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Title: TSECBIOSYS:


1
TSEC-BIOSYS Environmental Impacts of Bioenergy
Crops in the UKwww.tsec-biosys.ac.uk Rebecca
Rowe M. Hanley, D. Goulson, G. Taylor
University of Southampton
Biomass role in the UK energy futures The Royal
Society, London 28th 29th July 2009
2
Overview
  • Introduction
  • Knowledge gaps
  • Aims
  • Study sites
  • Survey completed
  • Key findings
  • Summary main outputs

3
Environmental Impacts of Bioenergy
  • ? Positive impact,,? Negative Impact, ? No
    Change, Limited data
  • R. Rowe, et al (2009). Renewable Sustainable
    Energy Rev. 13, 271-290

4
Knowledge Gaps Willow SRC Biodiversity
  • Limited information on large commercial sites
  • Small non-commercial sites
  • Commercial sites studied contained many young
    plantations
  • Range of species
  • Flora, avian, Lepidoptera and pest species well
    studied
  • Soil invertebrates, mammals and non-pest
    invertebrates less well studied
  • Few direct comparisons between SRC and arable
    land and none for set-aside land
  • Few studies on ecosystem processes (herbivory,
    decomposition, predation)

5
Aims
  • To assess impacts of mature commercial willow SRC
    plantations on winged invertebrates and ground
    flora in comparison to alternative land uses
  • To explore possible effects of willow SRC
    ecosystem processes

6
Field Sites
  • Three sites each containing
  • Willow SRC plantation
  • Arable field containing cereal crops
  • Set-aside field
  • Willow plantations
  • Commercial plantations
  • Greater than 5 ha in size
  • Sites at least 5 years old (1998-2000)

Willow SRC
7
Surveys Conducted
  • Species Composition (Summer 2006)
  • Winged Invertebrates (e.g. Wasps)
  • Abundance
  • Distribution of Orders/Size classes
  • Ground Flora (Weeds)
  • Species richness and abundance
  • Plant strategies
  • Ecosystem Processes (Summer 2007)
  • Herbivory and Decomposition
  • Predation (2007- 2008)

8
Key Findings Winged Invertebrates
  • Abundance of winged invertebrates were similar
    between land-uses,
  • Invertebrates abundance in Willow SRC increased
    with height

Height
Distance
?
?
?
Land-use F2,4 0.004 P 0.96 Land-usedistances
F8,16 2.93 P 0.032
HL F4,8 10.37 P 0.003
9
Distribution of Winged Invertebrate Orders
Mean number of individuals per trap (SE)
Yellow increased in willow SRC, Blue decreased
in Willow, White similar abundance in all
land-uses
10
Ground Flora Species Richness Abundance
  • Species richness
  • Similar in all headlands
  • In the cultivated area set-aside land gt willow
    SRC gt arable land
  • Ground flora biomass
  • Similar in set-aside and willow SRC, reduced in
    arable land

Species Richness
Biomass
F2,4 24.65 P 0.006
F2,4 13.64 P 0.016
11
Plant Strategies (1)
  • Fraction of plant cover provided by each of three
    plants strategies
  • Life history, life form and establishment
    strategy (Grime et al.1990).

12
Plant Strategies (2)
  • Perennial species dominate in willow SRC

13
Plant Strategies (3)
  • Grass cover was highest in the headlands of all
    land-uses
  • No overall effect of land-use, with all
    land-uses showing a mix of forbs and grasses

Life Form
Fraction of cover per 4m-2 quadrate
14
Plant Strategies (4)
  • Willow SRC higher fraction of competitive species
    few ruderal species

Establishment Strategy
Fraction of cover per 4m-2 quadrate
C F 2, 4 9.53 P 0.030, R F 2, 4 19.53 P
0.009
15
Plant Strategies (5)
  • In contrast to other land-uses, willow
    plantations were dominated by a mix of perennial
    grass and forbs with competitive and generalist
    establishment strategies
  • Result suggest that levels of disturbance in
    willow SRC affect plant species and species
    richness

Fraction of cover per 4m-2 quadrate
16
Conclusions (2006)
  • Result suggest Willow SRC can help to increase
    farm scale biodiversity.
  • By providing a habitat where plant species and
    invertebrate Orders uncommon in arable land can
    persist
  • Are these reflected in changes in ecosystem
    processes?

17
Ecosystem Processes
  • The movement of nutrients, energy or matter
    between compartments within a ecosystem.
  • Understand the rates of these processes is first
    step in managing ecosystems for maximum benefit
    for both biodiversity and yield.

18
Methods Ecosystem Processes
  • Herbivory lettuce seedlings were exposed in the
    field to assess herbivory pressure by molluscs,
    mammals and invertebrates
  • Decomposition litter bags were placed in the
    field to assess decomposition rates by macro and
    meso-micro fauna (1mm, and 5mm)
  • Predation fly pupae were exposed in the field to
    assess small mammal and ground invertebrate
    predation

19
Key Findings Herbivory
  • Summer herbivory pressure was similar in all
    land-use
  • Mollusc grazing was found to be the most
    significant factor affecting seedling survival in
    all land-uses

Herbivory Pressure
20
Key Findings Decomposition
  • Summer decomposition rates are reduced in arable
    land in comparison to the other land-uses due to
    reduced macrofauna and mesofauna activity

Decomposition rates
21
Key Findings Predation
  • Predation rates highest in arable land gt willow
    SRC gt set-aside for both small mammals and ground
    invertebrates

Predation pressure
22
Detailed Predation Study (2008)
  • Predation assay with enclosure design to separate
    small mammals and large and small ground
    invertebrates
  • Ground invertebrate activity and density
    (Pit-fall trapping and soil searches)
  • Small mammal activity and density (Mark and
    recapture)
  • Land-use, diurnal, seasonal

23
Seasonal Predation Rates
Percentage of pupa taken
24
Mammal Abundance Cultivated area
Autumn
Summer
Spring
Mean captures per site given as captures per 100
trap rounds adjusted for sprung traps
Field Vole
Wood Mouse
Pygmy Shrew
Bank Vole
Water Shrew
Common Shrew
25
Mammal Abundance Cultivated Area
Autumn
Summer
Spring
ns
26
Mammal Abundance Cultivated Area
Autumn
Summer
Spring
27
Small Mammal Breeding
Percentage of individuals trapped
16 21 49 5 8 6 40 9
Number of individuals
28
Summary of Key Outputs
  • Assessed the current knowledge bases on the
    environmental impacts of bioenergy crops (Rowe et
    al 2009)
  • Mature commercial willow SRC plantations are
    beneficial for farm-scale biodiversity
  • Variation in the winged invertebrate and plant
    communities of willow SRC in comparison to
    alternative land-uses
  • Highlighted the relative important of small
    mammals in predation in willow SRC
  • Identified willow SRC as a breeding site for
    several small mammal species.

29
Acknowledgments
  • Land Owners,
  • Russell Fraser, Dave Barrett and Fred Walter
    (CRL)
  • Field Assistance
  • Suzie Milner, Alex Wan, Sarah-Jane Yorke, Matt
    Aylott, Lisa Durrant, Stefan George, Katie Finn,
    Stacey Travers, Judy Gallimore, Carl Wardill, Jo
    Seymour, Matt Guy, Dr Donna Clarke
  • Supervisors
  • Prof. Gail Taylor, Dr. Mick Hanley, Dr. Dave
    Goulson
  • NERC and TSEC

30
Thank you for your attention!
www.tsec-biosys.ac.uk
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