1/51
Looks like no tags are added yet.
Name | Mastery | Learn | Test | Matching | Spaced |
---|
No study sessions yet.
what does biological activity of aquatic ecosystems depend on
activities of primary producers
the activities and net numbers of phytoplankton depends on:
temperature
light received
availability of specific limiting nutrients such as nitrogen and phosphorous
what is the photic zone
the depth into the water that light will penetrate in clear water
300m
relevancy: microorganisms must be able to harvest the light that reaches them using accessory pigments
characteristics of marine environments
high salinity (halotolerant organisms)
below 100m the temperature is constant 2-3C
open ocean characteristics (pelagic zone)
low primary productivity due to low inorganic nutrients
oligotrophic
cool, constant temperatures
wind and ocean currents can cause upwelling to bring nutrients to the surface and promote productivity
where does most primary productivity in the open ocean happen
prochlorophytes (related to cyanobacteria) - prochlorococcus
what are adaptations seen in pelagic microorganisms
reduced size for higher S:V ratio
high affinity transport systems
what are the characteristics of coastal waters
eutrophic: productivity is higher because of the influx of nutrients from rivers and other polluted water sources
can cause red rides - nitrogen is a limiting nutrient
higher concentration of animals due to higher primary productivity
what are the primary producers in coastal waters
algae and cyanobacteria
what is the deep sea
300-1000m deep
chemoheterotrophs live off dead organic matter that falls (psychrophiles)
organic carbon is scarce, there are very few microorganisms below 1000m
what are hydrothermal vents
sources of heat, nutrients, electron donors and aceptors
generates community of microorganisms and animals
example of animal in hydrothermal vents
tube worms - symbiosis with sulfur oxidizing chemoautotrophs
trap and transport nutrients to bacterial symbionts
freshwater environment characteristics
highly variable
microbial populations depend on nutrient availability and light and oxygen availability
limited by N and P
lakes have poor mixing and aeration while rivers have good
oligotrophic lakes (N and P limited)
low primary productivity and organic matter
growth of aerobic chemoheterotrophs limited by nutrient supply
organic matter doesn’t accumulate
rate of oxygen dissolution is higher than the comsumption rate - oxygen saturated
clear water - deep light penetration
eutrophic lakes (nutrient rich)
high primary productivity and organic matter
rapid growth of chemoheterotrophs and rapid depletion of dissolved oxygen
low O2
anaerobic zones are created
poor light penetration
there’s another slide i’m overwhelmed by
how do anaerobic zones develop
due to summer stratification (temperature differences)
how does temperature stratification work
when air temperature rises, surface water is warmed forming the epilimnion which is less dense
the cold bottom layer - hypolimnion - is separated from the epilimnion by the thermocline
what is the thermocline
zone of rapid temperature change that separates the hypolimnion and the epilimnion in temperature lakes
what is mixing in lakes
happens in fall and spring when water temperature is constant in all layers
brings nutrients up the water column
mixing in rivers
good
ensures organic matter is degraded effectively
no fermentation or H2S production occurs
excess organic matter may happen in anaerobiosis which leads to similar things as eutrophic lakes
pollution of fresh water
deliberate discharge of effluents into a water way
why is sewage a pollutant
rich in organic matter
contains a large number of organisms - some may be pathogens
organic matter is oxidized using dissolved oxygen - high BOD
what happens when biochemical oxygen demand (BOD) is high due to pollution
water becomes anaerobic, microbial metabolisms increase
fermented products, sulfate reduction, nitrate reduction
what is biofilm
microbial cells embedded inside an extracellular matrix
usually produced by mixed populations of species
resistant cells
found in water systems
how do biofilms happen
attachement of a few motile cells
colonization and growth
development
active dispersal of motile cells - triggered by environmental factors
properties of biofilm (slide)
localized gradients, sorption, enzyme retention, cooperation, competition, tolerance and resistance
water borne pathogens
grow in intestinal tract and transmission is mediated by fecal contamination of water supplies
what are sources of water borne infections
potable water and recreational water (swimming)
examples of water borne pathogens (slide)
salmonella typhi, campylobacter, enterovirus
what does entamoeba histolytica cause (water born pathogenic protozoa)
amoebic dysentery
what does giardia lamblia cause (water born pathogenic protozoa)
giardiasis (beaver fever)
diarrhea
associated wtih drinking water in wilderness areas
cryptosporidium parvum (water born pathogenic protozoa)
diarrhea
no reliable treatment
cyst formation of G lambia and C parvum
form cysts that are resistant to disinfectants
c parvum cysts are not removed by plant filtreation of water
how can water be tested for quality
test for organisms that are present in large numbers in feces
indicates that the water might also contain pathogens
presence of fecal coliforms indicate contamination
absence does not guarantee water quality because of cysts
what are the two water quality indicators
coliforms and fecal coliforms
coliforms as quality indicators
can ferment lactose, are facultative aerobes
bacteria that are not all of intestinal origin
fecal coliforms as quality indicators
coliforms derived from the intestines of warm-blooded animals
thermotolerant
membrane filtration testing
drains a water sample through a filter to catch the pathogen cells which are then cultured
tests large volumes of water
detects both coliforms and fecal foliforms
faster and easier than MPN
most probable number (MPN) testing
tests for coliforms
samples are added to a lactose broth
positive when gas is produced
uses statistical tables to estimate number
requires further testing to confirm
what are the goals of water treatment
remove pathogens
improve clarity
remove compounds that taste or smell poor
soften the water
what are the steps of water treatment
sedimentation
flocculation treatment (chemical coagulation)
filtration
disinfection
what is the sedimentation step
leaving water to stand
allows large particle to settle
what is the flocculation step
a coagulant is added
water in transferred to a flocculation basin and allowed to settle
precipitates form and trap fine particles
80% of bacteria and colour have been removed
what is the filtration stage
water is filtered through sand to remove remaining particles and cysts
most bacteria has been removed
filter is backflushed to prevent clogging
what is the disinfection step
chlorination to kill remaining organisms and neutralize stinky chemicals
residual chlorine: leftover chlorine when it leaves treatment plant intended to protect the water in the distribution system
using ozone for disinfection
more effective than chlorine because it can kill cysts however it has a very short half life
wastewater/sewage treatment aims
reduce BOD and removes organic matter
destroys pathogens
requires a primary and secondary and tertiary treatment
primary treatment
sedimentation tanks and flocculation
produces primary sludge
reduces BOD
can be discharged into waterways or to secondary treatment
secondary treatment (liquid stage)
trickling filter: liquid from primary treatment is sprayed over rock so that microorganisms form a biofilm and oxidize organic matter - reduces BOD
activated sludge: air is blown through the liquid, slime forming bactera clump and form activated sludge to oxidize OM. sludge is removed for disposal - reduces BOD
secondary treatment (sludge)
sludge is microbially digested under anaerobic conditions
CH4 produced can power the plant
BOD is reduced
remaining material is burned
tertiary treatment - liquid
reduced BOD, bacteria and N and P
can be biological treatment, flocculation, filtration, chlorination
final liquid effluent may be suitable for drinking
septic tank
minimal treatment
inside the tank the material settles and minimal sludge digestion happens
effluent flows to a leaching field so the soil can filter and decompose organic matter
cannot contaminate groundwater or waterways because it is disgusting!