Title: Rivers
1Rivers
2River Water
- Water
- Suspended inorganic matter
- Sand, silt, clay
- Dissolved major species
- Elements with no gaseous phases in atmosphere
- Ca2, Na, K, Cl-, etc.
- Elements with gaseous phases in atmosphere
- SO42-, HCO3-
- Dissolved nutrient elements
- N and P
- Suspended and dissolved organic matter
- Trace metals
- Dissolved and suspended
3Source of River Water
- Direct precipitation
- Surface flow runoff
- Interflow flow through soil in stream valley
- Residence time in soils hours to 10s hours.
- Groundwater variable residence time in
subsurface hours-millennia
4Stream Hydrographs
- Records stream flow (discharge) through time
5Major Rivers
6Suspended Matter
- Small particles carried by turbulence
- Generally less than 100 microns, but varies with
water velocity - At high velocities can carry 10s to 1000s mm
- At very low velocities can carry lt 10 microns
(clay size) - Colloids common
7Suspended Matter
- Colloids
- Suspension of solids in water, not solid, not
solution - Colloidal particles are charged double layer
- Clays a common constituent
- Cation Exchange Capacity
- Much of the humic matter in natural waters is
colloidal - 80 of the oxidizable carbon in raw domestic
sewage is colloidal or larger.
8Colloids
- Much of the dissolved iron in rivers is
colloidal - Fe3 oxyhydroxides occur in colloidal form
between pH 5-10. - Both in surface and subsurface waters
- lt5 microns
- Can comprise up to 70 measured Fe in water.
- the colloidal iron found in many rivers has a net
negative charge whereas should be positively
charged - the colloidal iron oxide is coated with humic
matter and other dissolved organic matter. - The excess negative charge on the organics
confers a negative charge to the colloid. - Can transport generally immobile trace elements
and radioactive elements
9Colloids
- 3 main classes of colloids
- Hydrophilic colloids
- very large molecules or ions, large molecules
such as proteins which interact strongly with
water - Hydrophobic colloids
- interact less strongly with water but are stable
because the particles repel each other. - clays
- Association colloids - typical of soaps
- Collections of ions and molecules which associate
as micelles. The head groups interact strongly
with the water whilst the hydrophobic tails group
together away from the water.
10Colloids
- Colloidal material must first be aggregated
(flocculated) to be removed from the system - Colloids can be destabilized by
- compression of the double layer
- By increasing the dissolved salt content of the
solution - adsorption causing charge neutralization
- enmeshment in a precipitate
11Suspended Matter
- Controlled by
- Relief of the drainage basin
- Drainage basin area
- Amount of water discharge
- Climate
- Season
- Geology of the river basin
- Presence of lakes/reservoirs along river length
12Suspended Matter
13Human Influence
- Increases due to
- Deforestation and cultivation
- Overgrazing
- Construction
- Decreases due to
- Building of dams and reservoirs
- Bank stabilization of rivers
- Soil conservation practices
- The effect of European settlement of the U.S. has
been to increase the sediment loss to the oceans
by a factor of 2.6
14Chemical Composition of Suspended Matter
- Controlled by
- Climate
- Weathering patterns in the drainage basins
- Tropical rivers have high Al and Fe because
particulate originate from lateritic soils - Temperate and Arctic rivers have a suspended load
close to average surface rock compositon
15River Water Chemistry
16Chemical Classification of Rivers
- Gibbs (1970) Classification
- Precipitation Dominant
- Surface water chemistry controlled by Atmospheric
Precipitation - River water composition resembles rainfall
- Low TDS
- High Na relative to Ca
- High Cl relative to HCO3
- Tropical rivers
17Chemical Classification of Rivers
- Gibbs (1970) Classification (Cont.)
- Rock Dominant
- Surface water chemistry controlled by rock
weathering - TDS are intermediate
- Na/(NaCa) is low
- Cl/(Cl HCO3) is low
- Rock weathering supplies most dissolved salts
- Dissolution of CaCO3 dominates
- Includes most of the major rivers
18Chemical Classification of Rivers
- Gibbs (1970) Classification (Cont.)
- Evaporation crystallization Dominant
- Surface water chemistry controlled by evaporation
and fractional crystallization - Evaporation along stream distance controls
concentration of salts - Increasingly higher downstream
- Irrigation contributes significantly
- TDS are high
- Na/(Na Ca) is high
- Cl/(Cl HCO3) is high
- Rock weathering supplies most dissolved salts
- Rivers are in arid climates
19Chemical Classification of Rivers
- Stallard and Edmund (1983) classification
- Rock weathering dominates the composition of all
rivers.
20Chemical Classification of Rivers
- Ternary plot from Berner and Berner (1996)
21The Amazon
- Illustrates the importance of relief
- In lowlands, only dilution of solutes acquired in
Andes
22Seasonal Variation
- North Fork of the Shoshone River, WY
23Seasonal Variation
- Change in chemistry after a rainstorm
- North Fork of the Shoshone River, WY, July 20,
1973 - Na, HCO3-, Ca2, and Mg2 increased during first
11 hrs - Leaching of highly soluble material in soils
- After 11 hrs, dilution
- K increased as runoff increased indicating
leaching from leaves, pollen, and insects
Arrow shows point of peak flow
24Major Dissolved Components
- Cations
- Sodium
- Calcium
- Magnesium
- Potassium
- Silica
- Organic Matter
- Anions
- Sulfate
- Chloride
- Bicarbonate
- Nutrients
- Nitrogen
- Phosphorus
25Major Dissolved Components
- Sodium
- Sea salt (cyclic salt)
- Rainfall
- Dry deposition
- Dissolution of halite in bedded deposits and
shales - Weathering of Plagioclase feldspar
- Redissoluiton of saline crusts in desert basins
(minor) - Cation exchange of dissolved Ca2 with Na on
detrital clay minerals - Pollution
- Domestic and industrial sewage
- fertilizer
- Oil and gas well brines
- Mining
- Road salt
- Detergents
- Water softeners
26Major Dissolved Components
- Potassium
- Dissolution of sylvite in bedded deposits
- Weathering of orthoclase feldspar
- Cation exchange of dissolved Ca2 with Na on
detrital clay minerals - Pollution
- Domestic and industrial sewage
- fertilizer
- Oil and gas well brines
- Mining
- Biogenic element
- Used by growing vegetation
- Concentrated in leaves
- Increase in K during autumn when trees lose
leaves and they degrade
27Major Dissolved Components
- Calcium and Magnesium
- Sea salt (cyclic salt)
- Rainfall
- Dry deposition
- Dissolution of CaCO3 and CaSO4
- Weathering of Calcic Plagioclase feldspar
- Mg from weathering of dolomite and ferromagnesian
silicate minerals (olivine, pyroxene, amphibole,
biotite) - Pollution
- fertilizer
- Oil and gas well brines
- Mining
- Road salt
28Major Dissolved Components
- Chloride
- Sea salt (cyclic salt)
- Rainfall
- Dry deposition
- Dissolution of halite in bedded deposits and
shales - Thermal and mineral springs in volcanic areas
- Redissoluiton of saline crusts in desert basins
(minor) - Pollution
- Domestic and industrial sewage
- Chlorination of public water supply
- fertilizer
- Oil and gas well brines
- Mining
- Road salt
29Major Dissolved Components
- Bicarbonate (HCO3-)
- Dissolution of CaCO3
- Reaction of CO2 dissolved in soil and groundwater
with carbonate and silicate minerals - Silica (SiO2)
- As H4SiO4
- Weathering of silicate minerals
- Dependent on level of precipitation
- High precip high flushing and high removal of
silica - Low precip low flushing and little silica
removal - Biogenic
- Used by Freshwater (and saltwater) diatoms for
test formation - Removes silica from water
30Major Dissolved Components
- Sulfate
- Sea salt (cyclic salt)
- Rainfall
- Dry deposition
- Weathering of bedded gypsum and anhydrite
- Weathering of pyrite
- Volcanism
- SO2 gas
- Pollution returned as wet and dry deposition
- Industrial
- Auto/truck internal combustion
- Power plants burning fossil fuels
- Fertilizer
- Industrial and municipal waste
31Major Dissolved Components
- Organic Matter (Organic Carbon)
- dissolved (DOC)
- Wide range due to location (2-25 mg/L)
- particulate matter (POC)
- 1 suspended load
- In rivers with DOC gt TDS
- Chemistry dominated by humic and fulvic acid
carboxyl groups - ?inorganic cation charge gt ?inorganic anion
charge - Balanced by organic anions
- Fe and Al are mobile as organic complexes and
colloidal oxyhydroxides - Tend to be acidic
32Nutrients in River Water
- Nitrogen in Rivers
- Dissolved inorganic nitrogen (DIN)
- NH4 and NO3-, NO2-
- NO3 is most important
- it is most abundant, and directly taken up by
plants - NH3 and NO2- are quickly oxidized to NO3-
- - both of these are also toxic to most organisms,
- - and are usually found in minute concentrations
- Dissolved organic nitrogen (DON)
- amino acids, proteins, and urea
- complex, high molecular weight compounds
- Particulate nitrogen
33Nutrients in River Water
- Nitrogen (cont.)
- Dissolved pollutive nitrogen
- 1/3 to 2/3 DIN and DON are pollutive
- Point sources
- Municipal and industrial sewage
- Septic tanks
- Refuse dumps
- Animal feed lots
- Diffuse (non-point) sources
- Runoff from urban and rural settings
- Fertilized fields
- Pastures
- Yards and gardens
- Nitrogen fixing crops
- Storm water runoff
- Precipitation directly into lakes and streams
- Wet and dry deposition
34Nutrients in River Water
- Phosphorus
- No stable gas phase in atmosphere
- Limiting nutrient in plant growth
- Dissolved Phosphorus in rivers
- Inorganic
- Orthophosphate anions
- PO43-, HPO42-, H2PO4- (dissociated
orthophosphoric acid) - these are readily available to plants
- concentrations usually low in water 5-20 µg/l
- Polyphosphates- may be hydrolyzed to soluble
orthophosphate form - Sourced from
- natural weathering of phosphate rich minerals
- Accelerated dissolution due to human induced soil
erosion - Phosphate from fertilizers
- Soluble phosphate from detergents and domestic
and industrial waste
35Nutrients in River Water
- Phosphorus
- Dissolved Phosphorus in rivers
- Organic
- Proteins
- Particulate inorganic and organic compounds
- large molecules that settle quickly and lost
indefinitely in deep sediments - or can be broken down by decomposition to usable
PO4 - There is a seasonality to phosphate
concentrations in water - related to plant activity
- greater in summer than in winter therefore
concentrations less in summer than winter - fairly soluble in water,
- can tie up with Ca, Fe and Al and quickly settle
out into deep sediments and therefore not
available to plants
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