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Felice Sartori1, Donato Loddo2, Ilaria Piccoli1, and Antonio Berti1
1) DAFNAE Dept, Padova University, Legnaro (PD), Italy
2) IPSP, CNR, Legnaro (PD), Italy
Corresponding author: [email protected]
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental
ecosystem development research and coevolution of soils, landforms and vegetation1
Weed infestation during the transition phase from conventional to
conservation agriculture
© Sartori et al. All rights reserved
© Sartori et al. All rights reserved
Conservation agriculture and weed management
Despite conservation agriculture and,overall, the reduction of soil disturbanceare considered soil improving croppingsystems, these practices could conflictwith weed control. Indeed, reducedtillage is usually linked to increasedweed species richness and abundanceand, thus, it could increase thedependence on chemical treatments.Weed management is one of thereasons behind the distrust of Europeanfarmers in the conservation agriculture,that is still not widespread, despitesEuropean subsidies. In fact, conservationagriculture is implemented only in the2.8% of European cropland.
Conservation agriculture
Dependence on chemical treatments
So
il im
pro
vin
g
cro
pp
ing
syst
em
Weed
man
ag
em
en
t
Sustainability
Distrust
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
2
Introduction
© Sartori et al. All rights reserved
Aim of the study
The aim of this study is to evaluate theeffect of different tillage intensities onspring-summer weeds richness andabundance in a maize monoculture,during the transition phase fromconventional to conservation agriculture.
Weed
richness and
abundance
Effect of soil
tillage
Maize
monoculture
Diversity
indices
Conservation
agriculture
transition
phase
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
3
Introduction
© Sartori et al. All rights reserved
The weed survey was conducted in June2019 on an experiment comparing threelevels of tillage management:conventional agriculture (CT), whichrepresents the most common choice inVeneto region, involving deep ploughingand harrowing in spring; minimumtillage (MT), consisting only in harrowingat 20 cm; and no tillage (NT), namelysod seeding. The experiment started in2018, at Padova University experimentalfarm, in a sub-humid area, with a siltyclay loam soil.
•Conventional
tillage
•Spring
ploughing (30
cm)
•Harrowing
(20 cm)
CT
•Minimum
tillage
•Spring
harrowing (20
cm)
MT
•No tillage
•Conservation
agriculture
NT
Field operations
• 28/03/2019 → Tillage
• 02/04/2019 → Maize seeding
• 03/06/2019 → Weed scouting
Experimental design
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
4
Treatments (Factors)
Materials and methods
© Sartori et al. All rights reserved
The weed survey
• The frame random throws technique is the same described in Berti et al., 1992 Weed Research (doi.org/10.1111/j.1365-3180.1992.tb01860.x)
The survey was conducted with a set ofrandom throws of a 30×30 cm squareframe in each plot (ca. 3300 m2). Weedplants found within the frame wereclassified and counted. Subsequently,data analysis assessed which botanicalfamilies were promoted by eachtreatment.
Random throws
• 6 random sampling
point per plot
• 3 replications
Weed
observation
• Species
determination
• Count of the
individuals
Statistical
analyses
• Conversion in n° of
individuals per m2
• Indices calculation
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
5
Materials and methods
© Sartori et al. All rights reserved
Weed richness and abundance
The NT resulted the treatment with thehighest weed density (915 plant/m2): 6%higher than MT (823 plant/m2) and four-fold more than CT (209 plant/m2). Thelatter showed to be the treatment withhigher diversity, according to bothShannon and Simpson indices. Thesurvey evidenced higher weed speciesrichness in MT, where both annual andperennial species were identified, whilethe lowest number of species weredetected in NT.
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
6
2326
15
0
10
20
30
CT MT NT
Species abundance
207
821915
0
500
1000
CT MT NT
Weed richness (plant/m2)
Shannon indexGini-Simpson
indexEvenness
CT 2.64 0.91 0.58
MT 1.22 0.43 0.25
NT 0.67 0.26 0.17
Results
© Sartori et al. All rights reserved
Dominant species
Plantago major and Chenopodiumalbum were the species with the highestdensity in CT (>32 plant/m2) while theyare negligible in NT and MT (7 plant/m2,on average). Digitaria sanguinalis wasinstead the dominant species in MT andNT (>600 plant/m2) while a lowerdensity was observed in CT (11plant/m2). Low levels of Asteraceaeweeds were measured in all treatments.
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
7
783 59 28 10 540
50
100
150
33 32 26 24
124
0
50
100
150
616 35 34 33 1430
50
100
150
NT
MTCT
Asterceae
n° Species plant/m2
CT 5 22
MT 5 43
NT 3 15
Results
© Sartori et al. All rights reserved
Actual flora differences
These results show that the actual florarapidly changes depending on tillageintensity, with an increase of bothdominance and number of species inMT. Differently, only a limited number ofadapted species germinated in NT,despite higher infestations if comparedwith the other treatments.
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
8
CT
MT
NT
Average weed density (plant/m2) in each treatment (Digitaria sanguinalis
excluded). The number indicates the average density between
treatments.
Discussion
© Sartori et al. All rights reserved
Main findings
It should be expected that other speciesmore adapted to conservationagriculture (namely Asteraceae), stillmarginally present in the seed bank, willspread in the next years. This stressesthe importance of a continuousmonitoring and effective control ofweeds to avoid uncontrolled evolutionsof the weed flora and increase of seedbank in the transition phase fromconventional to conservation agriculture.
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
9
No significant increase of Asteraceae was observed after 2 years
Selection of adapted species in NT
Dominance of a D. sanguinalis in reduced tillage systems (MT and NT)
Conclusions
© Sartori et al. All rights reserved
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
10
Thanks for your attention
© Sartori et al. All rights reserved
Supplementary material – diversity indices
EGU2020: Sharing Geoscience Online - SSS8.8 Ecosystem development and critical zone research: Experimental ecosystem development research and coevolution of soils, landforms and vegetation
11
Shannon index (H) Gini-Simpson index (ത𝛌) Evenness (J)
𝐻 = −
𝑖=0
𝑆
ln 𝑝𝑖𝑝𝑖 ҧ𝜆 = 1 −
𝑖=0
𝑆
𝑝𝑖2 𝐽 = ൗ𝐻 log2 𝑆
p: proportion of individuals belonging to the ith speciesS: total number of species (richness)