Scientia Horticulturae 107 (2006) 365–372
www.elsevier.com/locate/scihorti
The influence of drip irrigation or subirrigation on tomato grown in
closed-loop substrate culture with saline water
L. Incrocci *, F. Malorgio, A. Della Bartola, A. Pardossi
Dipartimento di Biologia delle Piante Agrarie, Viale delle Piagge, 23 I-56124 Pisa, Italy
Received 21 January 2005; received in revised form 13 September 2005; accepted 7 December 2005
Abstract
In closed-loop soilless culture, one of the most relevant problems may be the accumulation in the recirculating nutrient solution of ions
contained in irrigation water that are not or scarcely absorbed by the plants (e.g. Na, Cl) In order to verify the possibility to reduce the rate of
recirculating water salinisation by means of subirrigation, an experiment was carried out in the spring of 2002 and 2004, with tomato plants (cv.
Jama) grown in glasshouse and watered by conventional drip irrigation (D) or by subirrigation (trough bench system; S). The plants were cultivated
in pots filled with a peat-perlite substrate for approximately 3 months and fed with complete nutrient solution, which was prepared with fresh water
containing 10 mol m3 NaCl; the nutrient solution in the collecting tank was replaced when the value of electrical conductivity (EC) exceeded
6.0 dS m1. Water and nutrient crop use, salt accumulation in the substrate, and fruit yield were monitored. In S culture, the composition and EC of
the recirculating nutrient solution changed slightly, while in D treatment there was a fast water salinisation that made it necessary to flushed out the
nutrient solution in six different occasions, with consequent loss of water and fertilisers. In S culture, the upward water movement in the substrate,
coupled with selective mineral uptake by the roots, caused salinity build-up in the upper region of the substrate, which was associated with Na+
accumulation. No significant influence of irrigation methods on fruit yield and quality was observed. These findings suggest that subirrigation can
be a tool to reduce the water consumption and nutrient runoff in closed-loop substrate culture of tomato conducted with saline water.
# 2005 Elsevier B.V. All rights reserved.
Keywords: Hydroponics; Lycopersicon esculentum mill; NaCl; Salinity; Soilless culture; Subirrigation; Substrate
1. Introduction
In protected horticulture closed-loop aggregate (substrate)
cultures with drip (top) or bottom irrigation (trough or ebb-andflow bench systems) are increasingly used since they can
minimise water use and limit the environmental pollution
resulting from nutrient runoff (Voogt and Sonneveld, 1997). In
these systems, the nutrient solution drained from the growing
medium is collected and recirculated after proper adjustment of
pH and nutrient concentration, the latter being generally
assessed by measuring electrical conductivity (EC).
In terms of water relations, four main components can be
identified in closed substrate culture: (1) the water added to the
mixing tank to compensate for plant transpiration and growth;
(2) the recirculating nutrient solution; (3) the substrate; (4) the
plants. Inevitably, any ion contained in the irrigation water that
is not fully absorbed by the plants (such as Na and Cl) would
* Corresponding author. Tel.: +39 050 2216529; fax: +39 050 2216524.
E-mail address: incrocci@agr.unipi.it (L. Incrocci).
0304-4238/$ – see front matter # 2005 Elsevier B.V. All rights reserved.
doi:10.1016/j.scienta.2005.12.001
accumulate in the recirculating water (Silverbush and BenAsher, 2001; Carmassi et al., 2005) and in the growing medium,
in a proportion that depends on how the water moves in the
substrate, then on the irrigation method.
In drip-irrigated culture, water is generally distributed in
excess. Therefore, the salts not taken up by the crop are
removed from the substrate by drainage water and tend to
accumulate in the recirculating nutrient solution, which has to
be flushed out more or less frequently (semi-closed system),
with consequent waste of water and fertilisers. Compared to
drip irrigation, bottom irrigation (subirrigation) may reduce salt
accumulation in the recirculating nutrient solution, since the
upward water movement (by capillary force and evapotranspiration-driven mass flow) makes soluble salts to accumulate
in the growing medium (Reed, 1996). The use of poor-quality
water accelerates the salinity build-up in the substrate and may
produce negative effects on salt-sensitive crops.
Several papers (e.g. Molitor, 1990; Dole et al., 1994; Reed,
1996; Morvant et al., 1997; Todd and Reed, 1998; Uva et al.,
1998; Treder et al., 1999; Lenzi et al., 2000; Cox, 2001; James
and van Iersel, 2001; Guarino et al., 2002) have documented the
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L. Incrocci et al. / Scientia Horticulturae 107 (2006) 365–372
advantages of zero-runoff subirrigation (e.g. reduced labour
costs and lower risk for root diseases) for greenhouse
cultivation of pot ornamentals. However, less attention has
been paid to the application of this technique to vegetable
production (Santamaria et al., 2003; Serio et al., 2004).
In this study, drip irrigation and subirrigation (trough bench
system) were compared to cultivate tomato plants in a closedloop system using fresh water with 10 mol m3 NaCl for
preparing the nutrient solution. The aim was to verify the
possibility to reduce, by means of subirrigation, the rate of salt
accumulation in the recirculating nutrient solution with a
consequent decrease in water use and nutrient leaching.
Santamaria et al. (2003) published a similar paper, in which
open-loop (without recirculating nutrient solution) drip
irrigation and a trough bench system were evaluated to grow
cherry tomato, which is considered relatively tolerant to salinity
(Cough and Hobson, 1990), for 4 months under the typical
greenhouse conditions of Mediterranean autumn. With respect
to that work, in our study: (i) water was recycled in both
irrigation systems; (ii) a more salt-sensitive tomato genotype
and saline (NaCl-enriched) water were employed; (iii) the
plants were grown in spring, that is under conditions enhancing
evapotranspiration and rendering the plants more susceptible to
salinity stress; (iv) an expedient was adopted to mitigate the
possible effect of salinity build-up in the root zone of
subirrigated plants (specifically, the volume of substrate was
doubled with respect to drip irrigation treatment).
system (roughly 20 L m2) was greater by 25% than the one in
D culture (roughly 16 L m2), notwithstanding a slightly lower
substrate moisture in S pots (1.9 L pot1) with respect to D ones
(2.5 L pot1).
Drip irrigation was automatically controlled on the basis of
GR, which was measured with a piranometer. Depending on the
growing stage, a watering dose of 0.6–1.2 L m2 was supplied,
whenever cumulated GR reached 1.0 MJ m2; one emitter was
placed in each pot. Leaching fraction (i.e. the ratio between
drainage and irrigation volume) was around 0.60.
In S treatment the pots were flooded, at a flow rate of
approximately 3.0 L min1 and to a height of 20–22 mm, for
15 min, six times during the day and once during the night,
since nocturnal plant transpiration was not negligible (it
accounted for up to 10–15% of daily water uptake).
Every day, the collecting tank of each growing unit was
automatically refilled with newly prepared nutrient solution to
compensate for crop water uptake. The EC and the ion
composition (mol m3) of the refill water was the following:
EC 3.0 dS m1; 11.0 N-NO3; 1.0 H2PO4, 7.5 K+, 2.5 Mg2+,
4.0 Ca2+, plus Hoagland’s microelement concentration. The
nutrient solution was prepared using NaCl-enriched water
(10 mol m3).
The nutrient solution was checked daily for EC and pH; the
latter was eventually adjusted to 5.5–6.0 with sulphuric acid.
The nutrient solution of the collecting tank was renewed
whenever the EC value exceeded 6.0 dS m1.
2. Materials and methods
2.2. Determinations
2.1. Plant material and growing conditions
In addition to the weight and number of fruits harvested in
due course at turning-red stage, the incidence of nonmarketable (too small, cracked, affected by blossom-end rot
or by Botritys) berries was recorded. Several quality attributes
were also determined on the purée of marketable fruits: dry
matter content, acidity (determined by titration with 0.1 mM
NaOH and expressed as citric acid) and total soluble solids
(determined with a bench refractometer).
The volume and ion concentration of the refill water and of
exhausted solutions (EC > 6.0 dS m1) were systematically
measured; the ion concentration of recirculating water was also
determined every 3–7 days. Flame photometry was used for the
analysis of K and Na; Ca and Mg were determined by EDTA
titration method, while ion chromatography was used for anions.
At the end of the experiment, two plants were sampled from
each replicate and subdivided in leaves, stems, fruits and
substrate (including some roots). Leaf area was measured with
a digital planimeter and leaf area index (LAI) was calculated.
Afterwards, plant samples were dried at 80 8C in a ventilated
oven and then analysed for N, P, K and Na. Total N was
determined by measuring both reduced N (with a mini-Kjeldhal
system) and N-NO3; the latter was determined on the aqueous
extract of dry matter (1:300, w:w) using Cataldo’s method
(Cataldo et al., 1975). After perchloric acid digestion (90 min at
150 8C) of dry matter, K and Na were determined by flame
photometry, and P by colorimetric method. The dry matter of
fruits that had been previously collected from each plant was
Round-fruit tomato plants (Lycopersicon esculentum Mill.,
cv. Jama F1) were grown in pots (18-cm diameter, 15-cm
height, approximately 3.2-L volume) filled with a peat-perlite
mixture (1:1, v:v), in a recirculating water system. Plant density
was roughly 3.0 plant m2. The experiment was conducted in a
heated glasshouse at the University of Pisa in the spring of 2002
and repeated in 2004. The culture was initiated at the end of
March by transplanting 50-day-old seedlings (raised in
standard rockwool cubes) and lasted 13 weeks.
Plants were grown vertically with single stem and stopped
by cutting at the second leaf above the fifth truss. Bumblebees
were kept in the glasshouse to improve flower pollination. The
minimum (heating) and ventilation air temperature inside the
glasshouse were 16 and 27 8C, respectively; maximum
temperature reached up to 33–35 8C during sunny hours in
late spring. Maximum photosynthetic photon flux density
(PPFD) ranged from 500 to 700 mmol m2 s1; mean values of
daily global radiation (GR) was 9.9 MJ m2.
A complete randomised block experimental design was
adopted with three replicates for subirrigation (S) and drip
irrigation (D) treatment. Each replicate consisted of 48 plants
grown in four gullies (5-m long and 0.22-m wide) connected to
an individual collecting tank (140 L; 8.8 L m2). In S treatment
each seedling was planted with the roots split in two adjacent
pots. As a consequence, the volume of recirculating water in S
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included in the calculation of total fruit dry weight. The
quantity of tested elements accumulated in the root zone during
the cultivation was corrected for the substrate mineral content,
determined at the transplanting time.
At the end of experiment, some determinations were also
performed on the aqueous extracts of substrate. The substrate of
sampled pots was divided horizontally in three equal layers
(5 cm), from which major roots were removed. Afterwards, a
sub-sample was extracted with distilled water with a dry
substrate:water ratio (w:w) of 1:10 (for that, moisture content
was determined in another sub-sample); finally, EC and the
concentration of Na and K (as representative of nutrients) were
measured in the filtered extracts.
The contribution of Na and K to the substrate salinity was
calculated on the basis of the equation proposed by Sonneveld
et al. (1999):
EC ¼ 0:10 C þ
(1)
This equation allows the calculation of EC from the total
equivalent concentration (C+; eq m3) of cations or anions,
assuming that the cationic–anionic balance maintains the electroneutrality of the water solution. The contribution of K and
Na was calculated as the percent ratio of their concentration on
the total cation concentration calculated with Eq. (1).
2.3. Salt leaching
In 2004, a simple experiment was performed to assess the
salt leaching from D and S pots during a typical irrigation event.
For that, after 10 weeks from planting, eight plants in their pots
for each treatment were gently removed from the gullies and
placed in separate growing units, which were made by a 1.5-m
long gully connected to a tank with 10 L of deionised water.
The pots removed from D culture were drip-irrigated for 90 s
(about 400 mL of water were supplied to each pot), while S pots
were subirrigated for 15 min. By 0, 5, 10 and 15 min, the EC of
recirculating water was measured and the following equation
was used to convert EC (dS m1) to salt concentration (SC,
g L1) (Maynard and Hochmuth, 1997):
EC ¼ 0:64 SC
(2)
2.4. Statistics
Since the experiment carried out in 2002 and 2004 gave
similar results, only the second experiment has been reported
herein. The values are means (S.E.) of three replicates; after
ANOVA, LSD test was used for mean separation.
3. Results
3.1. Plant growth, mineral status and fruit yield
Neither LAI nor plant dry matter accumulation was affected
significantly by watering method (Table 1). On the other hand,
compared to D, S decreased the leaf and stem concentration of
Table 1
The influence of subirrigation on plant dry weight, leaf area index (LAI),
mineral composition and fruit yield of tomato plants grown in closed-loop
substrate culture, as determined 91 days after planting
Parameter
LAI
Dry weight
(kg m2)
Nitrogen
(% DM)
Leaves
and stem
Fruits
Whole shoot
Leaves
and stem
Fruits
Phosphorus
(% DM)
Leaves
and stem
Fruits
Potassium
(% DM)
Leaves
and stem
Fruits
Sodium
(% DM)
Fruit yield
Subirrigation
Drip
irrigation
Significance
4.01 0.08
0.62 0.02
4.25 0.12
0.66 0.02
ns
ns
0.67 0.02
1.29 0.03
0.70 0.02
1.36 0.02
ns
ns
3.06 0.08
3.70 0.15
**
2.18 0.15
2.01 0.14
ns
0.31 0.01
0.52 0.03
***
0.25 0.01
0.26 0.01
ns
3.80 0.21
3.96 0.22
ns
3.65 0.29
3.84 0.22
ns
Leaves
and stem
Fruits
2.57 0.29
1.75 0.22
**
1.50 0.12
1.10 0.08
*
Kg m2
N fruits m2
10.6 0.5
63 2.0
10.9 0.6
63.9 2.4
ns
ns
The data represent the mean values of three replicates (S.E.); for each row, the
significance of the difference between irrigation systems is shown; ns: not
significant.
*
Significant for P < 0.05.
**
Significant for P < 0.01.
***
Significant for P < 0.001.
both N and P and increased that of Na (Table 1); no differences
were recorded between D and S treatments for the concentration of K in green parts. Subirrigation also promoted the
accumulation of Na in the fruits, which had a similar
concentration of N, P and K in both irrigation systems (Table 1).
Regardlessofirrigationmethod,therewas nodifferencein fruit
production (Table 1) and quality, as assessed by the determination
of a seriesof parameters in marketableberries (data notshown); on
average, dry residue, titrable acidity and total soluble solids were
6.4%, 0.80% of citric acid and 5.28 Brix, respectively. Nevertheless, the fruits picked from the last two trusses of S plants had
lower fresh weight (25%) and higher total soluble solids (+10%)
with respect to D treatment (data not shown).
3.2. EC and ion concentration of recycling water
Due to salinity build-up, the nutrient solution was replaced
in six different occasions in D culture (Fig. 1, top; Table 2). On
the contrary, S plants were grown with the same nutrient
solution during the whole growing period (about 3 months)
since EC, albeit increasing, never reached the EC threshold
(6.0 dS m1) for flushing. In D treatment, the first renewal of
nutrient solution occurred after 48 days from planting, when the
cumulated crop water uptake was around 120 L m2; at the
same date, EC was only 3.95 dS m1 in S culture. Periodical
flushings did not restore the original EC value (3.0 dS m1) of
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L. Incrocci et al. / Scientia Horticulturae 107 (2006) 365–372
total ion concentration by more than 50% compared to 33% in
the fresh nutrient solution (Table 2).
A tendency to rise during the last weeks was noticed also for
all the macronutrients with the exception of P, as illustrated by
Fig. 1 (bottom) where, for the sake of brevity, only K+
concentration has been shown. Presumably, this phenomenon
resulted from reduced nutrient uptake by the crop in reason of
low growth rate.
With respect to the refill nutrient solution, the concentration
of macronutrients in the exhausted nutrient solutions of D
culture was 14–33% higher, although its contribution to the
total salinity was lower (Table 2).
3.3. Water and nutrient balance
Fig. 1. The influence of subirrigation (empty circle) or drip irrigation (filled
circle) on the electrical conductivity (EC) and the concentration of Na and K of the
recirculating nutrient solution in a closed-loop substrate culture of tomato. The
value of EC threshold for flushing (as indicated by arrows in the upper graph) and
the Na+ or K+ concentration in the refill water are also shown. The data represent
the mean values of three replicates (the vertical bars represent the S.E.).
recycling water on account of the salt-enriched nutrient solution
retained by the substrate.
In both irrigation treatments, the progressive rise in the EC
of recirculating water was associated with the vast increase in
Na concentration (Fig. 1, middle; Table 2), which in D culture
rose up to values that were nearly four times greater than in the
refill water (10 mol m3). The change in the Cl concentration of
recirculating water paralleled that of the Na. The concentration
of these ions was roughly equal and in the exhausted culture
solutions of D treatment was 36–38 mol m3, accounting for
Irrigation method did not influence significantly daily water
uptake, which tended to increase during growing period (Fig. 2)
because of leaf development and the occurrence of environmental conditions more favourable to leaf transpiration.
In D culture, the periodical flushing produced a runoff of
nearly 62 L m2 and, therefore, total water use was significantly larger (+15%) than in S culture, in which water use
efficiency (the fruit yield per cubic meter of water applied) was
also improved (Table 3).
Using the data obtained from the analysis of nutrient
solutions, substrates and plant tissues, a balance for N, P, K and
Na was compiled for each culture (Table 4). The mineral supply
in Table 4 was calculated on the basis of the volume and the ion
concentration of refill water. For S culture, the estimated crop
mineral uptake incorporated the nutrients contained in the
residual nutrient solution at the end of cultivation; diversely,
this residue was considered in calculating runoff in D treatment,
since EC was higher than 6.0 dS m1.
Irrigation system did not influence considerably the
macronutrient consumption, which was estimated as the
differences between nutrient supply and leaching, or by
determining the nutrients accumulated in leaves, stems, fruits
and growing medium. A noteworthy divergence between the
two procedures was found only for P. Actually, the value
derived from the supply-leaching difference was higher
(roughly by 30%) than the one determined on the basis of
chemical analysis. This difference was presumably due to the
precipitation of P salts in the growing benches and in the
collecting tank.
On account of leaching requirement, the total use of N, P and
K was higher in D treatment than in S (Table 4). In D treatment
the runoff of N (115 kg ha1) and P (18 kg ha1) was massive,
also in consideration of the short growing cycle (3 months).
The irrigation method also changed the nutrient allocation.
At least for N and P, the amount of nutrients contained in leaves
and stems was higher in D than in S (Table 4), as a result of the
increased element concentration in dry biomass (Table 1). Due
to the larger volume of substrate, in S culture the N, P and K
retained by the root zone was two- or three-fold greater than in
D (Table 4). Different results were found for Na (Table 4),
however. Indeed, the estimated or measured Na consumption in
S culture was much larger than in D treatment due to an increase
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L. Incrocci et al. / Scientia Horticulturae 107 (2006) 365–372
Table 2
Electrical conductivity (EC) and ion concentration in the refill water, in the exhausted nutrient solutions periodically discarded from drip-irrigated culture or in the
residual nutrient solution in subirrigated culture
EC
(dS m1)
Na+
(mol m3)
K+
(mol m3)
Mg2+
(mol m3)
Ca2+
(mol m3)
N-NO3
(mol m3)
P-H2PO4
(mol m3)
Cl
(mol m3)
Total
concentration
(mol m3)
3.1
10.0
21.7
7.5
16.4
2.5
5.4
4.0
8.7
11.0
23.9
1.0
2.2
10.0
21.7
46.0
100.0
Exhausted nutrient solution (drip irrigation)
6.07
37.1
I (48 dat*)
II (59 dat)
6.74
36.3
III (66 dat)
6.26
38.5
IV (72 dat)
6.08
37.0
V (81 dat)
6.81
36.1
VI (86 dat)
6.81
35.7
VII (91 dat; residue)
7.05
35.3
7.9
7.9
8.4
8.7
11.9
12.1
12.9
4.0
3.4
3.8
3.7
3.7
3.7
3.7
5.9
5.5
5.1
5.1
5.2
5.5
5.5
10.0
11.9
12.0
11.6
14.0
14.0
14.5
0.8
0.9
1.0
0.9
0.8
0.9
1.1
35.4
38.4
34.8
36.9
38.9
39.7
39.7
91.2
95.4
94.7
95.1
101.7
102.4
112.7
Refill nutrient solution
Contribution (%)
Mean value
Contribution (%)
6.55
%
36.6
34.3
10.0
9.3
3.6
3.4
5.3
5.0
12.6
11.8
0.9
0.9
37.7
35.3
106.7
100.0
4.20
18.7
25.3
11.9
16.0
5.6
7.5
4.3
5.8
13.0
17.5
1.3
1.7
19.5
26.2
74.3
100.0
Residue (subirrigation)
Contribution (%)
The contribution of each ion to the total concentration of measured ions is also shown.
*
Dat: days after transplanting.
in plant uptake and, principally, to the massive ion deposit in the
root zone (seemingly, in the medium).
The apparent ion uptake concentration (CU; i.e. the ratio
between ion and water uptake) for Na was 9.5 and 2.7 meq L1
for S and D plants, respectively. This difference resulted from
the Na accumulation in the growing medium, since no
difference between S and D treatment was recorded when
CU for both Na and macronutrients was calculated on the basis
of crop water uptake and genuine element accumulation in
plant tissues (data not shown).
3.4. Substrate salinity
The pattern of salt distribution in the root zone of D and S
plants was investigated by measuring, at the end of cultivation,
pH, EC and the concentration of K and Na in the aqueous
extract of different substrate regions.
As indicated by the value of EC (Fig. 3, top), in S treatment
the salts tended to concentrate in the upper layer where there
were much less roots, which grew preferentially in the lower
region (as found by visual assessment). By contrast, a
decreasing EC from the bottom to the top third of the substrate
was found in D culture, in which roots tended to occupy the
whole pot. In D culture, the EC of the upper region was three
times lower than in S treatment (Fig. 3, top).
At least in S pots, a large vertical gradient was found in Na
concentration that showed a tendency to accumulate in the top
region (Fig. 3, middle); the reverse phenomenon was observed
in D pots.
In both treatments, K concentration was less stratified
among the substrate regions although, when compared to
middle and bottom layer, a significant increase (S) or decrease
(D) was found in the top portion (Fig. 3, bottom).
Table 3
The influence of subirrigation or drip irrigation on the water use of a closed-loop
substrate culture of tomato
Fig. 2. The influence of subirrigation (empty columns) or drip irrigation (filled
columns) on the weekly averages of daily water uptake of tomato plants grown
in closed-loop substrate culture. The data represent the mean values of three
replicates (the vertical bars represent the S.E.).
Parameter
Subirrigation
Drip
irrigation
Significance
Water supply (WS; L m2)
Residue or runoff (R; L m2)
Crop water uptake (WS-R; L m2)
Water use efficiency (g L1)
324
9
315
32.7
373
62
312
29.2
*
**
ns
*
The data represent the mean values of three replicates; for each row, the
significance of the difference between irrigation systems is shown; ns: not
significant.
*
Significant for P < 0.05.
**
Significant for P < 0.01.
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L. Incrocci et al. / Scientia Horticulturae 107 (2006) 365–372
Table 4
The influence of subirrigation or drip irrigation on the mineral use of a closedloop substrate culture of tomato
Parameter
Subirrigation
Drip irrigation
Significance
2
Nitrogen (g m )
Supply
Residue or runoff
Estimated crop uptakea
Measured crop uptakeb
Allocated mineral content
Leaves and stem
Fruits
Whole shoot
Substrate
Phosphorus (g m2)
Supply
Residue or runoff
Estimated crop uptakea
Measured crop uptakeb
Allocated mineral content
Leaves and stem
Fruits
Whole shoot
Substrate
Potassium (g m2)
Supply
Residue or runoff
Estimated crop uptakea
Measured crop uptakeb
Allocated mineral content
Leaves and stem
Fruits
Whole shoot
Substrate
Sodium (g m2)
Supply
Residue or runoff
Estimated crop uptakea
Measured crop uptakeb
Allocated mineral content
Leaves and stem
Fruits
Whole shoot
Substrate
*
48.6
1.5
47.1
46.6
55.8
11.5
44.3
43.5
19.0
14.6
33.6
13.0
24.4
14.1
38.5
5.0
10.0
0.3
9.7
7.0
11.6
1.8
9.8
6.4
1.9
1.7
3.6
3.4
3.4
1.8
5.2
1.2
92.8
3.4
89.4
87.5
106.2
24.1
82.1
79.1
23.6
24.5
48.1
39.4
26.1
26.9
53.0
26.1
ns
ns
ns
74.5
3.8
70.7
71.0
85.8
51.8
34.0
30.1
*
15.9
10.1
26.0
45.0
11.6
7.7
19.3
10.8
*
***
ns
ns
*
ns
*
***
*
***
ns
ns
***
ns
**
***
*
***
ns
*
**
***
***
***
*
*
***
The data represent the mean values of three replicates; for each row, the
significance of the difference between irrigation systems is shown; ns: not
significant.
a
The values were calculated as the difference between supply and residue or
runoff.
b
The values were calculated on the basis of plant dry biomass and its element
concentration.
*
Significant for P < 0.05.
**
Significant for P < 0.01.
***
Significant for P < 0.001.
The contribution of Na to the total cation concentration
increased with pot height in S and diminished in D (Fig. 3,
middle), while the opposite trends were found for K (Fig. 3,
bottom).
Irrigation system and sample type did not influence
significantly substrate pH, which ranged between 5.8 and
6.4, although a slight alkalisation with increasing pot height
Fig. 3. The influence of subirrigation (empty columns) or drip irrigation (filled
columns) on the electrical conductivity (EC) and the Na+ or K+ concentration of
the aqueous extracts of different substrate layers sampled in a closed-loop
culture of tomato. The data represent the mean values of three replicates (the
vertical bars represent the S.E.); in each graph, the bars accompanied by the
same letter are not significantly different (P < 0.05). The values within brackets
represent the Na or K contribution to total cation concentration.
was observed in S plants. The initial pH of growing medium
was nearly 6.0.
3.5. Salt leaching
Fig. 4 shows the results of an experiment conducted to
quantify the salt leaching that occurred during a typical
L. Incrocci et al. / Scientia Horticulturae 107 (2006) 365–372
Fig. 4. The influence of subirrigation (empty circle) or drip irrigation (filled
circle) on the salt leakage that occurred from pots with tomato plants during a
typical irrigation event. Drip irrigation lasted 90 s and some 400 mL of
deionised water were supplied to each pot, while subirrigation lasted
15 min. Salt leakage was assessed on the basis of the measurement of electrical
conductivity (EC) of the solution in the mixing tank. The data represent the
mean values of three replicates (the vertical bars represent the S.E.).
irrigation event in D and S culture. After the end of watering
and drainage, it was calculated from EC value that 1.22 g of
salts were leached out of each D pot against 0.04 g in S
treatment.
4. Discussion
This work showed that subirrigation may reduce substantially the salinisation of the recirculating nutrient solution that
typically occur in drip-irrigated substrate culture as a
consequence of the accumulation of ions contained in the
fresh water that are not fully absorbed by the crop.
In this growing system, the volume (V) of recirculating
nutritive culture, which includes the water retained by the
substrate and represents the water buffer, influences the change
in salt concentration, according to a model recently published
by Carmassi et al. (2005).
Using this model, the change in the Na concentration of S
culture was simulated using two values for V: the actual one
(20 L m2) and the one used in D culture (16 L m2), with the
aim to estimate how much the difference (in terms of
recirculating water salinity) between D and S treatments was
due to the irrigation system and to the different water buffer.
The rate of Na accumulation was higher with lower V, but the
concentration (data not shown) never reached the values (nearly
40 mol m3; Table 3) that typically led to the EC limit for
flushing.
In S culture, the salt tended to accumulate in the growing
medium, in particular in the upper third, as a result from the
ascendant water movement coupled with the selective root
mineral uptake. Indeed, in S culture the increase in substrate EC
was associated with the large accretion of Na+; in addition, the
contribution of this ion to substrate salinity increased with pot
height in S and diminished in D, while the opposite trend was
found for K. A differential contribution of tested nutritive ions
371
to the EC of different substrate layers was observed in pot
culture by other authors (Treder et al., 1999).
Apparently the higher EC in the upper portion of substrate
did not cause salinity stress to S plants, because their roots grew
mostly in the bottom region, where the values of determined
parameters were similar in both treatments. In fact, no symptom
of nutrient deficiency and/or salt injury (wilting or desiccation
of leaves) was shown by S plants and no differences between D
and S treatment were found in terms of plant growth, leaf
development, crop yield and fruit quality.
The absence of any important effect of root zone salinisation
on plant growth in S culture was also related to the use of a
much larger volume of substrate. In fact, in a preliminary
experiment with one pot only per plant, subirrigation decreased
remarkably plant growth and fruit yield (data not shown). This
result, actually, suggested the expedient of a double volume of
substrate for S treatment.
The considerable deposit of Na in the root zone of S culture
stimulated plant uptake of this ion (as suggested by higher Na
concentration of both green parts and fruits of S plants,
compared to D treatment) and reduced that of N and P, at least
in leaves and stems (Table 1). Other authors reported that in
plants Na uptake is proportional to its concentration in the root
zone (Sonneveld, 2000; Silverbush and Ben-Asher, 2001;
Malorgio et al., 2001), and that a relatively high Na content in
the growing medium may reduce the shoot content of N and P
(Savvas and Lenz, 2000; Cox, 2001).
The accumulation of Na in plant tissues could be responsible
for a decrease in fruit production in a cultivation that takes
longer than in this study. Indeed, a smaller size of the fruits
picked from upper trusses was observed both in our experiment
as well as by Santamaria et al. (2003). These authors also found
that, compared to open-loop drip irrigation, closed-loop
subirrigation reduced significantly total fruit yield, although
the quality of marketable berries was slightly improved.
To conclude, trough bench system proved to be a method to
reduce the water consumption and nutrient runoff of closedloop tomato culture, when saline water is available. Work is in
progress to investigate how subirrigation influences plant
growth and fruit yield in long-cycle tomato culture and,
eventually, to develop measures for limiting crop salinity stress.
Acknowledgement
This work was supported by Italian Ministry of University
and Research (MIUR-PRIN 2003, ‘‘La gestione di sistemi fuori
suolo a ciclo chiuso: adattamento, ottimizzazione e controllo in
ambienti mediterranei su colture ortofloricole’’: paper n8. 5).
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