Content uploaded by P.A. Verweij
Author content
All content in this area was uploaded by P.A. Verweij on May 14, 2019
Content may be subject to copyright.
Zurich Open Repository and
Archive
University of Zurich
Main Library
Strickhofstrasse 39
CH-8057 Zurich
www.zora.uzh.ch
Year: 2018
The impact of soil and vegetation management on the rehabilitation of
ecosystem services in almond orchards
Leijster, V; Santos, Maria J; Diaz, M; Wassen, M J; Belen, A B; Ramos, M E; Verweij, P A
Abstract: This study examines the use of green manure, no-tillage and compost to improve nutrient
cycling and plant species richness. Therefore we conducted a full factorial design with four treatments in
ve almond plantations. The treatments include the business as usual management, conventional tillage
(CT) and no-tillage (NT), compost (CM) and green manure (GM). Soil enzymatic activity was used as
a proxy for nutrient cycling and plant richness and cover for habitat provisioning. Phosphatase activity
increased with 50% in the alternative treatments, and the activity of glucosidase was twice as high in
CM compared to CT. Plant species richness was highest in NT, but the vegetation cover was found to
be equal in GM and NT. To conclude, implementing green manure, no-tillage and compost application
on a monoculture almond farm appear to be eective strategies to improve ecosystem services provided
on the farm, such as nutrient cycling and plant species conservation.
Posted at the Zurich Open Repository and Archive, University of Zurich
ZORA URL: https://doi.org/10.5167/uzh-162993
Conference or Workshop Item
Published Version
Originally published at:
Leijster, V; Santos, Maria J; Diaz, M; Wassen, M J; Belen, A B; Ramos, M E; Verweij, P A (2018). The
impact of soil and vegetation management on the rehabilitation of ecosystem services in almond orchards.
In: 4th European Agroforestry Conference - Agroforestry as a sustainable land use, Nijmegen (NL), 28
May 2018 - 30 May 2018, 227-231.
Environmental benefits of agroforestry
227
4th European Agroforestry Conference – Agroforestry as Sustainable Land Use
THE IMPACT OF SOIL AND VEGETATION
MANAGEMENT ON ECOSYSTEM SERVICES IN
EUROPEAN ALMOND ORCHARDS
Leijster V1*, Santos MJ1, 2, Diaz M1, Wassen MJ1,Belen AB3, Ramos ME3, Verweij PA1
(1) Copernicus Institute of Sustainable Development, Utrecht University, Heidelberglaan 2, 3584 CS Utrecht,
Netherlands (2) URPP GCB Global Change and Biodiversity, University of Zurich, Winterthurerstrasse 190, 8057
Zurich, Switzerland (3) Estación experimental del Zaidín (CSIC), C/Profesor Albareda, 1, 18008 Granada, Spain
*Corresponding author: v.deleijster@uu.nl
Abstract
This study examines the use of green manure, no-tillage and compost to improve nutrient
cycling and plant species richness. Therefore we conducted a full factorial design with four
treatments in five almond plantations. The treatments include the business as usual
management, conventional tillage (CT) and no-tillage (NT), compost (CM) and green manure
(GM). Soil enzymatic activity was used as a proxy for nutrient cycling and plant richness and
cover for habitat provisioning. Phosphatase activity increased with 50% in the alternative
treatments, and the activity of glucosidase was twice as high in CM compared to CT. Plant
species richness was highest in NT, but the vegetation cover was found to be equal in GM and
NT. To conclude, implementing green manure, no-tillage and compost application on a
monoculture almond farm appear to be effective strategies to improve ecosystem services
provided on the farm, such as nutrient cycling and plant species conservation.
Keywords: ecosystem services; agroecology; conservation agriculture; tree-crop; nutrient
cycling; habitat provisioning
Introduction
Over 30% of Mediterranean Europe is experiencing degradation of biophysical processes on
land (Zdruli 2014). Within Europe, Spain has the largest issues related to land degradation as
an estimated 12.5 % of the total territory is degraded (Bai et al. 2008), moreover other authors
are even estimating that the extent of the problem is reaching 28 – 54 % of the territory (Dregne
2002). Tree-crop systems play an important role in the reduction of ecosystem services due to
the widespread conventional management. In this conventional management, clean sweeping is
a common practice whereby soils are frequently tilled to assure that understory vegetation is
permanently removed (Meerkerk et al. 2008). This management results in a loss of soil of 5.70-
10.5 Mg ha-1 yr-1 and runoff of 10.9-58.1 mm ha-1 (Durán Zuazo and Rodríguez Pleguezuelo
2008). Additionally, the removal of understory vegetation in almond orchards is estimated to
reduce the abundance of pollinators by 64.3-86.8 % (Norfolk et al. 2016; Saunders et al. 2013).
Moreover, the frequent tillage practices are driving the breakage of soil aggregates and the loss
of 20 – 30 % soil organic carbon pool (West and Post 2002). This physical degradation of the
soil negatively affects the abundance and activity of soil biota that play a crucial role in
belowground ecosystem processes (Barrios 2007). Nonetheless, recent evidence is mounting to
show that alternative land management practices, such as cover crops or natural vegetation
covers, reduced or no-tillage and organic soil amendments, can contribute to the rehabilitation
of biophysical and ecological processes in almond orchards (Ramos et al. 2010; Almagro et al.
2013; Saunders et al. 2013; Ramos et al. 2011; Duran Zuazo et al. 2008; Martínez Raya et al.
2006; Macci et al. 2010). However, all these studies have been conducted on just a single, or in
some cases two experimental sites making it difficult to draw conclusions related to best
management practices. Therefore, this study experimentally tested the use of green manure,
no-tillage and compost applications in five farms, to assess their impact on nutrient cycling and
on habitat provisioning for plant species.
Environmental benefits of agroforestry
228
4th European Agroforestry Conference – Agroforestry as Sustainable Land Use
Enzymatic activity was assessed as a proxy for nutrient cycling service in the soil. Soil
enzymatic activities have been proven to be a powerful tool to assess soil quality as they
respond rapidly to changes in soil management (Burns et al. 2002). For this study, the enzymes
β-Glucosidase, Phosphatase, Urease and Dehydrogenase were chosen because they catalyse
the hydrolysis of organic compounds. They give an indication for the decomposition processes
in the soil, as they are indicators for the breakdown of cellulose (β-Glucosidase) and the P-cycle
(Phosphatase), N-cycle (Urease) and C-cycle (Dehydrogenase) (Das and Varma 2011).
Materials and methods
The research was conducted in the high planes of the provinces Granada and Almeria in the
East of Andalusia, SE Spain.
Experimental design
We conducted a full factorial design with four treatments in five existing almond plantations. On
each farm a homogeneous site was chosen where the four treatments were randomly
implemented, a treatment within a farm is hereafter referred to as a „plot‟. Each plot
corresponded to a rectangular area of at least four by eight trees, but only the inner two rows
with almond trees were included in the research, to optimize the effect of the treatment and
exclude the influence of adjacent management. The dimensions of the research plots were then
14 m x 56 m = 784 m2 (7m average distance between trees), and included a minimum of 15
trees (Figure 1).
In each farm, the four plots were implemented as follows:
CT – Conventional tillage: the plot is tilled 2-3 times a year to remove the understorey
vegetation using a cultivator.
NT – No-tillage: the plot is not tilled and has spontaneous understory vegetation.
GM –Green Manure: Common vetch (Vicia sativa; 50 kg ha-1), Bitter vetch (Vicia ervilia; 50 kg
ha-1) and Barley (Hordeum vulgare; 20 kg ha-1) were sown in the plots. Seeds were mixed in a
ratio of 5:5:2 and were sown by hand in December 2016 in a quantity of 120 kg ha-1. After
sowing, a cultivator passed to incorporate the seeds into the soil. In addition, after the ground
cover sampling, between the end of May and the beginning of June, the ground cover was
plowed into the soil with a cultivator.
CMP – Compost, type Bokashi: the plot is fertilized with compost, which was purchased from a
local vendor (Moreno Basura - Maria, Alméria). The compost was applied in December with a
quantity of approximately 6 m3 ha-1 and incorporated in the soil with a cultivator. During the rest
of the year, the plot was tilled 1-2 times to remove weeds.
Figure 1: Schematic overview of the four treatment plots. a) tillage (CT), b) green manure
(RTGM), c) no-tillage (NT), d) compost (CM). White soil color indicates bare soil, grey indicates
permanent vegetation, white/grey stripes indicate inpermanent vegetation (green manure seed
mixture), dots indicate that compost is applied.
Environmental benefits of agroforestry
229
4th European Agroforestry Conference – Agroforestry as Sustainable Land Use
Soil sampling
In each plot three soil samples of 1-2 kg were taken in April 2017, each consisted of ten sub-
samples that were randomly taken from the 0-20 cm soil layer from the plot. Soil samples were
sieved at field moisture through a 2 mm sieve. The samples were stored at 4°C until lab
analyses.
Enzymatic activity
Dehydrogenase activity was measured according to the methodology described by García et al.
(1997). To assess the Phosphatase activity and β-glucosidase we used the methodology of
Ramos et al. (2011). Urease activity was determined according to Nannipieri et al. (1982).
Vegetation sampling
The ground cover vegetation composition was assessed in May 2017 using the point-intercept
method, modified as proposed by Ruiz-Mirazo and Belén (2012). In each treatment plot, six 10
m long transects were randomly laid out, and each consisted of one hundred points measured
at a distance of 10 cm. At each point of the transect, a needle of 30 cm was put in the ground
and all plants that touched the needle were identified to the species level. When there was no
plant touching the needle, we recorded bare soil. From these data, we calculated vegetation
cover (%) and plant species richness (number of species per unit area).
Statistical analysis
Data was analysed with a generalized linear mixed model to test the effect of the treatments on
enzymatic activity, vegetation cover and plant species richness by using the lme4 package in R.
In this analysis the treatments were taken as a fixed factor and the farms were taken as a
random factor.
Results
We found a significant effect of treatment on soil enzymatic activities (Table 1), especially for
the enzyme phosphatase, where CT (conventional tillage) was related to a lower enzymatic
activity than the three other treatments, NT (no tillage), GM (green manure) and CM (compost).
We found that urease in NT was twice as high than CT, however this was not significant, also
the activity of this enzyme in CM and GM was higher than CT. Glucosidase enzymatic activity
was higher in CM than CT, however, GM and NT did not statistically differ from the other
treatments, but had on average higher activity than CT. Dehydrogenase activity was not
influenced by the treatments.
Both vegetation parameters turned out to be significantly affected by the implemented
management regimes (Table 1). The plant species richness was significantly higher for NT
treatment, followed by GM treatment. CM and CT had on average lower plant species richness.
Vegetation cover was significantly lower in CT than in all other treatments, except for CM. This
was mainly due to the large variation in cover in the compost treatment.
Environmental benefits of agroforestry
230
4th European Agroforestry Conference – Agroforestry as Sustainable Land Use
Table 1: Mean values ± standard error of the activity of dehydrogenase (mgr INTF h-1),
glucosidase (mgr PNP h-1), phosphatase (mgr PHO h-1), Urease (mgr NH4 h-1), and vegetation
cover (%) and plant species richness (# species transect-1), for the treatments conventional
tillage (CT), no-tillage (NT), green manure (GM) and compost (CM).
ES indicator
p-value
CT
NT
GM
CM
Nutrient cycling
Dehydrogenase
0.7
2.1 ± 1.4
2.7 ± 1.9
2.5 ± 1.9
2.7 ± 1.5
Glucosidase
0.01
140 ± 78
b
365 ± 215
ab
270 ± 97
ab
330 ± 140
a
Phosphatase
0.001
102 ± 72
b
157 ± 59
a
150 ± 59
a
159 ± 67
a
Urease
0.6
33 ± 32
65 ± 50
51 ± 30
55 ± 35
Habitat provisioning
Vegetation cover
1E-07
25 ± 25
b
72 ± 27
a
72 ± 18
a
34 ± 43
b
Plant species richness
1E-07
6.3 ± 5.1
b
11.2 ± 2.9
a
7.4 ± 3.0
ab
5.3 ± 4.6
b
Discussion
In this study we found that improved management practices, such as green manure, no-tillage
and compost application, played a significant role in the rehabilitation of soil services
provisioning and plant species conservation. The enhancement of phosphatase activity in all
treatments compared to conventional tillage shows that the capacity to release organically-
bound phosphorus may be increased with improved management practices leading to a boost
in the P-cycle for the benefit of all plants present including the almond trees. Additionally, we
found that dehydrogenase, an enzyme that plays a role in the decomposition process within the
C-cycle, is not sensitive to changes in these soil and vegetation management practices. The
other enzymatic activities, that play roles in the N-cycle and P-cycle and in the breakdown of
cellulose, have shown to be enhanced after implementation of these management practices. To
improve plant species richness, no-tillage management is most effective. However, for
increasing vegetation green manure is just as effective.
To conclude, implementing green manure, no-tillage and compost application on a monoculture
almond farm appear to be effective strategies to improve and rehabilitate ecosystem services
provided on the farm, such as nutrient cycling and plant species conservation.
References
Almagro M, de Vente J, Boix-Fayos C, García-Franco N, Melgares de Aguilar J, González D, Martínez-Mena M (2013)
Sustainable land management practices as providers of several ecosystem services under rainfed
Mediterranean agroecosystems. Mitig Adapt Strateg Gl 21: 1029-1043.
Bai ZG, Dent DL, Olsson L, Schaepman ME (2008) Proxy global assessment of land degradation. Soil Use Manag 3:
223–234.
Barrios E (2007). Soil biota, ecosystem services and land productivity. Ecol Econ 64: 269–285.
Burns RG, Nannipieri P, Kandeler E, Ruggiero P (2002) Enzymes in the Environment± Activity, Ecology, and
Applications. Marcek Dekker.
Das SK, Varma A (2011). Role of Enzymes in Maintaining Soil Health. Soil Biol 22: 25–42.
Dregne HE (2002) Land Degradation in the Drylands. Arid Land Res Manag 16: 99–132.
Durán Zuazo VH, Rodríguez Pleguezuelo CM (2008). Review article Soil-erosion and runo ff prevention by plant covers
. A review. Agron Sustain Dev 28: 65–86.
Duran Zuazo VH, Rodriguez Pleguezuelo CR, Marinez-Raya A, Francia Martinez JR, Panadero LA, Rodriguez BC
(2008) Environmental and Agronomic Benefits of Aromatic and Medicinal Plant Strips for Rainfed Almond
Orchards in Semiarid Slopes (SE, Spain). Open Agr J 2: 15–21.
García C, Hernández T, Cota F (1997) Potential Use of Dehydrogenase Activity as an Index of Microbial Activity in
Degraded Soils. Commun Soil Sci Plant Anal 28:123-134
Macci C, Doni S, Peruzzi E, Masciandaro G, Mennone C, and Ceccanti B (2010). Almond tree and organic fertilization
for soil quality improvement in southern Italy. J Environ Manag 95: 215–222.
Martínez Raya A, Durán Zuazo VH, Francia Martínez JR (2006) Soil erosion and runoff response to plant-cover strips
on semiarid slopes (SE Spain). Land Degrad Dev 17: 1–11.
Meerkerk A, van Wesemael B, Cammeraat E (2008) Water availability in almond orchards on marl soils in southeast
Spain: The role of evaporation and runoff. J Arid Environ 72: 2168–2178.
Nannipieri P, Ceccanti B, Cervelli S, Conti C (1982) Hydrolases extracted from soil: Kinetic parameters of several
enzymes catalysing the same reaction. Soil Biol Biochem 5: 429-432.
Norfolk O, Eichhorn MP, Gilbert F (2016) Flowering ground vegetation benefits wild pollinators and fruit set of almond
Environmental benefits of agroforestry
231
4th European Agroforestry Conference – Agroforestry as Sustainable Land Use
within arid smallholder orchards. Insect Conserv Diver 9: 236–243.
Ramos ME, Benítez E, García PA, Robles AB (2010) Cover crops under different managements vs. frequent tillage in
almond orchards in semiarid conditions: Effects on soil quality. Appl Soil Ecol 44: 6–14.
Ramos ME, Robles AB, Sánchez-Navarro A, González-Rebollar JL (2011) Soil responses to different management
practices in rainfed orchards in semiarid environments. Soil Till Res 112: 85–91.
Ruiz-Mirazo J, Belén AB (2012) Impact of targeted sheep grazing on herbage and holm oak saplings in a silvopastoral
wildfire system in south-eastern Spain. Agrofor Syst 86: 477-491.
Saunders ME, Luck GW, Mayfield MM (2013) Almond orchards with living ground cover host more wild insect
pollinators. J Insect Conserv 17: 1011–1025.
West OW, Post WM (2002) Soil Organic Carbon Sequestration Rates by Tillage and Crop Rotation : A Global Data
Analysis Soil Organic Carbon Sequestration Rates by Tillage and Crop Rotation : A Global Data Analysis. Soil
Sci Soc Am J 66: 1930–1946.
Zdruli P (2014) Land resources of the Mediterranean: Status, pressures, trends and impact on future regional
development. Land Degrad Dev 384: 373–384.