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Impacts of Organic and Conventional Management on the Nutritional Level of Vegetables

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The nutrient concentration of fruits and vegetables in the U.S.A. has declined in the past 50–70 years. Crop management practices utilizing on-farm inputs are thought to increase crop nutritional quality, but few studies have evaluated this under long-term side-by-side trials. An experiment was conducted from 2004 to 2005 at Rodale Institute’s long-term Farming Systems Trial to investigate the nutritional quality of vegetables under organic manure (MNR) and conventional (CNV) farming systems, with or without arbuscular mycorrhizal fungi (AMF) treatment. AMF reduced the vitamin C content in carrots in both systems in 2004, but the reduction was 87% in CNV and 28% in MNR. AMF also reduced antioxidants in carrots in both CNV and MNR. This trend was likely due to the suppression of native AMF colonization by the non-native AMF inoculum used. Between 2004 and 2005, MNR increased the vitamin C in green peppers by 50% while CNV decreased the vitamin C in red peppers by 48%. Tomatoes under MNR had a 40% greater vitamin C content compared to CNV in 2005. The vegetable yield declined between 2004 and 2005, except for tomato, where the yield increased by 51% and 44% under CNV and MNR, respectively. In general, MNR tended to increase the nutrient concentration of vegetables compared with CNV, while the AMF effects were inconclusive.
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sustainability
Article
Impacts of Organic and Conventional Management
on the Nutritional Level of Vegetables
Atanu Mukherjee 1,2, Emmanuel C. Omondi 1, 3, * , Paul R. Hepperly 1,4, Rita Seidel 1,5
and Wade P. Heller 6
1Rodale Institute, Kutztown, PA 19530, USA; am@miu.edu (A.M.); paul.hepperly@gmail.com (P.R.H.);
Rita.Seidel@berkscd.com (R.S.)
2Sustainable and Regenerative Living Department, Maharishi International University,
Fairfield, IA 52557, USA
3Department of Agricultural and Environmental Science, Tennessee State University,
Nashville, TN 37209, USA
4Hepperly Enterprises, Mayagüez, PR 00682, USA
5Berks County Conservation District, Leesport, PA 19533, USA
6USDA-ARS, NEA, Eastern Regional Research Center, Wyndmoor, PA 19038, USA; wade.heller@usda.gov
*Correspondence: eomondi@tnstate.edu; Tel.: +1-307-703-0167
Received: 21 July 2020; Accepted: 21 October 2020; Published: 28 October 2020


Abstract:
The nutrient concentration of fruits and vegetables in the U.S.A. has declined in the
past 50–70 years. Crop management practices utilizing on-farm inputs are thought to increase
crop nutritional quality, but few studies have evaluated this under long-term side-by-side trials.
An experiment was conducted from 2004 to 2005 at Rodale Institute’s long-term Farming Systems Trial
to investigate the nutritional quality of vegetables under organic manure (MNR) and conventional
(CNV) farming systems, with or without arbuscular mycorrhizal fungi (AMF) treatment. AMF reduced
the vitamin C content in carrots in both systems in 2004, but the reduction was 87% in CNV and 28%
in MNR. AMF also reduced antioxidants in carrots in both CNV and MNR. This trend was likely due
to the suppression of native AMF colonization by the non-native AMF inoculum used. Between 2004
and 2005, MNR increased the vitamin C in green peppers by 50% while CNV decreased the vitamin C
in red peppers by 48%. Tomatoes under MNR had a 40% greater vitamin C content compared to
CNV in 2005. The vegetable yield declined between 2004 and 2005, except for tomato, where the yield
increased by 51% and 44% under CNV and MNR, respectively. In general, MNR tended to increase the
nutrient concentration of vegetables compared with CNV, while the AMF eects were inconclusive.
Keywords:
carrot; green pepper; tomato; nutrition; antioxidant; vitamin C; carotenoids; lycopene;
organic agriculture; conventional agriculture
1. Introduction
Organic farming practices have been shown to have significant impacts on soil quality. Studies have
shown that organically managed soils usually have higher contents of soil organic matter (SOM),
soil organic carbon (SOC), soil organic nitrogen (SON), macro and micro elements, and biological
components and a lower bulk density (BD) compared to conventionally managed soils [
1
,
2
]. A 21-year
study in central Europe found that organic farming not only improved key soil fertility components,
but also reduced the fertilizer, energy, and pesticide input by 34%, 53%, and 97%, respectively,
when compared to conventional farming systems [
3
]. A long-term study of organically and
conventionally managed farming practices in a Nasilt loam soil in Washington indicated that
organically farmed soil had a significantly higher SOM by up to 1%, a higher cation exchange capacity
Sustainability 2020,12, 8965; doi:10.3390/su12218965 www.mdpi.com/journal/sustainability
Sustainability 2020,12, 8965 2 of 25
(CEC) by up to 11%, a higher polysaccharide content by up to 13%, a higher total N by up to 11%,
a higher exchangeable K by up to 71%, as well as a higher water content and aggregate structure
compared to conventionally managed adjacent soil [4].
However, studies have also shown that, in general, the global crop yield from organically
managed farms is 80–81% of the yield from conventionally grown crops, suggesting a 20% yield gap
on average [
5
7
]. Lower organic yields have been attributed to challenges associated with (i) weed
pressure, (ii) nutrient management without synthetic fertilizer input, (iii) systems’ inability to adapt to
the transition [
5
,
8
,
9
], and (iv) climate change [
10
]. However, while the extensive use of agro-chemicals
in conventional farming has increased crop yields and enhanced food security around the globe [
11
],
advances in modern agricultural technology with a sole focus on crop yields has resulted in a
decline, over the past 70 years, in the crop nutrient quality from the baseline values to which food
have traditionally been compared [
12
]. The nutrient decline in crop produce has been attributed to
several factors, such as crop variety, geographical location, ripeness, as well as the degradation of
the soil in which crops are grown [
13
]. For example, the lower mineral nutrient concentrations in
crops were suggested to be related to changes in cultivars selected for higher growth, as dierent
cultivars extract, transport, and synthesize proteins, vitamins, and other nutrients dierently [
14
].
While that study revealed that the lower mineral concentrations in varieties bred for higher yields
with increased carbohydrate were not accompanied by proportional increases in minerals, implying
a “dilution eect” [
14
], a selective dilution eect was also observed, suggesting that not all soil
nutrients can be decreased at the same rate [
15
]. Conventional farming systems are also associated
with declines in soil quality, declines in soil microbial diversity and abundance, decreases in water
infiltration, increases in nitrogen leaching and ground water contamination, and the depletion of soil
nutrients [
16
19
]. These dynamics call for side-by-side field trials to understand the relationships
between soil quality and nutrient density in crop produce.
In addition to significantly improving soil quality, organic farming has also been shown to increase
crop yield under weather-challenged conditions such as droughts when compared to conventional
farming [
20
]. The greater yields in organic farming under drought conditions have been attributed to
improved soil health indicators such as SOM and soil aggregate stability, leading to a greater water
holding capacity [
4
,
21
,
22
]. In a summarized review collected from 88 research studies conducted in
the tropics and sub-tropics, a 26% higher yield under organic compared to conventional management
practices was attributed to soil fertility improvement as well as the better response of organic compared
to conventional systems to input- or resource-poor conditions [
23
]. Additionally, organic farming
improves the environmental impacts of agriculture when compared to traditional conventional
farming [
24
26
]. A recent meta-analysis based on 107 studies and 360 observations published from
1977 to 2012 revealed that significant improvements in energy eciency and reductions in greenhouse
gas (GHG) emissions were associated with organic rather than conventional farming [
26
]. Thus,
while there may be global evidence of crop yield gap in favor of conventional management practices,
there is a strong case to be made for organic farming, as reported in a recent in-depth comparative
system analysis [
27
]. There are also concerted research eorts to close or reduce the yield gap between
the two systems [8,28].
Various studies have reported the impacts of organic farming practices on the nutritional quality
of produce. In one study, organically grown tomatoes (Solanum lycopersicum) were more enriched
with higher human health-promoting nutrients, phytochemical content, and antioxidant activity than
conventionally grown tomatoes [
29
]. Similarly, several studies found that a range of organically
grown produce such as orange (Citrus x sinensis), apple (Malus spp.), potato (Solanum tuberosum),
tomato, and papaya (Carica papaya) had higher levels of vitamin C, phenolic compounds, total sugars,
and flavonoids than those grown conventionally [3033].
Although a number of studies have documented the quantity and quality of nutrients in organic
produce, most of those analyses have been based on crop produce obtained from grocery stores or
from separate organic and conventional farms [
34
,
35
]. A few studies have assessed the nutritional
Sustainability 2020,12, 8965 3 of 25
quality of vegetables and fruits in side by side comparisons of organic and conventional crop
management practices, but the results from these studies have often been contradictory. For example,
organically produced jujube fruit (Ziziphus spp.) had a significantly higher content of pigments,
chlorophyll, carotenoid, sugars, organic acids, and total volatile compounds but a significantly lower
size of fruit and lower protein and flavonoid contents than conventional jujubes in a 2-year study
in Spain [
36
]. In another study, dierent cultivars of organically produced jambu (Acmella oleracea)
fruit had higher contents of total phenolics and carotenoids than conventionally grown fruit [
37
].
However, the vitamin C in the fruit and the total organic N in the leaves and flowers were higher under
the conventional than the organic system. Maggio et al. [
38
] reported that the marketable yields of
cauliflower (Brassica oleracea L. var. botrytis) and zucchini (Cucurbita pepo L.) were significantly higher
under the conventional than the organic system, and although the protein content was not significantly
aected, the K content and hydrophilic antioxidant activities in the zucchini were significantly increased
under the organic compared to the conventional system. A recent comprehensive review suggests that,
due to inconsistencies in the vegetable nutritional quality under organic systems, it is dicult to make
systematic general conclusions on the higher health-promoting value of organic vegetables compared
to conventionally grown produce [39], and hence there is need for more field research on this aspect.
Arbuscular mycorrhizal fungi (AMF) are soilborne fungi that form mutualistic symbiotic
associations with a majority of crop plants and benefit host plants through the enhanced mineral
nutrient uptake of immobile soil nutrients such as P, improved water relations and disease resistance,
as well as improving the soil food web and soil structure by external hyphae [4042]. Several studies
have shown that AMF can improve soil health and crop yield [
43
,
44
]. Agricultural operations can also
aect AMF populations [
45
,
46
]. A recent meta-analysis conducted using 54 field studies found that
low-intensity tillage increased AMF colonization by 30% [
47
]. Farmers can enhance their utilization of
AMF symbiosis through the adoption of farm management practices that enhance the functioning of
the AMF community indigenous to the soil [
48
]—for example, through the use of overwintering cover
crops [
49
,
50
], reduced tillage [
51
], and diverse crop rotations [
52
]. Organic farming practices have been
reported to enhance AMF colonization due to diverse crop rotations, the use of summer and winter
cover crops, enhanced SOM, and the absence of synthetic chemical usage compared to conventionally
managed fields [
53
]. A comprehensive study involving 32 farm fields in Korea revealed that AMF
inoculum significantly improved red peppers (Capsicum annum L.) grown under organic rather than
conventional farming practices, and the AMF abundance and diversity were higher under organic
compared to conventional management practices [
54
]. Although agricultural benefits of AMF have
been widely reported, we are not aware of studies that have evaluated the eects of side-by-side organic
and conventional management practices on the concentration of phytochemicals (such as vitamins,
antioxidants, and plant pigments) in vegetables over two-year period. The objective of this study was
to evaluate the eects of dierent agricultural cropping systems and AMF inoculation on the yield and
nutritional quality of vegetables, measured as vitamins, antioxidants, and other phytochemicals such
as fruit pigmentation under side-by-side organic and conventional management systems over two
successive growing seasons. The parameters evaluated included disease incidence, total antioxidants,
vitamin C, lycopene, alpha and beta carotenoids, mineral composition, vegetable quality assessment,
and yield.
2. Materials and Methods
2.1. Study Site and Weather
Between 2004 and 2005, a two-year experiment was superimposed within the Farming Systems
Trial (FST) at Rodale Institute Experimental Farm, Kutztown, Pennsylvania, to evaluate the nutritional
dierences in select vegetables between the organic and conventional crop management systems.
The goal of the project was to assess the long-term (24 years) organic and conventional management
systems’ eects on the nutrient quality of those vegetables. The FST was established in 1981 at Rodale
Sustainability 2020,12, 8965 4 of 25
Institute in Berks County, south-eastern Pennsylvania (40
37
0
97
00
N and 40
75
0
98
00
W), and is the
longest running side-by-side comparison of organic and conventional grain cropping systems in North
America. Nested within a 135 ha research farm that has been managed organically since 1975, the FST
field occupies an area of 6.1 ha and had moderately well-drained Comly silt loam soil with a neutral
average pH of 6.8. The weather during the experimental period was variable, and the temperature
and precipitation data are presented in Figure 1(monthly summary), and Supplementary Figure S1
(daily data). The rainfall during the growing season of 2004 was 95% higher than in 2005. This was a
100-year high summer rainfall (Figure 1, Supplementary Figure S1).
Sustainability 2020, 12, x FOR PEER REVIEW 4 of 25
soil with a neutral average pH of 6.8. The weather during the experimental period was variable, and
the temperature and precipitation data are presented in Figure 1 (monthly summary), and
Supplementary Figure S1 (daily data). The rainfall during the growing season of 2004 was 95% higher
than in 2005. This was a 100-year high summer rainfall (Figure 1, Supplementary Figure S1).
Weather During Growing Period
Time
Growing Season
April
May
June
July
August
September
October
Rainfall (mm)
0
200
400
600
800
1000
(Temperature (
o
C)
8
10
12
14
16
18
20
22
24
26
Rainfall in 2004 (mm)
Rainfall in 2005 (mm)
Temperature in 2004 (
o
C)
Temperature in 2005 (
o
C)
Start : April 26, 2004)
Apri 5, 2005
Transplant: June 7, 2004
June 9, 2005
Har ves t : Sept ember 20, 2005
Har ves t: October 8, 2004
Figure 1. Total growing season, monthly rainfall, and temperature in 2004 and 2005.
2.2. Experimental Design
The experimental design was a split-plot randomized complete block with eight replications.
The main plots consisted of one conventional (CNV) and one organic (MNR) system. The main plots
measured 18 × 92 m and were separated by 1.5 m grass strips to minimize the transport of soil,
fertilizers, and pesticides among the cropping system plots. Three 6 × 92 m subplot treatments (crop
rotation sequence entry points) were located within each main plot. Entry point subplots ensured
that multiple crops from the rotations were present each year. The management practices conducted
were similar to those described in Ryan et al. [55] and are summarized in Table 1. The CNV system
utilized synthetic fertilizers and herbicides according to the Pennsylvania State University (Penn
State) Cooperative Extensive Service recommendations.
Table 1. Management cropping systems differences between organic manure (MNR) and
conventional (CNV) systems in the Farming Systems Trial.
System Nitrogen Source Cover Crops Herbicides * Primary
Tillage
Secondary
Tillage/Cultivation *
Winter Summer Tine
Rotary
Hoe
Inter-
row
MNR Manure, legume cover
crops, crop rotation
Rye, hairy
vetch Clovers None Moldboard 1–2 1–2 1–2
CNV Mineral fertilizers Rye None 1–2 Chisel None None None
* Number of applications made in single growing season.
The organic manure system (MNR) used composted manure applied at 40 Mg ha1 (wet weight)
for grain corn and 60 Mg ha1 (wet weight) for silage corn. The characteristics of the compost used
are listed in Supplementary Table S1. Cultural and mechanical weed management strategies were
utilized in the MNR system. These included delayed planting, cover crops, and the crop rotation of
summer-grown row crops with winter cover crops. Depending on the weed density and ability to
Figure 1. Total growing season, monthly rainfall, and temperature in 2004 and 2005.
2.2. Experimental Design
The experimental design was a split-plot randomized complete block with eight replications.
The main plots consisted of one conventional (CNV) and one organic (MNR) system. The main
plots measured 18
×
92 m and were separated by 1.5 m grass strips to minimize the transport of
soil, fertilizers, and pesticides among the cropping system plots. Three 6
×
92 m subplot treatments
(crop rotation sequence entry points) were located within each main plot. Entry point subplots ensured
that multiple crops from the rotations were present each year. The management practices conducted
were similar to those described in Ryan et al. [
55
] and are summarized in Table 1. The CNV system
utilized synthetic fertilizers and herbicides according to the Pennsylvania State University (Penn State)
Cooperative Extensive Service recommendations.
Table 1.
Management cropping systems dierences between organic manure (MNR) and conventional
(CNV) systems in the Farming Systems Trial.
System Nitrogen Source Cover Crops Herbicides * Primary Tillage Secondary Tillage/Cultivation *
Winter Summer Tine Rotary Hoe
Inter-row
MNR
Manure, legume
cover crops,
crop rotation
Rye, hairy
vetch Clovers None Moldboard 1–2 1–2 1–2
CNV Mineral fertilizers Rye None 1–2 Chisel None None None
* Number of applications made in single growing season.
Sustainability 2020,12, 8965 5 of 25
The organic manure system (MNR) used composted manure applied at 40 Mg ha
1
(wet weight)
for grain corn and 60 Mg ha
1
(wet weight) for silage corn. The characteristics of the compost used
are listed in Supplementary Table S1. Cultural and mechanical weed management strategies were
utilized in the MNR system. These included delayed planting, cover crops, and the crop rotation of
summer-grown row crops with winter cover crops. Depending on the weed density and ability to
cultivate, as determined by the soil moisture and crop height, mechanical weed management included
one to two passes with a rotary hoe or spring tine cultivator prior to crop emergence, one to two
passes with a rotary hoe or spring tine cultivator after crop emergence, and one to three passes with an
inter-row cultivator. Additional field site and experiment details can be found in Liebhardt et al. [
56
];
Lotter et al. [
57
]; Pimentel, Hepperly, Hanson, Douds, and Seidel [
20
]; and Ryan, Smith, Mortensen,
Teasdale, Curran, and Seidel [55].
2.2.1. Establishment of Vegetables
Vegetable strip plots measuring 6.1
×
6.1 m were established in one of the three entry points
in organic manure (MNR) and CNV main plots that had soybean (Glycine max) in 2004 and 2005.
Tomatoes, peppers (Capsicum annuum “Jalapeño”), and carrots (Daucus carota) were planted in those
strip plots in three out of the eight replications (Rep) (Rep 1, 3, and 4 in 2004; Rep 3, 5, and 8
in 2005). Soybeans were planted with 76.2 cm row spacing using a Monosem precision vacuum
planter (Monosem Inc./North America) in the sub-plot entry points before establishing the strip plots.
Soybeans in the strip plots were then uprooted after germination. One-month-old tomato and pepper
seedling plugs, previously established in the greenhouse, were transplanted into previous soybean
rows at a 76.2 cm row spacing (to facilitate cultivation) and 45.7 cm apart within the row (intra-row
spacing), as recommended by the Campbell Soup Company production practices. Carrots were directly
seeded in the fields. The Campbell Soup Company had previously provided the Rodale Institute with
seeds of the “Malinta” cultivar tomato, “SOC1374” commercial carrot, and “PX109” sweet jalapeno
pepper in 2004, and “CXD253” tomato, “SDC1374” carrot, and “PX109” pepper in 2005. The Malinta
variety of tomato was replaced by CXD253 in 2005 as a disease-resistant variety due to crop failure in
2004. Tomatoes and peppers were started in the greenhouse in the month of April in each year of the
study (on 26 April 2004 and 5 April 2005, Figure 1).
2.2.2. Mycorrhizal Culture and Inoculation
Mycorrhizal inoculum was cultivated on-farm the season before each use, as previously described
(Douds et al. 2010). Briefly, individual AMF species: Glomus mosseae (Nicol. and Gerd.), Gerdemann and
Trappe; Glomus claroideum, Schenck and Smith; Glomus geosporum (Nicol. and Gerd.), Walker;
Glomus etunicatum, Becker and Gerdemann; and Glomus intraradices, Schenck and Smith (DAOM 181602)
were inoculated onto bahiagrass (Paspalum notatum Flugge) seedlings and grown for 3 months in a
greenhouse prior to out planting in 28-liter grow bags filled with a 1:4 mixture of compost:vermiculite.
The bags were watered and weeded as needed to support the plants, then overwintered outdoors to
winterkill the bahiagrass. The media containing AMF spores were then combined and homogenized
prior to use in the seedling germination pots for tomatoes and peppers or applied to the furrow in the
case of directly seeded carrots.
Mycorrhizae inoculum was placed directly with the seeds in half of the pots. In the 20-foot-wide
plot, 16 tomato plants (four rows by four plants) with mycorrhizae and 16 plants without mycorrhizae
were planted in each of the three reps (3
×
32 =96 plants per system). Data were collected from
the four center plants of each section. At least 192 tomato plants (96
×
2 systems) and 192 pepper
plants were initially planned to be planted in the greenhouse. Peppers were set up the same way as
tomatoes. Carrots were directly seeded in 4 rows with mycorrhizae and 4 rows without mycorrhizae.
A total of 216 pots of both tomatoes and peppers (with two seeds per pot) were planted. In each
system, the transplanted strip plots were split into plants that were inoculated with mycorrhizae fungi
(Myc) and plants without mycorrhizae (Non-Myc). Carrots were directly seeded in the month of
Sustainability 2020,12, 8965 6 of 25
June (on 7 June 2004 and 9 June 2005, respectively) and later thinned to 6 plants per 30.5 cm of row,
with 4 rows with mycorrhizae and 4 rows without mycorrhizae (Supplementary Figure S2).
2.2.3. Vegetable Management, Harvesting, and Sample Collection
Plants in the conventional system received mineral fertilizer and herbicide spray regiment based
on the Penn State Extension recommendations. Plants in the organic system received dairy manure-leaf
compost at planting time and several applications of compost tea during plant development as
supplementary fertilizer. Weeds were controlled with black plastic in both the organic and conventional
plots. Any additional weeds were removed by hand hoeing and hand weeding in both the organic and
conventional systems, as there are few selective herbicide options for conventional vegetables and
the preplant and pre-emergent herbicides recommended for vegetables have a short residual activity.
Watering took place as necessary by hand as well.
Sound, undamaged fresh fruit and carrot roots were harvested and shipped fresh to Campbell Soup
Company, R&D, Davis, California. Upon arrival, the samples were prepared for analysis, analyzed,
and the reference samples stored. Tomato fruits were harvested from the center of the plants when 90%
of the fruit was red. Peppers were harvested twice—once “early” when all the fruit was green and a
second time for red-only fruits. Vegetables were harvested by 180 days to maturity either in September
or October of the studied years. Carrots were harvested as late as October. The center two rows of
plots were harvested for yield determination and sampled for quality tests (Supplementary Figure S2).
Note that the tomato yield and, consequently, the nutritional quality were not monitored in the initial
year of 2004 due to crop failure. As protocol, any fruit that was either too small, not firm any more, or
in any other way diseased was rejected. Green pepper rejects were usually too small, red pepper rejects
were too soft or had blossom end rot. Various diseases aecting the studied vegetables in 2004 and 2005
are listed in Supplementary Table S2. Marketable yields were determined by separating the harvested
vegetables based on the visual appearances of the disease-impacted produce along with the size of the
vegetables. The harvested vegetables that were not counted as “marketable” were canker-sore carrots;
virus-aected peppers; and any small or undeveloped, too small, too soft, misshapen, split/scarred,
damaged, diseased, or rotten vegetables.
2.2.4. Determination of Phytochemicals and Vegetable Nutrient Quality
For the vegetable nutritional quality, the vitamin C and total antioxidants were determined for
all vegetables: tomatoes, peppers, and carrots. In addition to these,
α
- and
β
-carotenes were also
determined in carrots, and lycopene determined in tomatoes. Further, peppers were sub-divided
into two groups–green and red for most analyses. For the determination of the ascorbic and total
antioxidant, the Campbell Soup, Food Analytical Laboratory in Camden, New Jersey, was used.
Water-soluble and fat-soluble antioxidants from vegetables were extracted using a method
described by Roberts and Gordon, [
35
]. Specifically, 100–200 g of chopped up vegetables was
homogenized under argon with an industrial blender. A 5% metaphosphoric acid (MPA): methanol
mixture was immediately added to the homogenate in a flask, flushed with argon for 20 s, and sealed.
This was then shaken for ten minutes on a mechanical shaker, after which the extract solution was
filtered under vacuum with a Whatman no. 1 filter paper. The residue was washed with 10 mL of
MPA-methanol mixture, after which an evaporator was used to remove the methanol from the filtrate
in a water bath set at 40
C. Pulp and filter paper from the original extraction were then extracted
using 10 mL of a 50:50 solution of water:methanol. Water-soluble extract was then obtained by mixing
the two aqueous fractions obtained after the evaporation of methanol and made up to 75 mL with
water. To obtain a lipid-soluble extract, the remaining residue and filter paper were mixed with 15 g of
anhydrous sodium sulfate, extracted twice with 50 mL of acetone, and then the acetone extracts were
combined and evaporated to dryness on an evaporator in a water bath at 40
C. Re-dissolving the dry
solid in 75 mL of methanol produced the lipid-soluble extract.
Sustainability 2020,12, 8965 7 of 25
After filtering the water-soluble and lipid-soluble extract through a Whatman 0.1
µ
m polycarbonate
cyclopore membrane, High Performance Liquid Chromatography (HPLC) was used to assess the
antioxidant activity of the extract using the liposome peroxidation assay [35].
The HPLC analysis was also used to determine the ascorbic acid in plant extracts diluted with 1:1
mobile phase (ammonium dihydrogen phosphate buer containing 0.15% (w/v) MPA with detection at
245 nm), and 20
µ
L of the solution injected onto a 5
µ
m Nucleosil (250 mm
×
4.6 mm I.D) C18 analytical
column protected by a C18 guard column (Hichrom, Reading, UK) [35].
Liposomes were prepared by an extrusion method described by Hope et al. (1985) and extracted
using a method described in detail by Roberts and Gordon [35].
The mineral nutrient contents in the dried produce samples were determined by atomic spectral
analysis at Pennsylvania State Agricultural Analytical Services Laboratory using ICP and presented in
Supplementary Table S2.
2.3. Statistical Analysis
All values in the tables or figures are presented as means and standard deviations. A 3-way
analysis of variance (ANOVA) was run to analyze response variables. Three independent
variables, systems (organic manure and conventional), mycorrhizal treatment [AMF (mycorrhizae or
no-mycorrhizae)], time (years), and their interactions were tested. Significant dierences between
the classification variables were analyzed using Tukey’s adjusted multiple comparison procedure
by the Tukey–Kramer grouping in PROC GLIMMIX in SAS version 9.4 [
58
]. Treatment dierences
were considered significant at p<0.05. The figures were plotted using Sigmaplot version 14.0 [
59
].
The systems and AMF are abbreviated in the figures and tables as the following: organic manure
(MNR), conventional (CNV), mycorrhizae (Myc), and without mycorrhizae (Non-Myc).
There is no universal agreement whether the post-hoc mean separation should be reported as valid
in cases where the overall ANOVA was not statistically significant. However, while ANOVA compares
the entire (nested) model, Tukey–Kramer grouping compares individual levels, thereby responding to
two dierent questions. In other words, while ANOVA gives a more general pattern of the overall
data, especially when several levels (three levels in the present study) are present in the model,
Tukey’s multiple comparison test is considered to be much stronger than ANOVA to find dierences in
means between the individual groups.
3. Results
3.1. Crop Diseases
Record-breaking summer rainfall in 2004 (Figure 1, Supplementary Figure S1) resulted in a high
disease incidence observed in all vegetables (Supplementary Table S3). On tomatoes, late blight
(Phytophthora infestans) was particularly damaging, eliminating the marketable yield and antioxidant
analysis, thus rendering tomatoes in 2004 a crop failure. On carrots and peppers, however, a good
dierentiation of antioxidants and vitamins was achieved between treatment combinations, with or
without AMF inoculation in either organically managed or conventionally managed soil. Disease was
also a major factor in carrots, with root canker being a key quality issue.
Other diseases were green pepper virus complex in 2004 and alternaria leaf blight (Alternaria dauci)
of carrot in 2004 and 2005 (Supplementary Table S3). In general, plots under organic management
showed a lower disease incidence and severity than those under conventional management. In 2005,
25% of the carrots in the conventional system were cankered compared to 5% to 7% in organic
plots. In 2004, no virus was observed in green jalapeno peppers grown in the organic system,
while 67% of conventionally grown green peppers had visible symptoms of pepper virus complex
(Supplementary Table S3). Mycorrhizal inoculation had a less observable impact on these diseases,
as no statistically significant dierences were noted between inoculated and non-inoculated plants
Sustainability 2020,12, 8965 8 of 25
within each system (data not shown). There was a tendency for a non-significant increase in diseases
in mycorrhizal-inoculated vegetables in both systems.
3.2. Analysis of Variance
Analysis of variance for this study did not reveal a statistically significant three-way interaction
between year, cropping systems, and AMF for any of the vegetable nutrients (Table 2A–C). There was
also no statistically significant cropping system by AMF interaction for any of the nutrients. However,
year had variously statistically significant two-way interaction eects with cropping systems or
AMF for antioxidants, vitamin C, and lycopene in several of the vegetables. Data were therefore
analyzed separately by year and AMF or year and cropping system where the interaction eects were
statistically significant.
Table 2.
Analyses of variance (ANOVA) to test the eects of management, Arbuscular mycorrhiza
fungal (AMF) treatment, and years on the produce yield (
A
) and vegetable nutrient concentrations
((
B
) and (
C
)); underlined values are statistically significant at the 0.05 level, and italic ones are significant
at the 0.1 level.
(A) Yield Marketable Yield
Carrot Pepper Tomato Carrot Pepper Tomato
year 0.2099 0.7259 0.0085 0.2502
system 0.7624 0.0641 0.8547 0.0414 0.025 0.8548
AMF 0.0942 0.166 0.3878 0.3499 0.1598 0.3877
year x system 0.6236 0.2527 0.4395 0.006
year x AMF 0.2068 0.4756 0.309 0.3818 0.8707
system x AMF 0.0803 0.1243 0.1843 0.3424 0.309
year x system x AMF 0.0441 0.556 <0.0001 0.0101
(B) Antioxidant Vitamin C
Carrot Green
Pepper
Red
Pepper Tomato Carrot Green
Pepper
Red
Pepper Tomato
year <0.0001 <0.0001 0.0908 0.8608 0.0004 0.0506
system 0.7155 0.0703 0.6634 0.1415 0.0788 0.6005 0.7054 0.0102
AMF 0.0144 0.0767 0.464 0.9574 0.0012 0.0005 0.7551 0.6822
year x system 0.0523 0.2674 0.0639 0.0997 0.0044 0.0126
year x AMF 0.6109 0.2953 0.6088 0.1737 0.056 0.0181 0.4373 0.6271
system x AMF 0.8577 0.3544 0.953 0.2373 0.8421 0.7905
year x system x AMF 0.7725 0.1671 0.8626 0.4551 0.1776 0.6762
(C) Carrot Tomato
α-Carotene β-Carotene Lycopene
year 0.1213 0.5063
system 0.7968 0.6544 0.0408
AMF 0.0062 0.0337 0.4683
year x system 0.7968 0.7525
year x AMF 0.6788 0.4172 0.0322
system x AMF 0.2704 0.2396
year x system x AMF 0.5689 0.1865
3.2.1. Mycorrhizal Treatment Eects
1. Vitamin C
Analysis of variance for this study found, respectively, a marginally significant and statistically
significant year by mycorrhizal fungal inoculation interaction for vitamin C in carrots and green
peppers (p=0.0560 and 0.0181, respectively, Table 2); hence, data were presented separately by these
variables (Figures 2and 3). Mycorrhizal treatment significantly reduced the vitamin C content in
carrots grown in both systems in 2004, but the reduction in CNV was 87% compared to 28% in MNR
(Figure 2). There was a similar reduction in 2005, but the change was not statistically significant.
However, there was no statistical dierence in the vitamin C content between the two systems in 2004
Sustainability 2020,12, 8965 9 of 25
and 2005 (Figure 2). Similarly, mycorrhizal treatment reduced the vitamin C content in green peppers
in both systems in each of the two years, but the decline was only statistically significant in the CNV
system in 2005 (Figure 3). Vitamin C was also significantly greater in AMF-treated green peppers
grown in the MNR system in 2005. There was no statistical dierence in the vitamin C content of
treated and non-treated green peppers between CNV and MNR in 2004 or non-treated green peppers
in 2005 (Figure 3).
Sustainability 2020, 12, x FOR PEER REVIEW 9 of 25
Carrot
2004
Myc Non-Myc Myc Non-Myc
Vitamin C (kg ha
-1
)
0
2
4
6
8
CNV
MNR
2005
a
ab
ab
b
ab
ab
bb
Figure 2. Effects of management and AMF on vitamin C in carrot over a two-year period. Means on
a bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Figure 3. Effects of management and AMF on vitamin C in green pepper over a two-year period.
Means on a bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc
(mycorrhizal treatment), MNR (organic), CNV (conventional).
Figure 2.
Eects of management and AMF on vitamin C in carrot over a two-year period. Means on
a bar followed by the same letter are not statistically dierent (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Sustainability 2020, 12, x FOR PEER REVIEW 9 of 25
Carrot
2004
Myc Non-Myc Myc Non-Myc
Vitamin C (kg ha
-1
)
0
2
4
6
8
CNV
MNR
2005
a
ab
ab
b
ab
ab
bb
Figure 2. Effects of management and AMF on vitamin C in carrot over a two-year period. Means on
a bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Figure 3. Effects of management and AMF on vitamin C in green pepper over a two-year period.
Means on a bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc
(mycorrhizal treatment), MNR (organic), CNV (conventional).
Figure 3.
Eects of management and AMF on vitamin C in green pepper over a two-year
period. Means on a bar followed by the same letter are not statistically dierent (alpha 0.05).
Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Sustainability 2020,12, 8965 10 of 25
2. Antioxidants
There was no statistically significant year by mycorrhizal treatment interaction for antioxidants in
all the vegetables. However, the mycorrhizal treatment had a statistically significant eect (p=0.0144)
and marginally significant eect (p=0.0767) on antioxidants in carrots and green peppers, respectively
(Table 2B). Time (years of study) had a highly significant eect (p<0.0001) on both vegetables (Table 2).
Mycorrhizal treatment reduced the antioxidants in carrots in both CNV and MNR in both 2004 and
2005, even though the reduction was not statistically significant, but surprisingly there was a 68%
reduction in the antioxidant concentration in MNR compared to only 26% in CNV in 2004 (Figure 4).
However, both the treated and non-treated carrots significantly increased their antioxidant level from
2004 to 2005, except for the treated carrots in the CNV system (Figure 4).
Sustainability 2020, 12, x FOR PEER REVIEW 10 of 25
2. Antioxidants
There was no statistically significant year by mycorrhizal treatment interaction for antioxidants
in all the vegetables. However, the mycorrhizal treatment had a statistically significant effect (p =
0.0144) and marginally significant effect (p = 0.0767) on antioxidants in carrots and green peppers,
respectively (Table 2B). Time (years of study) had a highly significant effect (p < 0.0001) on both
vegetables (Table 2). Mycorrhizal treatment reduced the antioxidants in carrots in both CNV and
MNR in both 2004 and 2005, even though the reduction was not statistically significant, but
surprisingly there was a 68% reduction in the antioxidant concentration in MNR compared to only
26% in CNV in 2004 (Figure 4). However, both the treated and non-treated carrots significantly
increased their antioxidant level from 2004 to 2005, except for the treated carrots in the CNV system
(Figure 4).
Similar results as above were observed for antioxidants in green peppers. There was no statistical
difference in antioxidant concentration in both the AMF-treated and untreated green peppers
between the CNV and MNR systems within each year (Figure 5). However, there was a statistically
significant increase in the antioxidants in green peppers under both CNV and MNR between 2004
and 2005 (Figure 5).
Figure 4. Effects of management and AMF on the antioxidants in carrot over a two-year period. The
Trolox equivalent antioxidant capacity assay was used to measure the antioxidant capacity in the
vegetable compared to the standard. Means on a bar followed by the same letter are not statistically
different (alpha 0.05). Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Figure 4.
Eects of management and AMF on the antioxidants in carrot over a two-year period.
The Trolox equivalent antioxidant capacity assay was used to measure the antioxidant capacity in the
vegetable compared to the standard. Means on a bar followed by the same letter are not statistically
dierent (alpha 0.05). Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Similar results as above were observed for antioxidants in green peppers. There was no statistical
dierence in antioxidant concentration in both the AMF-treated and untreated green peppers between
the CNV and MNR systems within each year (Figure 5). However, there was a statistically significant
increase in the antioxidants in green peppers under both CNV and MNR between 2004 and 2005
(Figure 5).
3. Pigments
Our results found no statistically significant year by AMF inoculation eects for alpha- and beta
carotenes in carrots (C in Table 2). However, AMF inoculation had a statistically significant eect on
the alpha (p=0.0062) and beta carotenes (p=0.0337) in carrots, but as both year and system had no
statistically significant impacts on the pigments many of the observed trends were non-significant
at
p<0.05
. Mycorrhizal treatment marginally decreased both the alpha- and beta carotenes in carrots
under MNR and CNV systems in 2004, but the decline in beta carotenes was marginally significant
only in CNV-managed carrots in both years (p<0.107 and p<0.1, respectively) (Figures 6and 7).
Sustainability 2020,12, 8965 11 of 25
A pair-wise analysis by year did not reveal any significance between treatments under management
practices over the two-year period.
Sustainability 2020, 12, x FOR PEER REVIEW 11 of 25
Green Pepper
2004
Myc Non- Myc Myc Non- Myc
Antioxidant (kmol TE ha
-1
)
0
10
20
30
40
50 CNV
MNR
2005
b
a
a
b
b
a
b
a
Figure 5. Effects of management and AMF on the antioxidants in green pepper over a two-year
period. Means on a bar followed by the same letter are not statistically different (alpha 0.05). Key:
Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
3. Pigments
Our results found no statistically significant year by AMF inoculation effects for alpha- and beta
carotenes in carrots (C in Table 2). However, AMF inoculation had a statistically significant effect on
the alpha (p = 0.0062) and beta carotenes (p = 0.0337) in carrots, but as both year and system had no
statistically significant impacts on the pigments many of the observed trends were non-significant at
p < 0.05. Mycorrhizal treatment marginally decreased both the alpha- and beta carotenes in carrots
under MNR and CNV systems in 2004, but the decline in beta carotenes was marginally significant
only in CNV-managed carrots in both years (p < 0.107 and p < 0.1, respectively) (Figures 6 and 7). A
pair-wise analysis by year did not reveal any significance between treatments under management
practices over the two-year period.
Cropping systems had no statistically significant effects on lycopene in tomatoes. While there
was a statistically significant (p = 0.0408) year by mycorrhizal treatment interaction for lycopene in
tomatoes, only data for 2005 are reported due to a crop failure of tomatoes in 2004. Mycorrhizal
treatment did not have a statistically significant effect on the lycopene concentration in tomatoes
under both systems (Figure 8). However, treated tomatoes under the MNR system had a significantly
greater lycopene concentration than under the CNV system. Even though our results indicate that
mycorrhizal treatment tended to reduce the lycopene in tomatoes under CNV systems, the effect of
year could not be accounted for due to crop failure in 2004, and hence these results should be
interpreted carefully.
Figure 5.
Eects of management and AMF on the antioxidants in green pepper over a two-year
period. Means on a bar followed by the same letter are not statistically dierent (alpha 0.05).
Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Sustainability 2020, 12, x FOR PEER REVIEW 12 of 25
Figure 6. Effects of management and AMF on the α-carotene in carrot over a two-year period. Means
on a bar followed by the same letter are not statistically different (alpha 0.05). The asterisks define
marginally significant (p = 0.1) of mycorrhizal treatment reduction in beta carotene in CNV managed
carrots compared to MNR. Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Figure 7. Effects of management and AMF on the β-carotene in carrot over a two-year period. Means
on a bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Figure 6.
Eects of management and AMF on the
α
-carotene in carrot over a two-year period. Means
on a bar followed by the same letter are not statistically dierent (alpha 0.05). The asterisks define
marginally significant (p=0.1) of mycorrhizal treatment reduction in beta carotene in CNV managed
carrots compared to MNR. Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Sustainability 2020,12, 8965 12 of 25
Sustainability 2020, 12, x FOR PEER REVIEW 12 of 25
Figure 6. Effects of management and AMF on the α-carotene in carrot over a two-year period. Means
on a bar followed by the same letter are not statistically different (alpha 0.05). The asterisks define
marginally significant (p = 0.1) of mycorrhizal treatment reduction in beta carotene in CNV managed
carrots compared to MNR. Key: Myc (mycorrhizal treatment), MNR (organic), CNV (conventional).
Figure 7. Effects of management and AMF on the β-carotene in carrot over a two-year period. Means
on a bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Figure 7.
Eects of management and AMF on the
β
-carotene in carrot over a two-year period. Means on
a bar followed by the same letter are not statistically dierent (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Cropping systems had no statistically significant eects on lycopene in tomatoes. While there was
a statistically significant (p=0.0408) year by mycorrhizal treatment interaction for lycopene in tomatoes,
only data for 2005 are reported due to a crop failure of tomatoes in 2004. Mycorrhizal treatment
did not have a statistically significant eect on the lycopene concentration in tomatoes under both
systems (Figure 8). However, treated tomatoes under the MNR system had a significantly greater
lycopene concentration than under the CNV system. Even though our results indicate that mycorrhizal
treatment tended to reduce the lycopene in tomatoes under CNV systems, the eect of year could not
be accounted for due to crop failure in 2004, and hence these results should be interpreted carefully.
4. Yields
There was a statistically significant year by cropping systems by AMF treatment eect for the
total yield of carrots (p=0.0441; Table 1A), hence the data were analyzed separately by those three
independent variables. As observed in the nutrients described above, mycorrhizal treatment marginally
reduced the total carrot yields in 2004. Although the yields in both the AMF-treated and non-treated
carrots significantly declined in 2005 compared to 2004, there was no statistical total yield dierence
between the CNV and MNR in both years (Figure 9).
While there was no statistically significant year by cropping systems by AMF treatment interaction
for the total yield in pepper, there was a marginally significant cropping systems eect (p=0.0641)
(Table 2A). However, there was no statistical yield dierence between CNV and MNR in peppers in
both years.
Sustainability 2020,12, 8965 13 of 25
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Tomato
Myc Non-Myc
Lycopene (kg ha
-1
)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
CNV
MNR
2005
a
ab
b
ab
Figure 8. Effects of management and AMF on the lycopene in tomato in 2005. Means on a bar followed
by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal treatment), MNR
(organic), CNV (conventional).
4. Yields
There was a statistically significant year by cropping systems by AMF treatment effect for the
total yield of carrots (p = 0.0441; Table 1A), hence the data were analyzed separately by those three
independent variables. As observed in the nutrients described above, mycorrhizal treatment
marginally reduced the total carrot yields in 2004. Although the yields in both the AMF-treated and
non-treated carrots significantly declined in 2005 compared to 2004, there was no statistical total yield
difference between the CNV and MNR in both years (Figure 9).
While there was no statistically significant year by cropping systems by AMF treatment
interaction for the total yield in pepper, there was a marginally significant cropping systems effect (p
= 0.0641) (Table 2A). However, there was no statistical yield difference between CNV and MNR in
peppers in both years.
There was, however, a highly significant year by cropping systems by AMF treatment
interaction for the marketable yield of pepper (p < 0.0001) and carrot (p = 0.0101) (Table 2A), and thus
data were analyzed separately by those independent variables for carrot and pepper (Figure 10a,b).
Mycorrhizal treatment had no statistically significant effect on the marketable yield of the two
vegetables, but cropping systems had a statistically significant effect on the marketable yield of both
vegetables (p = 0.0414 and 0.0250, respectively, for carrot and pepper), while year had a statistically
significant effect on the marketable yield of carrot (p = 0.0085). While MNR tended to have a higher
marketable yield of carrot than CNV in both years, the difference was not statistically significant
(Figure 10a). However, CNV had a statistically significantly greater marketable yield of pepper than
MNR in 2004 (Figure 10b).
Figure 8.
Eects of management and AMF on the lycopene in tomato in 2005. Means on a bar
followed by the same letter are not statistically dierent (alpha 0.05). Key: Myc (mycorrhizal treatment),
MNR (organic), CNV (conventional).
Sustainability 2020, 12, x FOR PEER REVIEW 14 of 25
Carrot
2004
Myc Non-Myc Myc Non-Myc
Yield (kg ha
-1
)
0
20
40
60
80 CNV
MNR
2005
a
ab
ab
ab
ab
b
ab
b
Figure 9. Effects of management and AMF on the yield in carrot over a two-year period. Means on a
bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
(a)
Figure 9.
Eects of management and AMF on the yield in carrot over a two-year period. Means on
a bar followed by the same letter are not statistically dierent (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
Sustainability 2020,12, 8965 14 of 25
There was, however, a highly significant year by cropping systems by AMF treatment interaction
for the marketable yield of pepper (p<0.0001) and carrot (p=0.0101) (Table 2A), and thus data
were analyzed separately by those independent variables for carrot and pepper (Figure 10a,b).
Mycorrhizal treatment had no statistically significant eect on the marketable yield of the two
vegetables, but cropping systems had a statistically significant eect on the marketable yield of both
vegetables (
p=0.0414
and 0.0250, respectively, for carrot and pepper), while year had a statistically
significant eect on the marketable yield of carrot (p=0.0085). While MNR tended to have a higher
marketable yield of carrot than CNV in both years, the dierence was not statistically significant
(Figure 10a). However, CNV had a statistically significantly greater marketable yield of pepper than
MNR in 2004 (Figure 10b).
Sustainability 2020, 12, x FOR PEER REVIEW 14 of 25
Carrot
2004
Myc Non-Myc Myc Non-Myc
Yield (kg ha
-1
)
0
20
40
60
80 CNV
MNR
2005
a
ab
ab
ab
ab
b
ab
b
Figure 9. Effects of management and AMF on the yield in carrot over a two-year period. Means on a
bar followed by the same letter are not statistically different (alpha 0.05). Key: Myc (mycorrhizal
treatment), MNR (organic), CNV (conventional).
(a)
Sustainability 2020, 12, x FOR PEER REVIEW 15 of 25
(b)
Figure 10. Total and marketable yields of (a) carrot and (b) pepper in 2004 and 2005. Means on a bar
followed by the same upper- or lower-case letter are not statistically different (alpha 0.05). The upper-
case letters compare the means of the total yield while the lower-case letters compare the means of
the marketable yield. Key: MNR (organic), CNV (conventional).
3.2.2. Cropping Systems Effects
1. Vitamin C
The analysis of variance revealed a statistically significant year by cropping systems interaction
effects for vitamin C concentration in green peppers (p = 0.0044) and red peppers (p = 0.0126) and a
marginally significant interaction for carrots (p = 0.0997) (Table 2B), hence the data were analyzed
separately by year and cropping systems. Organic MNR system significantly increased vitamin C
concentration in green peppers in 2005 compared to 2004 (Figure 11), while there was a statistically
significant decline in the vitamin C concentration in red peppers under CNV systems in the same
year period (Figure 10). However, there was no statistical difference in the vitamin C concentration
between the two cropping systems in the two vegetables within each year of the study (Figures 12
and 13). As mentioned earlier, there was a crop failure in tomatoes in 2004, and hence data from that
year were not reported for tomato. However, tomatoes under organic MNR had a significantly
greater (p = 0.0102) vitamin C concentration compared to CNV in 2005 (Table 2B, Figure 13). There
was no statistically significant difference in the vitamin C concentration in carrots between the two
cropping systems in 2004 and 2005 (Figure 14). Changes in the vitamin C concentration in carrots
between 2004 and 2005 were also not statistically significant (data not shown).
Figure 10.
Total and marketable yields of (
a
) carrot and (
b
) pepper in 2004 and 2005. Means on
a bar followed by the same upper- or lower-case letter are not statistically dierent (alpha 0.05).
The upper-case letters compare the means of the total yield while the lower-case letters compare the
means of the marketable yield. Key: MNR (organic), CNV (conventional).
Sustainability 2020,12, 8965 15 of 25
3.2.2. Cropping Systems Eects
1. Vitamin C
The analysis of variance revealed a statistically significant year by cropping systems interaction
eects for vitamin C concentration in green peppers (p=0.0044) and red peppers (p=0.0126) and a
marginally significant interaction for carrots (p=0.0997) (Table 2B), hence the data were analyzed
separately by year and cropping systems. Organic MNR system significantly increased vitamin C
concentration in green peppers in 2005 compared to 2004 (Figure 11), while there was a statistically
significant decline in the vitamin C concentration in red peppers under CNV systems in the same
year period (Figure 10). However, there was no statistical dierence in the vitamin C concentration
between the two cropping systems in the two vegetables within each year of the study (Figures 12
and 13). As mentioned earlier, there was a crop failure in tomatoes in 2004, and hence data from that
year were not reported for tomato. However, tomatoes under organic MNR had a significantly greater
(p=0.0102) vitamin C concentration compared to CNV in 2005 (Table 2B, Figure 13). There was no
statistically significant dierence in the vitamin C concentration in carrots between the two cropping
systems in 2004 and 2005 (Figure 14). Changes in the vitamin C concentration in carrots between 2004
and 2005 were also not statistically significant (data not shown).
Sustainability 2020, 12, x FOR PEER REVIEW 16 of 25
Green Pepper
2004 2005
Vitamin-C (kg ha
-1
)
0
1
2
3
4
5
6
7
CNV
MNR
a
ab
b
ab
Figure 11. Effects of management on the vitamin C in green pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Red Pepper
2004 2005
Vitamin-C (kg ha
-1
)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
CNV
MNR
a
ab
ab
b
Figure 12. Effects of management on the vitamin C in red pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Figure 11.
Eects of management on the vitamin C in green pepper in 2004 and 2005. Means on
a bar followed by the same letter are not statistically dierent (alpha 0.05). Key: MNR (organic),
CNV (conventional).
2. Antioxidants
There was a statistically significant year by cropping systems interaction eects for the antioxidant
concentration in carrots (p=0.0523) and marginally significant interaction for red peppers (p=0.0639)
(Table 2B), hence the data for antioxidant concentration for carrots and red peppers were analyzed
separately by year and cropping systems. There was no statistical dierence in the antioxidant
concentration between the CNV and MNR systems in carrots and red peppers within a single year
(Figures 15 and 16). The antioxidant concentration significantly increased in carrots under both CNV
and MNR in 2005 compared to 2004 (Figure 15). However, the increase was only statistically significant
in MNR in red peppers (Figure 16).
Sustainability 2020,12, 8965 16 of 25
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Green Pepper
2004 2005
Vitamin-C (kg ha
-1
)
0
1
2
3
4
5
6
7
CNV
MNR
a
ab
b
ab
Figure 11. Effects of management on the vitamin C in green pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Red Pepper
2004 2005
Vitamin-C (kg ha
-1
)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
CNV
MNR
a
ab
ab
b
Figure 12. Effects of management on the vitamin C in red pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Figure 12.
Eects of management on the vitamin C in red pepper in 2004 and 2005. Means on
a bar followed by the same letter are not statistically dierent (alpha 0.05). Key: MNR (organic),
CNV (conventional).
Sustainability 2020, 12, x FOR PEER REVIEW 17 of 25
Tomato
2005
Vitamin-C (kg ha
-1
)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
CNV
MNR
a
b
Figure 13. Effects of management on the vitamin C in red pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Carrot
2004 2005
Vitamin-C (kg ha
-1
)
0
2
4
6
8
10
CNV
MNR
a
a
a
a
.
Figure 14. Effects of management on the vitamin C in carrot in 2004 and 2005. Means on a bar followed
by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV (conventional).
2. Antioxidants
There was a statistically significant year by cropping systems interaction effects for the
antioxidant concentration in carrots (p = 0.0523) and marginally significant interaction for red peppers
(p = 0.0639) (Table 2B), hence the data for antioxidant concentration for carrots and red peppers were
Figure 13.
Eects of management on the vitamin C in tomato in 2004 and 2005. Means on a bar followed
by the same letter are not statistically dierent (alpha 0.05). Key: MNR (organic), CNV (conventional).
Sustainability 2020,12, 8965 17 of 25
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Tomato
2005
Vitamin-C (kg ha
-1
)
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
CNV
MNR
a
b
Figure 13. Effects of management on the vitamin C in red pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Carrot
2004 2005
Vitamin-C (kg ha
-1
)
0
2
4
6
8
10
CNV
MNR
a
a
a
a
.
Figure 14. Effects of management on the vitamin C in carrot in 2004 and 2005. Means on a bar followed
by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV (conventional).
2. Antioxidants
There was a statistically significant year by cropping systems interaction effects for the
antioxidant concentration in carrots (p = 0.0523) and marginally significant interaction for red peppers
(p = 0.0639) (Table 2B), hence the data for antioxidant concentration for carrots and red peppers were
Figure 14.
Eects of management on the vitamin C in carrot in 2004 and 2005. Means on a bar followed
by the same letter are not statistically dierent (alpha 0.05). Key: MNR (organic), CNV (conventional).
Sustainability 2020, 12, x FOR PEER REVIEW 18 of 25
analyzed separately by year and cropping systems. There was no statistical difference in the
antioxidant concentration between the CNV and MNR systems in carrots and red peppers within a
single year (Figures 15 and 16). The antioxidant concentration significantly increased in carrots under
both CNV and MNR in 2005 compared to 2004 (Figure 15). However, the increase was only
statistically significant in MNR in red peppers (Figure 16).
Carrot
2004 2005
Antioxidant (kmol TE ha
-1
)
0
5
10
15
20
25
30
a
a
b
b
Figure 15. Effects of management on the antioxidants in carrot in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Red Pepper
2004 2005
Antioxidant (kmol TE ha
-1
)
0
2
4
6
8
10
12
a
ab
ab
b
Figure 16. Effects of management on the antioxidants in red pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Figure 15.
Eects of management on the antioxidants in carrot in 2004 and 2005. Means on a bar followed
by the same letter are not statistically dierent (alpha 0.05). Key: MNR (organic), CNV (conventional).
Sustainability 2020,12, 8965 18 of 25
Sustainability 2020, 12, x FOR PEER REVIEW 18 of 25
analyzed separately by year and cropping systems. There was no statistical difference in the
antioxidant concentration between the CNV and MNR systems in carrots and red peppers within a
single year (Figures 15 and 16). The antioxidant concentration significantly increased in carrots under
both CNV and MNR in 2005 compared to 2004 (Figure 15). However, the increase was only
statistically significant in MNR in red peppers (Figure 16).
Carrot
2004 2005
Antioxidant (kmol TE ha
-1
)
0
5
10
15
20
25
30
a
a
b
b
Figure 15. Effects of management on the antioxidants in carrot in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Red Pepper
2004 2005
Antioxidant (kmol TE ha
-1
)
0
2
4
6
8
10
12
a
ab
ab
b
Figure 16. Effects of management on the antioxidants in red pepper in 2004 and 2005. Means on a bar
followed by the same letter are not statistically different (alpha 0.05). Key: MNR (organic), CNV
(conventional).
Figure 16.
Eects of management on the antioxidants in red pepper in 2004 and 2005. Means on
a bar followed by the same letter are not statistically dierent (alpha 0.05). Key: MNR (organic),
CNV (conventional).
3. Mineral nutrients
Like organic nutrients, all the mineral nutrients from vegetative tissue analyses were not aected
by treatments across the systems and year regime (ANOVA not shown). Thus, all the mineral nutrients
data were presented by management practices over a two-year period (Supplementary Table S2).
Although various macro- and micro-nutrients were either significantly increased or decreased from
2004 to 2005 in 15 cases, only seven cases were significantly impacted by management practices,
with five of those in 2005 (Supplementary Table S2). The organic MNR system significantly increased
the Na (in carrot and pepper), Fe, Mg, and S (in pepper) and decreased the Zn in tomato compared to
the CNV system. However, except in one case (S in pepper), all the statistically significant changes
were observed only in the first year (2004) (Supplementary Table S2).
4. Discussion
Diseases as a consequence of weather: A plant physiological stress mechanism for antioxidant
production explains the observed results from this study. Extreme weather conditions and changes,
from a historically wet 2004 to a relatively dry 2005 (Figure 1, Supplementary Figure S1), may have
caused statistically significant stress to the vegetables in this project. In 2005, an early and periodic
drought stress dierentiated the growing season conclusively from the wet 2004. The interpretation of
our results is based on the hypothesis that significant drought stress conditions induce plant antioxidants
as plant-defensive reactions [
60
,
61
]. Water stress was the bigger problem in 2005, while excessive
water challenges were prevalent in 2004; both extremes resulting in marked dierences in the order
of antioxidant production, which explains the statistically significant treatment by year interaction
for antioxidant production. In general, the highest levels of ascorbic acid (vitamin C) and lycopene
were found in the mycorrhizal treated vegetables in the organic system and the lowest levels in the
conventional mycorrhizal treatment. A range from about 35% to 60% more antioxidant vitamins were
found under the organic system with mycorrhizal inoculation. However, the major influencing factor
appears to be the system rather than mycorrhizal inoculation. Our results suggest that improved
soil (under long-term organically managed plots) and mycorrhizal inoculation may work together
Sustainability 2020,12, 8965 19 of 25
to mitigate stress under dry (2005) but generally favorable agronomic environments. Prior studies
indicate that both organic soil improvement and mycorrhizae expand the ability of plants to absorb
water from the soil [
40
42
], supporting this hypothesis. Our results suggest that the antioxidant
response was more flexible under improved organically managed soil than under conventional soils.
The higher antioxidant production in 2005 compared to 2004 in carrots and peppers suggest that
those vegetables responded to water stress by increasing antioxidant production (drought tolerance)
(Figures 4and 5). Since vegetables were grown under plastic, excessive rains in 2004 did not cause
flooding, hence the substantially lower physiological drought stress and lower antioxidant production
in 2004. Disease tolerance was also consistently improved under organic management compared
to conventional management. On the other hand, the total crop yields were generally not dierent
between the organic and conventional soils. However, through the improved plant stress reaction,
the quality and marketable yield were favored in the organic system under stress environments
(Table 2A, Figure 10). We propose that the biggest advantages for organic production in this study
were tolerance to water and disease stress. At low stress levels, improved organic soil conditions
avoided the stress reaction and thereby caused a lower antioxidant production. At a higher water
stress level, however, as observed in 2005, it activated a higher defense reaction measured in a specific
antioxidant reaction, including vitamin C and lycopene production. These observations suggest
that organic systems with improved soil are more flexible in their plant stress reaction compared to
conventional systems.
This study did not find statistically significant total yield dierences for the organic, conventional,
mycorrhizal, and non-mycorrhizal treatment combinations. However, while the conventional system
had a greater marketable yield of pepper in the wetter, non-water stressed 2004, the organic system
tended to yield a greater, but non-significant marketable carrot yield in the dryer 2005 (Figure 10).
These results are in conformity with multiple studies that have shown that conventional systems tend
to yields that are about 20% higher than organic yields under non-water stress conditions [
5
7
],
while organic systems generally produce greater crop yields than conventional systems under
water-stressed conditions [
4
,
20
22
]. These results coupled with the lower disease incidence observed
in all vegetables under the organic system in both years compared to the conventional system
(Supplementary Table S3) suggest that organic management has the potential to stabilize yields and
better manage crop diseases. However, there is a need to carry out similar studies over a much longer
period than two years to ascertain this potential.
Eects of cropping systems: Our results show that, in general, organic systems performed better
than conventional systems; for example, vitamin C significantly increased in green peppers under
MNR (Figure 11) and the same nutrient significantly decreased in red peppers under CNV in 2005
(Figure 12). While the dierences were not statistically significant (except in tomatoes under MNR,
which had significantly greater vitamin C than CNV in 2005 (Figure 13)), conventional systems
tended to perform better in 2004 but the reverse was the case in 2005 (Figures 11,12 and 1416).
The better performance of the CNV in 2004, which was a wet year compared to 2005, may partly be
attributed to more options for providing synthetic mineral nutrients to vegetables, including foliar
application under soil water saturation conditions, as well as pesticide control of diseases that were
more prevalent in 2004. The better performance of the organic system in 2005 may be attributed to
an improvement in our crop management practices with time, increased colonization and mycelial
network of functional mycorrhizal fungi under drier conditions, and enhancement of soil biology
in organic systems. A number of recent studies found that vitamin C and the antioxidant levels of
fruits, vegetables, and crops grown under organic farming system were significantly enhanced when
compared to the same under conventional farming practices [
62
]. For example, various studies found
significantly higher vitamin C under organically grown (i) tomato [
29
,
63
], (ii) dierent fruits [
31
,
64
,
65
],
and (iii) spinach [
66
] compared to conventional farming. Similarly, higher antioxidant activities were
found in tomatoes and tomato-juice under organic than conventional management practices [
63
,
67
,
68
].
A meta-analysis indicated that organically produced fruits significantly increased the overall carotenoid
Sustainability 2020,12, 8965 20 of 25
content by 25% compared to a decrease of 38% in the same under conventionally grown fruits [
62
].
However, further and longer-term studies are required to measure the eect of management practices;
microbial community structure; mechanisms for nutrient synthesis and/or uptake; and changes in soil
physical, chemical, and biological properties with time on influencing the nutrient concentration in
vegetables. Environmental factors such as excessive precipitation or droughts, the availability of N,
or disease intensity might also be responsible for the changes in vitamin C and antioxidant levels in
vegetables. The availability of N has been attributed to synthesis of high antioxidant and vitamin C
in crop produce [
69
,
70
]. However, specific eects of N content, disease severity, and abiotic stresses
on vegetable nutrients were not statistically quantified in the current study and are researchable
priorities. Our results also indicate that the organic system increased most of the minerals that had
significantly greater concentration in two of the three studied vegetables, including sodium in carrot
and pepper and iron, magnesium, and sulfur in pepper. However, given that the majority of the mineral
results were inconsistent and/or insignificant, there is need for further studies over a longer period
of time that will focus on mineral nutrient dynamics in vegetable production under the long-term
side by side comparison of organic and conventional management systems. Such a study will also
examine the potential interactions between minerals that might influence their availability, deficiency,
or plant uptake.
While cropping systems did not have a statistically significant eect on the total pepper yields
(Figure 10b), CNV tended to have greater yields than MNR in the wetter 2004. As already mentioned,
this is in conformity with multiple studies that have revealed that yields of organically managed crops
tend to be lower than those of conventionally managed crops under stress-free conditions [
5
,
8
,
9
,
71
].
Te Pas [
23
] reported a 26% higher yield under organic than conventional farming in a summarized
review collected from 88 research studies conducted in the tropics and sub-tropics; the higher organic
yields were attributed to soil fertility improvement as well as the better response of organic than
conventional systems to inputs under resource-poor conditions. The benefits of organic management
practices often require a “whole systems approach” that includes long and diverse crop rotations,
the use of cover crops between cash crops, the tactical use of inputs such as composted and green
manures, and substantial time [
72
,
73
]. While our study was superimposed upon a long-term FST study,
the inclusion of mycorrhizal treatment and the fact that the FST is a grain-based study (with dierent
management needs, rotations, and input systems than vegetables) may have required more time than
two years to realize more consistent yield eects. However, the fact that, even within a short amount
of time spanning just two years, organic systems generally performed better than conventional system
with regard to vitamin C, antioxidants, and other phytonutrients, and produced vegetable yields
that were generally not significantly dierent from the conventional yields, but of better marketable
quality than the conventional produce, suggests that organic systems can play a more prominent role
in facilitating food security, both quantitatively and qualitatively. Ongoing concerted eorts to close or
reduce the yield gap between organic and conventional systems [8,28] are encouraging.
5. Conclusions
The data from this study reveal how the concentration of organic nutrients in carrot, pepper,
and tomato can be impacted not only by dierent farming systems and AMF inoculation, but also by
extremes of weather. Our research suggests that antioxidants are turned on and oby environmental
stress cues. The flexibility of this response appears enhanced under organic legacy with improved
soil. This implies that stress management will be an eective strategy for increasing antioxidants,
vitamins, and other phytonutrients. While water stress is erratic under sub-humid rainfall, it is
much more manageable under semi-arid and arid conditions, whereby the programmed and precise
management of water applications can be used to apply and withdraw stress to crop plants. Studies such
as the current research can provide additional tools needed to generate defined stress levels than
can enhance the antioxidant quality of vegetables and fruits. Given that limited soil moisture
was identified as a key factor for antioxidant production, the major findings of this study, thus,
Sustainability 2020,12, 8965 21 of 25
were that (1) antioxidant responses were more flexible under organically improved soil, given the lower
concentration of antioxidants produced in organically grown produce under no-stress environments
and the higher concentrations under drought conditions compared to conventionally grown produce;
(2) disease tolerance was consistently improved under organic management compared to conventional
management; and (3) the total crop yields were not dierent between the organic and conventional
soils. However, through improved plant stress reaction, the quality and marketable yield was favored
in the organic system under a drought stress environment. We can thus surmise that the biggest
advantages for organic production were identified as tolerance to water and disease stress.
Contrary to expectations, AMF inoculation reduced the vitamin C, antioxidants, and phytonutrients
in vegetables during the first year of the study, which was partly attributed to the wet conditions in 2004.
Because of potential antagonistic and synergistic interactions between native and introduced fungal
species, a longer-term study with more vegetable species is required to establish these relationships
and eects over time. Management systems eects on pests and diseases and the secondary eect
of those on nutrients were not quantified by this research. Future research should combine disease
identification with quantifying key soil nutrients (N, P, K) in a long-term study to further investigate if
these trends persist.
Our research gives scientific support to contention held by organic agriculture pioneersthat organic
soil management has a significant general beneficial eect on lowering disease damage compared to
conventional management. This is related to the better stress tolerance in organically managed soils.
Sustainable and conventional farmers can utilize this soil buering capacity by concentrating more
eort on soil improvement rather than employing strategies that require heavy fertilization.
Supplementary Materials:
The following are available online at http://www.mdpi.com/2071-1050/12/21/8965/s1:
Figure S1: Daily rainfall, and temperature during the growing seasons in 2004, and 2005; Figure S2: Map,
and plot layout for both years; Table S1: Characteristics of compost (dairy manure and leaf) used (date sampled:
13 April 2016); units are given in parenthesis; Table S2: Impacts of management practices of dierent vegetative
mineral (macro- and micro-) nutrients over two years period; Nutrients concentrations are expressed in ppm.
Means within a row within a nutrient followed by the same letter are not statistically dierent (alpha 0.05).
Key: MNR (organic); CNV (conventional); Table S3: Disease epidemic, and environmental factors during 2004,
and 2005.
Author Contributions:
The followings are the specific contributions from the authors of this manuscript:
Conceptualization, P.R.H.; methodology, P.R.H., R.S.; software, A.M. and E.C.O.; validation, A.M., E.C.O., R.S.,
P.R.H. and W.P.H.; formal analysis, A.M. and E.C.O.; investigation, P.R.H., R.S., A.M., E.C.O. and W.P.H.; resources,
P.R.H., A.M. and E.C.O.; data curation, A.M. and E.C.O.; writing—original draft preparation, A.M., P.H. and E.C.O.;
writing—review and editing, A.M., E.C.O., P.R.H., R.S. and W.P.H.; visualization, A.M., E.C.O.; supervision, E.C.O.;
project administration, P.R.H.; funding acquisition, P.R.H. All authors have read and agreed to the published
version of the manuscript.
Funding: This research was funded by Campbell Soup Company, R&D, Davis, California.
Acknowledgments:
We want to extend gratitude to the Campbell Soup Company for providing material (such as
seed) and funding support towards this project. We also want to thank David Douds, formerly of USDA, ARS NEA,
Eastern Regional Research Center, Pennsylvania, for culturing and providing the arbuscular mycorrhizal inoculum
used for this study as well as the detailed consultancy on the AMF component of this research.
Conflicts of Interest:
The funders of this study provided additional support in analyzing vegetables for the
phytonutrients in their well-equipped laboratory. As is the common practice, sample identities were not required
or provided to the laboratory for these analyses. The authors declare no other conflict of interest.
References
1.
Carr, P.M.; Delate, K.; Zhao, X.; Cambardella, C.A.; Carr, P.L.; Heckman, J.R. Impacts on Soil, Food, and Human
Health. In Soils and Human Health; CRC Press: Boca Raton, FL, USA, 2012; Volume 241.
2.
Reeve, J.; Hoagland, L.; Villalba, J.; Carr, P.; Atucha, A.; Cambardella, C.; Davis, D.; Delate, K. Organic farming,
soil health, and food quality: Considering possible links. In Advances in Agronomy; Elsevier: Amsterdam,
The Netherlands, 2016; Volume 137, pp. 319–367.
3.
Maeder, P.; Fliessbach, A.; Dubois, D.; Gunst, L.; Fried, P.; Niggli, U. Soil Fertility and Biodiversity in Organic
Farming. Science 2002,296, 1694. [CrossRef] [PubMed]
Sustainability 2020,12, 8965 22 of 25
4.
Reganold, J.P. Comparison of soil properties as influenced by organic and conventional farming systems.
Am. J. Altern. Agric. 2009,3, 144–155. [CrossRef]
5.
de Ponti, T.; Rijk, B.; van Ittersum, M.K. The crop yield gap between organic and conventional agriculture.
Agric. Syst. 2012,108, 1–9. [CrossRef]
6.
Ponisio, L.C.; Ehrlich, P.R. Diversification, Yield and a New Agricultural Revolution: Problems and Prospects.
Sustainability 2016,8, 1118. [CrossRef]
7.
Seufert, V.; Ramankutty, N. Many shades of gray—The context-dependent performance of organic agriculture.
Sci. Adv. 2017,3, e1602638. [CrossRef]
8.
Roos, E.; Mie, A.; Wivstad, M.; Salomon, E.; Johansson, B.; Gunnarsson, S.; Wallenbeck, A.; Homann, R.;
Nilsson, U.; Sundberg, C.; et al. Risks and opportunities of increasing yields in organic farming. A review.
Agron. Sustain. Dev. 2018,38, 21. [CrossRef]
9.
Weyers, S.L.; Archer, D.W.; Forcella, F.; Gesch, R.; Johnson, J.M.F. Strip-tillage reduces productivity in
organically managed grain and forage cropping systems in the Upper Midwest, USA. Renew. Agric. Food Syst.
2018,33, 309–321. [CrossRef]
10.
Smith, M.R.; Myers, S.S. Impact of anthropogenic CO
2
emissions on global human nutrition. Nat. Clim. Chang.
2018,8, 834–839. [CrossRef]
11.
Pang, X.P.; Letey, J. Organic farming: Challenge of timing nitrogen availability to crop nitrogen requirements.
Soil Sci. Soc. Am. J. 2000,64, 863–885. [CrossRef]
12.
World watch. Crop Yields Expand, but Nutrition Is Left Behind. In Vision for a Sustainable World; World watch:
Washington, DC, USA, 2016; Volume 2016.
13.
Marles, R.J. Mineral nutrient composition of vegetables, fruits and grains: The context of reports of apparent
historical declines. J. Food Compos. Anal. 2017,56, 93–103. [CrossRef]
14.
Davis, D.R.; Epp, M.D.; Riordan, H.D. Changes in USDA food composition data for 43 garden crops, 1950 to
1999. J. Am. Coll. Nutr. 2004,23, 669–682. [CrossRef] [PubMed]
15.
Ficco, D.; Riefolo, C.; Nicastro, G.; De Simone, V.; Di Gesu, A.; Beleggia, R.; Platani, C.; Cattivelli, L.; De Vita, P.
Phytate and mineral elements concentration in a collection of Italian durum wheat cultivars. Field Crop. Res.
2009,111, 235–242. [CrossRef]
16.
Ikemura, Y.; Shukla, M.K. Soil quality in organic and conventional farms of New Mexico, USA. J. Org. Syst.
2009,4, 34–47.
17.
McGarry, D.; Bridge, B.J.; Radford, B.J. Contrasting soil physical properties after zero and traditional tillage
of an alluvial soil in the semi-arid subtropics. Soil Tillage Res. 2000,53, 105–115. [CrossRef]
18.
Ara
ú
jo, A.S.; Leite, L.F.; Santos, V.B.; Carneiro, R.F. Soil microbial activity in conventional and organic
agricultural systems. Sustainability 2009,1, 268–276. [CrossRef]
19.
Lori, M.; Symnaczik, S.; Mäder, P.; De Deyn, G.; Gattinger, A. Organic farming enhances soil microbial
abundance and activity—A meta-analysis and meta-regression. PLoS ONE
2017
,12, e0180442. [CrossRef]
[PubMed]
20.
Pimentel, D.; Hepperly, P.; Hanson, J.; Douds, D.; Seidel, R. Environmental, energetic, and economic
comparisons of organic and conventional farming systems. BioScience 2005,55, 573–582. [CrossRef]
21.
Johnson, J.M.-F.; Reicosky, D.C.; Allmaras, R.R.; Sauer, T.J.; Venterea, R.T.; Dell, C.J. Greenhouse gas
contributions and mitigation potential of agriculture in the central USA. Soil Tillage Res.
2005
,83, 73–94.
[CrossRef]
22. Hudson, B.D. Soil organic matter and available water capacity. J. Soil Water Conserv. 1994,49, 189–194.
23.
Te Pas, C.M.; Rees, R.M. Analysis of Dierences in Productivity, Profitability and Soil Fertility between Organic
and Conventional Cropping Systems in the Tropics and Sub-tropics. J. Integr. Agric.
2014
,13, 2299–2310.
[CrossRef]
24.
Tuomisto, H.L.; Hodge, I.D.; Riordan, P.; Macdonald, D.W. Does organic farming reduce environmental
impacts?—A meta-analysis of European research. J. Environ. Manag. 2012,112, 309–320. [CrossRef]
25.
Puech, C.; Baudry, J.; Joannon, A.; Poggi, S.; Aviron, S. Organic vs. conventional farming dichotomy: Does it
make sense for natural enemies? Agric. Ecosyst. Environ. 2014,194, 48–57. [CrossRef]
26.
Lee, K.S.; Choe, Y.C.; Park, S.H. Measuring the environmental eects of organic farming: A meta-analysis of
structural variables in empirical research. J. Environ. Manag. 2015,162, 263–274. [CrossRef] [PubMed]
27.
Fess, T.; Benedito, V. Organic versus Conventional Cropping Sustainability: A Comparative System Analysis.
Sustainability 2018,10, 272. [CrossRef]
Sustainability 2020,12, 8965 23 of 25
28.
Cordoa, E.M.; Chirinda, N.; Li, F.; Olesen, J.E. Contributions from carbon and nitrogen in roots to closing the
yield gap between conventional and organic cropping systems. Soil Use Manag.
2018
,34, 335–342. [CrossRef]
29.
Vinha, A.F.; Barreira, S.V.; Costa, A.S.; Alves, R.C.; Oliveira, M.B. Organic versus conventional tomatoes:
Influence on physicochemical parameters, bioactive compounds and sensorial attributes. Food Chem. Toxicol.
Int. J. Publ. Br. Ind. Biol. Res. Assoc. 2014,67, 139–144. [CrossRef]
30.
Magkos, F.; Arvaniti, F.; Zampelas, A. Organic food: Nutritious food or food for thought? A review of the
evidence. Int. J. Food Sci. Nutr. 2003,54, 357–371. [CrossRef]
31.
Tarozzi, A.; Hrelia, S.; Angeloni, C.; Morroni, F.; Biagi, P.; Guardigli, M.; Cantelli-Forti, G.; Hrelia, P.
Antioxidant eectiveness of organically and non-organically grown red oranges in cell culture systems.
Eur. J. Nutr. 2006,45, 152–158. [CrossRef] [PubMed]
32.
Petkovsek, M.M.; Slatnar, A.; Stampar, F.; Veberic, R. The influence of organic/integrated production on the
content of phenolic compounds in apple leaves and fruits in four dierent varieties over a 2-year period.
J. Sci. Food Agric. 2010,90, 2366–2378. [CrossRef]
33.
Hallmann, E. The influence of organic and conventional cultivation systems on the nutritional value and
content of bioactive compounds in selected tomato types. J. Sci. Food Agric.
2012
,92, 2840–2848. [CrossRef]
[PubMed]
34.
Al-Sayyed, H.; Refa’t Al-Kurd, M.M.; Qader, S.A. Determination of Antioxidant Content and Activity in
Eight Jordanian Fresh Green Leafy Vegetables. Agric. Res. Technol. Open Access J.
2019
,19, 556102. [CrossRef]
35.
Roberts, W.G.; Gordon, M.H. Determination of the total antioxidant activity of fruits and vegetables by a
liposome assay. J. Agric. Food Chem. 2003,51, 1486–1493. [CrossRef]
36.
Reche, J.; Hern
á
ndez, F.; Almansa, M.; Carbonell-Barrachina,
Á
.; Legua, P.; Amor
ó
s, A. Eects of organic
and conventional farming on the physicochemical and functional properties of jujube fruit. LWT
2019
,
99, 438–444. [CrossRef]
37.
da Silva Borges, L.; de Souza Vieira, M.C.; Vianello, F.; Goto, R.; Lima, G.P.P. Antioxidant compounds of
organically and conventionally fertilized jambu (Acmella oleracea). Biol. Agric. Hortic.
2016
,32, 149–158.
[CrossRef]
38.
Maggio, A.; De Pascale, S.; Paradiso, R.; Barbieri, G. Quality and nutritional value of vegetables from organic
and conventional farming. Sci. Hortic. 2013,164, 532–539. [CrossRef]
39.
Sobieralski, K.; Siwulski, M.; Sas-Golak, I. Nutritive and health-promoting value of organic vegetables.
Acta Sci. Pol. Technol. Aliment. 2013,12, 113–123.
40.
Chen, M.; Arato, M.; Borghi, L.; Nouri, E.; Reinhardt, D. Beneficial Services of Arbuscular Mycorrhizal
Fungi—From Ecology to Application. Front. Plant Sci. 2018,9, 14. [CrossRef]
41.
Douds, D.; Nagahashi, G.; Hepperly, P. Production of inoculum of indigenous AM fungi and options for
diluents of compost for on-farm production of AM fungi. Bioresour. Technol.
2010
,101, 2326–2330. [CrossRef]
42. Smith, S.E.; Read, D.J. Mycorrhizal Symbiosis; Academic Press: Cambridge, MA, USA, 2010.
43.
Pellegrino, E.; Öpik, M.; Bonari, E.; Ercoli, L. Responses of wheat to arbuscular mycorrhizal fungi:
A meta-analysis of field studies from 1975 to 2013. Soil Biol. Biochem. 2015,84, 210–217. [CrossRef]
44.
Lekberg, Y.; Koide, R.T. Is plant performance limited by abundance of arbuscular mycorrhizal fungi?
A meta-analysis of studies published between 1988 and 2003. New Phytol. 2005,168, 189–204. [CrossRef]
45. Kabir, Z. Tillage or no-tillage: Impact on mycorrhizae. Can. J. Plant Sci. 2005,85, 23–29. [CrossRef]
46.
Ryan, M.H.; Graham, J.H. Is there a role for arbuscular mycorrhizal fungi in production agriculture? Plant Soil
2002,244, 263–271. [CrossRef]
47.
Bowles, T.M.; Jackson, L.E.; Loeher, M.; Cavagnaro, T.R. Data from: Ecological intensification and arbuscular
mycorrhizas: A meta-analysis of tillage and cover crop eects. J. Appl. Ecol.
2017
,54, 1785–1793. [CrossRef]
48.
Douds, D.; Seidel, R. The contribution of arbusclar mycorrhizal fungi to the success or failure of agricultural
practices. In Microbial Ecology; Taylor Francis Group: Boca Raton, FL, USA, 2012; pp. 133–152.
49.
Boswell, E.; Koide, R.; Shumway, D.; Addy, H. Winter wheat cover cropping, VA mycorrhizal fungi and
maize growth and yield. Agric. Ecosyst. Environ. 1998,67, 55–65. [CrossRef]
50.
Galvez, L.; Douds, D.; Wagoner, P.; Longnecker, L.; Drinkwater, L.; Janke, R. An overwintering cover crop
increases inoculum of VAM fungi in agricultural soil. Am. J. Altern. Agric. 1995,10, 152–156. [CrossRef]
Sustainability 2020,12, 8965 24 of 25
51.
Castillo, C.G.; Rubio, R.; Rouanet, J.L.; Borie, F. Early eects of tillage and crop rotation on arbuscular
mycorrhizal fungal propagules in an Ultisol. Biol. Fertil. Soils 2006,43, 83–92. [CrossRef]
52.
Johnson, N.C.; Copeland, P.J.; Crookston, R.K.; Pfleger, F. Mycorrhizae: Possible explanation for yield decline
with continuous corn and soybean. Agron. J. 1992,84, 387–390. [CrossRef]
53.
Gosling, P.; Hodge, A.; Goodlass, G.; Bending, G.D. Arbuscular mycorrhizal fungi and organic farming.
Agric. Ecosyst. Environ. 2006,113, 17–35. [CrossRef]
54.
Lee, S.W.; Lee, E.H.; Eom, A.H. Eects of organic farming on communities of arbuscular mycorrhizal fungi.
Mycobiology 2008,36, 19–23. [CrossRef]
55.
Ryan, M.R.; Smith, R.G.; Mortensen, D.A.; Teasdale, J.R.; Curran, W.S.; Seidel, R. Weed–crop competition
relationships dier between organic and conventional cropping systems. Weed Res.
2009
,49, 572–580.
[CrossRef]
56.
Liebhardt, W.; Andrews, R.; Culik, M.; Harwood,R.; Janke, R.; Radke, J.; Reiger-Schwartz, S. Crop production
during conversion from conventional to low-input methods. Agron. J. 1989,81, 150–159. [CrossRef]
57.
Lotter, D.W.; Seidel, R.; Liebhardt, W. The performance of organic and conventional cropping systems in an
extreme climate year. Am. J. Altern. Agric. 2003,18, 146–154. [CrossRef]
58. SAS. SAS 9.4 Language Reference: Concepts; SAS Institute Inc.: Cary, NC, USA, 2014; p. 828.
59. SigmaPlot. SigmaPlot Version 14.0; Systat Software Inc.: San Jose, CA, USA, 2018.
60.
Ahmad, R.; Hussain, S.; Anjum, M.A.; Khalid, M.F.; Saqib, M.; Zakir, I.; Hassan, A.; Fahad, S.; Ahmad, S.
Oxidative stress and antioxidant defense mechanisms in plants under salt stress. In Plant Abiotic Stress
Tolerance; Springer: Berlin/Heidelberg, Germany, 2019; pp. 191–205.
61.
Laxa, M.; Liebthal, M.; Telman, W.; Chibani, K.; Dietz, K.-J. The role of the plant antioxidant system in
drought tolerance. Antioxidants 2019,8, 94. [CrossRef]
62.
Mditshwa, A.; Magwaza, L.S.; Tesfay, S.Z.; Mbili, N. Postharvest quality and composition of organically and
conventionally produced fruits: A review. Sci. Hortic. 2017,216, 148–159. [CrossRef]
63.
Oliveira, A.B.; Moura, C.F.H.; Gomes-Filho, E.; Marco, C.A.; Urban, L.; Miranda, M.R.A. The Impact
of Organic Farming on Quality of Tomatoes Is Associated to Increased Oxidative Stress during Fruit
Development. PLoS ONE 2013,8, e56354. [CrossRef] [PubMed]
64.
Cardoso, P.C.; Tomazini, A.P.B.; Stringheta, P.C.; Ribeiro, S.M.R.; Pinheiro-Sant’Ana, H.M. Vitamin C and
carotenoids in organic and conventional fruits grown in Brazil. Food Chem. 2011,126, 411–416. [CrossRef]
65.
Janzantti, N.S.; Macoris, M.S.; Garruti, D.S.; Monteiro, M. Influence of the cultivation system in the aroma
of the volatile compounds and total antioxidant activity of passion fruit. LWT-Food Sci. Technol.
2012
,
46, 511–518. [CrossRef]
66.
Koh, E.; Charoenprasert, S.; Mitchell, A.E. Eect of Organic and Conventional Cropping Systems on Ascorbic
Acid, Vitamin C, Flavonoids, Nitrate, and Oxalate in 27 Varieties of Spinach (Spinacia oleracea L.). J. Agric.
Food Chem. 2012,60, 3144–3150. [CrossRef]
67.
de Oliveira, A.B.; Lopes, M.M.D.; Moura, C.F.H.; Oliveira, L.D.; de Souza, K.O.; Gomes, E.; Urban, L.;
de Miranda, M.R.A. Eects of organic vs. conventional farming systems on quality and antioxidant
metabolism of passion fruit during maturation. Sci. Hortic. 2017,222, 84–89. [CrossRef]
68.
Vallverd
ú
-Queralt, A.; Medina-Rem
ó
n, A.; Casals-Ribes, I.; Lamuela-Raventos, R.M. Is there any dierence
between the phenolic content of organic and conventional tomato juices? Food Chem.
2012
,130, 222–227.
[CrossRef]
69.
Berry, P.M.; Sylvester-Bradley, R.; Philipps, L.; Hatch, D.J.; Cuttle, S.P.; Rayns, F.W.; Gosling, P. Is the
productivity of organic farms restricted by the supply of available nitrogen? Soil Use Manag.
2002
,
18, 248–255. [CrossRef]
70.
Seufert, V.; Ramankutty, N.; Foley, J.A. Comparing the yields of organic and conventional agriculture. Nature
2012,485, 229. [CrossRef] [PubMed]
71.
Brandt, K.; Leifert, C.; Sanderson, R.; Seal, C. Agroecosystem management and nutritional quality of plant
foods: The case of organic fruits and vegetables. Crit. Rev. Plant Sci. 2011,30, 177–197. [CrossRef]
Sustainability 2020,12, 8965 25 of 25
72.
Simmons, B.L.; Coleman, D.C. Microbial community response to transition from conventional to conservation
tillage in cotton fields. Appl. Soil Ecol. 2008,40, 518–528. [CrossRef]
73.
Jonason, D.; Andersson, G.K.; Öckinger, E.; Rundlöf, M.; Smith, H.G.; Bengtsson, J. Assessing the eect of the
time since transition to organic farming on plants and butterflies. J. Appl. Ecol.
2011
,48, 543–550. [CrossRef]
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... Bhardwaj et al. [14] also reported that fruits and vegetables grown in organic fields are more nutritious with good organoleptic qualities. Natural farming methods would be the best solution to overcome nutrient deficiency by improving the bioavailability of macro-and micronutrients on cultivable land [36], adding to the soil organic matter, organic carbon, soil organic nitrogen, macro-and microelements, and biological components [32]. Worthington [155] reported that organically grown vegetables contained significantly higher minerals and vitamin C than presently grown vegetables (Table 6). ...
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... Both topics are mainly centered on farm management issues, but, while in the former a production-oriented approach is evident, studies related to the latter usually screen farm management practices through an ecological lens. It is therefore common to find in the Production methods topic studies trying to untangle the effects of specific agricultural practices on crop yields or on food quality [67][68][69][70], such as fertilization [71], irrigation [72], cover cropping, or soil management [73]. On the other hand, some recurrent themes in the Ecological sustainability topic are the general provision of ecosystem services [74,75], the study of insect biodiversity and control [76][77][78], the use of cover crops and their effects on the agroecosystem [79,80], and the use of certain permaculture practices [81]. ...
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We are at a pivotal time in human history, as the agricultural sector undergoes consolidation coupled with increasing energy costs in the context of declining resource availability. Although organic systems are often thought of as more sustainable than conventional operations, the lack of concise and widely accepted means to measure sustainability makes coming to an agreement on this issue quite challenging. However, an accurate assessment of sustainability can be reached by dissecting the scientific underpinnings of opposing production practices and crop output between cropping systems. The purpose of this review is to provide an in-depth and comprehensive evaluation of modern global production practices and economics of organic cropping systems, as well as assess the sustainability of organic production practices through the clarification of information and analysis of recent research. Additionally, this review addresses areas where improvements can be made to help meet the needs of future organic producers, including organic-focused breeding programs and necessity of coming to a unified global stance on plant breeding technologies. By identifying management strategies that utilize practices with long-term environmental and resource efficiencies, a concerted global effort could guide the adoption of organic agriculture as a sustainable food production system.
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Organic food is associated with improved nutritional properties, and this consumer expectation has led to increasing demand for organic fruits and vegetables. The objective of this study was to evaluate the changes in physical, chemical, and nutraceutical parameters of the jujube fruits 'Grande de Albatera' cultivar, grown under organic or conventional production systems. Results showed that the organic jujubes were smaller, with a slightly more intense yellow and red color, with higher contents of chlorophylls, carotenoids, sugars, organic acids, and total volatile compounds, but with lower protein and flavonoids, contents than conventional jujubes. Therefore, it can be concluded that the market quality of organic jujubes was similar to that of the conventional ones because fruits were smaller but with a more intense coloration. However, the flavor quality was better as they had more sugars, acids, and volatile compounds, making the flavor of fruits more attractive for consumers. Finally, there were no significant differences in the antioxidant attributes, as organic and conventional jujubes had similar total contents of phenols and antioxidant activity.