Home Selecting Coriandrum sativum (Apiaceae) varieties to promote conservation biological control of crop pests in south Florida
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Selecting Coriandrum sativum (Apiaceae) varieties to promote conservation biological control of crop pests in south Florida

  • Joseph M. Patt ORCID logo EMAIL logo
Published/Copyright: August 18, 2025

Abstract

Coriandrum sativum L. (Apiaceae) is an annual herb that produces numerous flowerheads and is a host plant for aphids. Studies have demonstrated that adding C. sativum to different kinds of cropping systems can enhance biological control of pests in those crops. This study represents a first step towards selecting C. sativum accessions that would perform well as insectary plants in citrus groves. Coriander accessions were grown and evaluated to determine which would grow well and flower quickly in south Florida. Because latitude may affect flowering time, accessions that were tested originated from localities within 10° latitude of the study site (27.418 °N), i.e., India, Pakistan, north Africa. Two of the Indian accessions produced healthy plants that flowered more quickly than the others. Seed from these two accessions were saved, which when sowed produced an open-pollinated (OP) hybrid that grew well in south Florida. A second test was performed to determine if co-sowing the seeds of the quick-flowering OP hybrid coriander with the seeds of a slow-to-flower variety (cilantro) would result in overlapping flowering periods. The flowering periods of the two varieties overlapped by approximately 1 week while the overall flowering period was extended by 35 days relative to planting each variety by itself. The results showed that the coriander and cilantro varieties of C. sativum can be co-sown to ensure an extended flowering period, saving the grower time and effort and providing a better habitat for biological control insects.

Resumen

Coriandrum sativum L. (Apiaceae) es una hierba anual que produce numerosas inflorescencias y es una planta hospedera de áfidos. Diversos estudios han demostrado que la incorporación de C. sativum a diferentes sistemas de cultivo puede mejorar el control biológico de plagas en estos cultivos. Este estudio representa un primer paso hacia la selección de accesiones de C. sativum que se desarrollarían bien como insectarias en plantaciones de cítricos. Se cultivaron y evaluaron accesiones de la variedad ‘coriander’ para determinar, en el sur de Florida, cuáles crecen bien y cuales florecen rápidamente. Dado que la latitud puede afectar el tiempo de floración, las accesiones analizadas provenían de localidades dentro de los 10° de latitud del sitio de estudio (27,418 °N), es decir, India, Pakistán y el norte de África. Dos de las accesiones indias produjeron plantas sanas que florecieron más rápidamente que las demás. Se conservó la semilla de estas dos accesiones, que, al sembrarse, produjo un híbrido de polinización abierta (OP) que creció bien en el sur de Florida. Se realizó una segunda prueba para determinar si la cosiembra de semillas de ‘coriander’ híbrido OP de floración rápida con semillas de una variedad de floración lenta (cilantro) resultaría en periodos de floración superpuestos. En comparación con la siembra de cada variedad por separado, los periodos de floración de las dos variedades se superpusieron aproximadamente una semana, mientras que el periodo de floración total se prolongó a 35 días. Los resultados demostraron que las variedades de ‘coriander’ y cilantro de C. sativum pueden cosembrarse para asegurar un periodo de floración prolongado, ahorrando tiempo y esfuerzo al agricultor y proporcionando un mejor hábitat para los insectos de control biológico.

1 Introduction

Effective conservation biological control of crop pests depends on attracting and maintaining effective populations of predaceous and parasitic arthropods in targeted cropping systems (Gurr et al. 2017; Landis et al. 2000; Shields et al. 2019). Monoculture cropping systems typically do not provide essential nutritional and other resources, which mitigates against meaningful recruitment and establishment of natural enemies of crop pests in the system (Altieri and Whitcomb 2003; Altieri and Letourneau 1982; Jervis and Kidd 1996). This may be especially problematic when pest populations are beginning to establish in the crop and natural enemy abundance and recruitment is low (Altieri et al. 1982). Adding complimentary non-crop plants to the crop may be an effective management strategy for attracting and maintaining natural enemies in cropping systems (Gurr et al. 2024; Lundgren 2009; van Emden 2003; Wäckers 2005).

This is because these complimentary non-crop plants attract natural enemies (Colazza et al. 2023; Foti et al. 2017) and provide them with critical resources, such as shelter, nectar, alternate prey, and pollen, also referred to as ‘SNAP’ resources (Gurr et al. 2017; Snyder 2019). ‘SNAP’ plants have been shown to promote and support natural enemy recruitment, survivorship, growth, and fecundity in agricultural ecosystems (Bottrell et al. 1998; Cortesero et al. 1998; Gurr et al. 2017, 2024; Jervis and Kidd 1996; Wolcott 1942).

Umbels, the open flat inflorescences that are typical of the plant family Apiaceae are a good SNAP resource because they provide food for many beneficial insects. Umbels consist of numerous florets whose exposed nectar and pollen are fed upon by diverse assemblages of predators, parasitoids and pollinators (Bugg and Wilson 1989; Proctor and Yeo 1972; Wojciechowicz-Zytko 2019). The Apiaceae family includes culinary plants such as carrots, parsley, fennel, dill, and caraway.

Another familiar apiaceous plant, Coriander sativum L., known as coriander and cilantro, is a hardy annual herb that has been used for the past 8,000 years for its pungent foliage, aromatic seeds, and medicinal properties (Diederichsen 1996; Diederichsen and Hammer 2003; Ramadan 2023; Spence 2023). The plant grows to between 0.2 and 1.4 m tall, has a short life cycle, is adaptable to many different soil and growing conditions and is cultivated worldwide (Diederichsen 1996; López et al. 2008). Its rapid life cycle allows it to fit into different growing seasons, making it possible to grow the crop under a wide range of conditions (Kassahun 2020).

The wild progenitor of cultivated coriander is unknown, though a recent study suggests this species originated in the eastern Mediterranean region (Arora et al. 2021). There are three subspecies of coriander, sativum, microcarpum, and indicum, which are further divided into 10 botanical varieties (Arora et al. 2021; Diederichsen and Hammer 2003). According to Diederichsen and Hammer (2003), the subspecies sativum predominates in the Mediterranean area and western Europe while subspecies indica arose in Pakistan and India, and subspecies microcarpum originated in the Caucasus and then spread widely into southeastern Europe, Central Asia and China. The domestication of these various C. sativum varieties across different geographical regions has yielded a wide range of phenotypically diverse landraces that vary in their morphological traits and essential oil composition (Arora et al. 2021; Diederichsen 1996).

In the U.S., commercially available C. sativum seeds are predominately varieties of ‘cilantro’, which is the name also used for the soft, fragrant leaves used in salsa and garnishes that these plants produce. ‘Cilantro’ varieties have been bred from the subspecies sativum and microcarpum and have a prolonged juvenile phase during which a large basal rosette of fragrant leaves is produced (Diederichsen and Hammer 2003; Spence 2023) and may take up to 90 days before flowering (López et al. 2008). On the other hand, C. sativum varieties that are grown to produce the aromatic seeds which are used as a spice or mixed into a masala are known as ‘coriander’ (in the U.S.). These ‘coriander’ varieties are from the subgenus indicum and have been selected to flower quickly (within a few weeks) and profusely and to produce large seeds with highly aromatic, flavorful oils (Diederichsen and Hammer 2003; Spence 2023), which is the harvested commodity. Seeds of ‘coriander’ varieties are difficult to obtain in the U.S. as most of the commercial demand is for ‘cilantro’.

Coriandrum sativum plants are highly multibranched and each branch finishes with a compound umbel, which is open for 5- to 7-days (Diederichsen 1996). Many anthophilous insects are attracted to C. sativum and outcrossing from pollinators increases seed setting and fruit yield (Bhowmik et al. 2017; Patil and Pastagia 2016). A disk-like nectary is located at the base of the style (‘stylopodium’) while the stamen protrude above the pinkish-white recurved petals (Diederichsen 1996), making the nectar and pollen accessible to a wide variety of natural enemies (Baggen and Gurr 1998; Patt and Rohrig 2017; Patt et al. 1997a,b; van Rijn and Wäckers 2016; Vattala et al. 2006). The nectar and pollen of C. sativum provides important nutrients to natural enemies of crop pests (Baggen and Gurr 1998; D’Ávila et al. 2016; de Abreu et al. 2017; Patt et al. 2003; Resende et al. 2017; Togni et al. 2016; van Rijn and Wäckers 2016). The odors emitted by coriander flowers are attractive not only to pollinators but to generalist insect predators as well (Lenardis et al. 2017). Generalist insect predators also are attracted to the odors emitted by vegetative C. sativum plants (Salamanca et al. 2015, 2018; Togni et al. 2016). Some predator species preferentially oviposit on coriander plants and use the foliar volatiles to assess habitat quality (Togni et al. 2016). The maturing infructescence can be infested by several aphid species, which are a major pest of coriander when it is grown as a seed crop (Meena et al. 2017). Natural enemy populations develop on aphid-infested umbels (Kant et al. 2019; Kumar et al. 2023; Pareek et al. 2014; Regar et al. 2022; Swami et al. 2018), which then have the potential to migrate to adjacent crops. Studies have shown that the addition of coriander as an insectary plant to cropping systems can enhance biological control of crop pests (Baggen and Gurr 1998; Medeiros et al. 2009; Mena and Gospodarek 2024; Patt et al. 1997b; Resende et al. 2010; van Rijn and Wäckers 2016).

Many citrus groves in Florida have row middles that are bare earth or covered with ruderal vegetation and exotic grasses. Because these plants provide few nutritional resources, the citrus grove environment is not very supportive of predaceous and parasitic insects and is not optimal with respect to promoting biological control of citrus pests. Growing ‘SNAP’ plants along the borders and in the row middles should increase the abundance and diversity of predaceous and parasitic insects in citrus groves, leading to suppression of pest insects. Because studies have established that coriander flowers support a wide variety of predaceous and parasitic insects (Baggen and Gurr 1998; Patt and Rohrig 2017; Patt et al. 1997a,b; van Rijn and Wäckers 2016; Vattala et al. 2006), C. sativum could be an ideal SNAP plant to use in citrus groves. Coriander plants attract and support coccinellids, syrphids, and chrysopids, which prey upon and suppress populations of Asian citrus psyllid (Diaphorina citri Kuwayama; Heteroptera: Psyllidae) (Michaud 2002; Michaud et al. 2004; Qureshi et al. 2009, 2014; Kondo et al. 2015; Hoddle et al. 2022; Qasim et al. 2024), the most serious citrus pest insect in Florida (Halbert and Manjunath 2004; Grafton-Cardwell et al. 2013; Hall et al. 2013). This study represents a first step towards selecting C. sativum accessions that would perform well as insectary plants in Florida citrus groves.

The first goal of this study was to screen C. sativum accessions to identify those that would grow vigorously and flower quickly for the purpose of providing nutritional resources to support natural enemies in citrus groves. These selected accessions would then be grown and allowed to open-pollinate for several generations to produce a population adapted for local conditions. The open-pollinated progeny could then be tested for their capacity to attract and support natural enemies of citrus pest insects. The second goal was to co-sow seeds of the open-pollinated ‘coriander’ with seeds of a commercially-available ‘cilantro’ variety and determine the extent to which their flowering and fruiting periods overlapped. The idea here was that coriander plants from the open-pollinated seed should flower rapidly and begin to complete their blooming period as the cilantro plants complete their prolonged juvenile phase and begin to flower. The resultant interplanted population would result in an extended period of floral and prey resource availability for natural enemies versus planting either one by itself.

2 Materials and methods

2.1 Study site

The study was conducted at Heathcote Botanical Gardens, a public display garden located in Fort Pierce, in south Florida, U.S.A. (27.4 °N, 80.3 °W) and is within the United States Department of Agriculture (USDA) plant hardiness growth zone 10A, with a mean minimum winter temperature of −1 °C to 1.7 °C (USDA 2023). The study site is located in the Indian River citrus growing region.

2.2 Coriander accessions

The 21 accessions of C. sativum used for this study were obtained from the USDA North Central Regional Plant Introduction Station (NCRPIS) in Ames, Iowa, USA. Most of the accessions chosen for the study originated within 10° latitude of the study site in south Florida (Table 1). This criterion was chosen because flowering phenology varies strongly with latitude and accessions from similar latitudes tend to flower at similar times (Debieu et al. 2013).

Table 1:

Coriandrum sativum accessions received from United States Department of Agriculture North Central Region Plant Introduction Station in Ames, Iowa, USA, in July 2018 listed in alphanumeric order (column 1). Information is provided about each accession’s infraspecific designation (subspecies) (Diederichsen and Hammer 2003), and geographic origin, including the differences in latitude and elevation between the collection sites and the study site in southeastern Florida, located at 27.3 °N, elevation 10 m).

Accession ID Region & country of origin Locality information Subspecies Elevation (m) Elevational difference (m) Latitude (°N) Latitudinal difference (°)
Ames 7546 Himachal Pradesh, India Simla, from market indicum 2,276 2,266 31.6 4.3
Ames 32045 Agadir-Ida-Ou Tanane, Morocco Agadir, from market sativum 74 64 30.3 3.0
Ames 32046 Draa-Tafilalet, Morocco Errachidia, from market sativum 1,009 999 31.6 4.3
PI 193769 Ethiopia Unknown sativum 2,143 2,133 9.1 −18.2
PI 193770 Ethiopia Unknown sativum 2,143 2,133 9.1 −18.2
PI 253146 Isfahan, Iran From bazaar microcarpum 1,574 1,564 32.4 5.1
PI 274290 Gujarat, India Palanpur indicum 209 199 24.1 −3.2
PI 274291 Himachal Pradesh, India Kullu, from bazaar indicum 1,279 1,269 32.0 4.7
PI 274292 Rajastan, India Jodhpur, from farm indicum 231 221 26.3 −1.0
PI 664512 Sughd, Tajikistan Bulok, from market microcarpum 472 462 40.6 13.3
PI 665268 Médinine, Tunisia Guellala, from market sativum 250 240 32.2 4.9
PI 665269 Sidi Bouzid, Tunisia Sidi Bouzid, from market sativum 375 365 35 7.7
PI 665270 Sfax, Tunisia Sfax, from market sativum 10 0 34.4 7.1
PI 665271 Tunisia Bizerte, from pasture sativum 10 0 37.2 9.9
PI 669960 Bihar, India Samastipur indicum 50 40 25.5 −1.8
PI 669963 Bihar, India Samastipur indicum 50 40 25.5 −1.8
PI 674300 Baluchistan, Pakistan Roadside between Quetta & Kalat indicum 1,800 1,790 29.5 2.2
PI 674301 Buluchistan, Pakistan Ziarat indicum 2,410 2,400 30.4 3.1
PI 674302 Buluchistan, Pakistan Khejj Khajjak indicum 190 180 29.6 2.3
PI 674291 Thimphu Valley, Bhutan Luntiphu indicum 2,150 2,140 27.5 0.2
PI 674314 Buluchistan, Pakistan Maharghar indicum 230 220 29.2 1.9

Because the rapid flowering trait of subspecies indica was desired, over half of the accessions were from India and Pakistan. Nine of the 21 accessions were acquired from spice markets while the others were collected from ruderal or cultivated plants. Information about the accessions was provided by USDA-Germplasm Resources Information Network and López et al. (2008).

2.3 Sowing and seedling care

Seeds for the screening test were sown on 11 November 2018 in a peat-based potting soil (Fafard 4P Mix, SunGro Horticulture, Agawam, Maine, U.S.A.) in 7.6 × 7.6 cm square plastic pots. Five seeds of each accession were planted in each pot at a depth of approximately 0.5–1.0 cm, with a total of 18 pots sown for each accession (=90 seeds per accession per test). The pots for each accession were grouped in plastic trays placed on an outdoor bench exposed to full sunlight. The seedlings received supplemental water as needed and received a weekly application of dissolvable fertilizer (20–20–20; 15 mL fertilizer/3.9 L water; Jack’s, J. B. Peters, Inc., Allentown, Pennsylvania, U.S.A.).

2.4 Coriander accession screening test

A comparison was made of the germination level and flowering and fruiting periods of C. sativum plants grown from the 21 accessions received from USDA-NCRPIS. Each pot was examined twice per week and scored for the number of seedlings present, seedling health, and the number of plants flowering and/or fruiting. Seedling health was scored from 1 to 5, with a score of 1 indicating that the seedling was in very poor condition and a score of 5 indicating that the seedling was healthy, i.e., the cotyledon were unblemished, and the first true leaves were deep green. This permitted calculation of the percentage of germinated seeds, seedling condition, the number of days until maximum germination, and the percentage of plants in bloom and in fruit over the course of study for each accession. The first assessment was made on 23 November 2018 and the final one on 1 April 2019. The mature dried fruit produced by each accession were collected and allowed to air dry for 1 week in the laboratory before a sample of the fruits was weighed.

2.5 Co-planting coriander and cilantro test

A test was performed to determine the extent of overlap in flowering periods when the seeds of one coriander variety and one cilantro variety were co-sown. The cilantro variety used was ‘Santo’ (Johnny’s Selected Seeds, Albion, Maine, U.S.A.), which has a prolonged juvenile phase and resists producing flower stalks. A coriander accession adapted to local conditions was obtained from open pollination of the two earliest flowering accessions observed in the accessions screening test, PI 274290 and PI 274292, for eight generations. Seeds from these coriander hybrids were used in the co-planting test. The plants were grown in planter boxes as described below. Seeds were collected from each generation, cleaned, and stored in sealed containers with a desiccant pack at 4.5 °C, and then replanted at the appropriate time to produce the next generation. The coriander seeds used in the test were from the eighth generation following the initial open pollination of the two parental accessions.

Seeds were sown in pots as described for the accession test above on 11 March 2022. On 8 April 2022, the plants were transplanted into planter boxes made from 68 L plastic tote boxes (60.9 L × 41.9 W × 39.4 D cm) (Roughneck Box, Rubbermaid, Leominster, Maine, U.S.A.). The boxes were filled to approximately 80 % capacity with commercial potting soil (Fafard 4P Mix). Four plants were transplanted into each planter box and four planter boxes were established for each variety (=16 plants/variety). Fifteen ml (volumetric) of slow-release fertilizer (20–20–20 Osmocote, The Scotts Company, Marysville, Ohio, U.S.A.) was sprinkled on the soil surface of each planter box after transplanting. The boxes were watered daily with an automatic irrigation system to maintain plant health.

2.6 Statistical analysis

In the coriander accession test, the health rankings of the seedlings from each accession were compared with analysis of variance (ANOVA) (www.statisticskingdom.com). The relationship among the weight of the seeds of the parental generation, the percentage of plants in flower, and the weight of the seeds produced by the open-pollinated flowers was examined with the Pearson’s correlation coefficient test (www.socscistatistics.com).

3 Results

3.1 Coriander accession screening test

Seeds from all accessions germinated and produced plants, although the maximum total percentage of seeds that germinated varied from a low of 20 % to a high of >90 % (Table 2). The accessions that had the highest percentage of seeds that germinated were PI 274291 (91.7 %) and Ames 7546 (88.3 %), which originated from markets in the Indian states of Gujarat and Himachal Pradesh, respectively. The seedlings of all accessions had similar mean health rankings that ranged from 3.9 to 5.0, showing they were in good to excellent health, except for the single Iranian accession, PI 253146, which differed from the others with a health rank of 2.7 (F (20,209) = 5.644; P < 0.001). The number of days until maximum germination varied from as few as 14 days (PI 674300, which originated in Ethiopia) to as many as 45 days after sowing (PI 674314, which originated in Pakistan).

Table 2:

Germination of Coriandrum sativum accessions received from United States Department of Agriculture North Central Region Plant Introduction Station in Ames, Iowa, USA, in July 2018. Accessions are ranked by maximum percentage of seeds that germinated (n = 90 seeds sown/accession) (column 7). Information is provided about each accession’s geographic origin, including the differences in latitude and elevation between the collection sites and the study site in southeastern Florida (27.3 °N, elevation 10 m), its infraspecific designation (subspecies) (Diederichsen and Hammer 2003), the weight of 100 seeds (HSWT), the maximum percentage of seeds that germinated, and the days to maximum germination.

Accession ID Region & country of origin Subspecies Elevation difference (m) Latitude difference (°) HSWT (g) Max. % germination Days to max. germination
PI 274291 Himachal Pradesh, India indicum 1,269 4.7 0.7 91.7 28
Ames 7546 Himachal Pradesh, India indicum 2,266 4.3 0.6 88.3 38
PI 665270 Sfax, Tunisia sativum 0 7.1 1.4 75.0 21
PI 664512 Sughd, Tajikistan microcarpum 462 13.3 0.5 71.7 21
PI 674291 Thimphu Valley, Bhutan indicum 2,140 0.2 0.5 70.0 24
PI 669960 Bihar, India indicum 40 −1.8 1.3 68.3 28
PI 665271 Tunisia sativum 0 9.9 1.0 68.3 28
PI 674314 Buluchistan, Pakistan indicum 220 1.9 0.7 66.7 45
PI 665268 Médinine, Tunisia sativum 240 4.9 1.4 66.7 38
Ames 32045 Agadir-Ida-Ou Tanane, Morocco sativum 64 3.0 1.6 65.0 38
PI 665269 Sidi Bouzid, Tunisia sativum 365 7.7 1.3 65.0 24
PI 674300 Baluchistan, Pakistan indicum 1,790 2.2 0.7 65.0 14
Ames 32046 Draa-Tafilalet, Morocco sativum 999 4.3 1.6 63.3 34
PI 674302 Buluchistan, Pakistan indicum 180 2.3 0.5 61.7 21
PI 274292 Rajastan, India indicum 221 −1.0 1.7 60.0 18
PI 669963 Bihar, India indicum 40 −1.8 0.8 58.3 21
PI 674301 Buluchistan, Pakistan indicum 2,400 3.1 0.4 48.3 28
PI 193770 Ethiopia sativum 2,133 −18.2 1.2 46.7 18
PI 274290 Gujarat, India indicum 199 −3.2 1.5 28.3 24
PI 253146 Isfahan, Iran microcarpum 1,564 5.1 0.6 26.7 21
PI 193769 Ethiopia sativum 2,133 −18.2 0.8 20.0 42

With respect to the amount of time between sowing and flowering, the accessions could be divided roughly into three groups (Figure 1, Table 3). The early flowering group consisted of accessions that flowered soon after sowing and included accessions PI 274292 and PI 274290, which originated from markets in the Indian states of Rajasthan and Gujarat, respectively. The plants from these two accessions began flowering 48 days after sowing and reached peak flowering 60–65 days after sowing, with >70 % of the plants flowering. The mid-flowering group consisted of accessions that began flowering 56–83 days after sowing and reached peak flowering approximately 85–90 days after sowing, with >70 % of the plants flowering. This group included accessions PI 193770, which originated in Ethiopia, and PI 669960, and PI 669963, which originated from the Indian state of Bihar. The late flowering group consisted of accessions that began flowering at approximately 93 days after sowing and reached peak flowering 108–111 days after sowing, with <70 % of the plants flowering. This group included accessions PI 674302 and PI 665271, which originated from the Pakistani state of Buluchistan and northern Tunisia, respectively.

Figure 1: 
Percentage of Coriandrum sativum plants in each accession in flower during the 3 weeks of the peak blooming period at the study site in southeastern Florida. Only accessions in which >50 % of the plants flowered are shown.
Figure 1:

Percentage of Coriandrum sativum plants in each accession in flower during the 3 weeks of the peak blooming period at the study site in southeastern Florida. Only accessions in which >50 % of the plants flowered are shown.

Table 3:

Flowering levels of Coriandrum sativum accessions received from United States Department of Agriculture North Central Region Plant Introduction Station in Ames, Iowa, USA, in July 2018. Accessions are ranked by the mean percentage of plants flowering (column 6) during the peak flowering period. Information also is provided for each accession about the weight of 100 seeds (HSWT), the mean weight (g) of the seeds obtained from the open-pollinated plants (OP F1) and the number of days to initial flowering. Each accession’s geographic origin, including the differences in latitude and elevation between the collection sites and the study site in southeastern Florida (27.3 °N, elevation 10 m), its infraspecific designation (subspecies) (Diederichsen and Hammer 2003) also are listed.

Accession ID Region & country of origin Subspecies Elevation difference (m) Latitude difference (°) HSWT (g) Mean % plants flowering Mean weight (g) of seed obtained from OP F1 Days to initial flowering
PI 274292 Rajastan, India indicum 221 −1.0 1.7 0.73 0.59 49
PI 274290 Gujarat, India indicum 199 −3.2 1.5 0.67 0.51 49
PI 193770 Ethiopia sativum 2,133 −18.2 1.2 0.62 0.31 87
PI 669960 Bihar, India indicum 40 −1.8 1.3 0.55 0.28 69
PI 669963 Bihar, India indicum 40 −1.8 0.8 0.54 0.32 83
PI 674314 Buluchistan, Pakistan indicum 220 1.9 0.7 0.48 0.26 59
PI 665271 Tunisia sativum 0 9.9 1.0 0.43 0.35 93
PI 665270 Sfax, Tunisia sativum 0 7.1 1.4 0.42 0.3 83
PI 665269 Sidi Bouzid, Tunisia sativum 365 7.7 1.3 0.40 0.32 83
Ames 7546 Himachal Pradesh, India indicum 2,266 4.3 0.58 0.37 0.16 83
PI 674302 Buluchistan, Pakistan indicum 180 2.3 0.53 0.37 0.3 93
PI 193769 Ethiopia sativum 2,133 −18.2 0.8 0.36 0.34 87
PI 674300 Baluchistan, Pakistan indicum 1,790 2.2 0.7 0.35 0.21 56
PI 664512 Sughd, Tajikistan microcarp. 462 13.3 0.5 0.34 0.26 77
PI 665268 Médinine, Tunisia sativum 240 4.9 1.4 0.32 0.4 93
PI 674301 Buluchistan, Pakistan indicum 2,400 3.1 0.4 0.31 0.28 97
Ames 32046 Draa-Tafilalet, Morocco sativum 999 4.3 1.6 0.28 0.43 83
Ames 32045 Agadir-Ida-Ou Tanane, Morocco sativum 64 3 1.6 0.27 0.39 97
PI 253146 Isfahan, Iran microcarp. 1,564 5.1 0.6 0.26 0.22 93
PI 274291 Himachal Pradesh, India indicum 1,269 4.7 0.7 0.26 0.22 93
PI 674291 Thimphu Valley, Bhutan indicum 2,140 0.2 0.5 0.00 NA NA

The accessions in the early flowering group had a prolonged fruiting period that lasted until 91 days after sowing, at which point the plants senesced (Figure 2). Nearly all of the plants in this group produced seed. The accessions in the mid-flowering group also had an extended fruiting period that lasted until over 120 days past sowing. In the late flowering group, < 60 % of the plants produced fruit, with fruit production extending beyond 125 days past sowing. The two accessions from the first flowering group, PI 274292 and PI 274290, also produced seeds with the highest mean weight (Table 3).

Figure 2: 
Percentage of Coriandrum sativum plants in each accession in fruit during the three weeks of the peak fruiting period at the study site in southeastern Florida. The accessions with the highest percentage of plants that fruited are shown.
Figure 2:

Percentage of Coriandrum sativum plants in each accession in fruit during the three weeks of the peak fruiting period at the study site in southeastern Florida. The accessions with the highest percentage of plants that fruited are shown.

An overall positive relationship was observed between the weight of the parental seed of each accession (hundred seed weight (HSWT)) and the corresponding mean percentage of parental plants in flower (r(19) = 0.8231, P < 0.001) (Figure 3A). As well, the accessions that had higher percentage of plants in flower per observation produced the largest seeds (r(18) = 0.8754, P < 0.001) (Figure 3B).

Figure 3: 
Relationship between seed size and percentage of plants flowering in each Coriandrum sativum accession at the study site in southeastern Florida. A. Relationship between weight of seeds from each accession (the weight of 100 seeds = HSWT), and mean percentage of plants flowering/week; and B. mean percentage of plants in flower/week and weight of resultant seeds (OP F1).
Figure 3:

Relationship between seed size and percentage of plants flowering in each Coriandrum sativum accession at the study site in southeastern Florida. A. Relationship between weight of seeds from each accession (the weight of 100 seeds = HSWT), and mean percentage of plants flowering/week; and B. mean percentage of plants in flower/week and weight of resultant seeds (OP F1).

3.2 Co-planting coriander and cilantro test

Seed from both the cilantro (variety Santo) and open-pollinated coriander accessions produced healthy plants that flowered and produced fruit (Figure 4). The tallest umbels of the coriander variety were approximately 55 cm tall while those of the cilantro variety grew to a height of approximately 105 cm (Figure 5). At 31 days after sowing, plants of both varieties were in the juvenile stage (Figure 4). By 36 days, some of the coriander plants were producing floral shoots while the cilantro plants remained in the juvenile condition. The coriander plants began to flower at approximately 45 days and were in full flower by 54 days, while stem elongation had just begun in some of the cilantro plants. The cilantro began to flower at approximately 65 days, overlapping with the coriander flowers. By 76 days, the coriander plants had completed flowering and had mature fruit while the cilantro plants were still producing flower buds and flowers and were beginning to produce fruit. By 91 days, half of the coriander plants had senesced while the cilantro plants remained in full bloom. At 115 days, all the coriander plants had senesced while the cilantro plants continued to produce flowers and fruit, with some plants just beginning to senesce.

Figure 4: 
Phenology of container-grown coriander and cilantro varieties of Coriandrum sativum, spring and summer 2022 at the study site in southeastern Florida, showing the extended flowering period obtained when the two varieties are sown together. The orange arrows show the onset and conclusion of flowering the period of the coriander variety and the green arrow indicates the onset of flowering in the cilantro variety.
Figure 4:

Phenology of container-grown coriander and cilantro varieties of Coriandrum sativum, spring and summer 2022 at the study site in southeastern Florida, showing the extended flowering period obtained when the two varieties are sown together. The orange arrows show the onset and conclusion of flowering the period of the coriander variety and the green arrow indicates the onset of flowering in the cilantro variety.

Figure 5: 
Height of tallest umbels observed in container-grown coriander and cilantro varieties of Coriandrum sativum, spring and summer 2022 at the study site in southeastern Florida.
Figure 5:

Height of tallest umbels observed in container-grown coriander and cilantro varieties of Coriandrum sativum, spring and summer 2022 at the study site in southeastern Florida.

4 Discussion

Our results demonstrate the feasibility of conducting small-scale screening tests to identify C. sativum accessions that grow vigorously and flower quickly in south Florida for the purpose of providing habitat for natural enemies of crop pests. The use of latitude as a guide to narrow the selection of accessions to test worked well overall, although there was a surprising exception, i.e., the Ethiopian accession whose origins were the most different in terms of latitude and elevation from those of the study. Comparisons of the germination success and flowering and fruiting periods of C. sativum plants grown from 21 accessions received from USDA-NCRPIS revealed differences in the levels of germination, fruiting, and flowering among them when they were planted in southeastern Florida. For example, two accessions, PI 274290 and PI 274292, flowered much sooner than the others, with peak flowering occurring 55–65 days after sowing (Figure 1). In comparison, peak flowering occurred 20 days later for accession PI 669960 and not for another 40–60 days later for other accessions tested. In other studies where several C. sativum accessions were co-planted, differences were observed among the accessions in numerous agronomic, morphological, and biochemical traits (Angelini et al. 1997; Berkomah et al. 2022; López et al. 2008).

Considering only the accessions where >70 % of the plants flowered (Figure 1, Table 3), some similarities regarding geographic origin were noted. The accessions that flowered first, PI 274290 and PI 274292, originated in northwestern India, from the states of Gujarat (24.1 °N) and Rajasthan (26.2 °N), which have latitudes similar to that of the study site in southeastern Florida (27.3 °N) (Table 1). Both collection locations and the study site are situated below 250 m in elevation. Of the second flowering group, accessions PI 669960 and PI 669963 were collected in Samastipur, a city in northern India located at 25.5 °N at an elevation below 250 m. However, the other accession in this group, PI 193370, originated in Ethiopia at 9.1 °N and at an elevation above 2,100 m. In an evaluation of 62 C. sativum accessions conducted in Ames, Iowa, USA, the Samastipur accession PI 669960 was in first group of accessions to flower while PI669963 was in the second group (López et al. 2008). Similarity in latitude and elevation of the accessions’ geographic origin relative to the study site may have factored into the rapid umbel production observed here. As well, these four Indian accessions would be classified as C. sativum subspecies indicum, which typically has a short juvenile stage and flowers quickly (Diederichsen and Hammer 2003; López et al. 2008) and would be expected to grow as observed.

All of the accessions produced fruit, with fruit production in general lasting for several weeks after the peak blooming period (Figure 2). In certain management situations, growers may want their insectary plants to reseed to reduce costs and effort associated with re-sowing. For example, a quick-flowering insectary plant could be sown so that it provides habitat for natural enemies before pest populations develop in the crop. The results here suggest that these coriander accessions would readily reseed themselves. Interestingly, there was a strong correlation between the weight of the parental seed and the mean percentage of plants flowering in a particular accession; and in a similar way, the percentage of plants flowering and the weight of the open pollinated (OP) F1 seeds were strongly correlated (Figure 3, Table 3). In C. sativum, seed mass and shape and floral shoot production have high heritability (Arif et al. 2014; Bhandari and Gupta 1991, 1993; Kumar et al. 2022; López et al. 2008; Nair et al. 2012; Verma et al. 2018), and our results align with those findings. Our results also indicate that seed weight is an important trait to consider for varietal selection for conservation biological control purposes because it is predictive of flowering outcome.

The accession screening test was conducted in the cooler part of the Florida growing season. It is possible that different results would have been obtained if the test was replicated in a warmer period of the growing season. However, we have observed that C. sativum grows poorly when temperatures are consistently above 30 °C during the hottest part of the growing season in south Florida and so it is likely to be unsuitable as an insectary crop for the summer.

The two accessions, PI 274290 and PI 274292, which the screening test identified as optimal in terms of rapidity of growth and flowering, were used as parental plants to produce an open-pollinated coriander hybrid adapted for south Florida growing conditions. When these hybrid coriander seeds were co-sown with a cilantro variety, an extended flowering period could be generated, relative to the flowering period of each alone (Figure 4). The results showed that planting either variety alone resulted in flower production for 30 days while co-planting the two varieties extended flower production by approximately 35 days (Figure 4). These results showed that co-planting quick-flowering coriander varieties with bolting-resistant cilantro varieties could provide natural enemy habitat for an additional month without the need to stagger-plant the two varieties to obtain a similar outcome. While it is unknown how the resultant population of C. sativum subspecies sativa × indicum hybrids would sort with respect to the time to onset of flowering, it is likely that bimodal flowering times would persist among the progeny for several years.

An alternative strategy for extending the flowering period of C. sativum plantings would be to co-sow the early-flowering Gujarat or Rajasthan accessions, PI 274290 and PI 274292, with the mid-flowering Bihar accessions, PI 669960 and PI 669963. We anticipate that co-sowing these accessions would result in sequential flowering similar to that obtained from co-planting coriander and cilantro varieties. As these accessions belong to subspecies indicum, the manner in which the resultant hybrids sort with respect to time to onset of flowering might be different than in hybrid populations generated from crossing subspecies sativum and indicum. However, additional experimentation is needed to confirm whether sequential flowering would occur when the different accessions are co-planted.

Other studies have shown that different mixtures or growth stages of C. sativum can influence recruitment of natural enemies. For example, Lenardis et al. (2017) examined three different C. sativum accessions sown in the early and late part of the growing season and evaluated the abundance and diversity of pollinators and natural enemies in the umbels of each accession. They also found distinctive flowering peaks among the accessions, with one accession flowering sooner after sowing than the other two and found that beneficial insect composition and abundance differed among accessions. They attributed these differences, in part, to differences in the floral fragrance profiles among the different accessions. Because the floral volatile profile of each accession attracted a different suite of insects, they suggested that combining different genotypes of C. sativum would enhance overall beneficial insect abundance and diversity in the planting. In other plant species, plots that contained a mixture of genotypes which varied with respect to traits such as flowering phenology, chemical composition of plant tissue, and odor signals, had increased diversity in arthropod species assemblages relative to those plots or patches with fewer genotypes (Bálint et al. 2016; Burkle et al. 2013; Johnson and Agrawal 2005). Further testing is needed to determine whether the floral fragrance and other traits are different among the accessions tested here and whether growing these accessions in combination would have a synergistic effect on promoting the occurrence of natural enemies (Patt et al. 2020).

In a mixture study of C. sativum with a different crop, tomatoes (Solanum lycopersicum L.; Solanaceae), Togni et al. (2016) demonstrated that coccinellids were attracted to the volatiles emitted by C. sativum and that they used these volatiles to assess habitat quality. They found that C. sativum functioned as an oviposition site for lady beetles, and that larval beetles hatched on C. sativum readily dispersed to adjacent crop plants. They suggest that intercropping Csativum with crop plants will attract lady beetles that oviposit in C. sativum before the arrival of aphids in the crop, thus enhancing biological control of the aphids. Further work is needed to determine whether the foliar volatiles emitted by the different coriander accessions tested here also would have a differing attractiveness to natural enemies of citrus pests.

Patt et al. (2020) found that proportional mixing of insectary plants could synergize the effects of various traits that promote natural enemy abundance and diversity. For example, as shown here and by Lenardis et al. (2017), co-sowing different C. sativum varieties resulted in the production of flowers for a relatively long period. The prolonged availability of both food resources and chemical signaling provided over time by co-planting each accession are expected to result in a strong foraging and colonization response by beneficial insects.

Although not measured as part of this study, observations indicated that aphid abundance can be very high on the umbels and shoots of both the open-pollinated coriander variety and cilantro variety Santo grown in planters at the study site (Patt, unpublished data). This resulted in recruitment of natural enemies, and the development of their immatures (Figure 6) (Patt, unpublished data). Further studies are planned to determine whether proportional mixing of different C. sativum accessions can lead to mixtures that optimally attract and support natural enemies and whether this results in a suppression of pest insects in citrus groves.

Figure 6: 
The arrows point to two coccinellid pupae attached to the infructescence of an open-pollinated hybrid variety of Coriandrum sativum spp. indicum. The plant was previously infested with aphids.
Figure 6:

The arrows point to two coccinellid pupae attached to the infructescence of an open-pollinated hybrid variety of Coriandrum sativum spp. indicum. The plant was previously infested with aphids.

In addition to C. sativum, other annual plant species will need to be utilized to provide natural enemies with SNAP resources across the entire citrus growing season in Florida. Examples are established insectary plants, such as buckwheat (Fagopyrum esculentum Moench; Polygonaceae), mustards (Brassica spp. Brassicacea), and sorghum (Sorghum bicolor (L.) Moench) (Bowie et al. 1995; Wäckers and Van Rijn 2012; Harris-Schultz et al. 2022). Growing plants that reliably provide SNAP resources for natural enemies will be key to implementing successful conservation biological control against citrus pests.


Corresponding author: Joseph M. Patt, U.S. Department of Agriculture-Agricultural Research Service, 2001 South Rock Rd., Fort Pierce, FL 34945, USA, E-mail:

Award Identifier / Grant number: 6034-22320-007-000-D

Funding source: American Floral Endowment, Floriculture and Nursery Research Initiative

Award Identifier / Grant number: 6034-22320-007-004S

Acknowledgments

The author expresses sincere gratitude to A. Tarshis Moreno, biological science technician at the USDA-ARS laboratory in Fort Pierce, Florida and to M. Cook, a volunteer from the St. Lucie County Master Gardener Program, for their dedicated assistance with all stages of the study, to the USDA-North Central Regional Plant Introduction Station in Ames, Iowa, for supplying the accessions used in the study, and to Heathcote Botanical Gardens for logistical support and granting access to the study site. Mention of trade names or commercial products in this publication is solely for the purpose of providing specific information and does not imply recommendation or endorsement by the United States Department of Agriculture for its use.

  1. Research ethics: Not applicable.

  2. Informed consent: Not applicable.

  3. Author contributions: The author has accepted responsibility for the entire content of this manuscript and approved its submission.

  4. Use of Large Language Models, AI and Machine Learning Tools: None declared.

  5. Conflict of interest: The author states no conflict of interest.

  6. Research funding: Funding for this research was provided by the United States Department of Agriculture Agricultural Research Service, Project 6034-22320-007-000-D and by the American Floral Endowment Floriculture and Nursery Research Initiative Project number 6034-22320-007-004S.

  7. Data availability: Upon request to the author.

References

Altieri, M.A. and Letourneau, D.K. (1982). Vegetation management and biological control in agroecosystems. Crop Prot. 1: 405–430, https://doi.org/10.1016/0261-2194-82-90023-0.Search in Google Scholar

Altieri, M.A., Letourneau, D.K., and Risch, S.J. (1982). Vegetation diversity and insect pest outbreaks. Crit. Rev. Plant Sci. 2: 131–169, https://doi.org/10.1080/07352688409382193.Search in Google Scholar

Altieri, M.A. and Whitcomb, W.H. (2003). The potential use of weeds in the manipulation of beneficial insects. HortScience 14: 12–18, https://doi.org/10.21273/hortsci.14.1.12.Search in Google Scholar

Angelini, L.G., Moscheni, E., Colonna, G., Belloni, P., and Bonari, E. (1997). Variation in agronomic characteristics and seed oil composition of new oilseed crops in Central Italy. Industr. Crop. Prod. 6: 313–323, https://doi.org/10.1016/s0926-6690-97-00022-8.Search in Google Scholar

Arif, M., Khurshid, H., and Khan, S. (2014). Genetic structure and green leaf performance evaluation of geographically diverse population of coriander (Coriandrum sativum L.). Eur. Acad. Res. 2: 3269–3285.Search in Google Scholar

Arora, V., Adler, C., Tepikin, A., Ziv, G., Kahane, T., Abu-Nassar, J., Golan, S., Mayzlish-Gati, E., and Gonda, I. (2021). Wild coriander: an untapped genetic resource for future coriander breeding. Euphytica 217: 138, https://doi.org/10.1007/s10681-021-02870-4.Search in Google Scholar

Baggen, L.R. and Gurr, G.M. (1998). The influence of food on Copidosoma koehleri (Hymenoptera: Encyrtidae), and the use of flowering plants as a habitat management tool to enhance biological control of potato moth, Phthorimaea operculella (Lepidoptera: Gelechiidae). Biol. Control. 11: 9–17, https://doi.org/10.1006/bcon.1997.0566.Search in Google Scholar

Bálint, J., Zytynska, S.E., Salamon, R.V., Mehrparvar, M., Weisser, W.W., Schmitz, O.J., Benedek, K., and Balog, A. (2016). Intraspecific differences in plant chemotype determine the structure of arthropod food webs. Oecologia 180: 797–807, https://doi.org/10.1007/s00442-015-3508-y.Search in Google Scholar PubMed

Berkomah, J., Li, H., Siddiqui, R., Kim, C., and Bhardwaj, H. (2022). Cilantro and coriander yield as affected by cultivars and row spacings in fall and spring production in Virginia. HortScience 57: 1156–1158, https://doi.org/10.21273/hortsci16759-22.Search in Google Scholar

Bhandari, M.M. and Gupta, A. (1991). Variation and association analysis in coriander. Euphytica 58: 1–4, https://doi.org/10.1007/bf00035333.Search in Google Scholar

Bhandari, M.M. and Gupta, A. (1993). Association analysis in coriander. Indian J. Genet. Plant Breed. 53: 66–70.Search in Google Scholar

Bhowmik, B., Sarita, S., Alok, S.K.B., and Kakali, B. (2017). Role of insect pollinators in seed yield of coriander (Coriandrum sativum L.) and their electroantennogram response to crop volatiles. Agric. Res. J. 54: 227–235.10.5958/2395-146X.2017.00042.4Search in Google Scholar

Bottrell, D.G., Barbosa, P., and Gould, F. (1998). Manipulating natural enemies by plant variety selection and modification: a realistic strategy? Annu. Rev. Entomol. 43: 347–367, https://doi.org/10.1146/annurev.ento.43.1.347.Search in Google Scholar PubMed

Bowie, M.H., Wratten, S.D., and White, A.J. (1995). Agronomy and phenology of “companion plants” of potential for enhancement of insect biological control. N.Z. J. Crop Hortic. Sci. 23: 423–427, https://doi.org/10.1080/01140671.1995.9513919.Search in Google Scholar

Bugg, R.L. and Wilson, L.T. (1989). Ammi visnaga (L.) Lamarck (Apiaceae): associated beneficial insects and implications for biological control, with emphasis on the bell-pepper agroecosystem. Biol. Agric. Hort. 6: 241–268, https://doi.org/10.1080/01448765.1989.9754521.Search in Google Scholar

Burkle, L.A., Souza, L., Genung, M.A., and Crutsinger, G.M. (2013). Plant genotype, nutrients, and G × E interactions structure floral visitor communities. Ecosphere 4: 113, https://doi.org/10.1890/es13-00039.1.Search in Google Scholar

Colazza, S., Peri, E., and Cusumano, A. (2023). Chemical ecology of floral resources in conservation biological control. Annu. Rev. Entomol. 68: 13–29, https://doi.org/10.1146/annurev-ento-120220-124357.Search in Google Scholar PubMed

Cortesero, A.M., Stapel, J.O., and Lewis, W.J. (1998). Understanding and manipulating plant attributes to enhance biological control. Biol. Control. 17: 35–49, https://doi.org/10.1006/bcon.1999.0777.Search in Google Scholar

D’Ávila, V.A., Aguiar-Menezes, E.L., Gonçalves-Esteves, V., Mendonça, C.B.F., Pereira, R.N., and Santos, T.M. (2016). Morphological characterization of pollens from three Apiaceae species and their ingestion by twelve-spotted lady beetle (Coleoptera: Coccinellidae). Brazilian J. Biol 76: 796–803, https://doi.org/10.1590/1519-6984.07615.Search in Google Scholar PubMed

de Abreu, D’Ávila, V., de Lima Aguiar-Menezes, E., Pereira, R.N., Gonçalves-Esteves, V., Mendonça, C.B.F., de Melo, S.J., and dos Santos, T.M. (2017). Effect of provision of apiaceous flowers associated to foods on the biology of Coleomegilla maculata. Phytoparasitica 45: 471–484, https://doi.org/10.1007/s12600-017-0616-8.Search in Google Scholar

Debieu, M., Tang, C., Stich, B., Sikosek, T., Effgen, S., Josephs, E., Schmidtt, J., Nordborg, M., Koornneef, M., and de Meaux, J. (2013). Co-variation between seed dormancy, growth rate and flowering time changes with latitude in Arabidopsis thaliana. PloS One 8: e61075, https://doi.org/10.1371/journal.pone.0061075.Search in Google Scholar PubMed PubMed Central

Diederichsen, A. (1996). Coriander (Coriandrum sativum L.). Promoting the conservation and use of underutilized and neglected crops, 3. Institute of Plant Genetics and Crop Plant Research, Gatersleben/International Plant Genetic Resources Institute, Rome, pp. 1–32.Search in Google Scholar

Diederichsen, A. and Hammer, K. (2003). The infraspecific taxa of coriander (Coriandrum sativum L.). Genet. Res. Crop Evol. 50: 33–63, https://doi.org/10.1023/a-1022973124839.Search in Google Scholar

Foti, M.C., Rostás, M., Peri, E., Park, K.C., Slimani, T., Wratten, S.D., and Colazza, S. (2017). Chemical ecology meets conservation biological control: identifying plant volatiles as predictors of floral resource suitability for an egg parasitoid of stink bugs. J. Pest Sci. 90: 299–310, https://doi.org/10.1007/s10340-016-0758-3.Search in Google Scholar

Grafton-Cardwell, E.E., Stelinski, L.L., and Stansly, P.A. (2013). Biology and management of Asian citrus psyllid, vector of the huanglongbing pathogens. Ann. Rev. Entomol. 58: 413–432, https://doi.org/10.1146/annurev-ento-120811-153542.Search in Google Scholar PubMed

Gurr, G.M., Liu, J., and Pogrebna, G. (2024). Harnessing artificial intelligence for analysing the impacts of nectar and pollen feeding in conservation biological control. Curr. Opin. Insect Sci. 62: 101176, https://doi.org/10.1016/j.cois.2024.101176.Search in Google Scholar PubMed

Gurr, G.M., Wratten, S.D., Landis, D.A., and You, M. (2017). Habitat management to suppress pest populations: progress and prospects. Annu. Rev. Entomol. 62: 91–109, https://doi.org/10.1146/annurev-ento-031616-035050.Search in Google Scholar PubMed

Halbert, S.E. and Manjunath, K.L. (2004). Asian citrus psyllids (Sternorrhyncha: Psyllidae) and greening disease of citrus: a literature review and assessment of risk in Florida. Fla. Entomol. 87: 330–353, https://doi.org/10.1653/0015-4040-2004-087-0330-acpspa-2.0.co;2.Search in Google Scholar

Hall, D.G., Richardson, M.L., Ammar, E.D., and Halbert, S.E. (2013). Asian citrus psyllid, Diaphorina citri, vector of citrus huanglongbing disease. Entomol. Exp. Appl. 14: 207–223.10.1111/eea.12025Search in Google Scholar

Harris-Shultz, K.R., Armstrong, J.S., Caballero, M., Hoback, W.W., and Knoll, J.E. (2022). Insect feeding on Sorghum bicolor pollen and Hymenoptera attraction to aphid-produced honeydew. Insects 13: 1152, https://doi.org/10.3390/insects13121152.Search in Google Scholar

Hoddle, M.S., Hoddle, C.D., Morgan, D.J., and Milosavljević, I. (2022). Successful biological control of Asian citrus psyllid, Diaphorina citri, in California. In: van Driesche, R.G., Winston, R.L., Perring, T.M., and Lopez, V.M. (Eds.). Contributions of classical biological control to the US food security, forestry, and biodiversity, FHAAST-2019-05. United States Department of Agriculture Forest Service, Morgantown, West Virginia, USA, pp. 127–143.Search in Google Scholar

Jervis, M. and Kidd, N. (Eds.) (1996). Insect natural enemies. Practical approaches to their study and evaluation. Chapman & Hall, London.10.1007/978-94-011-0013-7Search in Google Scholar

Johnson, M.T. and Agrawal, A.A. (2005). Plant genotype and environment interact to shape a diverse arthropod community on evening primrose (Oenothera biennis). Ecology 86: 874–885, https://doi.org/10.1890/04-1068.Search in Google Scholar

Kant, K., Meena, S.R., Sharma, Y.K., Meena, N.K., Vishal, M.K., Saxena, S.N., and Mishra, B.K. (2019). Development of aphids Hyadaphis coriandri (Das), its natural enemies and pollinators on coriander (Coriandrum sativum L.). Int. J. Seed Spices 9: 79–84.Search in Google Scholar

Kassahun, B.M. (2020). Unleashing the exploitation of coriander (Coriander sativum L.) for biological, industrial and pharmaceutical applications. Academic Res. J. Agric. Sci. Research. 8: 552–564.Search in Google Scholar

Kondo, T., González, G., Tauber, C., Sarmiento, Y.C.G., Mondragon, A.F.V., and Forero, D. (2015). A checklist of natural enemies of Diaphorina citri Kuwayama (Hemiptera: Liviidae) in the department of Valle del Cauca, Colombia and the world. Insecta Mundi 0457: 1–14.Search in Google Scholar

Kumar, M.A., Choudhary, G., Garhwal, O.P., and Netwal, M. (2022). Correlation coefficient and path analysis for yield traits in coriander (Coriandrum sativum L.) genotypes. Elec. J. Plant Breeding 13: 253–257.10.37992/2022.1301.035Search in Google Scholar

Kumar, V., Deshwal, H.L., Gurjar, M.K., and Kumawat, R. (2023). Population dynamics of the coriander aphids in hyper arid region of Rajasthan and their correlation with biotic and abiotic factors. Int. J. Environ. Climate Change 13: 384–389.10.9734/ijecc/2023/v13i113181Search in Google Scholar

Landis, D.A., Wratten, S.D., and Gurr, G.M. (2000). Habitat management to conserve natural enemies of arthropod pests in agriculture. Annu. Rev. Entomol. 45: 175–201, https://doi.org/10.1146/annurev.ento.45.1.175.Search in Google Scholar PubMed

Lenardis, A.E., Gil, A., Torretta, J.P., Ganly, D., Bouilly, J.P., and de la Fuente, E.B. (2017). Floral visitor assemblages related to coriander genotypes and sowing dates: relationship with volatile signals. NJAS-Wageningen J. Life Sci. 83: 22–29, https://doi.org/10.1016/j.njas.2017.09.004.Search in Google Scholar

López, P.A., Widrlechner, M.P., Simon, P.W., Rai, S., Boylston, T.D., Isbell, T.A., Bailey, T.B., Gardner, C.A., and Wilson, L.A. (2008). Assessing phenotypic, biochemical, and molecular diversity in coriander (Coriandrum sativum L.) germplasm. Genet. Res. Crop Evol. 55: 247–275, https://doi.org/10.1007/s10722-007-9232-7.Search in Google Scholar

Lundgren, J.G. (2009). Relationships of natural enemies and non-prey foods, 7. Springer Science & Business Media, New York.10.1007/978-1-4020-9235-0Search in Google Scholar

Medeiros, M.A., Sujii, E.R., and Morais, H.C. (2009). Effect of plant diversification on abundance of South American tomato pinworm and predators in two cropping systems. Hort. Bras. 27: 300–306, https://doi.org/10.1590/s0102-05362009000300007.Search in Google Scholar

Meena, N.K., Lal, G., Meena, R.S., Harisha, C.B., and Meena, S.R. (2017). Pest scenario of coriander (Coriandrum sativum L.) and population dynamics in semi-arid region of Rajasthan. Int. J. Trop. Agric. 35: 779–783.Search in Google Scholar

Mena, G.T. and Gospodarek, J. (2024). White mustard, sweet alyssum, and coriander as insectary plants in agricultural systems: impacts on ecosystem services and yield of crops. Agriculture 14: 550, https://doi.org/10.3390/agriculture14040550.Search in Google Scholar

Michaud, J.P. (2002). Biological control of Asian citrus psyllid, Diaphorina citri (Hemiptera: Psyllidae) in Florida: a preliminary report. Entomol. News 113: 216–222.Search in Google Scholar

Michaud, J.P., Olsen, L.E., and Olsen, L.E. (2004). Suitability of Asian citrus psyllid, Diaphorina citri, as prey for ladybeetles. BioControl 49: 417–431, https://doi.org/10.1023/b-bico.0000034605.53030.db.Search in Google Scholar

Nair, B., Sengupta, S.K., Naidu, A.K., Mehta, A.K., Singh, K.P., and Jain, P.K. (2012). Assessment of heritability and genetic advance in coriander germplasms. JNKVV Res. J. 46: 317–321.Search in Google Scholar

Pareek, R.K., Sharma, A., and Kumawat, K.C. (2014). Feeding potential of Coccinella septempunctata L. on coriander aphid, Hyadaphis coriandri (Das). Ind. J. Entomol. 76: 52–54.Search in Google Scholar

Patil, P.N. and Pastagia, J.J. (2016). Effect of bee pollination on yield of coriander, Coriandrum sativum Linnaeus. Int. J. Plant Protect. 9: 79–83, https://doi.org/10.15740/has/ijpp/9.1/79-83.Search in Google Scholar

Patt, J.M., Hamilton, G.C., and Lashomb, J.H. (1997a). Foraging success of parasitoid wasps on flowers: interplay of insect morphology, floral architecture and searching behavior. Entomol. Exp. Appl. 83: 21–30, https://doi.org/10.1046/j.1570-7458.1997.00153.x.Search in Google Scholar

Patt, J.M., Hamilton, G.C., and Lashomb, J.H. (1997b). Impact of strip-insectary intercropping with flowers on conservation biological control of the Colorado potato beetle. Adv. Hort. Sci. 11: 175–181.Search in Google Scholar

Patt, J.M. and Rohrig, E. (2017). Laboratory evaluations of the foraging success of Tamarixia radiata (Hymenoptera: Eulophidae) on flowers and extrafloral nectaries: potential use of nectar plants for conservation biological control of Asian citrus psyllid (Hemiptera: Liviidae). Fla. Entomol. 100: 149–156, https://doi.org/10.1653/024.100.0121.Search in Google Scholar

Patt, J.M., Tarshis Moreno, A.M., and Niedz, R.P. (2020). Response surface methodology reveals proportionality effects of plant species in conservation plantings on occurrence of generalist predatory arthropods. PloS One 15: e0231471, https://doi.org/10.1371/journal.pone.0231471.Search in Google Scholar PubMed PubMed Central

Patt, J.M., Wainright, S.C., Hamilton, G.C., Whittinghill, D., Bosley, K., Dietrick, J., and Lashomb, J.H. (2003). Assimilation of carbon and nitrogen from pollen and nectar by a predaceous larva and its effects on growth and development. Ecol. Entomol. 28: 717–728, https://doi.org/10.1111/j.1365-2311.2003.00556.x.Search in Google Scholar

Proctor, M. and Yeo, P. (1972). The pollination of flowers. Taplinger Publishing Co, New York, p. 418.Search in Google Scholar

Qasim, M., Su, J., Noman, A., Ma, T., Islam, W., Hussain, D., Rizwan, M., Hameed, M.S., Khan, A.K., Ghramh, H.A., et al.. (2024). Citrus psyllid management by collective involvement of plant resistance, natural enemies and entomopathogenic fungi. Microb. Pathog. 197: 107047, https://doi.org/10.1016/j.micpath.2024.107047.Search in Google Scholar PubMed

Qureshi, J.A., Kostyk, B.C., and Stansly, P.A. (2014). Insecticidal suppression of Asian citrus psyllid Diaphorina citri (Hemiptera: Liviidae) vector of huanglongbing pathogens. PloS one 9: e112331, https://doi.org/10.1371/journal.pone.0112331.Search in Google Scholar PubMed PubMed Central

Qureshi, J.A., Rogers, M.E., Hall, D.G., and Stansly, P.A. (2009). Incidence of invasive Diaphorina citri (Hemiptera: Psyllidae) and its introduced parasitoid Tamarixia radiata (Hymenoptera: Eulophidae) in Florida citrus. J. Econ. Entomol. 102: 247–256, https://doi.org/10.1603/029.102.0134.Search in Google Scholar PubMed

Ramadan, M.F. (2023). Introduction to handbook of coriander (Coriandrum sativum): chemistry, functionality, and applications. In: Ramadan, M.F. (Ed.). Handbook of coriander (Coriandrum sativum). CRC Press, Boca Raton, pp. 1–8.10.1201/9781003204626-1Search in Google Scholar

Regar, P.K., Mahla, M.K., Lekha, P.A., and Chhangani, G. (2022). Population dynamics of coriander aphid and occurrence of their natural enemies in organic coriander. Pharm. Innov. J. 11: 1201–1205.Search in Google Scholar

Resende, A.L.S., Souza, B., Ferreira, R.B., and Aguiar-Menezes, E.L. (2017). Flowers of Apiaceous species as sources of pollen for adults of Chrysoperla externa (Hagen) (Neuroptera). Biol. Control. 106: 40–44, https://doi.org/10.1016/j.biocontrol.2016.12.007.Search in Google Scholar

Resende, A.L.S., Viana, A.J.D.S., Oliveira, R.J., Aguiar-Menezes, E.D.L., Ribeiro, R.D.L., Ricci, M.D.S., and Guerra, J.G.M. (2010). Consórcio couve-coentro em cultivo orgânico e sua influência nas populações de joaninhas. Hort. Bras. 28: 41–46, https://doi.org/10.1590/s0102-05362010000100008.Search in Google Scholar

Salamanca, J., Pareja, M., Rodriguez-Saona, C., Resende, A.L.S., and Souza, B. (2015). Behavioral responses of adult lacewings, Chrysoperla externa, to a rose–aphid–coriander complex. Biol. Control. 80: 103–112, https://doi.org/10.1016/j.biocontrol.2014.10.003.Search in Google Scholar

Salamanca, J., Souza, B., and Rodriguez-Saona, C. (2018). Cascading effects of combining synthetic herbivore-induced plant volatiles with companion plants to manipulate natural enemies in an agro-ecosystem. Pest Manag. Sci. 74: 2133–2145, https://doi.org/10.1002/ps.4910.Search in Google Scholar PubMed

Shields, M.W., Johnson, A.C., Pandey, S., Cullen, R., González-Chang, M., Wratten, S.D., and Gurr, G.M. (2019). History, current situation and challenges for conservation biological control. Biol. Control. 131: 25–35, https://doi.org/10.1016/j.biocontrol.2018.12.010.Search in Google Scholar

Snyder, W. (2019). Give predators a complement: conserving natural enemy biodiversity to improve biocontrol. Biol. Control 135: 73–82, https://doi.org/10.1016/j.biocontrol.2019.04.017.Search in Google Scholar

Spence, C. (2023). Coriander (cilantro): a most divisive herb. Int. J. Gastronomy Food Sci. 33: 100779, https://doi.org/10.1016/j.ijgfs.2023.100779.Search in Google Scholar

Swami, D., Jat, B.L., and Dotasara, S.K. (2018). Population dynamics of insect pests of coriander and their correlation with biotic and abiotic factors. J. Entomol. Zool. Stud. 6: 460–464.Search in Google Scholar

Togni, P.H., Venzon, M., Muniz, C.A., Martins, E.F., Pallini, A., and Sujii, E.R. (2016). Mechanisms underlying the innate attraction of an aphidophagous coccinellid to coriander plants: implications for conservation biological control. Biol. Control. 92: 77–84, https://doi.org/10.1016/j.biocontrol.2015.10.002.Search in Google Scholar

United States Department of Agriculture (2023). USDA plant hardiness zone map. Available at: http://planthardiness.ars.usda.gov/PHZMWeb/#.Search in Google Scholar

van Emden, H.F. (2003). Conservation biological control: from theory to practice. In: International symposium on biological control of arthropods. United States Department of Agriculture Forest Service, Morgantown, West Virginia, USA, pp. 199–208.Search in Google Scholar

van Rijn, P.C. and Wäckers, F.L. (2016). Nectar accessibility determines fitness, flower choice and abundance of hoverflies that provide natural pest control. J. Appl. Ecol. 53: 925–933.10.1111/1365-2664.12605Search in Google Scholar

Vattala, H.D., Wratten, S.D., Phillips, C.B., and Wäckers, F.L. (2006). The influence of flower morphology and nectar quality on the longevity of a parasitoid biological control agent. Biol. Control. 39: 179–185, https://doi.org/10.1016/j.biocontrol.2006.06.003.Search in Google Scholar

Verma, M.K., Pandey, V.P., Singh, D., Kumar, S., and Kumar, P. (2018). Studies on genetic variability in germplasm of coriander (Coriandrum sativum L.). J. Pharmacogn. Phytochem. 7: 2490–2493.Search in Google Scholar

Wäckers, F.L. (2005). Suitability of (extra-)floral nectar, pollen, and honeydew as insect food sources. In: Wäckers, F.L., van Rijn, P.C.J., and Bruin, J. (Eds.). Plant-provided food for carnivorous insects: a protective mutualism and its applications. Cambridge University Press, Cambridge, UK, pp. 17–74.10.1017/CBO9780511542220.003Search in Google Scholar

Wäckers, F.L. and Van Rijn, P.C. (2012). Pick and mix: selecting flowering plants to meet the requirements of target biological control insects. In: Gurr, G.M., Wratten, S.D., Snyder, W.E., with Read, D.M.Y. (Eds.). Biodiversity and insect pests: key issues for sustainable management. John Wiley & Sons, Ltd., West Sussex, UK. pp. 139–165.10.1002/9781118231838.ch9Search in Google Scholar

Wojciechowicz-Zytko, E. (2019). Attractiveness of some Apiaceae flowers for Syrphidae (Diptera) – pollinators and biotic agents. Acta Hortic. 1264: 275–282, https://doi.org/10.17660/actahortic.2019.1264.34.Search in Google Scholar

Wolcott, G.N. (1942). The requirements of parasites for more than hosts. Science 96: 317–318, https://doi.org/10.1126/science.96.2492.317.Search in Google Scholar PubMed

Received: 2024-08-28
Accepted: 2025-03-31
Published Online: 2025-08-18

© 2025 the author(s), published by De Gruyter on behalf of the Florida Entomological Society

This work is licensed under the Creative Commons Attribution 4.0 International License.

Articles in the same Issue

  1. Frontmatter
  2. Research Articles
  3. Establishment and monitoring of a sentinel garden of Asian tree species in Florida to assess potential insect pest risks
  4. Parasitism of Halyomorpha halys and Nezara viridula (Hemiptera: Pentatomidae) sentinel eggs in Central Florida
  5. Genetic differentiation of three populations of the fall armyworm, Spodoptera frugiperda (Lepidoptera: Noctuidae), in Mexico
  6. Tortricidae (Lepidoptera) associated with blueberry cultivation in Central Mexico
  7. First report of Phidotricha erigens (Lepidoptera: Pyralidae: Epipaschiinae) injuring mango inflorescences in Puerto Rico
  8. Seed predation of Sabal palmetto, Sabal mexicana and Sabal uresana (Arecaceae) by the bruchid Caryobruchus gleditsiae (Coleoptera: Bruchidae), with new host and distribution records
  9. Genetic variation of rice stink bugs, Oebalus spp. (Hemiptera: Pentatomidae) from Southeastern United States and Cuba
  10. Selecting Coriandrum sativum (Apiaceae) varieties to promote conservation biological control of crop pests in south Florida
  11. First record of Mymarommatidae (Hymenoptera) from the Galapagos Islands, Ecuador
  12. First field validation of Ontsira mellipes (Hymenoptera: Braconidae) as a potential biological control agent for Anoplophora glabripennis (Coleoptera: Cerambycidae) in South Carolina
  13. Field evaluation of α-copaene enriched natural oil lure for detection of male Ceratitis capitata (Diptera: Tephritidae) in area-wide monitoring programs: results from Tunisia, Costa Rica and Hawaii
  14. Abundance of Megalurothrips usitatus (Bagnall) (Thysanoptera: Thripidae) and other thrips in commercial snap bean fields in the Homestead Agricultural Area (HAA)
  15. Performance of Salvinia molesta (Salviniae: Salviniaceae) and its biological control agent Cyrtobagous salviniae (Coleoptera: Curculionidae) in freshwater and saline environments
  16. Natural arsenal of Magnolia sarcotesta: insecticidal activity against the leaf-cutting ant Atta mexicana (Hymenoptera: Formicidae)
  17. Ethanol concentration can influence the outcomes of insecticide evaluation of ambrosia beetle attacks using wood bolts
  18. Post-release support of host range predictions for two Lygodium microphyllum biological control agents
  19. Missing jewels: the decline of a wood-nesting forest bee, Augochlora pura (Hymenoptera: Halictidae), in northern Georgia
  20. Biological response of Rhopalosiphum padi and Sipha flava (Hemiptera: Aphididae) changes over generations
  21. Argopistes tsekooni (Coleoptera: Chrysomelidae), a new natural enemy of Chinese privet in North America: identification, establishment, and host range
  22. A non-overwintering urban population of the African fig fly (Diptera: Drosophilidae) impacts the reproductive output of locally adapted fruit flies
  23. Fitness of Bactrocera dorsalis (Hendel) (Diptera: Tephritidae) on four economically important host fruits from Fujian Province, China
  24. Carambola fruit fly in Brazil: new host and first record of associated parasitoids
  25. Establishment and range expansion of invasive Cactoblastis cactorum (Lepidoptera: Pyralidae: Phycitinae) in Texas
  26. A micro-anatomical investigation of dark and light-adapted eyes of Chilades pandava (Lepidoptera: Lycaenidae)
  27. Scientific Notes
  28. Early stragglers of periodical cicadas (Hemiptera: Cicadidae) found in Louisiana
  29. Attraction of released male Mediterranean fruit flies to trimedlure and an α-copaene-containing natural oil: effects of lure age and distance
  30. Co-infestation with Drosophila suzukii and Zaprionus indianus (Diptera: Drosophilidae): a threat for berry crops in Morelos, Mexico
  31. Observation of brood size and altricial development in Centruroides hentzi (Arachnida: Buthidae) in Florida, USA
  32. New quarantine cold treatment for medfly Ceratitis capitata (Diptera: Tephritidae) in pomegranates
  33. A new invasive pest in Mexico: the presence of Thrips parvispinus (Thysanoptera: Thripidae) in chili pepper fields
  34. Acceptance of fire ant baits by nontarget ants in Florida and California
  35. Examining phenotypic variations in an introduced population of the invasive dung beetle Digitonthophagus gazella (Coleoptera: Scarabaeidae)
  36. Note on the nesting biology of Epimelissodes aegis LaBerge (Hymenoptera: Apidae)
  37. Mass rearing protocol and density trials of Lilioceris egena (Coleoptera: Chrysomelidae), a biological control agent of air potato
  38. Cardinal predation of the invasive Jorō spider Trichophila clavata (Araneae: Nephilidae) in Georgia
  39. Retraction
  40. Retraction of: Examining phenotypic variations in an introduced population of the invasive dung beetle Digitonthophagus gazella (Coleoptera: Scarabaeidae)
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