise than other PA, but still 63% have x2 normal levels. PAs with buffer zones have lower noisy levels. Pa< unprotected. Even if we keep people out can still get noise from planes etc.

21
Q

Challenges to understanding sound effects

A

Confounding effects- robin light/sound

Realism of exp- noise playback not always true copy of actual sounds. Particle movement is prominent manifestation of noise in tanks (less pressure waves) But it does ensure animal cant escape noise so we can see reaction

Bc of immediacy of effects of light and sound pollution means organisms cant adapt in many cases

22
Q

How does s and n get into the atmosphere

A

Burning of cheap coal