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SÃO MIGUEL, A.S.D.C. et al. Cover crops in the weed management in soybean culture
(9 páginas) PROVA GRÁFICA
1
SOCIEDADE BRASILEIRA DA
CIÊNCIA DAS PLANTAS DANINHAS ISSN 0100-8358 (print)
<http://www.sbcpd.org> 1806-9681 (online)
1
Universidade Federal de Mato Grosso (UFMT), Rondonópolis-MT, Brasil.
Doi: 10.1590/S0100-83582018360100072
Planta Daninha 2018; v36:e018172534
SÃO MIGUEL, A.S.D.C. et al. Cover crops in the weed management in soybean culture 2
INTRODUCTION
Soybean is one of the oleaginous plants of major interest in the world and its development is
often affected by various factors, among them weeds, which compete with soybean for water,
light and nutrients, causing reduced grain yields and difficulties in harvesting (Pittelkow et al.,
2009). The species known as Jamaican crabgrass (Digitaria horizontalis), sourgrass (Digitaria
insularis), couvinha (Porophyllum ruderale) and coatbuttons (Tridax procumbens) are difficult to
control in soybean, maize and millet crops (Pittelkow et al., 2009; Meschede et al., 2007; Martins
et al., 2016). As a result, there is a need for techniques that can be used to assist in the chemical
control of integrated weeds management.
The no-tillage cropping system (NT) is an effective soil management alternative for weeds
suppression by means of the phytomass produced by cover plants. The species of cover plants
used in the production systems need to establish quickly and produce adequate amounts of
phytomass to cover the soil. Maize growing systems intercropped with U. ruziziensis P. glaucum
and Cajanus cajan have a phytomass production capacity of 10,000 to 16,000 kg ha-1 (Carneiro
et al., 2008; Pacheco et al., 2013; Queiroz et al., 2016). Single crops with Pennisetum glaucum,
Urochloa ruziziensis and Crotalaria spectabilis or intercropped with annual cultures can be effective
in suppressing the infesting community.
In the NT system, weeds control is achieved by the phytomass of cover plants, which acts as
a physical barrier to the passage of sunlight and makes weeds’ seed germination and seedlings
growth difficult (Borges et al., 2013). Cover crops also have allelopathic effects on weeds, in their
seeds or seedlings, through root exudation or during phytomass decomposition, interfering
with the plants growth and development (Borges et al., 2013). Some studies with sorghum
identified allelopathic action of this species, which has high phytotoxic activity as photosystem
II inhibitors, acting similarly to the triazine group of herbicides (Czarnota et al., 2003; Santos
et al., 2012).
Furthermore, an even bed of plant cover on the soil is capable of diminishing weeds
infestations and improving the soil structure and fertility (Cosdta et al., 2015). To promote these
improvements, the cover species in cerrado lands need to adapt to the biome edaphoclimatic
conditions and produce large amounts of phytomass. Therefore, knowing the behavior of each
cover plants species is necessary for an optimal production in monocropping, crop rotation or
intercropping farming systems (Meschede et al., 2007) as well as for weeds control. This study
aimed to evaluate the cover plants’ effectiveness in suppressing weeds in no-till soybean
production system.
The experiment was carried out in 2013/2014, 2014/2015 and 2015/2016 crop years at the
Federal University of Mato Grosso - UFMT, Campus of Rondonópolis (16o27’75" S and 54o34’55" O
and altitude of 292 meters). The soil in the area is Dystrophic Oxisol (Embrapa, 2006),
whose chemical and physical attributes are described on Table 1. The climate, according to
Köppen classification, is Cwa, with well-defined dry and rainy seasons, the rainy season
beginning in October and ending in May (Souza et al., 2013). Precipitation rates and mean
maximum and minimum air temperatures during the experiment conduction are described in
Figure 1.
Figure 1 - Monthly and accumulated precipitation and minimum and maximum average air temperatures during the conduction of
the experiment in Rondonópolis-MT.
Prior to the experiment installation, the area was cleared, followed by plowing and harrowing
and manual roots removal. On Oct 08, 2013, liming was applied to the area (4,000 kg ha-1) with
Filler lime (PRNT: 99.02%), incorporated with a plow and harrow. The experiment was implemented
in a randomized block design with nine treatments (Table 2) and four replications. Each
experimental plot was 7 m wide x 9 m long.
In all production systems, soy was cultivated in two crop seasons. After being harvested, the
second season began, when annual cereal crops were grown (60,000 maize plants ha-1, 55,000
sunflower plants ha-1, 160,000 Vigna unguiculata plants ha-1) and the following cover plants:
Pennisetum glaucum (18 kg ha-1), Urochloa ruziziensis and Urochloa brizantha (15 kg ha-1 with 60%
of cultural value), Crotalaria breviflora (17 kg ha-1), Crotalaria spectabilis (15 kg ha-1), Cajanus cajan
(40 kg ha-1) and Stylosanthes capitata + S. macrocephala (8 kg ha-1), as described in Table 2. The
systems with single cover crops were implemented with spacing of 0.45 m between rows; in the
intercropping systems, annual crops (maize and sunflower) were implemented with spacings of
0.45 m, and the intercropped cover crops were sowed in between rows. All systems during the
second season were sowed and fertilized manually. As can be seen in Table 2, some treatments
(S4, S7, S8 and S9) had rotation of species sowed between the 2014 and 2015 second seasons, for
systems diversification. Fallow treatments (S1 and S2) are the controls.
Table 2 - Characterization of production systems for sowing second season soybean seeds and after 2014/15 and 2015/16 harvests
The soybean cultivar TMG 132 RR was sowed in November 2013, with spacing of 0.45 m
between rows and density of 12 plants m-1. After the soybean harvest, the cover crops of the
2013/2014 crop year were sowed. In the beginning of the 2014/2015 crop, in October, all cover
crops were desiccated using glyphosate herbicides (5 L ha-1) and 2.4-D (1.5 L ha-1). Afterwards,
the soybean cultivar ANTA 82 RR was sowed on the remaining plant residues deposited on the
soil, with a distribution of 29 plants m-1 and spacing of 0.45 m between rows. Soybean was
harvested in February 2015, and again cover crops were sowed manually. The soybean cultivar
used in 2015/16 was TMG 1175 RR, with a density of 25 plants m-1. In 2015/16 crop, soybean
was sowed on Oct. 29, 2015 and harvested on Feb. 16, 2016.
The fertilization used in soybean in both crop seasons was 120 kg ha-1 of P2O5 and 22 kg ha-1
of N, via monoammonium phosphate in the sowing grooves, and 100 kg ha-1 of K2O via potassium
chloride, half of it scattered over during pre-sowing and the rest when the soybean was in the V4
phenological stage. For all soybean plantations, the seeds were inoculated with liquid inoculant
(Cell Tech HC® Nitragin) at a dosage of 150 mL of inoculant per 50 kg of seeds, exhibiting a
bacterial concentration of 3x109 CFU per mL, with Bradyrhizobium japonicum bacteria (SEMIA
5079 and 5080). In the annual crops sowed during the second season (maize, V. unguiculata and
sunflower), fertilizations were made as recommended by Souza and Lobato (2004), while in the
parcels of land where single crops of cover plants were grown, no fertilizers were used.
The evaluations were carried out before desiccation for soybean sowing in the 2014/2015
(Oct. 23, 2014) and 2015/2016 crop years (Sept. 21, 2015), prior to application of the selective
herbicide in post-emergence of soybean in 2014/2015 (Dec. 09, 2014) and 2015/2016 (Nov. 12,
2015) and in the second season (June 12, 2015). In each parcel, a 5 x 5 m of useful area was
assessed, where all weed species were counted and identified, but only the four species with the
largest population amount were collected for phytomass determination. The four species were
cut close to the ground and dried in a forced-circulation oven at 65 oC during 72 hours;
subsequently, manual cleaning of residues was made to remove adhered soil and obtain dry
phytomass. Soybean grains yield was assessed by harvesting the plants in two 2 meter long
rows, expressed in kg ha-1 (standardized at 13% moisture).
The main weeds evaluated in the experimental area were Jamaican crabgrass (Digitaria
horizontalis), sourgrass (Digitaria insularis), couvinha (Porophyllum ruderale) and coatbuttons (Tridax
procumbens). The parameters used for the main weeds were density (plants m-2), phytomass
(kg ha-1), incidence:
Population of evaluated species
x 100 , expressed in percentage, and control effect:
Total population
The results were subjected to analysis of variance, with data transformed by equation “X+1,
except for the control treatment; means were compared by Scott-Knott’s test at 5%, using SISVAR
5.4 software (Ferreira, 2008).
The studied cover crops had an influence on weeds development (Table 3). D. horizontalis
was the species that exhibited the highest population density among the assessed weed species.
Edaphoclimatic conditions with rising temperature and rains are ideal conditions for breaking
the dormancy of this seed and, consequently, its development, suppressing other species (Andrade
et al., 2000).
In the evaluation prior to the desiccation of the area in 2015 (Sept 21, 2015), D. horizonthalis
plants were not counted because they had already senesced due to water stress occurred in this
period (Figure 1) and for not actually representing the situation of the species. These results are
confirmed in the evaluation conducted during the 2015/2016 crop (Nov.12, 2015), so that after
the rains, D. horizonthalis was present in the area. The other species did not appear in the
evaluations, probably because of the production systems, which, by means of the cover crops
phytomass control or the characteristics of each species, they may have been dormant for a
while, awaiting better conditions for germination.
P. ruderale and T. procumbens weeds were more numerous in the fallow area than in the
treatments with cover crops (Table 3), which indicates that there is a greater proliferation of
these species when there is no control by the cover crops phytomass. Rizzardi and Silva (2014)
studied management strategies to prevent the emergence of weeds in soybean crop, and Martins
et al. (2016) in maize crop, reported that in fallow areas, managed with or without chemical
control, contribute to the proliferation and a more difficult control of weeds. T. procumbens was
found in fallow areas at all times, and in the evaluation at the time of desiccation for planting
soybean, it was found in the area with P. glaucum. Cover crops phytomass exerts interspecific
inhibition on weeds species (Meschede et al., 2007), either by the physical suppression effect or
by the allelochemicals released by the plant matter in decomposition or produced by the roots of
photosynthetically active crops.
In the conventional till (CT) fallow system, incorporation of plant residues reduced the density
of infesting species in most of the soybean pre- and post-emergence evaluations, when compared
to the NT fallow treatments (Table 3). Results obtained by Pacheco et al. (2016) in rice production
system in the state of Piauí corroborate the temporary effectiveness of this management practice
in the early stage of crop development.
It is worth noting that in the off-season evaluation, the CT fallow system exhibited higher
counts of the species studied, except for D. insularis, which has a slower cycle and, therefore, did
not exhibit a great number of individuals of this species (Table 3). It is known that weeds control
by conventional tillage, when soil is turned over, is temporary, only by the time that soybean is
sowed. In addition, with soil mechanical agitation, the seeds bank has more stimulus to germinate
and emerge, resulting in a greater density of weeds in the off-season. So, the use of this technique
is not recommended because it causes an increased infestation and increased seeds bank in
the area over time.
The use of U. ruziziensis as cover crop promoted a lower incidence of weeds in most of
the times and species evaluated (Table 3). These results were obtained because this cover
species is able to produce a great amount of phytomass. Pacheco et al. (2016) obtained, in dry
rice cultivation systems with U. ruziziensis, amounts between 10,800 and 12,500 kg ha-1 of
phytomass for weeds control. Cover crops with this characteristic are vitally important for
the integrated management of weeds, because it reduces weed infestations and the use of
herbicides.
Gomes Jr. And Christoffoleti (2008) and Monquero et al. (2009) reported that the amount of
phytomass produced by cover crops can interfere with the process of germination of weed seeds
by reducing the soil temperature. This favors proliferation of soil micro- and mesofauna, which
feeds on the seeds or colonizes them, and can also prevent the passage of light that is required
for cellular histodifferentiation of positive photoblastic species. Mondo et al. (2010) examined
four species of the genus Digitaria and found that D. horizontalis has positive photoblastism,
differently from D. insularis, which exhibited negative photoblastism, which explains the high
density of D. horizontalis in the area.
Table 3 - Density and phytomass of four weeds at different times and cropping systems for growing soybean. Mato Grosso,
2014/2015 and 2015/2016
Oct 23, 2014 Dec 09, 2014 June 12, 2015 Sept 21, 2015 Nov 12, 2015
System Density Phytomass Density Phytomass Density Phytomass Density Phytomass Density Phytomass
(m-²) (kg ha-1) (m-²) (kg ha-1) (m-²) (kg ha-1) (m-²) (kg ha-1) (m-²) (kg ha-1)
Digitaria horizontalis
S1 : 11.55 a 136.64 a 8.72 a 15.63 a 17.44 a 1171.21 a -- -- 91.53 a 183.66 a
S2 : 11.49 a 150.13 a 4.31 a 5.56 a 22.13 a 1454.44 a -- -- 56.50 b 142.82 a
S3 : 0.00 b 0.00 b 3.92 a 4.12 a 0.05 b 1.07 b -- -- 28.75 c 71.39 b
S4 : 0.27 b 12.18 b 4.39 a 8.63 a 0.05 b 3.38 b -- -- 8.65 d 21.79 b
S5 : 0.44 b 10.01 b 0.97 a 1.26 a 0.00 b 0.00 b -- -- 8.85 d 17.37 b
S6 : 0.00 b 0.00 b 0.64 a 0.41 a 0.00 b 0.00 b -- -- 14.45 d 32.49 b
S7 : 0.00 b 0.00 b 2.10 a 8.73 a 3.07 b 93.25 b -- -- 43.90 b 170.91 a
S8 : 0.00 b 0.00 b 0.24 a 0.07 a 0.00 b 0.00 b -- -- 29.75 c 69.57 b
S9 : 0.19 b 0.97 b 6.36 a 7.58 a 0.00 b 0.00 b -- -- 10.19 d 25.31 b
VC (%) 17.4 43.78 45.98 61.99 31.6 61.09 -- -- 29.77 35.92
Digitaria insularis
S1 : -- -- -- -- 0.16 a 16.67 a 0.57 a 31.81 a -- --
S2 : -- -- -- -- 0.09 a 18.05 a 0.37 a 16.98 a -- --
S3 : -- -- -- -- 0.08 a 6.92 a 0.42 a 2.87 b -- --
S4 : -- -- -- -- 0.00 a 0.00 a 0.05 b 0.89 b -- --
S5 : -- -- -- -- 0.00 a 0.00 a 0.11 b 2.74 b -- --
S6 : -- -- -- -- 0.00 a 0.00 a 0.00 b 0.00 b -- --
S7 : -- -- -- -- 0.00 a 0.00 a 0.00 b 0.00 b -- --
S8 : -- -- -- -- 0.00 a 0.00 a 0.03 b 0.83 b -- --
S9 : -- -- -- -- 0.00 a 0.00 a 0.00 b 0.00 b -- --
VC (%) -- -- -- -- 4.8 92.5 10.64 66.43 -- --
Porophyllum ruderale
S1 : 1.52 a 18.87 a -- -- 0.51 b 47.41 b 0.14 a 2.31 a -- --
S2 : 0.89 b 13.95 a -- -- 0.88 a 106.48 a 0.32 a 13.05 a -- --
S3 : 0.07 c 0.38 b -- -- 0.22 c 5.43 c 0.01 a 0.21 a -- --
S4 : 0.00 c 0.00 b -- -- 0.00 c 0.00 c 0.00 a 0.00 a -- --
S5 : 0.60 b 22.61 a -- -- 0.06 c 0.43 c 0.09 a 0.55 a -- --
S6 : 0.00 c 0.00 b -- -- 0.00 c 0.00 c 0.00 a 0.00 a -- --
S7 : 0.00 c 0.00 b -- -- 0.03 c 0.35 c 0.00 a 0.00 a -- --
S8 : 0.00 c 0.00 b -- -- 0.02 c 0.35 c 0.00 a 0.00 a -- --
S9 : 0.00 c 0.00 b -- -- 0.00 c 0.00 c 0.00 a 0.00 a -- --
VC (%) 12.6 45.76 -- -- 5.25 60.59 7.12 72.32 -- --
Tridax procumbens
S1 : 0.53 a 4.05 a -- -- 0.14 a 31.73 a 0.24 a 11.65 a -- --
S2 : 2.51 a 51.70 a -- -- 0.15 a 32.98 a 0.16 a 11.15 a -- --
S3 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.00 b 0.00 b -- --
S4 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.00 b 0.00 b -- --
S5 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.03 b 0.57 b -- --
S6 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.00 b 0.00 b -- --
S7 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.00 b 0.00 b -- --
S8 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.00 b 0.00 b -- --
S9 : 0.00 a 0.00 a -- -- 0.00 b 0.00 b 0.00 b 0.00 b -- --
VC (%) 36.83 153.38 -- -- 3.88 105.71 5.1 73.51 -- --
Systems: S1- NT fallow; S2- CT fallow; S3- Crotalaria spectabilis; S4- C. breviflora (2014) and maize + C. spectabilis (2015); S5 P. glaucum
ADR 8010 (2014) and ADR 9010 (2015); S6- U. ruziziensis, S7- Pigeon beans (2014) and sunflower + U. ruziziensis (2015); S8- Stylosanthes
Campo Grande (2014) and cowpea bean (2015); S9- U. brizantha (2014) and maize + U. ruziziensis (2015). Evaluations: Oct 23, 2014 –
Prior to desiccation for growing soybean in 2014/15; Dec 09, 2014 – Prior to application of selective herbicide at soybean post-emergence
in 2014/15; June 12, 2015 – Second season; Sept 21, 2015 – Prior to desiccation for growing soybean in 2015/16; Nov 12, 2015 – Prior
to application of selective herbicide at soybean post-emergence in 2015/16. Means followed by same letters in column do not differ
statistically from each other by the Scott-Knott’s test (P<0.05).
Table 4 - Incidence and control of four weed species at different times and cropping systems for growing soybean. Mato Grosso,
2014/2015 and 2015/2016
Oct 23. 2014 Dec 09. 2014 June 12. 2015 Sept 21. 2015 Nov 12. 2015
System Incidence Control Incidence Control Incidence Control Incidence Control Incidence Control
(%) (%) (%) (%) (%) (%) (%) (%) (%) (%)
Digitaria horizontalis
S1: 17.81 a 76.41 b 22.54 a 0.00 b 14.81 a 80.30 b -- -- 21.85 a 0.00 d
S2: 13.45 a 0.00 c 16.57 a 87.64 a 17.55 a 0.00 c -- -- 16.95 a 84.56 c
S3: 0.00 b 100.00 a 20.48 a 88.76 a 1.47 b 99.94 a -- -- 18.95 a 92.14 b
S4: 10.38 a 99.44 a 15.31 a 87.41 a 5.00 b 99.94 a -- -- 18.86 a 97.63 a
S5: 3.50 b 99.10 a 20.52 a 97.22 a 0.00 b 100.00 a -- -- 17.14 a 97.58 a
S6: 0.00 b 100.00 a 9.00 a 98.16 a 0.00 b 100.00 a -- -- 23.85 a 96.05 a
S7: 0.00 b 100.00 a 11.65 a 93.98 a 16.44 a 96.53 a -- -- 21.10 a 88.00 c
S8: 0.00 b 100.00 a 10.00 a 99.31 a 0.00 b 100.00 a -- -- 13.60 a 91.87 b
S9: 14.71 a 99.61 a 19.47 a 81.76 a 0.00 b 100.00 a -- -- 18.00 a 97.21 a
VC (%) 56.33 1.80 46.7 12.19 44.81 4.57 -- -- 16.79 5.06
Digitaria insularis
S1: -- -- -- -- 0.13 a 0.00 b 5.23 a 0.00 c -- --
S2: -- -- -- -- 0.07 a 85.93 a 3.58 a 83.77 b -- --
S3: -- -- -- -- 2.35 a 87.50 a 11.10 a 81.58 b -- --
S4: -- -- -- -- 0.00 a 100.00 a 6.66 a 97.80 a -- --
S5: -- -- -- -- 0.00 a 100.00 a 5.00 a 95.17 a -- --
S6: -- -- -- -- 0.00 a 100.00 a 0.00 a 100.00 a -- --
S7: -- -- -- -- 0.00 a 100.00 a 0.00 a 100.00 a -- --
S8: -- -- -- -- 0.00 a 100.00 a 5.00 a 98.68 a -- --
S9: -- -- -- -- 0.00 a 100.00 a 0.00 a 100.00 a -- --
VC (%) -- -- -- -- 34.14 12.62 63.03 11.91 -- --
Porophyllum ruderale
S1: 0.02 b 0.00 d -- -- 0.00 b 85.51 c 0.02 a 88.67 c -- --
S2: 0.01 b 84.95 c -- -- 0.00 b 0.00 d 0.02 a 0.00 d -- --
S3: 0.02 b 98.84 a -- -- 0.14 a 93.75 b 0.05 a 99.22 a -- --
S4: 0.00 c 100.00 a -- -- 0.00 b 100.00 a 0.00 a 100.00 a -- --
S5: 0.05 a 90.13 b -- -- 0.03 b 98.29 a 0.05 a 92.97 b -- --
S6: 0.00 c 100.00 a -- -- 0.00 b 100.00 a 0.00 a 100.00 a -- --
S7: 0.00 c 100.00 a -- -- 0.00 b 99.14 a 0.00 a 100.00 a -- --
S8: 0.00 c 100.00 a -- -- 0.02 b 99.43 a 0.00 a 100.00 a -- --
S9: 0.00 c 100.00 a -- -- 0.00 b 100.00 a 0.00 a 100.00 a -- --
VC (%) 0.73 2.35 -- -- 1.74 3.53 1.86 1.74 -- --
Tridax procumbens
S1: 1.04 a 94.44 b -- -- 0.10 a 76.66 b 2.80 a 0.00 d -- --
S2: 2.78 a 0.00 c -- -- 0.11 a 0.00 c 1.65 a 84.11 c -- --
S3: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 0.00 b 100.00 a -- --
S4: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 0.00 b 100.00 a -- --
S5: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 1.34 a 96.61 b -- --
S6: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 0.00 b 100.00 a -- --
S7: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 0.00 b 100.00 a -- --
S8: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 0.00 b 100.00 a -- --
S9: 0.00 a 100.00 a -- -- 0.00 b 100.00 a 0.00 b 100.00 a -- --
VC (%) 40.99 0.77 -- -- 3.11 1.05 34.99 1.08 -- --
Systems: S1- NT fallow; S2- CT fallow; S3- Crotalaria spectabilis; S4- C. breviflora (2014) and maize + C. spectabilis (2015); S5 P. glaucum
ADR 8010 (2014) and ADR 9010 (2015); S6- U. ruziziensis, S7- Pigeon beans (2014) and sunflower + U. ruziziensis (2015); S8- Stylosanthes
Campo Grande (2014) and cowpea bean (2015); S9- U. brizantha (2014) and maize + U. ruziziensis (2015). Evaluations: Oct 23, 2014 –
Prior to desiccation for growing soybean in 2014/15; Dec 09, 2014 – Prior to application of selective herbicide at soybean post-emergence
in 2014/15; June 12, 2015 – Second season; Sept 21, 2015 – Prior to desiccation for growing soybean in 2015/16; Nov 12, 2015 – Prior
to application of selective herbicide at soybean post-emergence in 2015/16. Means followed by same letters in column do not differ
statistically from each other by the Scott-Knott’s test (P<0.05).
The lowest rates of weeds suppression were found in the fallow treatments (Table 4). This
was due to the absence of cover crops to exert control on weeds, which, without the inhibitory
effect of cover crops, proliferate in fallow treatments, and therefore increases the seeds bank for
the next crops, which makes control more difficult.
With regard to soybean yields, there was as a significant effect of the systems only in 2015/
2016 (Table 5). The system with Crotalaria spectabilis exhibited better results compared to the
other systems, with high control of weeds, among other factors. This weeds control minimized
interspecific competition for resources and contributed to higher yields of soybeans. In the fallow
systems, the absence of cover crops associated with the management system resulted in lower
soybeans yields. Management with spontaneous plant species and mechanical agitation of soil
showed, since the early stages of soybean growth, a high density of weeds and, consequently,
more competition between the crop and the infesting community.
Table 5 - Yields of soybean grown in rotation with annual crops and cover crops sown in second season in nine different
cropping systems in 2014/2015 and 2015/2016
The cropping systems with U. ruziziensis, P. glaucum, C. spectabilis and intercropping with
maize + U. ruziziensis, sunflower + U. ruziziensis and maize + C. spectabilis are good alternatives
to assist integrated weeds management, by reducing the incidence and increasing the control
of D. horizonthalis, D. insularis, P. ruderale and T. procumbens, detected in soybean growing systems
during the conduction of the experiment in the cerrado region in Rondonópolis-MT. The system
with C. spectabilis results in higher soybeans yield. With this integrated management, costs
with herbicides applications, use of implements and fuel are reduced, besides incorporating
phytomass to the system, making NT farming system an efficient method in managing
agricultural farming systems.
ACKNOWLEDGEMENTS
The authors are thankful to the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior
(CAPES) for the MD scholarship granted to the first and fourth authors. To the Conselho Nacional
de Desenvolvimento Científico e Tecnológico (CNPq) for the financial support (Universal Call no.
14/2012 – Project no. 484801/2012-0) and for the productivity scholarships granted to the second
and third authors. To the Fundação AGRISUS – Agricultura Sustentável (Project no. 1604/15) for
the financial support.
REFERENCES
Alsaadawi I.S. et al. Integration of sunflower (Helianthus annuus) residues with a pre-plant herbicide enhances weed suppression
in broad bean (Vicia faba). Planta Daninha. 2011;29:849-59.
Andrade A.C.S. et al. Germinação de sementes de jenipapo: temperatura, substrato e morfologia do desenvolvimento pós-seminal.
Pesq Agropec Bras. 2000;35:609-15.
Borges W.L.B., Freitas R.S., Mateus G.P. Plantas de cobertura no controle de plantas daninhas. Pesq Tecnol. 2013;10:1-5.
Carneiro M.A.C. et al. Produção de fitomassa de diferentes espécies de cobertura e suas alterações na atividade microbiana de solo
de cerrado. Bragantia. 2008;67:455-62.
Costa N.R. et al. Atributos do solo e acúmulo de carbono na integração lavoura-pecuária em sistema plantio direto. Rev Bras Cien
Solo, 2015;39:852-63.
Czarnota M.A., Rimando A.M., Weston L.A. Evaluation of root exudates of seven sorghum accessions. J Chem Ecol.
2003;29:2073-83.
Empresa Brasileira de Pesquisa Agropecuária – Embrapa. Sistema brasileiro de classificação de solos. 2ª.ed. Brasília: 2006.
306p.
Erasmo E.A.L. Efeito de extratos de adubos verdes sobre Lactuca sativa e Digitaria horizontalis. Bragantia. 2011;70:529-37.
Ferreira D.F. Sisvar: um programa para análises e ensino de estatística. Rev Cien Sympos. 2008;636-41.
Golisz A., Sugano, M., Fujii, Y. Microarray ex-pression profiling of Arabidopsis thaliana L. in response to allelochemicals
identified in buckwheat. J Exper Bot. 2008;59:3099-109.
Gomes JR., F.G.; Christoffoleti P.J. Biologia e manejo de plantas daninhas em áreas de plantio direto. Planta Daninha,
2008;26:789-98.
Machado A.F.L. et al. Análise de crescimento de Digitaria insularis. Planta Daninha. 2006;24:641-7.
Martins D., Gonçalves C.G., Silva Junio A.C. Coberturas mortas de inverno e controle químico sobre plantas daninhas na cultura
do milho. Rev Cienc Agron. 2016;47:649-57.
Meschede D.K.; Ferreira, A.B.; Ribeiro Jr., C.C. avaliação de diferentes coberturas na supressão de plantas daninhas no cerrado.
Planta Daninha. 2007;25:465-71.
Mondo V.H.V. et al. Efeitos da luz e temperatura na germinação de sementes de quatro espécies de plantas daninhas do gênero
Digitaria. Rev Bras Sementes. 2010;32:131-7.
Monquero P.A. et al. Efeito de adubos verdes na supressão de espécies de plantas daninhas. Planta Daninha. 2009;27:85-95.
Pacheco L.P. et al. Produção de fitomassa e acúmulo e liberação de nutrientes por plantas de cobertura na safrinha. Pesq Agropec
Bras. 2011;46:17-25.
Pacheco L.P. et al. Produção de fitomassa e acúmulo de nutrientes por plantas de cobertura no cerrado piauiense. Bragantia.
2013;72:237-46.
Pacheco L.P. et al. Sistemas de produção no controle de plantas daninhas em culturas anuais no Cerrado Piauiense. Rev Cienc
Agron. 2016;47:500-8.
Pittelkow F.K. et al. Interferência de plantas daninhas na cultura da soja transgênica. Global Sci Technol. 2009;02:38-48.
Queiroz R.F. de et al. Maize intercropped with Urochloa ruziziensis under no-tillage system. Pesq Agropec Tropical.
2016;46:238-44.
Rizzardi M.A., Silva L. Manejo de plantas daninhas eudicotiledôneas na cultura da soja Roundup Ready®. Planta Daninha.
2014;32:683-97.
Santos I.L.V.L. et al. Sorgoleone: benzoquinona lipídica de sorgo com efeitos alelopáticos na agricultura como herbicida. Rev Arq
Inst Biol. 2012;79:135-44.
Souza D.M.G.; Lobato, E. Cerrado: correção do solo e adubação. Planaltina: Embrapa Cerrados, 2004. 416p.
Souza A.P. et al. Classificação climática e balanço hídrico climatológico no estado de Mato Grosso. Nativa, 2013;1:34-43, 2013.