Water Quality

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01/23/2009

Monday: List of at least 5 journals that have aquatic topics • • • • Water quality Water pollution Water resources Lake management

Water quality

• •

Pure and essential character Utility of the water

○ Drinking water ○ Industry ○ Agriculture

Water pollution



Human caused deviation from the norm that degrades its use



Impairment of the suitability of water for any of its benifitial uses (actual or potential) by human caused changes in the quality of the water

Types of pollution • • Thermal Chemical

○ Toxins/metals ○ Nutrients

• • •

Organic matter Sediment Pathogens

Point-source pollution

• •

Pollution that can be traced to a specific source Examples: storm water and sewer pipe

Non Point source pollution • • • Agriculture Mining Forestry

Water quality criteria



Value or limit associated that elicit a response

Water quality standards • • Criteria taken and done via rule making to establish requirements No human activity can result in an increase of ambient water temperature by more than 5 degrees. • • No drop in oxygen by more than 5mg Done to assure criteria are met

01/23/2009

1956 – Federal Water Pollution Control Act (first significant water quality legislation)



First attempt of the federal government to address water pollution nationally

• • •

Construction grants for sewage treatment facilities 5-year grants for research and planning for water quality control Federal Water Pollution Control Federation established (Cincinnati, Ohio)



Network established to collect water quality data

1965 – Water Quality Act



Required states to develop and submit qater quality standards for its interstate water and tributaries. And the federal government was empowered to review and accept/reject states’ water quality standards



More $$ for treatment facilities, construction and technical assistance

01/23/2009

1972 – Federal water Pollution Control Act (earlier laws did not address interastate waters and agriculture was not covered, modified several times since). • Section 101 – ambitious objective to restore and maintain the chemical, physical and biological integrity of the nations waters. ○ Federal $ provided for treatment ○ Area-wide waste treatment management planning ○ $ for research and demonstration ○ Nodischarge into navigable waters ○ Fishable and swimmable waters by 1983 (since modified) ○ Prohibited discharge of toxic pollutants



Section 303 – Water Quality Standards and Implementation Plants (completed) ○ Required states to submit standards for EPA approval that meet or exceed national standards ○ Continuous planning



Section 304 – Information and Guidelines

01/23/2009

○ Requires EPA to supply state agencies with guidelines for identifying and evaluating the nature and extent of non-point source pollutants ○ Established processes, procedures and methods to control pollution resulting from non-point activities (agriculture, forestry, mining)



Section 402 – National Pollutant Discharge Elimination System (NPDES) ○ Permits required for discharge of pollutants ○ States develop their own programs that are approved by EPA ○ States must submit permit applications and recommendations to EPA



Section 404 – permits for Dredge and Fill Materials (wetland protection included)



Section 208 – Area-wide Waste Treatment Management

○ Designate problem areas ○ Continued planning and funding for non-point source control

01/23/2009



Section 315 – Clean Lakes ○ On a biennial basis each state must submit to EPA an identification and classification of all publically owned lakes ○ Must describe procedures for pollution control ○ Must list lakes that do not meet water quality standards ○ Must assess trends in water quality



Section 319 – non-point source management program (emphasis on BMP = best management practices) ○ Where most comes from

Overally, greater federal power to set and enforce standards (inter and intrastate). Plus, specifically addresses non-point pollution. Law has been modified many times to adjust to scientific concerns and technology

01/23/2009

2/3 of water that falls is transported elsewhere Brazil 20% of global water Residence time is how long a drop of water stays in a body of water Ocean = 2,500 years Atmosphere = 8 days Streams/Rivers = 1 month Lakes = depends on depth

Infiltration capacity



Depends on ○ Amount of water already in soil ○ Type of landscape

 Wal-mart parking lot (will not infiltrate)  Vegetation present  Surface flow



Figure 5-4 (runoff) ○ Rising limb

01/23/2009

 Mostly surface runoff  Dust, “urban slober”

 Picks up things ○ Falling limb  Less surface runoff  More subsurface flow  Deposits things

01/23/2009

○ Results  Bar configuration changes  Sand bars move  Changed water chemistry (on decending limb)

Figure 5-2 • Clearcutting makes rain more of a problem

Figure 1.10



Floodplain: when river hits peak flow and goes into floodplan it spreads nutrients into the floodplain as well as collecting the organic matter from the floodplains back into the river



“reach” of a river

○ encompasses pools and riffles  riffles  where bedrock/gravel deposits make water go at low flow as it travels over bedrock  very little sand and clay

01/23/2009

 Pool  Zone of scour, deposits materials in it

Stream order classification

• • • •

1, channel, doesn’t always have water 2, where two headwater streams come together 3, where two second order streams come together 4, (hinkson)

4x as many 1st order as 2nd etc etc direct relationship between length of stream and order on world scale, very few 8th order/ 9th order streams

Move from forested to impervious surfaces

• • •

Decreased deep infiltration (i.e. aquifer refill) from 25% to 5% Increased runoff from 10% to 55% Decreased evapo-transpiration 40% to 30%

01/23/2009

Ecosystem • Def: Where chemicals cycles and energy flows within various compartments • Boundries?

○ There aren’t but it depends on what scope you want to use ○ Watershed is best use of limits



Ecosystem obeys laws of thermodynamics ○ Lake Tahoe basin  Ship food in



Structure ○ Physical setting ○ Organization

 Food web  Native community  Introductions  Exotics

01/23/2009

○ Function  How energy is transferred  Green Plant Food Chain/Web • Upland ○ Grass  Bunny  • Primary ○ Herbivore  Carnivore  Lake • Sun and nutrients (nitrogen and phosphorous) lead to Coyote

01/23/2009

- Primary producers

○ Algae (vary in size remarkably) ○ Macrophytes ○ Periphyton (attached algae)

- Herbivores  Macroinvertebrates  Zooplankton  Water fleas  Filtration feeders  Fish

- Carnivores   Bass Birds

Autochthonous energy • Nutrients N + P > Primary > H > C > C

01/23/2009

○ All contribute to dead OM which returns as N and P watershed, nutrient cycling ○ Some herbivores also eat dead organic matter

• •

Bacteria are taking C-C-C and O2 and offputting CO2. Allochthonous energy

○ Energy produced outside the ecosystem and is transported in as dead organic matter ○ Example:

 corn stock floating to a reservoir  Decaying organic carbon  Hog waste pool

○ Human impacts  Organic carbon additions  Add fish species  Fertilizer runoff

01/23/2009

○ We depend on nutrient income from year to year in order to have primary production ○ Wet/dry year affects organic productivity

 Dry year could have 1/3 of organic production wet year has • How do lakes get on landscape? ○ Glacier  Carves it out  Huge chunks of ice breaking off being left behind

  

Melting Caved in “kettle lake” Raisin cookie without the cookie

○ Oxbow lakes ○ Volcano lakes

 Alaska  Indonesia

01/23/2009

○ Dams  4k year history ○ Landslide lakes ○ Techtronic lakes

 Lake Tahoe  Faults cause movements

○ Sinkhole  Karst topography  Erodes out, limestone, collapses

○ Wind activity  Playa lakes  Nebraska sandhill lakes

Lake names • • • Margin of lake is littoral Benthic is bottom Perfundal is near bottom

01/23/2009

• •

Pelegic Trophogenic

○ Enough light for green plant production  P/R > 1   R is respiration P is production

 This level is determined by  Water clarity • • • Which is determined by density of algo cells Clay materials/ suspended particles Color

 

Determines depth of light Hoping Production exceeds respiration



Tropholytic ○ Example being ocean floor ○ Depends on rain of organic matter from surface

01/23/2009

○ Below trophogenic ○ P/R < 1



Light ○ Some bounces off ○ Some enters body of water

 Some of this scatters  Some taken in by algae

  DOC  

Absorption

(color) absorbs light

○ Long wavelengths absorbed in upper centimeters  Thus warmer ○ Decrease in light with depth

Light meter reading

01/23/2009

• • •

One meter, half the light is gone 2 meters, half of that half if gone (25% of surface) etc

O -------------------100%  (Z) | | | | |



Productivity is a surface phenomena ○ Light decreases exponentially in a lake



Long wavelengths of light heat the lake but they are gone within a couple centimeters ○ Wind energy distributes it ○ Mixed water column

01/23/2009

○ Infrared molecules are absorbed at the surface

Color • • • Green, nutrients, algae cells, Dissolved organic carbon absorbs blue Blue, less nutrients, etc Brown lakes: suspended clay

Water molecule

• • • •

Dipole molecule H+ H+ (covalently bonded) to self, hydrogen bonded to each other

O-

break bonds to go from ice to water

○ ice tends to be fairly pure of chemicals compared to lake water ○ add of heat stenches hydrogen bonds

Density

01/23/2009

temp (see handout)

4 degrees C is max density of water beyond that hydrogen bonds are stretched which makes less hydrogen bonds in a given area ice floats because perfect tetrahedral cold water sinks warm goes to surface

Why does lake look blue? (test question)

Figure 3-4 Iced over lake

01/23/2009

1 meter ice 15%

depth 4 degrees

Melting

• • •

Lake warms incrementally (spring overturn) 4,5,6,7 sunny and not to winding will cause heat energy to not mix all the way to the bottom

○ determined by  depth  color of water



clear absorb more heat

 hills/orientation of lake in relation to wind direction

01/23/2009

○ See figure 4-1  Mixed water, above curve is called   Epilimnion Metalimnion

• 

Also called Thermocline

Hypolimnion

 In high temperatures a secondary thermocline can form  Can effect algae



Uv light destroying cells etc

 In early fall/ late summer    Stratified lake Cooling of epilimnion Deepen epilimnion until thermal stratification is eradicated  Cool bottom to 4 degrees, cool surface, creates ice

○ This kind of lake is called dimictic

01/23/2009

 Winter stratification, cold over warm water  Spring overturn, mixed  Summer, warm over cold water  Fall overturn then repeat

 

North are usually dimictic South they usually are monometic

• •

Only stratified summer Rest of the year it mixes without ice cover

Inflow • • Most lakes have around 28-32C temp in summer inflow comes in cold and will sink to bottom water column or interflow • cold water sinks

Oxygen

01/23/2009

• • • • •

Mirrors productivity of lake

Top of lake

------P/R (sent down lake as organic matter) O2



O2 decreases with depth ○ Depletion of O2 relates to increase of organic matter ○ Cold water holds more oxygen than warm water ○ Oxygen could go up with depth if bottom is colder and lakes lack organic matter



Oligotrophic ○ Low in nutrients, low in biomass, low in organic material ○ Tend to be clear, no alpha cells ○ O2 with depth



Eutrophic ○ Low clarity

01/23/2009

○ High nutrients ○ O2 depleation with depth



Mesotrophic ○ Between the two ○ 60% resivours in Missouri ○ 20% are Eutrophic ○ 10% are Oligotrophic



Hypereutrophic ○ Think about it



Problem ○ Warm surface, O2 depleation with depth ○ Increase temp 10 degrees, double metabolic activity (bacteria)

Water concentrations



Mg/l ppm (part per million)

01/23/2009

○ 0.040 mg/L P (phosphorous) • Mg/l ppb (parts per billion) ○ 40gm/L P

Total Particulate Dissolved

40 mg/L PO4-P



-P means weight of Phosphorous

40 mg/L PO4

Turbidity



NTU ○ Measure of tingle effect of light  Hinkson data  8

01/23/2009

   

20  (rain started before this sample) 100 80 54

 stable flow      10 12 13 10 11

 variance of hinkson   3 to 300 NTU TP 2-718 ug/c



LOTO ○ 1980  15 ug/c TP  18 ug/L

01/23/2009

○ 1981  47 ug/L  168 ug/L

Cations in water sample



Ca ○ 15 mg L



Mg ○ 4.1 mg L



Na ○ 6.3 mg L



K ○ 2.3 mg L

Ozark • Ca ○ 24 mg L • Mg ○ 9 mg L

01/23/2009



Na ○ 3 mg L



K ○ 2 mg L

Anions



HCO3 ○ 58 mg L



SO4 ○ 11 mg L



Cl ○ 8 mg L

Ozark • HCO3 ○ 64 mg L • SO4 ○ 9 mg L • Cl ○ 4 mg L

01/23/2009

meq/L



charge measurement via its weight

Na+ Cl-



Good indicators of mammalian contamination

Hinkson



Highest turbidity ○ Lowest conductivity

Ecological consequences of artificial night lighting



01/23/2009

1998 – EPA sets goal for states to have criteria by 2003 • • 50% of monitored surface waters impacted by excess nutrients nutrients most common impairment causing pollutant

2003 • No states meet deadline ○ Nutrients are naturally occurring ○ Nutrients are not direct cause of impairments ○ Nutrients/algae are required for a healthy aquatic ecosystem ○ Diverse population of water bodies with multiple uses

2005



MoDNR and EPA agree on plan of action in July, with first stakeholders meeting in October ○ Focus on lakes/reservoirs first, followed by streams/rivers then wetlands

01/23/2009

○ Stakeholders include agency personnel, industry and agriculture representatives, environmental groups, scientists and general public

2007 • Scientific sub-committee formed in January ○ After 15 months many ideas had been discussed but none accepted by stakeholders 2008 • • Approach for setting nutrient criteria for reservoirs submitted to MO Clean Water Commission in April

Suggested Approaches



Impairment-based Approach ○ Reduce nutrients to levels that eliminate impairments associated with high concentrations of algae.

01/23/2009

 Designate use  Identify impairment • Relate impairment to Algal Chlorophyll (biomass) ○ Correlate Algal Chlorophyll to Nutrient Concentration • Problems ○ Difficult to identify impairments for some uses ○ Impairments that are identifiable do not always relate to algal chlorophyll levels

 Drinking water odor problems Nutrient scale • Low nutrient and chlorophyll concentrations ○ Optimal range of water quality for swimming  Really low ○ Optimal range of water quality for fish production  mid to mid-high Reference Approach

01/23/2009



Reduce nutrient levels to match those that existed prior to human impacts. ○ Reference water bodies with little to no human impact  Use this data to set criteria  For example



16 lakes designated as pristine • take 75% percentile sets phosphorous criteria



If reference lakes are not available or numerous enough, criteria may be set using distribution of data from population of lakes or using EPA’s regional data.

Reservoirs



Focus on phosphorus ○ Consider differences in reservoirs  Surface area = 10 – 53,800 acres  Mean Depth = 4 – 62 feet  Watershed = 80 – 4,000,000 acres

01/23/2009

   

Forest = 0-95% Grass = 0-78% Crop = 0 – 74% Urban 0 – 96%



Ecoregions ○ Decision Matrix for Phosphorus  Influence of morphology, hydrology and watershed  Identify “reference” phosphorus levels

○ Plains, highlands and border  88 reservoirs in plains  37 in highlands  16 in border



Decision Matrix ○ Influence of morphology, hydrology and watershed  Plains  % Historic Prairie, Dam Height and Residence Time

01/23/2009



because



Historic prairie land cover provides a measure of the inherent nutrient levels found in the soil in which reservoirs were built



Shallow reservoirs mix sporadically, increasing internal loading of nutrients, deeper reservoirs have a large volume of water that acts to dilute nutrient inputs



Residence Time is a theoretical measure of how long it takes inflows to move through a reservoir

○ Residence time = reservoir volume / average annual inflow volume ○ 300/100 = residence time of 3 years

 (measured in acre/feet)  logner residence time means

01/23/2009



increased sedimentation of nutrients

 

increased de-nitrification increased dilution of nutrient inputs



Residence Times in Missouri reservoirs range from <1 month to >6 years.



Shorter residence time, higher phosphorous



Higher residence time, lower phosphorous

 Ozark Border and Ozark Highlands  Dam Height

Reference phosphorus levels • • • No point sources of CAFOs within the watershed <20% of watershed in combined crop and urban coverage >50% of watershed in dominant historic land cover

01/23/2009

Took these water values • • Protect last 10% of range with least phosphorus Listed past 75% as above expected level of phosphorous

Zone A



Reservoirs that are either below 10th percentile line or predicted to be below said line



Phosphorus levels are lower than measured in most regional reservoirs – protect from degrading



Site specific phosphorus criterion set on long-term mean

Zone B • Reservoirs that are between 10th and 75th percentile lines or are predicted to be above 75th percentile line. • Phorphorus levels are comparable to most regional reservoirs – take no action • Phosphorus criterion will be set at 7th percentile value or predicted value (which ever is highest)

01/23/2009

Nitrogen and Chlorophyll



Base nitrogen and chlorophyll criteria on phosphorus criteria and desired relationship between parameters.

P= 1degree R= CCC to

• •

CO2 O2

P/R < 1

• •

Lots of respiration Depends on outside

P/R> 1 • Fixing carbon

01/23/2009



Net producer of organic material

First order stream

• •

Light limited, canopy cover, depends on outside nutrients Fairly low nutrients in headwaters

Bigger stream • • • Outside of canopy cover Autochonous growth of organic material More fine particulate material

Wet Lands



Values ○ Habitat ○ Water quality

01/23/2009

• •

Defined: wet soil and adapted vegetation Major plants:

○ mosses ○ Grasses – sedges (seagass) ○ Reeds – (cattail, common reed) ○ Trees ( mangroves, cypress, water willow, tupelo)

• •

Hydrology – open and closed (peat?) Wetland types

○ Bog mosses (closed, accumulate organic matter) ○ Marsh – grasses (open, not much buildup, washed away)

 Extremely biologically productive ○ Swamp – trees (open) • Water quality ○ Slow water movement ○ High productivity ○ Nutrient demand

01/23/2009

 Helps reduce nutrients ○ Organic matter  Biomass, living and dead, provides surface area to filter pollutants ○ Microbial activity Hydrophyte • Water loving plants

Stream ecosystems



Nutrient spiraling ○ Nutrients = nitrogen, phosphorous, inorganic carbon ○ Energy = reduced carbon ○ Nutrients being picked up, transported and eventually deposited downstream



Rocky bottom of streams ○ Rocks flowing with nutrients ○ With light coming in ○ Algae develops, covers rocks

01/23/2009

○ Reason: light, nutrients and stability ○ Bubbles in algae growth

 Photosynthesis  Taking in CO2, releasing O2  A tension develops on bubble  Lower cells get shaded out by algae growing on top of it.  Lift occurs



Paraphyte chunk lifts and hits turbulence of stream

 

Break apart Able to reproduce in stream

○ Benthic  Attached ○ Suspended algae  In the stream ○ Relationships

01/23/2009

 Benthic algae and nutrients   Can correlate Can not relate due to

• • •

Light limitation Grazing by snails etc Flow

○ Flood can scour rocks, eliminate growth  Forested streams  Agriculture/row crop uplands



Some increase over time

 Discharge from effluents  Massive increase over time  Does increased phosphorous and nitrogen increase algal growth on rocks?  Phosphorous

01/23/2009

• 

some increased growth

Nitrogen • Most increased growth



Both • Less

 % forest increase  decrease in phosphorous, nitrogen

○ Watershed area  Surrogate for time in the system  More algae per unit phosphorous • • Has spent more time growing algal cells Has grown into resources



Forest and nutrients • If area is calculated compared to % forest and % cropland ○ Can predict chlorophyll levels ○ Can explain 90% of variation

○ World wide

01/23/2009

 Area relating to time algae cells has spent in stream  Levels out  Lake v. streams



A lot more chlorophyll in lake than streams at every level of phosphorus • • • Less light limitation Less flush from storms Stream must wait for benthic to be seed for in stream growth



Agriculture ○ Per person per year  1,000 kg of water for 1kg for corn  2,000 kg of water for 1kg of rice  620,000 gallons of water to sustain each American per year

○ Ag biggest polluter  Provides

01/23/2009



Sediment • 21 metric tons lost from ag land per hectare



nutrients • • fertilizer CAFO – confined animal feeding operation

○ Hogs ○ Poultry

 Grown on marginally productive land   Cheap land Food for animals transported in from iowa, illinois, north missouri

 Produces animal waste  sulfur waste pits

01/23/2009



dumped as nutrient amendment on land



sometimes crop land, pasture land.



High in phosphorous same as dairy waste



Low in nitrogen

 Animal equivalence   Number of chickens to equal output of human Number of hogs equal to output of one human

• • • •

Sow Dairy cow Chicken Turkey

 Waste   Rich in nutrients High in phosphorous

01/23/2009



75% of soils that have received manure to provide nutrients

• • Previously

saturated with phosphorous

○ As recently as 25 years ago  Smaller operations   Part of grain produced were fed to animals People doing both row crop and animal husbandry

 Now  Producing same number of hogs but in high concentration  Result  Tremendous amount of nutrients added to landscape  Nitrogen application has ramped up production



Can’t really apply it when plants need it the most

01/23/2009



Peak of growing season

○ For corn: july-august ○ Applied in Winter

 NH4, bacteria nitrify it to NO3  NO3 runs through soil, really soluble  Have to apply enough nitrogen to account for some loss and residual nitrogen will be available for plant

 Ag production in same area  Factors for bumper crop • Weather ○ Rain at right time •  Temp

Bumper year produces

01/23/2009

• 

Lower prices

Adding little extra nitrogen provides best chances for bumper crop

 We have moved from system of    Grain produced Animals taken care of Waste put back in for grain production

 To piecing this system out  Concentrating it

○ Little bit of nutrient slipping off farm is trivial economically  Except, these amounts effect aquatic ecosystems  Tragedy of the commons

○ High in phosphorous  Low in nitrogen  Trying to satisfy that demand



Produces runoff of high phosphorus and low nitrogen

01/23/2009



Danger: select for blue green algae that are nitrogen fixers



Really don’t want them in aquatic ecosystem

○ We put more nitrogen on land than we harvest Solutions • • Riparian forest buffer system Conservation Tillage

○ Harvest corn ○ Throw non-crop parts back to cover the soil

 Blunts rainfall  Reduces sediment loss

CAFO contribution to water quality Low flow – should be able to see it in nutrients such as potassium, etc

01/23/2009

• • •

Identified 100 streams with no cafos or cafos in next watershed Combination of forest and ag Picking up presence of CAFOs in streams, separate from cropland

○ Signs  Nitrogen, phosphorous  Enough effluent that we see saturation in some areas



Conservation tillage ○ Harvest produce, leave residual on landscape, organic matter on landscape  Indication that it reduces sediment runoff   Problem: not incorporating anything Tend to have surface runoff of fertilizers and herbicides   Hard to pickup at more than one watershed level Push to put it in as general practice to reduce input into lake Erie  Tragedy of the commons

01/23/2009



All these protection features can be put in but hard to measure outcome

 • Urban

Might change in 5-10 years

○ Major push to deal with storm water runoff ○ Change in cities?

 Porous pavement, water will go through, still support cars etc  Need to reduce the loss of water off of the landscape in cities, encourage infiltration  Retention basins could help



Encourages infiltration

 Taken out curbs and gutters, curved streets  Drainages on either side, natural vegetation

 Local plants are ideal for water uptake when it is needed  STL using Seattle as a model

01/23/2009

Great Lakes • Impeded by ○ Sediments ○ Exotic species

 Sea lamprey  Salmon introductions  Zebra mussels

○ depletion of fish stocks ○ Polluted



Understood must reduce TMDL ○ Canada and US agreed to reduce effluent and nutrient inflow into these water bodies ○ Near shore phosphorous concentration is dropping ○ In certain drainages, watershed management plans, buy-in from stakeholders, reducing loss of nutrients from agriculture



Paleolimnology

01/23/2009

○ Taken cores out of sediment ○ Can tack western expansion ○ From sediment increase in diatoms ○ Record of increase of fertility in lake from when Romans put in road ○ During years of severe eutrification, shift away from diatoms toward bluegreen algae and green algae, shift in remaining diatoms toward ones tolerate toward enriched waters ○ Lower phosphorous and nitrogen, haven’t switched back ○ Still altered today

Zebra mussels • • • Entire change of food system Move toward benthic fish away from plankton fish Zebra mussels filter water taking away plankton and providing quite a lot of benthic food for those who can eat mussels

Nacy Radalaiss or Eugene Turner articles • Read abstract, look at tables and figures, read discussion, results ○ Dealing with nitrate

01/23/2009

○ Dealing with decrease in silica ○ Wetlands discussion

Gulf Hypoxia



Lake conditions ○ Decreasing O2 with depth ○ Falling Organic Matter ○ Temp decline ○ Salinity cline

 Fresh water flowing over top of ocean water  Move nutrients off land into water, generating algal bloom  In productive areas of the planet, historic hypoxia



Streams ○ Output of nitrogen of upper Midwest killing off benthic fish in gulf

01/23/2009

○ Increased input of nitrogen down Mississippi river ○ Tied to use of nitrogen fertilizer

 ½ of total ○ Costal waters, nitrogen limited  Algal biomass and algal chlorophyll linked to nitrogen • Costal zone, rich in sediments, rich in phosphorous ○ Get rid of it?  Go anoxic  We supply phosphorous in costal zones



Because • • Shallow Surface goes anoxic

  

Nitrogen going downriver (tied to fertz) Delivering less silica to coasts %BS



percent biogenic silica

01/23/2009

○ define:  In river    Higher nutrients Less flow = more algae



diatoms algae ○ silica cells ○ result: recent sediments

 increased depositing of BS into sediments of river beds  Mississippi river is carrying less silica than previously

 

Taken up by algae Algae settle out

01/23/2009



Lots of nitrogen and not as much silica, more organic matter heading to gulf than previously

 

Not normal kind a of algae More green and bluegreen

 From upper Midwest   Nitrogen, phosphorous silica Diatoms lowering silica content

 As it flows   Coast  Deposit out due to size and salinity • Result: increase in organic matter ○ Pipeline of nitrogen toward coast, a by default nitrogen limited system ○ Most coast waters, nitrogen limited Increase in diatoms

01/23/2009

 Because: denitrafication  Dumped organic matter • • • • Results in less silica Results in different algae to grow Benthic system arises Fueling of green and bluegreen

 Humans     Doubling cycling of nitrogen Intensified agriculture Think of it as eutrification of the coasts Maybe tilting toward toxic algal forms



Solutions ○ fertilizer  admit, “we’re a big part of the problem”

○ reduce broadscale use of anhydrous ammonia ○ can reduce nitrogen off landscape if land put back in wetlands ○ $100 billion for harvestable cropland ○ reduce 20-30% of chlorophyl runoff

01/23/2009



How do you convince farmer that there is collective problem from his economically unimportant loss of nitrogen?

• •

reduce anoxia Hypoxia

○ 2-3 mg/L of oxygen • caused by ○ increased productivity ○ reduced oxygen

Mississippi River • increase in ○ Nitrogen and phosphorous ○ Algal growth



Results in ○ Using SO2

Gulf • Algal growth sent to gulf

01/23/2009

Solution

• • • •

Limit nitrogen Decrease nitrogen use in agriculture Put wetlands back on landscape Riparian buffer

Chances of • • Reducing chlorophyll in gulf Duration of time oxygen present

Dinoflagalate



Human contributions ○ Coastal eutrofication ○ Change in fish demographics ○ Disappearance of top predator fish ○ Response to coastal enrichment ○ Runoff from hog lagoons

01/23/2009



Discovered in Chesapeake Bay ○ Has aerosol nuerotoxin

Red tide • Dioflagalate ○ Puts out toxins • Increased by coastal eutrophication

Toxic dioflagalates have increased throughout the globe

Freshwater toxins



Cyanobacterial Blooms and the potential for Toxins

Early in season

• • •

Ions in water Nitrogen in water Small algal cells

Late in season • Sucked down nitrogen

01/23/2009

• • •

Precipitated and diluted calcium out of system Shift to blue greens and large bluegreens Net Chlorophyll is going up Microcystin is going up as well

Conclusions

• • • •

Common in Midwest Seasonal patterns are unique Max doesn’t occur in any one season No nice relationship between environmental relationships and algal toxins

Research needs

• • • •

Consistent sampling protocols Predictive models Able to shut down beaches Methods for early detection

01/23/2009

Biochemical Oxygen demand • How much oxygen it takes to break all the carbon bonds

Organic matter



C-C-C ○ input oxygen ○ output CO2

Water oxygen saturation during the summer, 8 milligrams / L

Concentrated sewage

• • •

1000mg/L Total suspended solids 500 = 200 mg/L Biochemical Oxygen (BoD) 200

01/23/2009

Would result in water going anoxic due to oxygen demand

Treatment breakdown (important)



Primary treatment (results in taking out 1/3 of BoD) ○ Screen out materials ○ Skim out floating materials ○ Settle



Secondary treatment (biological, 2/3rds of BoD)

01/23/2009

○ Put oxygen in contact with organic matter (dissolved organic matter)  Pushes off CO2. Sprinkle filter • Rocks ○ Zoogleal bacteria  Grow on rocks, huge demand on carbon, don’t grow much protoplasm ○ Protozoans ○ Sewage worms

• • •

Spray arms, water pushed over rocks Denitification occurs Don’t flood it with BoD demand, would go anaerobic

Huge biochemical oxygen demand

• •

Want to oxidize to produce CO2 Product bacterial bodies

01/23/2009

Activated sludge

• • •

Water removed from primary treatment Fill tank of up with fresh load of sewage water Zoogleal bacteria in tank

○ Blows off CO2, infused with oxygen from jets • • • Jets of air oxygenizing water Protozoan feeds on zoogleal bacteria Turn off jets and all things settle

○ 2/3rds of bacteria goes to sludge dealing ○ reuse 1/3rd of bacteria goes through trickle filter or holding facility



vulnerable to shock ○ PH shifts or pesticides  Bacteria will not perform to expectations  Bacteria might do “bulking”

01/23/2009

 

Single cells instead of snot strands Engineers borrow activated sludge to re-seed

What to do with the sludge?

• • • •

Stick in tank and go anaerobic Eternal flame, methane coming off Liquids head to activated sludge Dry solids material

○ Methane used to run the plant or send to city gas supply, natural gas ○ Land apply solids

 Milwaukee  Minneapolis, St. Paul

○ Not done as much because of heavy metals concentrated in sludge

01/23/2009

 Copper, chromium, mercury

Tertiary treatment (3)

• • • •

200 mg / L of BoD 10% left after 1st and second treatment 20mg/L NH4 > N03 solution

○ put in pond ○ spiny wheel ○ membrane filter ○ trickle filter



can ○ reduce BoD ○ Phosphorous reduction

 Waste waster usually has 5mg/L  Get rid of it?

01/23/2009



Microbial uptake (treat with bactera/algal uptake)

• •

Alum (Al+3PO+4) treatment Wetlands

○ Phosphorous uptake limited ○ Nitrogen reduction  Ammonium (NH4) (toxic to fish)  How?



NH4 – NO3 – N2 (BoD) • • Let go anaerobic Without oxygen goes to next best oxyidizing agent

○ NO3 Releases CO2 and N2  Ammonium can kill fish at high ph • Ammonium leads to algal blooms and high BoD • which raises ph

01/23/2009

Putting effluent into lake results in oxygen sag • Lowers oxygen in stream until bacteria satisfy the remaining BoD and oxidize the ammonium to nitrate • Extent of oxygen sag curve depends on

○ Volume of effluent ○ Volume of stream



Not much effect of ○ Low effluent high flow



Nutrients ○ High unless tertiary treatment ○ Oxidation ○ Uptake

 In short, algae growth ○ Curve goes from low prior to effluent input, peaks and declines in a curve due to decreasing and uptake • Extreme conditions ○ Anoxic

01/23/2009

 Sewage fungus can grow  Algal growth downstream  Change in macroinvertibrates

Inverts

• • •

Tolerant – EPT Community > index to fe Subjective score

○ %taxa • taken in comparison to region ○ habitat structure ○ water quality

 both effect population structure • Prairie streams ○ Not a wonderful index  Some extremely tolerant of harsh conditions.

01/23/2009

○ Nutrient enrichment  Response seen most in algae  Secondarily in invertebrates

 Response will be little dampened in fish  Can migrate

Bottled water

• •

When it entered the market, unregulated Tap water is regulated

Water treatment



Sand filter ○ Bottom – coarse gravel ○ Top – decreasing grain size



Result ○ Bacterial growth

01/23/2009

 Binds up particles  Bacteria is going to feed off of dissolved organic carbon

   

Reduces carbon Traps bacteria Traps viruses and protozonians Less particulate resulting water



Hit it with chlorine to keep bacteria down, reduce bacterial regrowth ○ Destroys cell membranes  Oxidizes bacteria

Drinking water desires

• • • • •

Plentiful No disease No taste No order Cheap

01/23/2009

Sand filter



Chlorine/uv light ○ Off into consumers

Water supply from surface waters

• • • •

Algal cells Algal blooms occasional PH bump up Requires

○ Activated carbon  Has bonding sights  Attaches to dissolved organic carbon

○ Yellow drinking water?  High dissolved organic carbon  Caused by tanic acids

01/23/2009

Adding chlorine to water with high dissolved organic carbon • Problem: ○ High bladder/colon cancer  Complex made by chlorine and organic carbon   Limit 100 ppb Now

• ○ Fix: now use  NH2Cl  Or

80 ppb

 

Ozone Uv radiation

○ TTHM also called DBP

01/23/2009

Water softening • Hard water ○ High concentrations of divalent metallic ions • Soft water ○ Less calcium and magnesium ○ Less white crust



Salt involved is sodium carbonate ○ Replaces calcium/magnesium in the water ○ Results in higher sodium in soft water

 Does not interact with soup  Up sodium intake

MTBE • Gasoline additive ○ Migrates rapidly through groundwater  Cancer precursor Arsonic • Increases tumors

01/23/2009



Problem when in water

NO3 - nitrate



10 miligrams per liter ○ NO3 – N  Goes to blood stream, binds up with bloodstream  Cuts off oxygen as it gets to blood

Fecal coliform

• • •

Bacteria indicative in GI tract Also environmental fecal As little as 1 fecal coliform per 100 milligrams of water

Geometric Mean Log 10

01/23/2009

• • •

1000 100 10

3 2 1

average: 370

6/3

log average is 2 or 100

fecal coliform standard



in guts of warm blooded animals ○ pretty good tracer of mammal contaminants in water ○ used as means of detecting potential contamination

 miner’s canary  sign of potential other contaminants

○ fecal coliforms limit for swimming water  200 cfu/100 ml  no more than 10% of samples are supposed to have >400cfu/100ml

01/23/2009

○ 1000 cfu/100ml E. coli standard • More specific to human guts

Swim standards



Fecal coliforms ○ 200/100ml



E. Coli ○ 126/100ml

Lake Phewa, Hepal



N

Geometic Mean 10/100ml 53 701 2 41,5000 6,000

Open lake 20 Lake shore 23 Wash sites 25 Stream Pfirke Seti 29 5 5

01/23/2009

0157:H7

• • • •

E. Coli bacteria problem Related to hamburger recalls Can kill Can be related to water supply

Water borne pathogens



Cryptosporidium ○ Protozoan ○ Outbreak in Milwaukee

 400,000 infected, boil order ○ Occupies wall of intestine ○ Feeds on material going through intestine ○ Releases a toxin ○ Reproduces by fission

01/23/2009



Forms cists

○ released out of feces ○ resistant to chlorination ○ survive in environment for awhile ○ 1976 realized could be problem in humans ○ ozone can cut cists numbers ○ more particles pass through during winter

 biofilter of sand doesn’t act as well ○ common in South America ○ fairly common, even in pristine waters



Cyclospora ○ Causes diarrhea ○ Common on lettuce



Giardia ○ Bigger, cists are about twice as large ○ First described by levenhook ○ Common in humans, beavers, mule deer etc

01/23/2009



Protozon, releases cists, toxin



Entamoeba – protozoan ○ Similar to Giardia

Bacteria • Cholera – Vibrio ○ Humans are only known host ○ Toxins cause rapid loss of fluids and electrolytes ○ Treatment is lots of water and electrolytes ○ Can chlorinate and kill bacteria



Salmonilla – Typhoid fever ○ Close cousin to Cholera



Legionella ○ 1976  200 year celebration of US   over 200 people became ill via convention hotel

01/23/2009

• •

pneumonia like fever like

 new genera of bacteria   water borne likes moderately hot water



associated with water vapor ○ inhaled  dealing with it   use hotter water don’t breath deeply in weak shower temp  no person to person spread

 Viruses •

tends to use iron for energy

65% of water borne disease are viruses ○ Hepatitis A

01/23/2009

 Can be carried in water  Common in North Chicago than South Chicago

 ○ Polio

North treatment didn’t have sand filtration

○ Rhoto viruses

 Good water treatment  Sand filtration  Removes viruses

○ Associated with shallow wells • Schistosomiasis ○ Worms, problem in parts of Africa • Malaria ○ Water borne with insect host ○ 1million dead per year

Aquatic toxicology

01/23/2009



Toxic substances control act ○ Human made chemicals  Kepone and Mirex        Highly resistance box organic structure Lots of chlorine Used as ant bait in south Tossed waste products in river Don’t break down Persist for a long time Carcinogenic

 PCB  Poly-chlorinated Bifenals • • Associated with hydraulic fluids Extremely long lived chemicals

 DDT   Insect control Still used in many parts of the world

01/23/2009

•  Love Canal 

Bad news bears

Chemical company putting drums of waste in ground



Result

Xenobiotics – foreign chemicals Toxin > organism

Exposure

breaking down chemical, top priority for toxicologists



want to know, ○ Does chemical degrade?  Primary degradation  Cleaving anything off original compound (breaking integrity) • DDT (breaks down in anaerobic conditions) ○ DDD  Degraded DDT

01/23/2009

 Changes it significantly  Clear Lake, CA  Plankton 250x DDD as the water  Fish 12,000x DDD as the water  Fish eating birds 80,000x DDD as the water

 Ultimate degradation  Breaking down into carbon, chloride, nitrogen

○ UV degradation  Breaks down chemicals ○ Biodegradation  Breaks down via organisms  Often have to be acclimated to these new chemicals ○ Influences to degradation  PH  Temperature  Dissolved Oxygen

01/23/2009

○ Water insoluble compounds  Don’t break down in water  Prefer lipids  Tend to persist  Attracted to clay surfaces  Absorbed by organisms

○ Water soluble compounds  Easily accessible  Readily degraded

○ Branchy organism  Persists more ○ Straight strain compounds  Tend to break down • ABS surfactant ○ Hardly degrade • LAS linear surfactant ○ Straight chain, breaks apart on way to sewage treatment plant

01/23/2009



Log concentration diagram ○ Straightens S curve ○ Y axis, response of population ○ X axis, concentration ○ LC50

 How much of chemical will kill 50% of organisms  How toxic it is



Use other markers chemicals to judge relative toxicity

 Alter hardness of water  Carbonate • • • Calcium carbonate Magnesium carbonate Buffer ph changes

○ Buffers carbonic coming out of fish ○ Soft water, puts out acid, does not buffer PH

01/23/2009

○ EC50  Zooplankton measure  Effective concentration • • Toxicants ○ Not all animals are susceptible to toxicants  Cold water fish tend to be more susceptible than warm water species  Tests use representative species Poke them and they don’t move



Fathead minnow • Represents warm water fish response



Rainbow Trout • Represents cold water fish response



Acute exposure ○ Large amounts over short time ○ Effects are death or immobilization



Chronic exposure ○ Small amounts over long time

01/23/2009

○ Reduction in fecundity, etc



Log

Plastics



Toxic to aquatics

Dioxins • Not intentionally released

Tributal 10 • • • • Ship hauls If put in paint slows growth of barnacles Leaches out of paint Extremely toxic to mulluscs, oysters

Water naturally acidic, carbonic acid • • • Picks up chemicals from smoke stacks Drops ph in rain -log of hydrogen ions (pH)

01/23/2009

○ 10 fold from 6 - 7  normal 6.8  some pH 4.5

 •

high 3s

drop in pH caused by ○ sulfuric acid (H2SO4)  coal burning ○ nitric acid ( HNO3) > N2 > NOx  automobiles  NH3 from agriculture does neutralizing, but can become nitric acid

○ hydrogen chloride (HCl)  burning garbage, industry • Prevailing winds, west to east ○ East Canada ○ Scandinavia



Ca(HCO3)

01/23/2009



Result

○ Lost species diversity ○ No recruitment, older fish less affected ○ Shellfish and mulluscs are susceptible (pH shock)

 Rain drops  Summer comes  pH comes back up  results in seasonal drop

○ eventual emitions controls  scrubbers on smoke stacks  burning garbage prohibited

○ limestone added to inflow ○ aquatic birds not effected by pH

 but effects food web • management

01/23/2009

○ lakes have been fertilized  stimulates algal production  increases pH



Recovery ○ Follows foodweb  Algae recover first  Zooplankton  Benthos  Fish



Paleolimnology ○ Track changes with  Lake cores  Diatoms • Neutral to acidic to

• • • •

01/23/2009

• • • • • Hi Emily!

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