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Phosphorus from Agriculture: Riverine Impacts Study PARIS

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... in relation to sediment dynamics and P uptake & release by sediments and biota ... stream uptake of SRP by sediments/biota. Sewage SRP:B = 9.5. Avon_at_Knapp ... – PowerPoint PPT presentation

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Title: Phosphorus from Agriculture: Riverine Impacts Study PARIS


1
Phosphorus from Agriculture Riverine Impacts
Study(PARIS)
Start date September 2003 End date August 2008
2
Diffuse Phosphorus Impacts in Rivers
  • Current knowledge
  • Eutrophication impacts based on lakes
  • Diffuse P inputs in PP and DP (lt 0.45 µm) forms
  • Variable, episodic and arrive in winter
  • Questions
  • Is riverine ecology sensitive to diffuse P
    inputs?
  • What level of P input is a problem?
  • How important is the timing of diffuse P inputs
    ?
  • How significant are P-supplies from bed
    sediments and porewaters?
  • How does P fractionation (e.g. DPPP ratio)
    affect impacts?

3
PARIS
Hypothesis Land management directly influences
river ecology by altering the concentration of P
in the water column bed sediments
Aim To better understand the impact of high-risk
farming practices on river nutrient chemistry and
ecology
  • Benefits
  • Assess the extent of P load reduction required
  • Target key practices for control
  • Inform catchment management planning

4
PARIS Experimental Approach
  • Paired study headwater streams (agriculturally
    impacted v. unimpacted) sites, with variable P
    loss risk
  • Response to implementation of management change
  • Apply manures to control area (Loddington)
  • Adopt BMPs in high-risk area (Sem)

Loddington Arable farming on drained clay soils
Coughton Brook Intensive row crops on dispersive
silty soils.
Sem Intensive dairy farming on drained clay
soils.
Colebrook Mixed beef/dairy on drained clay
soils.
5
PARIS Work Programme
  • Monitor flux and temporal pattern of PP and DP
    inputs from agriculture
  • Examine chemical impacts P concentrations in
    water column and bed sediments/porewaters
  • Examine in-stream fate of P inputs in relation
    to sediment dynamics and P uptake release by
    sediments and biota
  • Monitor ecological structure (biodiversity) and
    function (processes)

Focus on headwater stream sites Single
agricultural practices are only detectable at
headwater stream level Eliminate effects
of point-source discharges
6
Importance of eliminating influence of point
sources PSYCHIC agricultural high risk/rural
sub-catchments (lt c. 100km2) appear strongly
influenced by small point-source inputs
Sewage SRPB 9.5
Importance of in-stream uptake of SRP by
sediments/biota
7
Role of river bed sediments
  • Bed sediments provide a key link between
  • Agricultural inputs of sediment-associated P,
    delivered under winter high flows
  • And
  • P-availability at times of ecological
    sensitivity (i.e. spring summer low flows)
  • Storage of diffuse sediment-associated P on
    river bed
  • SRP exchange between bed-sediment and river
    water
  • Dissolved P in porewaters sediment-associated
    P available to rooted plants and benthic
    algae

8
PARIS Bed sediment sampling
  • River bed - highly heterogeneous environment
  • Nature of substrate
  • Water and sediment residence time
  • Light exposure
  • Reach-scale mapping of river-bed environment
  • Sampling based on bio-geomorphologically defined
    Representative Functional Habitats allow
    comparison between impacted unimpacted streams
  • Measurements
  • Total sediment nutrient concentrations,
  • Bioavailable P concentrations
  • Equilibrium P concentrations,
  • Porewater SRP concentrations

9
  • PARIS - sediments and chemistry
  • How does nutrient availability in different
    functional habitats vary with respect to
    unimpacted and impacted streams and for different
    high-risk agricultural practices?
  • How do bed sediment nutrient availability and
    river water nutrient concentrations relate to
    ecological indicators?
  • How does bed sediment nutrient availability
    change following the introduction of P-control
    measures?
  • Can we quantify changes in river-water P-fluxes
    along the stream during the growing season and
    how might these be attributed to biotic (plant
    uptake) and abiotic (sediment exchange)
    processes?

10
Agricultural P inputs
  • Diffuse P signal
  • Characterise land use, P inputs and
  • land management in each headwater catchment
  • Routine and storm-event based monitoring of PP
    and DP forms
  • Targeted sampling of field surface/subsurface
    runoff to define potential P bioavailability of
    PP/DP forms

11
  • PARIS - Ecology studies
  • Functional habitat-based sampling of macrophyte
    biomass and macroinvertebrate density biomass
  • Microbial biomass (bacteria fungi), respiration
    decomposition rates on standard leaf packs
  • In-stream algal biomass primary production on
    standard experimental tiles
  • Potential Ecological Impacts
  • Change in processes from P-limited heterotrophy
    increased decomposition rates
  • Increase in proportion of autotrophy
  • Decrease in phosphatase activity.
  • Shift in primary production towards macrophytes
  • Increased shredder activity, lower diversity

12
PARIS assessment of diffuse source P impacts on
river ecology
  • Agricultural P contributions to rivers often
    intermittent predominantly under winter high
    flows
  • How significant are these diffuse inputs for
    ecological impacts in relation to background
    inputs?
  • Issues of memory and lag effects linked to
    storage of diffuse sediment-associated P
    delivered during (winter) storm events
  • New contributions to process understanding of
    thresholds, lag effects and ecological
    sensitivity to P in lowland agricultural streams
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