Phytochemical responses to herbicide exposure and effects on herbivorous insects

10. Relationships between herbicide treatment of host plants and the performance of herbivorous insects

10.1 Methods and materials
10.1.1 Pieris-Brassica test system
10.1.2 Gastrophysa-Fallopia test system
10.1.3 Sitobion-Triticum test system
10.1.4 Spraying procedure
10.1.5 Statistical analyses
10.2 Results
10.2.1 Pieris
10.2.2 Gastrophysa
10.2.3 Sitobion
10.3 Discussion

The present chapter tests whether the negative effects on leaf chewing herbivores found in the literature are a general phenomenon or it is characteristic for the specific plant-herbivore pair and the compound tested. Therefore, the present study evaluates three insect/plant interaction systems for their susceptibility to sulfonylurea herbicides. The three test systems are representative of species which could be exposed to sulfonylurea herbicides due to spray drift into other crops or into semi-natural habitats. The organism pairs used are Pieris brassicae/Brassica napus (hereafter Pieris), G. polygoni/F. convolvulus (hereafter Gastrophysa), and Sitobion avenae/Triticum aestivium (hereafter Sitobion), respectively. The test design differs between systems due to their different feeding guilds.

10.1 Methods and Materials

10.1.1 Pieris-Brassica test system

Brassica napus is an annual plant (either spring or winter annual). This species occurs both as crop, weed, and wild species with scattered distribution in disturbed habitats. Pieris brassicae is a pierid butterfly. The larvae feed mainly on plants of the Brassica family (Feltwell, 1982) and prefer foliage for consumption in all life stages. The egg clutches are normally so large that the host plant is totally defoliated and the larvae are forced to migrate to other host plants in order to complete larval development (Davies and Gilbert, 1985). This species pair may experience herbicide effects both in natural habitats and in crops exposed to spray drift from adjacent fields. Both acute and chronic tests were conducted with the insects.

10.1.1.1 Insect bioassay

Brassica napus in the vegetative stage (i.e. possessing 4 true leaves) was sprayed with herbicide. Four days after spraying, 20 newly hatched larvae of Pieris brassicae were placed on each of the plants. After four days, the weight gain and survival of the larvae were assessed. Each dosage consisted of three independently prepared replicates of three samples each (spray dosages and used pesticides are presented in Table 1). At the day of placing larvae on the plants, a randomised sample of 40 larvae was collected in order to measure the average size of the experimental animals. The fresh and dry weights of these animals were measured as eight samples of five individuals each. The experiments were conducted in a controlled-environment-chamber administered at 20°C, 70% RH, and 16 h photoperiod. Living specimens were counted daily, and on day 8 after spraying, the weight of the larvae was measured. This time span was chosen because a pilot experiment had shown that plants at the higher dosages loose their leaves shortly after this point in time. Survival was estimated as the fraction of larvae remaining on the plant on day 4 after placing the larvae on the plant in relation to the numbers present after one day. This was done because a single experiment (chlorsulfuron) lost a good deal of specimens over the first 24 hours even in the control treatment. Subsequently, this was examined in a small experiment, which showed that within a short time span of 1-2 hours after hatching the larvae are vulnerable to handling. The procedure of applying larvae to the plants was hereafter altered, and larval disappearance was avoided in the remaining experiments.

In a long-term (chronic) experiment, larvae were allowed to complete larval development. Brassica napus plants were sprayed in the vegetative stage (i.e. possessing 4 true leaves) with the sulfonylurea-herbicide metsulfuron-methyl at different dosages, i.e. 0, 0.05, 0.1 and 0.2 times the recommended field rate. Four days after spraying, 20 newly hatched larvae of Pieris brassicae were placed on the sprayed plants. The experiments was conducted in a controlled-environment-chamber administered at 20°C, an RH of 70%, and a 16 h photo period. At the time when the larvae started to move on the plant these were moved to cages in a greenhouse cell and remained here for the rest of their development.

The survival of the larvae was registered throughout development, and developmental time from egg hatch to adult stage was measured. Hereafter, biomass of the adults was determined.

10.1.1.2 Plant bioassay

Simultaneously with the acute insect bioassay, host plants without larvae were treated with the herbicides to assess effects on the plants. The set-up was similar with respect to soil type, temperature, etc., but the plants were treated with a broader range of dosages, in order to a establish dose - response relation for the plants. The plants were treated when they possessed four leaves. Each treatment dosage was sprayed in three independently prepared replicates with three plants per replicate. At the time of spraying, 20 plants of similar size as the experimental plants were weighed, i.e. measures of root and shoot biomass (both dry and fresh weight). On the eighth day after spraying, the experimental plants were harvested, both shoot and root biomass (fresh and dry weight) was measured.

10.1.2 Gastrophysa-Fallopia test system

F. convolvulus is a strictly annual weed species. It often climbs adjacent crop plants. Under greenhouse conditions, the plant reproduces mainly by self-fertilisation. F. convolvulus has no leaf loss during development, but continues to grow until senescence, when all leaves die almost synchronously and the seeds ripen. Details of the life cycle of F. convolvulus are presented by (Hume et al., 1983). Plants for experiments and insect food were grown in pots in a greenhouse. Seeds were harvested and stored cold to break dormancy before sowing. G. polygoni is a chrysomelid beetle utilising mainly two food plants, viz. F. convolvulus and Polygonum aviculare L. It eats the foliage of the plants in all three larval instars and as adults. The larvae pupate in the soil. The beetles were kept in culture on F. convolvulus plants at 20°C and 16 h photoperiod.

10.1.2.1 Insect bioassay

A controlled environment experiment was conducted to measure the suitability of herbicide-sprayed F. convolvulus plants as hosts for G. polygoni. Newly hatched larvae of G. polygoni were placed on leaves of plants subjected to different herbicide dosages. After spraying, the plants were caged singly in polystyrene cylinders and placed in a controlled-environment-chamber (photoperiod of 16 h, constant temperature of 20°C, relative humidity of 60%, and a photo flux density of 350 mE m-2 sec-1). One day after herbicide treatment, 20 newly hatched G. polygoni larvae were placed on the leaves of the plants. Each treatment was replicated four times. The larvae were placed on the lower side of leaves in the middle section of the plant according to the behaviour of ovipositing females (Kjær et al., 1998). Subsequently, the number of larvae and adults emerging after pupation were recorded every second or third day. When the adult beetles emerged, they were removed and weighed.

Plant bioassay

Simultaneously with the insect bioassay host plants without insects were treated with the herbicides to assess effects on the plants. The set-up was similar to the insect bioassay. At the time of spraying, shoot dry weight of seven plants of similar size as the experimental plants were measured. On day 16 after spraying, the experimental plants were harvested and shoot biomass was measured.

10.1.3 Sitobion-Triticum test system

Sitobion avenae is an aphid pest of cereal crops and sucks from the phloem of the host plants. This aphid prefers to feed in the upper part of the host plant, due to a better food quality (El-Sayed in Klingauf (1987)) ). Unlike broad-leaved weeds, cereal crops are tolerant to sulfonylurea herbicides. Therefore, no plant bioassay was performed. The difference between sensitive and tolerant species is based on their ability to metabolise the pesticide . It is possible that this metabolism evokes a reallocation of resources from storage organs to the leaves to the potential benefit of the aphids. It is therefore important to test if the use of herbicide may improve the performance of the aphids.

10.1.3.1 Insect bioassay

The effects of the sulfonylurea herbicide metsulfuron on the performance of the aphid Sitobion avenae were assessed in a feeding experiment in a controlled-environment-chamber (20°C, 16 h photoperiod and 20°C). Seeds of Triticum aestivium (var. Lambros) germinated in compost soil at 20°C. The day following herbicide treatment, one 0-24 h old aphid nymph was applied to each plant. Prior to application the nymphs were weighed. Plants and aphids were enclosed in glass cylinders (diameter of 5 cm) which were closed in the top with a 0.1 mm mesh. Hereafter, the aphids were observed two times a day to register developmental time until adult stage (D± 0.5 day). When the aphids had reached adult stage, they were weighed and placed on the plant again. Hereafter, the fecundity of the aphids were assessed in a period equal to two times the developmental time of the specific individual, i.e. D. Approximately halfway in this period all nymphs produced were killed so that the original adult could be recognised and nymph production from the F1-generation was avoided. Replicates in which the adult had disappeared were excluded from the measures of fecundity.

10.1.4 Spraying procedure

Pieris

Plants were sprayed with a pot sprayer designed for automatic and controlled spraying of larger plants (Kristensen pot sprayer, Ringsted, Denmark; l ´ w ´ h = 120 ´ 100 ´ 170 cm). Table 10.1 gives the tested herbicides and the actual dosages. The trial with chlorsulfuron was conducted with the surfactant Citowett (BASF) added to the spray solutions (0.5% v/v). Control plants were treated with water. The sprayer was equipped with two Hardi flat fan nozzles type 411014 separated by 53 cm and used at a working pressure of 2 bar. The sprayer was calibrated to deliver a spray volume of 200 l ha-1.

Table 10.1
Presentation of the dosages and herbicides used on the Pieris/Brassica system.

Herbicide

Spray dosages, insect bioassay (times recommended field ratea)

Spray dosages in plant bioassay
(times recommended field ratea)

Chlorsulfuron

0-0.025-0.05-0.1-0.2

0-0.025-0.05-0.1-0.2-0.4-0.8

Metsulfuron

0-0.025-0.05-0.1-0.2

0-0.0125-0.025-0.05-0.1-0.2-0.4-0.8

Tribenuron

0-0.25-0.5-1

0-0.25-0.50-0.75-1

alist of recommended field rates in Denmark for cereals: Chlorsulfuron 4 g a.i. ha-1; Metsulfuron 4 g a.i. ha-1; and Tribenuron 7.5 g a.i. ha-1.

10.1.4.1 Gastrophysa

Plants were sprayed with a pot sprayer at rates of 0-0.067-0.125-0.25-0.5 times the field rate. In Denmark, the recommended field rates for the selected sulfonylurea herbicides in cereals are as follows: Metsulfuron-methyl (Allyâ) 4 g a.i. ha-1; tribenuron (Expressâ) 7.5 g a.i. ha-1. The trial with metsulfuron-methyl was conducted with the surfactant Citowett (BASF) added to the spray solutions (0.5% v/v). Control plants were treated with water. The sprayer was equipped with Hardi flat fan nozzles type 411014 and used at a work pressure of 2 bar. The sprayer was calibrated to a spray volume of 200 l ha-1. The plants were treated when they had 4-6 true leaves. Each treatment dosage was sprayed in four independently prepared replicates with three plants per replicate, i.e. one for the insect bioassay and two for the plant bioassay.

10.1.4.2 Sitobion

The plants were treated with metsulfuron-methyl (Gropperâ DuPont (179 g metsulfuron kg-1)) and Citowett (BASF) (0.5% v/v) with a hand held spray atomizer when the plants were in growth stage 12 (Zadoks et al., 1974) with dosages of 0 and 7.16 g a.i. ha-1 (recommended field rate). Twenty-five replicates were established for each treatment. The spray atomiser was calibrated to give a specified amount of water per time unit, and the speed of the sprayer was adjusted so that the specified spray volume was delivered over the whole surface and the point of run-off was reached.

10.1.5 Statistical analyses

10.1.5.1Pieris and Gastrophysa

Effects of herbicide treatment on biomass, Relative Growth Rate (RGR), and survival were tested in an ANOVA, (GLM-procedure SAS, Type III SS) . If no first order interactions appeared significant, the test was repeated omitting interactions. Differences between means were tested in a Tukey HSD t-test. Comparisons between control treatment and single dosages were done by a Dunnett’s T test. The overall level of significance was 0.05.

Sitobion

Effects of metsulfuron-methyl treatment on developmental time (D), growth rate and fecundity were compared by means of paired t-tests. The overall level of significance was 0.05.

10.2 Results

10.2.1 Pieris

Acute test

The relative growth rate for oilseed rape plants treated with metsulfuron-methyl was significantly reduced for both shoots (One-way anova, df=7, F=8.26, p<0.0001) (Fig 10.1B) and roots (One-way anova, df=7, F=17.82, p<0.0001). The same was observed for shoots (One-way anova, df=4, F=3.25, p=0.021) and roots (One-way anova, df=4, F=15.48, p<0.0001) (Fig 10.1D) when plants were treated with tribenuron. Chlorsulfuron treated plants failed to show any significant reduction in shoot growth rate (One-way anova, df=6, F=0.38, p=0.8863), while root growth rate was significantly reduced with application rate (One-way anova, df=6, F=3.19, p=0.0092).

Figure 10.1
Response of Pieris brassicae (RGR and survival) and the host plant Brassica napus (RGR of roots and shoot) to treatment of the plant with selected sulfonylurea herbicides. Fig. A and B: Metsulfuron, Fig. C and D: Chlorsulfuron, and Fig. E and F: Tribenuron.

Insects

Survival was not affected by replicate, dosage or trial, i.e. no significant mortality/disappearance was observed for any of the tested herbicides (Two-way anova, df=19, F=0.71, p=0.8099) (Figure 10.1A, C, and E). The relative growth rate of the catepillars was significantly increased with dosage in the trial with metsulfuron-methyl-treated host plants (One-way anova, df=3, F=9.55, p<0.0001). No significant changes were observed for Pieris brassicae on plants treated with either chlorsulfuron (One-way anova, df=4, F=2.16, p=0.0917) or tribenuron (One-way anova, df=3, F=0.128, p=0.2168). However, a trend toward increased growth rate was observed when the host plant was treated with low dosages of chlorsulfuron.

Chronic test

Plants treated with 0.1 and 0.15 times the recommended field rate of metsulfuron-methyl lost all leaves before larval development was completed. The larvae placed on plants treated with 0.05 times the recommended field rate performed equally well as those on plants treated with water. No significant changes were observed for either developmental time, larval growth or hatching weight of the adults (t-test, Table 10.2).

Table 10.2
Performance of Pieris brassica feeding on Brassica napus sublethally treated with metsulfuron-methyl at a rate of 0.05 times the recommended field rate. Fresh weight of the larvae was measured on day 12 after being placed on the plants. Values given are mean ± Standard Error of Mean.

Variable

N

Untreated plants

N

Treated plants

Developmental time, days

77

25.88 ± 0.14

56

25.85 ± 0.20

Larval fresh weight, mg

80

451.2 ± 8.3

58

441.9 ± 13.3

Adult dry weight, mg

77

55 ± 3

56

52 ± 2

No significant differences between sprayed and unsprayed host plants were observed (t-test)

10.2.2 Gastrophysa

Black bindweed plants were negatively affected by the herbicide treatment (Fig. 10.2). A one-way anova revealed the following results for tribenuron (One-way anova, df=4, F=5.58, p=0.0008) and for metsulfuron (One-way anova, df=4, F=11.29, p<0.0001). Leaf beetle larvae developing on the treated plants did not show changes in developmental rate (larvae to adult) with treatment. At least, a regression analysis showed that developmental rate was not correlated to dosage (Tribenuron: Rate = 0.0005 ´ dosage + 19.35, r2 = 2 ´ 10-6. Metsulfuron: Rate = 21.35 - 1.39 ´ dosage, r2 = 0.057) The size of the hatched adult was not different between treated and control animals (One-way anova, Tribenuron: df=4, F=0.12, p=0.974, R2=0.0042, and Metsulfuron df=4, F=1.86, p=0.12, r2=0.048). Regression analysis revealed that survival of larvae to adult stage showed a non-significant trend towards reduced survival (tribenuron: Number survivors = 7.4 - 5.95 ´ dosage, r2 = 0.071, and metsulfuron: Number survivors = 9.03 - 7.07 ´ dosage, r2 = 0.168).

Figur 10.2
Effects of tribenuron (A) and metsulfuron (B) on the size of adult beetles (G. polygoni) upon pupal hatch and on the relative growth rate (RGR) of host plants (F. convolvulus).

10.2.3 Sitobion

The treatment of the host plant with metsulfuron did not change the performance of Sitobion avenae. A t-test between values for treated and untreated plants, respectively, did not reveal any significant changes in developmental speed, growth rate, size of adult or fecundity (Table 10.3).

Table 10.3
Aphid (Sitobion avenae) performance on herbicide treated and untreated host plants (Triticum aestivium). Values given are mean ± Standard Error of Mean. No significant differences were found between aphids on sprayed and unsprayed host plants (t-test)

Variable

N

Untreated plants

N

Treated plants

Developmental rate, D days

29

9.297± 0.140

32

9.258± 0.150

Relative growth rate

26

0.0476± 0.0029

33

0.0464± 0.0030

Fresh weight of adults, mg

26

0.486± 0.025

33

0.466± 0.025

Fecundity, # of nymphs

27

13.56± 0.76

33

15.33± 0.65


10.3 Discussion

It was the aim of this study to test if treatment with sulfonylurea herbicides can be expected to cause effects on herbivorous species living on treated plants. None of the insect/plant relationships studied showed a reduced performance of the herbivore on treated plants, and P. brassicae even had an incereased growth rate on plants treated with metsulfuron-methyl. Consequently, it must be concluded that the palability of the hosts was unchanged. The observed tendency to a reduced survival for G. polygoni indicates, however, that the effects observed for chlorsulfuron (Kjær and Elmegaard, 1996) may be expected also for these herbicides, if higher dosages are used. In Chapter 3 it was observed that the content of compounds 2 and 3 in plants treated with chlorsulfuron and with tribenuron were comparable. Therefore, similar effects were expected on the leaf beetle for the two herbicides. This was not the case, probably because the comparison was made on basis of full field rate in Chapter 3 whereas in this study the dosage was 0.5 times the field rate at maximum.

The butterfly larvae were not directly affected in the dosage range tested for any of the herbicides, but the host plant lost the leaves at very low dosages. This observation suggests that that the butterfly will not increase its pest status following spray drift from adjacent fields and that the use of reduced dosages of herbicide are unlikely to benefit insects associated with Brassica napus. These experiments measured the end-points after 4 days, and it may be argued that sublethal effects would show up at a later stage. However, the plants were so affected that the leaves were lost shortly after this point in time even at dosages as low as 0.1 times the recommended field rate. This was also observed in the chronic test.

Further, there were no indications that the quality of the treated Triticum plants was changed, as the aphids developed and reproduced equally well on treated and untreated plants. This observation, first of all, expresses that the metabolism of the herbicide to compounds without herbicidal activity is so fast and inexpensively that an altered allocation is not seen, or that the insects suck on single cells rather that the conductive tissue.

So, on the basis of the present data set the conclusion is that sulfonylurea herbicides are unlikely to cause widespread effects on herbivorous insect other than the probable disappearance of the host plant.