Abstract
Tomato bacterial wilt caused by Ralstonia solanacearum bacterium is a severe problem in Southern China, where relatively high environmental temperatures commonly prevails during the crop seasons. Previous research has indicated that bacterial wilt disease incidence generally increases during the warm months of summer leading to reduced tomato yield. Moreover, the efficacy of bio-organic fertilizers (BOFs)–organic compost fortified with pathogen-suppressive bacteria—is often lost during the periods of high environmental temperatures. Here we studied if the disease incidence could be reduced and the BOF performance enhanced by simply preponing and postponing the traditional seedling transplantation times to avoid tomato plant development during periods of high environmental temperature. To this end, a continuous, two-year field experiment was conducted to evaluate the performance of BOF in two traditional (late-spring [LS] and early-autumn [EA]) and two alternative (early-spring [ES] and late-autumn [LA]) crop seasons. We found that changing the transplantation times reduced the mean disease incidence from 33.9% (LS) and 54.7% (EA) to 11.1% (ES) and 7.1% (LA), respectively. Reduction in disease incidence correlated with the reduction in R. Solanacearum pathogen density in the tomato plant rhizosphere and stem base. Applying BOF during alternative transplantation treatments improved biocontrol efficiency from 43.4% (LS) and 3.1% (EA) to 67.4% (ES) and 64.8% (LA). On average, the mean maximum air temperatures were positively correlated with the disease incidence, and negatively correlated with the BOF biocontrol efficacy over the crop seasons. Crucially, even though preponing the transplantation time reduced the tomato yield in general, it was still economically more profitable compared to LS season due to reduced crop losses and relatively higher market prices. Preponing and postponing traditional tomato transplantation times to cooler periods could thus offer simple but effective way to control R. solanacearum disease outbreaks.
Introduction
Bacterial wilt is one of the most devastating diseases of tomato in tropical and subtropical regions of the world. It is caused by the Ralstonia solanacearum (Smith) species complex, which is a soil-borne pathogen notorious for its virulence, broad host range, and wide geographic distribution [1]. Moreover, once successfully invaded to tomato fields, eradication of R. solanacearum is very difficult, because it can survive in soil, water or reservoir plants for long periods before coming into contact with a new host [2]. The disease process is very complex and involves several stages, which are dependent on environmental conditions, the physiological state of the pathogen, and the host. Ultimately, pathogen invades host vascular tissues, where it multiplies until it blocks the xylem and causes wilt symptoms. To control the disease, integrated control strategies that prevent pathogen invasion in the roots and the above-ground parts of host plants has been suggested [3–5]. These strategies include liming, fertilization, crop rotation and chemical controls [6,7]. Unfortunately, these strategies are often unable to reduce crop losses down to tolerable levels. Moreover, although chemical soil disinfection can temporarily eradicate most microbial flora, pesticide-resistant pathogens may rebound leading to ever more problematic disease outbreaks [7,8].
Environmentally friendly alternatives for pesticides, such as bio-organic fertilizers (BOFs), have been developed to better control soil-borne diseases [9]. BOFs are prime examples of next-generation sustainable agriculture. They are manufactured from agricultural waste products and thus reduce environmental pollution. Application of BOF could reduce the amount of inorganic fertilizer needed in crop production. Furthermore, BOFs can be fortified with some specific antagonistic microorganisms that suppress target pathogens in the soil [10]. Thus far, BOFs have been reported to be efficient in controlling soil-borne diseases, such as Fusarium wilt, damping off, bacterial wilt, and black shank [11,12]. However, the biocontrol effects of BOFs on tomato bacterial wilt have been inconsistent in field trials and it is thought that the environmental temperature could affect the efficacy of disease suppression by BOFs [13–16].
Environmental temperature could drive bacterial wilt outbreaks by directly affecting the pathogen invasion success [16]. For example, elevated temperatures have been found to increase the severity of bacterial wilt in R. solanacearum-resistant tomato plants in environmental chambers [16]. Moreover, pathogen density and disease incidence have been shown to correlate positively in two-year long field experiments with tomato [17,18]. However, even though some R. solanacearum biovars are specialized to cause bacterial wilt in high environmental temperatures [16], lots of inter-strain variation exists [19]. For example, Race 3, Biovar 2 (R3B2) strains can cause bacterial wilt in potatoes at temperatures as low as 16°C [20]. Besides having effect on pathogen, elevated temperatures could also affect the biocontrol efficacy of bio-organic fertilizers. Bacterial species belonging to genus Bacillus are commonly used as biocontrol agents because they are able to inhibit wide array of pathogenic microorganisms via production of antibacterial and antifungal compounds [21,22]. The production of antibiotic molecules by Bacillus bacteria depends on the environmental temperature, which could thus affect the efficacy of BOFs [16]. Furthermore, plant immune response to pathogens can differ depending on the environmental temperature [23,24], which could also affect the pathogen invasion success.
Here we focused on testing a simple ecological approach to reduce crop losses: preponing and postponing traditional transplantation times to avoid tomato plant development during periods of high environmental temperatures when the risk of bacterial wilt outbreak is highest and when the BOF biocontrol efficacy is the lowest [25]. Typical spring and autumn crop seasons in Nanjing last from February to June and from July to November, respectively, and tomato crop losses are especially high during relatively warmer autumn season [16]. We hypothesized that earlier and later transplantation times should result in lower bacterial wilt incidence if the pathogen growth in the soil and tomato stem is suppressed by lower temperature during crop season. Moreover, lower mean temperatures could potentially increase the efficiency of BOF biocontrol [16] and decrease the bacterial wilt disease incidence even further. To study this hypothesis, we set up a two-year long field experiment where we manipulated the transplantation time of both spring and autumn seasons. Specifically, we preposed the transplantation time of spring season with ~2–2.5 months and postponed the transplantation time of autumn season with ~1–1.5 months and compared these treatments with traditional spring and autumn transplantation times. To study how BOF biocontrol efficacy depended on the transplantation time, half of the plants were treated with BOF at seedling phase and other half were left untreated. Pathogen infection was let to occur naturally as the field has previously been shown to be contaminated by R. solanacearum race 1 biovar 3 on the basis of pathogen host range and carbon utilization patterns [16]. Bacterial wilt incidences were recorded in the end of all crop seasons, R. solanacearum pathogen densities measured both in the rhizosphere soil and in the tomato plant stems and average tomato yield and farmer income estimated for each year per every treatment.
Materials and Methods
Preparation of bio-organic fertilizer (BOF)
A BOF was prepared as described by Wei et al. [16], with some modifications. In the previous study, we used both rapeseed cake compost (RCC) and pig manure compost as a carrier mixture [16]. Further research has shown that pig manure compost facilitates R. solanacearum growth, whereas RCC inhibits it. As a result, only rapeseed cake compost was used in this study. The compost was fortified with Bacillus amyloliquefaciens QL–18 strain, which has previously been shown to be antagonist against R. solanacearum [16]. The B. amyloliquefaciens QL–18 strain was provided by the Jiangsu Provincial Key Lab of Organic Solid Waste Utilization and it was routinely cultured on LB medium plates [16]. The final concentration of QL–18 in the fortified RCC was approximately 109 cells (CFU) g−1 and this final mixture was designated as BOF.
Field experiment
The field experiment study site (no other specific permissions were required for these locations, and the field studies did not involve endangered or protected species) is located in the town of Qilin (118° 57' E, 32° 03' N; previously described in detail in Wei et al. [16]). Qilin is an important vegetable production base for nearby urban population of Nanjing, China. Recently, bacterial wilt of tomato has become a widespread problem in Qilin. Two tomato (Solanum lycopersicum Mill) crops can be grown per year at this location. For this study, we chose early- and late-spring crop seasons (ES and LS) and early- and late-autumn crop seasons (EA and LA), as shown in S1 Table. The tomato seedlings (cultivar Hezuo 903) were first grown in nursery trays for 30 (autumn) or 45 (spring) days before transplantation to the field. Tomato seedlings were grown with a nursery substrate (commercially available from Huaian Agricultural Technological Development Ltd., Huanyin, Jiangsu, China). Half of the seedlings received 1% (w/w) of BOF, which was mixed with the nursery substrate before sowing. The other half of the seedlings did not receive BOF and were assigned to the control treatment. BOF was not reapplied when the plants were transferred to the field.
Field trials were conducted during two consecutive years from January 2011 to December 2012. No pesticides were used and standard chemical fertilization was applied. Four different transplantation treatments were used (ES, LS, EA and LA) and every transplantation treatment was further divided into BOF and no-BOF (control) treatments for each year (total of 8 treatments per year). The trial was conducted following a randomized block design within every crop season treatment. Five independent replicate plots (blocks) were used for both no-BOF and BOF treatments in random block design and 108 plants were planted per each plot (1.8×9 m area). Within each plot, plants were spaced evenly at approximately 30 cm apart into 4 rows each containing 27 plants. Pathogen infection was let to occur naturally as the field has previously been shown to be contaminated by R. solanacearum [16]. Disease development was expressed as the disease incidence (DI), which denotes the percentage of wilted plants on the first day of the harvest (S1 Table). The decision to focus only on one time point was made based on our previous experience on Ralstonia wilt disease development: most damage will take place before the first date of harvest and subsequent wilting has only minor effect on tomato yield. The biocontrol efficacy (BCE) of treatment with BOF was calculated for each crop season using the following equation: BCE = (DI of control treatment—DI of BOF treatment) / DI of control treatment × 100%.
Measuring R. solanacearum densities in tomato plant rhizosphere and stem base
To determine R. solanacearum densities, rhizosphere soils were collected from three randomly selected tomato plants per plot on the first day of harvest. Excess soil was gently shaken from the roots, and the remaining soil that adhered closely to the roots was considered as rhizosphere soil. Five grams of rhizosphere soil was added to 45 mL of sterilized water and shaken for 30 min on a rotary shaker. Several 10-fold dilutions were made, and 0.1-mL aliquots were spread on the surface of modified semi-selective medium (M-SMSA) [16]. After 3 days of incubation at 30°C, bacterial densities were measured as the number of colonies per gram of soil (CFU g−1 dry soil) and expressed in log10 units. To determine R. solanacearum densities within the aboveground plant parts, fresh stem-base samples were collected from 2 plants per treatment replicate during the year 2011 (total of 8 to 11 sampling time points depending on the crop season). Collected plants were chosen randomly at every sampling time point. Fresh segments (~1.5 to 2.0 cm) of the stem-base surface were first sterilized by dipping into 95% alcohol and flamed for 5 s. The efficiency of surface sterilization was confirmed by placing the treated parts of the stems for five minutes on a CPG plate [16] and incubating at 30°C for two days. Complete surface sterilization was achieved with this method as no visible colonies were observed on plates after two days of incubation. The segments (~1 cm) were weighed, ground and mixed into 9 mL of sterilized water. Homogenates were then diluted 10-fold and plated on M-SMSA medium. After 3 days of incubation at 30°C, bacterial densities were measured as the number of colonies per gram of stem (CFU g−1 fresh weight) and expressed in log10 units.
Statistical analysis
Daily maximum air temperatures were obtained from Weather Online (http://www.weatheronline.co.uk/). The mean maximum temperature during each crop season was defined as T cs and the mean maximum temperature during each 10-day period after transplantation as T 10. DI data were analyzed with two-way and three-way ANOVAs with SigmaPlot 11.0 (Systat Software Inc., USA) where year, transplantation treatment and BOF treatment were used as explanatory variables. Similarly, crop season mean temperature and bacterial density data were analyzed with ANOVA as described above. Bacterial density data were log10-transformed before the analyses and only last sampling time point was used for analyzing bacterial densities in tomato stem base at year 2011. In all above analyses, replicate plot was included in the models as a blocking factor. Because different blocks were used between years 2011 and 2012, blocking factor × year interaction was also included in these models. Nonlinear regression analyses (Sigmoidal, Sigmoid, 3 Parameter) were used to analyze the relationships between DI and T cs, DI and BCE and DI and T cs, and to explain R. solanacearum density dynamics in tomato stems with T 10.
Results
Environmental air temperature dynamics in different transplantation treatments
The air temperature dynamics differed significantly between transplantation treatments (Fig 1). In general, T 10 increased in ES and LS treatments over time and decreased in EA and LA treatments. The air temperatures were most of the time below 25°C in ES and LA but above 25°C in LS and EA treatments. The T cs of the ES, LS, EA, and LA in 2011 and 2012 were 12.8~14.9°C, 24.9~26.0°C, 26.7~28.0°C, and 19.9~22.0°C, respectively.
The effect of transplantation treatment on disease incidence and BOF biocontrol efficacy
The disease incidence (DI) was significantly higher in traditional LS and EA transplantation treatments compared to experimental ES and LA transplantation treatments in the absence of BOF: DI for LS and EA crop seasons: 28.1~39.3% and 45~70%; DI for ES (6.8~16.3%) and LA (5.0~9.4%) treatments (Fig 2A, Table 1). Similarly, the biocontrol efficacy of BOF was significantly higher in experimental ES and LA transplantation treatments compared to traditional LS transplantation treatment: efficacy for ES and LA: 63.2~71.6% and 63.0~66.7% and efficacy for LS: 43.1~43.6%. BOF had no biocontrol effect in EA treatment (1.4~4.8%; non-significant; Fig 2A, Table 1). Trends of DI and the biocontrol efficacy of BOF were similar between different years (Fig 2A and Table 1).
Table 1. The effect of transplantation treatment, BOF treatment on bacterial wilt incidence, biocontrol efficacy of BOF and R. solanacearum densities in the rhizosphere soils and stems of tomato plants.
Source | SS | df | MS | F | P | SS | df | MS | F | P |
---|---|---|---|---|---|---|---|---|---|---|
Dependent Variable | Disease incidence | Biocontrol efficacy | ||||||||
Corrected Model | 32430.288 | 23 | 1410.013 | 89.623 | <0.0001 | 27452.725 | 15 | 1830.182 | 22.804 | <0.0001 |
Intercept | 42810.161 | 1 | 42810.161 | 2721.082 | <0.0001 | 79769.414 | 1 | 79769.414 | 993.919 | <0.0001 |
Year | 1.763 | 1 | 1.763 | 0.112 | 0.739 | 162.885 | 1 | 162.885 | 2.030 | 0.167 |
Transplantation | 30792.788 | 3 | 10264.263 | 652.413 | <0.0001 | 26509.593 | 3 | 8836.531 | 110.102 | <0.0001 |
BOF | 1019.771 | 1 | 1019.771 | 64.818 | <0.0001 | |||||
Block | 58.369 | 4 | 14.592 | 0.928 | 0.455 | 247.227 | 4 | 61.807 | 0.770 | 0.555 |
Transplantation × BOF | 465.991 | 3 | 155.330 | 9.873 | <0.0001 | |||||
Year × BOF | 12.700 | 1 | 12.700 | 0.807 | 0.373 | |||||
Year × Transplantation | 27.749 | 3 | 9.250 | 0.588 | 0.625 | 79.056 | 3 | 26.352 | 0.328 | 0.805 |
Year × Block | 46.064 | 4 | 11.516 | 0.732 | 0.574 | 453.965 | 4 | 113.491 | 1.414 | 0.260 |
Year × Transplantation × BOF | 5.093 | 3 | 1.698 | 0.108 | 0.955 | |||||
Error | 881.035 | 56 | 15.733 | 1926.179 | 24 | 80.257 | ||||
Total | 761212.484 | 80 | 109148.318 | 40 | ||||||
Corrected Total | 33311.323 | 79 | 29378.904 | 39 | ||||||
R Squared | 0.974 (Adjusted value, 0.963) | 0.934 (Adjusted value, 0.893) | ||||||||
Dependent Variable | Ralstonia solanacearum densities in rhizosphere | Ralstonia solanacearum densities in stem | ||||||||
Corrected Model | 0.109 | 23 | 0.005 | 52.060 | <0.0001 | 282.845 | 11 | 25.713 | 7.266 | <0.0001 |
Intercept | 55.147 | 1 | 55.147 | 603519.084 | <0.0001 | 3001.740 | 1 | 3001.740 | 848.174 | <0.0001 |
Year | 0.001 | 1 | 0.001 | 8.562 | 0.005 | |||||
Transplantation | 0.087 | 3 | 0.029 | 317.395 | <0.0001 | 197.311 | 3 | 65.770 | 18.584 | <0.0001 |
BOF | 0.014 | 1 | 0.014 | 155.985 | <0.0001 | 37.565 | 1 | 37.565 | 10.615 | 0.002 |
Block | <0.0001 | 4 | 4.244E-05 | 0.464 | 0.762 | 19.175 | 4 | 4.794 | 1.355 | 0.259 |
Transplantation × BOF | 0.004 | 3 | 0.001 | 14.917 | <0.0001 | |||||
Year × BOF | 0.001 | 1 | 0.001 | 11.229 | 0.001 | |||||
Year × Transplantation | 0.001 | 3 | <0.0001 | 4.915 | 0.004 | |||||
Year × Block | 0.001 | 4 | <0.0001 | 1.892 | 0.125 | |||||
Year × Transplantation × BOF | <0.0001 | 3 | 4.576E-05 | 0.501 | 0.683 | 28.793 | 3 | 9.598 | 2.712 | 0.052 |
Error | 0.005 | 56 | 9.138E-05 | 240.656 | 68 | 3.539 | ||||
Total | 55.262 | 80 | 3525.241 | 80 | ||||||
Corrected Total | 0.115 | 79 | 523.501 | 79 | ||||||
R Squared | 0.955 (Adjusted value, 0.937) | 0.540 (Adjusted value, 0.466) |
R. solanacearum densities in tomato rhizosphere
R. solanacearum densities in the rhizosphere of BOF-treated plants were significantly lower in the ES, LS, and LA seasons in 2011 and 2012 compared to control plots (Fig 2B, Table 1). The lowest R. solanacearum densities (5.8 log10 CFU g−1 of dry soil) were observed in BOF-treated plants in the LA transplantation treatment (Fig 2B). A positive correlation (P < 0.0001) was observed between the R. solanacearum densities in rhizosphere soil and the DI, regardless of whether the analyzed plants were treated untreated with BOF (S1 Fig). Consistent with DI data, BOF effect on R. solanacearum densities was not significant in EA treatment both in 2011 and 2012, and in LA treatment in 2012 (Fig 2B, Table 1). The trends of R. solanacearum densities were similar for all four transplantation treatments. The densities were the highest in LS treatment and the lowest in LA treatment (Fig 2B).
R. solanacearum densities in tomato plant stems
The R. solanacearum densities in the tomato stems were affected by both transplantation and BOF treatments (Fig 3, Table 1). In the ES treatment (Fig 3A), T 10 stayed below 18°C until 70 days after transplantation, and no R. solanacearum was detected in either BOF-treated or untreated plants. Once T 10 exceeded 20°C, R. solanacearum densities increased sharply. Pathogen densities were reduced approximately 50% in BOF-treated plants: 6.21 log10 CFU g−1 versus 3.16 log10 CFU g−1 bacteria per fresh weight of stem for control and BOF-treated plants, respectively. In the LS treatment (Fig 3B), T 10 increased from 20 to 31°C 20 d after transplantation and R. solanacearum densities increased quickly during this period. Finally, we observed 8.04 log10 CFU g−1 and 6.08 log10 CFU g−1 bacteria per fresh weight of stem for control and BOF-treated plants, respectively. In the EA treatment (Fig 3C), T 10 was above 25°C throughout the first 70 days after transplantation, and R. solanacearum densities increased sharply during this period. During the final 20 days, T 10 remained below 25°C and R. solanacearum densities increased only slightly. Pathogen densities reached approximately 8.0 log10 CFU g−1 bacteria per fresh weight of stem in both control and BOF-treatments. In the LA treatment (Fig 3D), T 10 was above 20°C throughout the first 70 days after transplantation and decreased sharply below 10°C for the final 20 days. The R. solanacearum density dynamics were similar to those in the EA treatment, with the exception that R. solanacearum densities were generally lower.
Correlation between disease incidence and temperature variation in different experimental treatments
The T cs correlated significantly with both DI (R = 0.9431, P < 0.0001, positive correlation) and BCE (R = -0.9086, P < 0.0001; negative correlation Fig 4). When T cs ranged from 12°C to 23°C, the DIs in both control and BOF-treated plants were approximately 10%, while the BOF biocontrol efficacy ranged from 60% to 70% (Fig 4). As T cs increased to 26°C, the DI increased to approximately 35%, and the BCE decreased to 45% (Fig 4). When T cs exceeded 28°C, the DI increased to 55%. Under such conditions, BOF lost its biocontrol efficacy (Fig 4).
The effect of transplantation and BOF treatments on tomato plant yield and income
Transplanting time and BOF application both had significant effects on the tomato yield and farmer income (Tables 2 and 3). While preponing transplantation time from LS to ES decreased tomato yield, postponing transplantation time from EA to LA increased tomato yield (Tables 2 and 3). Despite the reduced yield of ES treatment, farmer earnings were compensated by higher tomato prices leading to higher total income (Table 2). Applying BOF generally increased both the yield and income except for the EA transplantation treatment (Table 2).
Table 2. The effect of transplantation time and BOF treatment on tomato yield and farmer’s income (means ± SEM).
Price (RMB kg−1) | Actual Yield (ton ha−1) | Income (103 RMB ha−1) | ||||
---|---|---|---|---|---|---|
Control | BOF | Control | BOF | |||
2011 | ES | 5.0 | 38.39±0.96 | 42.41±0.36 | 191.95±4.82 | 212.03±1.79 |
LS | 3.0 | 49.88±2.71 | 61.28±1.30 | 149.63±8.12 | 183.83±3.90 | |
EA | 4.0 | 38.33±5.48 | 40.53±4.93 | 153.30±21.92 | 162.12±19.7 | |
LA | 4.0 | 55.50±1.03 | 58.50±0.38 | 222.00±4.11 | 234.00±1.5 | |
2012 | ES | 5.5 | 43.44±0.86 | 46.32±0.45 | 238.92±4.72 | 254.76±2.50 |
LS | 3.5 | 53.30±3.49 | 64.80±2.73 | 186.55±12.22 | 226.80±9.55 | |
EA | 4.5 | 39.60±8.13 | 40.26±4.12 | 178.20±36.58 | 181.17±18.55 | |
LA | 4.5 | 59.68±0.95 | 62.40±0.49 | 268.56±4.30 | 280.80±2.20 |
Table 3. The effect of transplantation time, BOF treatments and Blocks on tomato yield and income.
Dependent Variable | Actual Yield | Income | ||||||||
---|---|---|---|---|---|---|---|---|---|---|
Source | SS | df | MS | F | P | SS | df | MS | F | P |
Corrected Model | 0.549 | 23 | 0.024 | 17.558 | <0.0001 | 0.566 | 23 | 0.025 | 18.079 | <0.0001 |
Intercept | 1757.647 | 1 | 1757.647 | 1292360.971 | <0.0001 | 2254.544 | 1 | 2254.544 | 1656887.829 | <0.0001 |
Year | 0.014 | 1 | 0.014 | 10.278 | 0.002 | 0.125 | 1 | 0.125 | 91.993 | <0.0001 |
Transplantation | 0.473 | 3 | 0.158 | 115.966 | <0.0001 | 0.379 | 3 | 0.126 | 92.790 | <0.0001 |
BOF | 0.034 | 1 | 0.034 | 24.723 | <0.0001 | 0.034 | 1 | 0.034 | 24.693 | <0.0001 |
Block | 0.005 | 4 | 0.001 | 0.932 | 0.452 | 0.005 | 4 | 0.001 | 0.933 | 0.452 |
Transplantation × BOF | 0.015 | 3 | 0.005 | 3.736 | 0.016 | 0.015 | 3 | 0.005 | 3.735 | 0.016 |
Year × BOF | <0.0001 | 1 | <0.0001 | 0.284 | 0.596 | <0.0001 | 1 | <0.0001 | 0.284 | 0.596 |
Year × Transplantation | 0.005 | 3 | 0.002 | 1.122 | 0.348 | 0.004 | 3 | 0.001 | 1.062 | 0.373 |
Year × Block | 0.003 | 4 | 0.001 | 0.566 | 0.688 | 0.003 | 4 | 0.001 | 0.565 | 0.689 |
Year × Transplantation × BOF | <0.0001 | 3 | 4.09E-05 | 0.030 | 0.993 | <0.0001 | 3 | 4.084E-05 | 0.030 | 0.993 |
Error | 0.076 | 56 | 0.001 | 0.076 | 56 | 0.001 | ||||
Total | 1758.272 | 80 | 2255.186 | 80 | ||||||
Corrected Total | 0.625 | 79 | 0.642 | 79 | ||||||
R Squared | 0.878 (Adjusted value, 0.828) | 0.881 (Adjusted value, 0.833) |
Discussion
Here we studied experimentally if we can reduce bacterial wilt disease incidence and increase the BOF performance by simply altering the traditional seedling transplantation times of tomato. We found that both preponing and postponing traditional transplantation times to the cooler period significantly decreased bacterial wilt disease incidence, increased BOF biocontrol efficacy especially during the late-autumn crop season, and led to lower R. solanacearum pathogen densities in both tomato plant rhizosphere and tomato base stems. Correlation analyses indicated that these effects could be attributed to lower environmental temperatures during the experimental ES and LA crop seasons. Even though preponing transplantation time of spring crop season reduced the yield of tomato, this was financially compensated by relatively higher market prices leading to increased farmer income. Postponing transplantation time of autumn season increased both yield and farmer income. Altering traditional tomato transplantation times could thus offer simple but effective way to reduce bacterial wilt incidence and improve the effectiveness of BOF in the field setting.
Why did bacterial wilt incidence decrease with the lower environmental temperature? Several reports have shown that low temperatures can directly affect the virulence of R. solanacearum reducing or preventing the root colonization and invasion potentially via attenuated or lost twitching motility [26]. It has been also found that the expression of global virulence regulators, HrpG and HrpB, is temperature-regulated, and depending on the pathogen strain, can be positively correlated with increasing temperature [27,28]. Consistent with this, we observed a significantly positive correlation between mean crop season temperature and disease incidence. This suggests that high environmental temperature might be essential for triggering R. solanacearum virulence in the field. Temperature fluctuations are also known to affect R. solanacearum survival and persistence in the soil between different crop seasons. For example, Scherf et al. [28] reported that temperature fluctuations played a critical role for R. solanacearum R3B2 and native U.S. strain viability as both strains were able to survive at -20°C in infected geranium tissue for at least 6 months as long as the temperature was kept constant. In the present study, we observed relatively wider temperature fluctuations in experimental ES and LA transplantation treatments. As a result, occasional temperature drops below 18°C could have reduced pathogen viability, which could partly explain reduced disease incidence via lowered R. solanacearum densities in the soil.
Altering traditional tomato transplantation time also improved the efficacy of BOF biocontrol especially during the late-autumn crop season. B. amyloliquefaciens is able to produce broad-spectrum antibiotics that often protect plants either by directly antagonizing pathogens or indirectly by inducing systemic resistance in plants [29]. Establishment of such antagonists may then promote the root-colonization capacity of the antagonist and prevent the colonization of invading plant pathogens [30–32]. It has previously been shown that B. amyloliquefaciens exerts direct antagonism towards R. solanacearum in the laboratory conditions [13,33,34]. This could explain why BOF treated plants harbored generally lower R. solanacearum densities both in the soil rhizosphere and aboveground tomato stem base. However, BOF had no biocontrol efficacy during EA transplantation treatment. First, it is possible that elevated temperature directly reduced the biocontrol efficacy of Bacillus-fortified BOF. Earlier studies have shown that the production of antibiotic molecules by Bacillus bacteria depends on the environmental temperature [16]. Alternatively, elevated temperature could have affected R. solanacearum resistance to these antibiotics [23,24]. Even though pathogen densities in the EA rhizosphere were similar to other transplantation treatments, pathogen densities within the plant stems were the highest in the EA treatment. As a result, the BOF biocontrol efficacy could have depended on R. solanacearum density, resulting in more frequent pathogen invasion to xylem in EA transplantation treatment. While these hypotheses cannot be answered with the current data, additional experiments are on their way to study the role of elevated temperature for BOF biocontrol efficacy.
In addition to reducing bacterial wilt disease incidence, alternating traditional tomato transplantation times had positive effects on farmer total income. Even though preponing the tomato transplantation time in the spring season reduced the tomato yield, relatively higher tomato market prices were able to compensate the farmer income for the ES transplantation treatment. Postponing the autumn crop clearly increased tomato yield by reducing crop losses to bacterial wilt and by increasing BOF biocontrol efficacy. As a result, later transplantation time clearly increased farmer income during the second crop season. The late autumn crop was also preferred over the early spring crop, because early transplantation time overlapped with Chinese New Year. Even though some between-year variation was observed, the significant effect of transplanting time was similar over the two-year trial period. This has convinced the farmer who participated in this study to exclusively apply LA transplantation time for the second tomato crop.
In conclusion, our results demonstrate that simple alteration of tomato transplantation time to cooler periods can considerably lower bacterial wilt disease incidence. In addition to having positive immediate effects on tomato yield and the farmer’s income, reducing pathogen densities in the soil is likely to have positive long-term effects via reduced disease outbreak risk in the future. Postponing transplantation time also increased the BOF biocontrol efficacy, which suggests that biocontrol agents might be also affected by environmental temperature. We hope to resolve more detailed mechanisms behind temperature and pathogen-host and pathogen-biocontrol agent interactions in the future.
Supporting Information
Acknowledgments
We would like to thank the students and farmers who helped with fieldwork in Qilin Town of Nanjing city. We thank Prof. Shixue Yin for help preparing the manuscript, and two anonymous reviewers whose comments improved the manuscript.
Data Availability
All relevant data are within the paper and its Supporting Information files.
Funding Statement
This research was financially supported by the National Natural Science Foundation of China (41301262, Zhong Wei; 41471213, Yang-Chun Xu; and 31501837, Jian-Feng Huang), the National Science and Technology Support Program (2013BAD20B05, Zhong Wei), the Natural Science Foundation of Jiangsu Province (BK20130677, Zhong Wei), the China Postdoctoral Science Foundation (2013M541687, Zhong Wei), the Jiangsu Key Technology R&D Program (BE2014340, Yang-Chun Xu), Innovative Research Team Development Plan of the Ministry of Education of China (IRT1256, Qi-Rong Shen), and the Qing Lan Project (Yang-Chun Xu).
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