Cotton (
Rotating to a non-host crop may provide short-term suppression of plant-parasitic nematodes in cotton production (Starr et al., 2002). For instance, crop rotation to a non-host like peanut (
Nematicide application is another primary method to manage plant-parasitic nematodes in cotton (Moore and Lawrence, 2012; Khanal et al., 2018). Several studies have shown that plant-parasitic nematode populations decrease after nematicide treatments in horticultural crop production (Carrascosa et al., 2014; Coleman and Wall, 2015). However, there is a desire to minimize nematicide application because of cost and potential negative environmental impacts associated with its use (Khanal et al., 2018). Fluopyram is the active ingredient in a nematicide recently made available in cotton production. Most nematicides work by disrupting chemoreception and nervous system function in nematodes (Haydock et al., 2006). Fluopyram selectively inhibits Complex II of the mitochondrial respiratory chain in the mitochondria of nematodes, which results in immobility and death (Heiken, 2017). In the field,
Little published research exists on fluopyram effects on RN in cotton in the field since it is a relatively new nematicide. To address this paucity of information, there is a need to investigate fluopyram performance in conjunction with crop rotation in cotton because nematicide protection from yield loss may vary based on the population densities of the different plant-parasitic nematode genera present. If SBR sufficiently manages RN, applying nematicide may result in minimal yield impact, which may allow growers to eliminate nematicide application when using SBR. We hypothesize that fluopyram reduces populations of all plant-parasitic nematodes in both conventional cotton and SBR schemes. Previous studies showed that RN pressure was greater in conventional cotton than SBR at the site (Tsigbey et al., 2009). Therefore, we further hypothesize that yield impact of nematicide application will be greater in conventional rotation than SBR due to greater nematode pressure in conventional rotation than SBR.
Water management, such as irrigation, is used extensively in agriculture and can also influence nematodes. Water used in agricultural systems is responsible for 70% of freshwater use globally (FAO, 2007). Moore et al. (2010) showed that irrigation had no effect on the migration of RN females and juveniles, but males migrated faster in the presence of irrigation. Furthermore, RN can survive for long periods in an anhydrobiotic state (Birchfield and Martin, 1967). However, RN is not as well adapted to anhydrobiosis as organisms found in more stressed (i.e. drier) environments (Womersley and Ching, 1989). There is a need for more information on the impact of irrigation on plant-parasitic nematode populations in various agroecosystems and how this relates to other cultural methods like crop rotation. SBR reduces the need for irrigation in the subsequent crop due to larger roots of following crops, so comparing irrigation and non-irrigation in both conventional and SBR is of interest from an agronomic perspective as well (Katsvairo et al., 2006).
Main objectives for this research were to: (i) assess if SBR helps manage plant-parasitic nematodes by reducing population densities and increasing crop yields; (ii) determine if the addition of the fluopyram nematicide further reduces plant-parasitic nematodes in conventional and SBR; and (iii) determine if yield impacts of nematicide application vary by crop rotation system. Further objectives evaluated the effect of irrigation on plant-parasitic nematode population densities.
Studies were conducted at the University of Florida’s North Florida Research and Education Center (NFREC) in Quincy, FL (30°32.79’N, 84°35.50’W). A sod-based rotation study has been in place at this long-term agricultural research site since 2000 (Zhao et al., 2010). The soil was a Dothan sandy loam (fine-loamy, kaolinitic, thermic Plinthic Kandiudult) with 85% sand, 5% silt, and 10% clay (Zhao et al., 2010). The site was naturally infested with RN, spiral (
The study used a complete block design with a modified split-split plot arrangement (irrigation by crop rotation phase by nematicide) with three replicates. The research site includes four-year bahiagrass–bahiagrass–peanut–cotton (sod-based rotation, SBR) rotation and a three-year peanut–cotton–cotton (conventional) rotation where each crop phase of each rotation is present each year were compared based on previous research (Katsvairo et al., 2007). Of these, the three cotton crop phases were sampled for this study in 2017 and 2018, two from the conventional rotation (first and second-year cotton) and one from SBR (Table 1). Therefore, subplot treatments were first-year conventional cotton (C1), second-year conventional cotton (C2), and sod-based cotton (CS). All rotation phases were represented each year, with and without irrigation. Irrigation (main plot treatment) was supplied via a lateral line overhead system and applied to half of each replicate as necessary while the other half was rainfed only. Velum® Total nematicide (fluopyram and imidacloprid, Bayer Crop Science, Research Triangle Park, NC) was the sub-subplot treatment and all three cotton phases received this treatment in 2017 and 2018. The first half of the sub-sub plots received nematicide in-furrow at planting via a two-row tractor-driven Monosem planter (Monosem Co., Edwardsville, KS) using 8002 flat fan nozzles placed perpendicularly to the row spraying just before the seed was dropped into the furrow at a rate of 1.3 l/ha (0.24 kg a.i./ha) while the second half of the sub-subplots received no nematicide. The in-furrow spray was stopped before continuing to sub-subplots receiving no nematicide. Sub-subplots were 1.8 m by 9.1 m (10 rows of cotton). Sub-subplots planted to cotton (
Crop phase for bahiagrass, peanut, and cotton during 2016 to 2019a.
Phase number | Rotation | 2016 | 2017 | 2018 | 2019 |
---|---|---|---|---|---|
1 | Conventional | P |
|
|
P |
2 | Conventional | C1 |
|
P | C1 |
3 | Conventional | C2 | P |
|
C2 |
4 | Bahiagrass | CS | B1 | B2 | PS |
5 | Bahiagrass | B1 | B2 | PS | CS |
6 | Bahiagrass | B2 | PS |
|
B1 |
7 | Bahiagrass | PS |
|
B1 | B2 |
Detailed site maintenance information is provided in Table 2. Aside from crop rotation, irrigation, and nematicide treatments described above, planting and harvest were uniform across the site. The site used strip tillage and a winter cover crop of oats planted in December of each year (terminated in March) in the peanut and cotton rotations. A preplant 5-15-30 (N-P-K) fertilizer was applied at 280.2 kg/ha based on previous site recommendations. Additionally, all subplots received 27.2 kg N. Deltapine® 1646B2XF cotton was planted using a two-row Monosem planter at the rate of 13 seeds/m of row. The standard insecticide, herbicide, and growth regulators were applied uniformly as needed. Plots received irrigation at 1.5 cm per irrigation event. Cotton was harvested using a two-row Case IH (CNH Industrial America, LLC, Racine, WI) cotton picker from the third, fourth, seventh, and eighth rows of each plot and weighed (two weights per plot). Lint and seed yield were then calculated by ginning a 0.9 kg subsample from each plot.
Cotton planting, nematode sampling, cotton harvest, and irrigation dates in 2017 and 2018.
2017 | 2018 | |
---|---|---|
Cotton planting | April 28 | April 27 |
Soil samplinga | ||
Preplant (Pi) | April 13 | April 19 |
Midseason (Pm) | June 19 | June 22 |
Harvest (Pf) | September 25 | September 25 |
Root sampling | June 19 | June 22 |
Cotton harvest | October 17 | October 8 |
Irrigation eventsb | May 10 | May 12 |
July 5 | June 26 | |
August 2 | July 12 | |
August 25 | July 18 |
bAmount of water per irrigation event was 1.5 cm.
Soil samples from the two center rows of each plot (8 cm or less away from plants) were collected to a 30 cm depth using an Oakfield tube before planting, at midseason (52 and 56 days after planting in 2017 and 2018, respectively) and at harvest (150 and 151 days after planting in 2017 and 2018, respectively). In total, 12 cores were taken per plot and mixed to achieve a composite soil sample. Samples were stored at 4°C for less than three days before processing. Prior to extraction, soil samples were sieved through a screen with 0.64 cm apertures to achieve a more uniform soil particle size. Nematodes were extracted from 100 cm3 soil using a modified sucrose-centrifugation method (Jenkins, 1964).
Nematode samples were fixed in 2% formalin prior to identification. Nematodes were counted from soil samples using a 400× inverted microscope (Carl Zeiss Inc., Thornwood, NY) and identified morphologically. Total nematode population density was recorded, the first 200 nematodes encountered identified to genus based on a key by Mai and Mullin (1996), and then adjusted to the absolute abundance per 100 cm3 by adding up totals from each nematode genus present. Of the plant-parasitic nematode genera encountered, only RN, spiral, and ring nematodes were statistically analyzed. Furthermore, RN males were enumerated separately from immature females and juveniles. The ratio of RN immature females and juveniles to males was statistically analyzed. Reproduction factor (Pf/Pi) was also calculated for each plant-parasitic nematode in 2017 and 2018.
Nematode data were analyzed separately for each sampling date. Each variable within each sampling date of 2017 and 2018 (preplant, midseason, and harvest) was analyzed using three-way, split-split plot ANOVA in R version 3.3.1 (The R Foundation for Statistical Computing, Vienna, Austria). ANOVA models were checked for homogeneity of variances using Levene’s test and normality of residuals checked graphically (Levene, 1960; Cook and Weisburg, 1999). If there were significant (
Crop rotation significantly affected total RN population density in all seasons (Fig. 1, Table 3). RN populations were greatest in C2 and least in CS in preplant 2017, midseason 2018, and harvest 2018 soil samples. Total RN population density was greater in C1 and C2 than CS for midseason 2017 soil samples. Reproduction factor was greatest in CS and least in C2 in both 2017 and 2018. Plots receiving nematicide application in preplant 2018 had a significantly greater RN population density compared with untreated plots, but nematicide application did not affect the population density in any other season. There were significant irrigation by crop interactions for total RN population density in harvest 2017 and preplant 2018 soil samples. Irrigation effects varied significantly by cropping phase, but there was no consistent trend in these effects. Irrigation effects were significant in C1 and C2 for harvest 2017 soil samples, where total RN population density was greater in rainfed plots of C1 (6,151 RN/100 cm3 soil) and significantly lower in irrigated plots (3,513 RN/100 cm3 soil) while total RN population density was greater in irrigated plots of C2 (6,269 RN/100 cm3 soil) and significantly lower in rainfed plots (4,355 RN/100 cm3 soil). Irrigation effects were significant in CS and C2 for preplant 2018 soil samples, where total RN population density was greater in irrigated plots of CS (503 RN/100 cm3 soil) and significantly lower in rainfed plots (67 RN/100 cm3 soil) while total RN population density was greater in rainfed plots of C2 (11,559 RN/100 cm3 soil) and significantly lower in irrigated plots (7,845 RN/100 cm3 soil).
Effects of irrigation, crop phase, and nematicide application on
Total |
||||||||
---|---|---|---|---|---|---|---|---|
2017 | 2018 | |||||||
Pia | Pm | Pf | Rf | Pi | Pm | Pf | Rf | |
ANOVA ( |
||||||||
Irrigation (I) | 0.76 | 0.75 | 0.61 | 0.61 | 0.27 | 0.49 | 0.25 | 0.21 |
Crop phase (C) | < 0.01** | < 0.01** | < 0.01** | 0.02* | < 0.01** | < 0.01** | < 0.01** | < 0.01** |
I × C | 0.35 | 0.46 | 0.02* | 0.79 | 0.05* | 0.82 | 0.39 | 0.16 |
Nematicide (N) | 0.96 | 0.47 | 0.13 | 0.78 | 0.01** | 0.22 | 0.13 | 0.78 |
I × N | 0.89 | 0.70 | 0.22 | 0.62 | 0.10 | 0.72 | 0.53 | 0.16 |
C × N | 0.18 | 0.75 | 0.84 | 0.50 | 0.29 | 0.90 | 0.74 | 0.41 |
I × C × N | 0.67 | 0.80 | 0.65 | 0.90 | 0.18 | 0.84 | 0.53 | 0.34 |
Ratio of |
||||||||
2017 | 2018 | |||||||
Pia | Pm | Pf | Pi | Pm | Pf | |||
ANOVA ( |
||||||||
Irrigation (I) | 0.11 | 0.34 | 0.15 | 0.11 | 0.46 | 0.19 | ||
Crop phase (C) | 0.05* | 0.18 | 0.01** | 0.02* | 0.28 | 0.03* | ||
I × C | 0.93 | 0.38 | 0.92 | 0.10 | 0.36 | 0.43 | ||
Nematicide (N) | 0.95 | 0.61 | < 0.01** | 0.40 | 0.56 | 0.75 | ||
I × N | 0.18 | 0.84 | 0.08 | 0.37 | 0.43 | 0.95 | ||
C × N | 0.87 | 0.50 | 0.02* | 0.72 | 0.64 | 0.83 | ||
I × C × N | 0.97 | 0.37 | 0.06 | 0.43 | 0.73 | 0.94 |
* and ** represent significant effects at
Crop rotation significantly affected the ratio of RN immature females and juveniles to males in preplant and harvest soil samples in both 2017 and 2018 (Table 3). The ratio was greater in C2 than C1 and CS in preplant soil samples, but greater in CS than C1 and C2 in harvest soil samples. There was a significant crop by nematicide interaction on the ratio of RN immature females and juveniles to males in fall 2017. Nematicide effects were significant in CS, but not C1 or C2. In CS, the ratio of RN immature females and juveniles to males was greatest in nematicide-treated plots (14.0) and significantly lower in untreated plots (5.9).
Significant main effects of crop were observed in midseason 2017, harvest 2017, preplant 2018, and midseason 2018 soil samples (Fig. 2, Table 4). Ring nematode population density was greatest in CS and least in C1 and C2 in harvest 2017 and preplant 2018 soil samples. Ring nematode population density was greater in CS than C2 for midseason 2017 and midseason 2018 soil samples. Reproduction factor was greatest in C2 and least in CS in 2018. There was a significant irrigation by crop interaction for ring nematode population density in preplant 2017 soil samples. Irrigation effects were significant in CS, but not C1 or C2. In CS, ring nematode population density was greatest in irrigated plots (180 ring nematodes/100 cm3 soil) and significantly lower in rainfed plots (74 ring nematodes/100 cm3 soil). Ring nematode population density was greater in rainfed plots (292 ring nematodes/100 cm3 soil) than irrigated plots (210 ring nematodes/100 cm3 soil) in preplant 2018 soil samples. There was no statistical difference between nematicide-treated and untreated plots in any of the sampling dates.
Effects of irrigation, crop phase, and nematicide application on
2017 | 2018 | |||||||
Pia | Pm | Pf | Rf | Pi | Pm | Pf | Rf | |
ANOVA ( |
||||||||
Irrigation (I) | 0.14 | 0.19 | 0.29 | 0.96 | < 0.01** | 0.43 | 0.97 | 0.76 |
Crop phase (C) | < 0.01** | 0.02* | < 0.01** | 0.21 | < 0.01** | 0.05* | 0.76 | 0.03* |
I × C | 0.04* | 0.72 | 0.30 | 0.32 | 0.58 | 0.84 | 0.88 | 0.76 |
Nematicide (N) | 0.71 | 0.66 | 0.53 | 0.81 | 0.31 | 0.22 | 0.30 | 0.13 |
I × N | 0.68 | 0.42 | 0.15 | 0.98 | 0.78 | 0.10 | 0.27 | 0.74 |
C × N | 0.97 | 0.54 | 0.52 | 0.55 | 0.15 | 0.42 | 0.97 | 0.13 |
I × C × N | 0.34 | 0.87 | 0.63 | 0.42 | 0.99 | 0.25 | 0.55 | 0.76 |
2017 | 2018 | |||||||
Pia | Pm | Pf | Rf | Pi | Pm | Pf | Rf | |
ANOVA ( |
||||||||
Irrigation (I) | 0.33 | 0.60 | 0.93 | 0.31 | 0.06 | 0.28 | 0.22 | 0.36 |
Crop phase (C) | 0.56 | 0.03* | 0.19 | 0.90 | 0.07 | 0.15 | 0.04* | 0.43 |
I × C | 0.85 | 0.34 | 0.98 | 0.60 | 0.57 | 0.50 | 0.56 | 0.39 |
Nematicide (N) | 0.02* | 0.10 | < 0.01** | 0.75 | 0.02* | 0.01** | < 0.01** | 0.42 |
I × N | 0.07 | 0.64 | 0.52 | 0.39 | 0.57 | 0.44 | 0.03* | 0.50 |
C × N | 0.42 | 0.01** | 0.06 | 0.25 | 0.25 | 0.06 | 0.02* | 0.28 |
I × C × N | 0.64 | 0.09 | 0.29 | 0.37 | 0.40 | 0.15 | 0.09 | 0.24 |
* and ** represent significant effects at
Significant main effects of crop were observed in midseason 2017 and harvest 2018 samples where spiral nematode population density was greatest in CS (Table 4). Significant main effects of nematicide were observed in preplant 2017, harvest 2017, preplant 2018, and midseason 2018 soil samples where spiral nematode population density was greater in nematicide-treated plots than untreated plots (Fig. 3). Nematicide effects were significant in CS, but not C1 or C2 for midseason 2017 and harvest 2018 soil samples. In CS midseason 2017 soil samples, spiral nematode population density was greatest in nematicide-treated plots (104 spiral nematodes/100 cm3 soil) and significantly lower in untreated plots (16 spiral nematodes/100 cm3 soil). In CS harvest 2018 soil samples, spiral nematode population density was greatest in nematicide-treated plots (775 spiral nematodes/100 cm3 soil) and significantly lower in untreated plots (211 spiral nematodes/100 cm3 soil). Irrigation effects on spiral nematode population density were significant in nematicide-treated plots, but not in untreated plots in harvest 2018 soil samples. In nematicide-treated plots, spiral nematode population density was greatest under irrigation (569 spiral nematodes/100 cm3 soil) and significantly lower in rainfed plots (165 spiral nematodes/100 cm3 soil).
There was a significant crop by nematicide interaction for cotton seed yield in 2017 and 2018 (Table 5). In 2017, nematicide effects were significant in C2, but not CS or C1. In C2, cotton seed yield was greatest in nematicide-treated plots and significantly lower in untreated plots (Fig. 4). In 2018, nematicide effects were significant in CS, but not C1 or C2. In CS, cotton seed yield was greatest in untreated plots and significantly lower in nematicide-treated plots (Fig. 4). For cotton lint yield, significant main effects of crop and nematicide were observed in 2017 (Table 5). Cotton lint yield was greater in nematicide-treated plots than untreated plots. Cotton lint yield was greatest in CS and least in C2. There were no significant main effects of crop or nematicide observed on cotton lint yield in 2018.
Effects of irrigation, crop phase, and nematicide application on cotton seed yield and lint yield (kg/ha).
2017a | 2018 | |||
---|---|---|---|---|
Seed yield | Lint yield | Seed yield | Lint yield | |
ANOVA ( |
||||
Irrigation (I) | 0.50 | 0.32 | 0.06 | 0.31 |
Crop phase (C) | 0.01** | 0.01** | 0.19 | 0.41 |
I × C | 0.64 | 0.72 | 0.53 | 0.62 |
Nematicide (N) | < 0.01** | < 0.01** | 0.03* | 0.06 |
I × N | 0.81 | 0.79 | 0.40 | 0.65 |
C × N | 0.01** | 0.09 | 0.05* | 0.07 |
I × C × N | 0.45 | 0.58 | 0.07 | 0.22 |
* and ** represent significant effects at
Sod-based rotation managed RN populations better than conventional rotation. Our results were consistent with other research regarding greater RN population density in rotations with at least two years of cotton than those with more non-host crops (Cabanillas et al., 1999; Leach et al., 2012). A study by Davis et al. (2003) showed that effects of crop rotation on RN population density were undetectable by midseason when cotton was grown the following year. However, effects of crop rotation on RN population density at midseason were significant in our study, indicating that the populations were responding to specific crop phases, with the sod-based cotton phase resulting in fewer RN than conventional cotton phases. Possible explanations for differences between these studies are that our research was part of a long-term rotation (i.e. the non-host rotation was longer) and the aforementioned study utilized field sites with RN-resistant soybean in the crop rotation sequence. In this study, reproduction factor was greatest in sod-based cotton because initial RN population density was least in that phase. When growing a host crop, the lower the nematode population density is to begin with, the greater the reproductive potential, particularly following a non-host crop (Cabanillas et al., 1999). Therefore, bahiagrass and peanut helped reduce the initial population densities of RN in our study.
Little is known about RN sex ratios (i.e. proportions of females, juveniles, and males) throughout a growing season, although some studies estimate that these life stages exist in relatively equal numbers in the soil (Bird, 1983; Nakasono, 1966; Koenning et al., 2004). Nematode sex ratios may be influenced by environmental factors like food availability and temperature (Wright and Perry, 2006). In this study, RN sex ratios also followed this concept as the ratio of RN immature females and juveniles to males was greatest in second-year cotton before planting since that phase was the only one in which a host crop had been grown the previous year. At the end of the year, ratios of RN immature females and juveniles to males were greatest in sod-based cotton because the reproductive factor was greatest in that phase. Nakasono (2004) suggested that more RN males in relation to females could result from greater female death rate in the soil. In crop stress-inducing environments, such as rotations with non-host crops like SBR, the ratio of RN immature females and juveniles to males may be closer to one (i.e. equal numbers of males and immature females/juveniles) and in environments more favorable to the parasite, the ratio may be greater. It is important to understand RN sex ratios in order to estimate reproductive potential of RN populations in the soil. Another RN sex ratio study left out nematodes that are continuing their life cycles (i.e. maturing females) because they reside within cotton roots (Moore et al., 2010). We recognize information from sedentary females is missing in our RN sex ratio calculations, but the intent was to observe what happened with vermiform life stages in the soil. These ratios are important because they indicate RN reproductive favorability, and results of this study show that crop rotation systems affect these ratios reflecting RN reproductive capacity in the given environment.
Sod-based rotation increased populations of other plant-parasitic nematodes at the site, including spiral and ring nematodes. Because these nematodes have such broad host ranges, rotation, and cover crops may not be successful in managing their populations. Additionally, they are of minor importance in cotton production (Blasingame et al., 2002). It appears that sod-based rotation supported populations of both ring and spiral nematodes. Ring nematode population density was greatest in sod-based cotton, which was consistent with results from Tsigbey et al. (2009), where SBR reduced RN population density in peanut phases, but increased ring nematode population density compared to the conventional rotation. Our results differed in terms of spiral nematode population density, in which Tsigbey et al. (2009) reported a decrease in their numbers in sod-based rotation while we observed an increase. Bahiagrass is a poor host for RN but appears to be a suitable host for spiral nematodes (Andersen et al., 2016).
Fluopyram nematicide was not effective for managing plant-parasitic nematode populations at 50 or more days after planting in this study as it had no effect on ring nematode population density and increased spiral and RN population densities at various times compared with untreated control. Previous studies have found that fluopyram can be effective against other nematodes, including root-knot nematodes on vegetables (Hajihassani et al., 2019; Ji et al., 2019; Silva et al., 2019) and cotton (Roper, 2017) as well as a mixture of sting nematode (
The main hypothesis in this study was ‘yield impact of nematicide application will be greater in conventional than sod-based rotation due to greater nematode pressure in conventional than sod-based rotation.’ This hypothesis was partially supported by our results. In 2017, nematicide protection from crop damage in terms of cotton seed yield was greater in conventional than sod-based rotation, which supports the hypothesis. However, in 2018 there was no benefit for cotton seed yield or lint yield with nematicide application in any rotation. Additionally, nematicide application increased lint yield equally in both rotations in 2017. This does not support our hypothesis. The positioning of the nematicide application in-furrow and its strong binding activity to soil suggests that fluopyram may only be effective in a relatively small zone (Faske and Hurd, 2015). Cotton in a conventional rotation may have smaller root systems with more roots located within the fluopyram-treated zone. Sod-based rotation results in cotton with a larger root system that likely developed deep roots (outside of the fluopyram-treated zone) and may explain the nematode populations observed in this study (Dourte et al., 2015). This larger root system may have allowed the plant to compensate for nematode damage. Furthermore, according to the Florida Automated Weather Network, cotton received adequate rainfall in both 2017 and 2018 (78 cm and 71.5 cm, respectively), so drought stress was not evident and helps explain the lack of observed yield effect in irrigated versus rainfed plots. Ultimately, nematicide application was ineffective at reducing nematode population densities and inconsistent in improving yield in this research.
Cotton yield was generally greater in SBR than conventional rotation and corresponded with decreased RN population density in SBR relative to conventional rotation. This suggests that RN damage is involved in the yield decrease observed in SBR, but other factors are also likely to be involved. The threshold set by Blasingame et al. (2002) was exceeded in our study, with fall RN population density greater than 1,000 nematodes/100 cm3 soil in both rotations. Preceding crops can affect the yield of following crops through soil fertility, allelochemicals, and other agronomic factors aside from nematodes and these factors likely contributed to the yield benefit of SBR (Jacobs et al., 2018). Our results clearly show that rotation was more consistent for managing RN and increasing yield than nematicide. Crop rotation will continue to be a paramount nematode management strategy.
Irrigation generally did not affect nematode population densities. Our results were inconsistent with other research looking at irrigation. Moore and Lawrence (2013) showed that RN population density was greater under irrigation, but their study evaluated soil types and not crop rotation or nematicide application. Additionally, population density of
In summary, there is evidence that nematicide application can be reduced in a sod-based rotation. Nematicide yield impacts varied by RN pressure. Population density of RN decreased in sod-based rotation and cotton yield was greater than the conventional cotton. Furthermore, sod-based rotation increased population densities of ring and spiral nematodes. Although nematicide application increased 2017 yield in second-year conventional cotton, it did not increase yield in sod-based cotton or first-year conventional cotton. This indicates that nematicide was more effective in the conventional rotation regarding yield. From a practical standpoint, a grower adopting a sod-based cotton rotation may be able to reduce or eliminate nematicide application while achieving desirable yield goals.