Evaluation of δ15N analysis to trace the origin of Diaphorina citri (Hemiptera: Liviidae) to citrus orchard fertilization management

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Ecology

Introduction

Stable isotopes of an element share the same atomic number but differ in mass due to variations in the number of neutrons. These elements, called poly-isotopics, have multiple stable forms that coexist in the environment reaching variable stages of equilibrium (Aston, 1921; Thomson, 1913). The equilibrium ratios can be vertically transferred along the food chain through consumption (Kelly, 2000; McCutchan Jr et al., 2003). Variation of stable isotope ratios through trophic levels have proven useful in traceability studies aimed at food quality control (Bateman, Kelly & Jickells, 2005; Camin et al., 2011; Rogers, 2008; Rossmann, 2001), organismal (Heinrich & Collins, 2017; Hobson, Wassenaar & Taylor, 1999; Ouyang et al., 2014) and system ecology (Boecklen et al., 2011; Boyer, Snyder & Wratten, 2016; Gratton & Denno, 2006; Hood-Nowotny & Knols, 2007; Hyodo et al., 2010; Scheunemann et al., 2016). Additionally, fertilizers or diets that differ in their isotopic composition can be used to study their effects on plant and animal isotope abundance among individuals of the same species (Bateman, Kelly & Jickells, 2005; DeNiro & Epstein, 1978; Oelbermann & Scheu, 2002; Tillberg & Breed, 2004; Webb, Simpson & Hedges, 1998).

Nitrogen (N) is one of the bio-elements of the ecosystem that is poly-isotopic and has been widely used in agriculture, food science (Camin et al., 2011; Mariotti et al., 1981) and ecology studies (Boecklen et al., 2011; Boyer, Snyder & Wratten, 2016; Gratton & Denno, 2006; Hood-Nowotny & Knols, 2007; Hyodo et al., 2010; McCutchan Jr et al., 2003; Ouyang et al., 2014; Scheunemann et al., 2016). Previous works have made relevant progresses in quantifying N isotope patterns of plants and soils at local to global scales as well as the mechanisms that underlie these patterns including the possible difficulties that come with interpreting isotope data (e.g., species-specific fractionation rates) (Craine et al., 2015). In general, interpretation of the nitrogen stable isotope ratio 15N/14N (expressed as δ15N) values relies on the premise that they are determined by the diet of consumers (McCutchan Jr et al., 2003). Deamination and transamination enzymes in animals prefer 14N, resulting in whole animal δ15N that is approximately 3‰ higher than its diet. Hence δ15N is also useful as an indicator of trophic level (McCutchan Jr et al., 2003; Minagawa & Wada, 1984).

The δ15N in plant material is strongly influenced by the primary source of nitrogen (Evans, 2001), and has been shown to be one of the most useful indices used to distinguish between organically and conventionally cultivated crops, including citrus (Bateman, Kelly & Jickells, 2005; Camin et al., 2011; Rapisarda et al., 2005). Synthetic fertilizers derived from atmospheric nitrogen (δ15Natm = 0‰) in the Haber process have low δ15N and are not permitted for organic production (Bateman & Kelly, 2007; CDFA, 2019; USDA, 2019). Instead, soil fertility for organic agriculture relies on selected fertilizers which may be permitted by an inspecting authority (i.e., USDA Organic guidelines). These include products of plant and animal origin such as animal manures, composts, rape seed meal, blood meal and fish meal ( CDFA, 2019; USDA, 2019).

The citrus industry in California has an economic impact of about $7 billion per year, and California is the state with the largest share of organic production, with around 4.1 million of hectares in 2016 (California Department of Food and Agriculture , 2019; USDA, 2019). The California citrus industry has been threatened since 2008 by the arrival of the Asian citrus psyllid, Diaphorina citri Kuwayama (Hemiptera: Liviidae) (Grafton-Cardwell, Stelinski & Stansly, 2013), vector of the bacterium Candidatus Liberibacter asiaticus (CLas) (Bové, 2006). CLas is transmitted into citrus plants through the psyllid feeding and it causes the incurable and devastating disease known as citrus greening or Huanglongbing (HLB) (Bové, 2006). HLB-infected trees show symptoms of leaf and flush yellowing and they bear few, deformed, small and un-flavorful fruits (Bové, 2006). The life cycle of D. citri includes five nymphal stages before the winged adult stage, which can disperse and infest new trees (Grafton-Cardwell, Stelinski & Stansly, 2013). Two factors have proved important for the spread of HLB by its vectors. First, the nymphal stages of D. citri have low mobility and they stay within one branch of a single tree. However, nymphs readily acquire CLas if they feed on infected parts of the tree and transmit, as adults, to healthy trees. Second, adults grown on a healthy tree have low chances to become HLB vectors if they feed on HLB infected tree sporadically (Inoue et al., 2009; Pelz-Stelinski et al., 2010). For these reasons, it should be possible to locate the citrus trees (or orchards) that are HLB infected (HLB reservoirs) if we are able to track the origin of HLB-positive D. citri adults captured.

Different methods have been developed to mark and recapture D. citri (Boina et al., 2009; Nakata, 2008). However, biogeochemical markers, such as stable isotope ratios, do not require marking and recapturing individuals, and they provide time-integrated information that can be obtained passively to monitor seasonal migration of the populations (Peterson & Fry, 1987; Rubenstein & Hobson, 2004). In an experiment conducted to determine long-range dispersal capacity in the absence of severe weather events, D. citri were able to disperse at least 2 km within 12 days (Lewis-Rosenblum et al., 2015). Nevertheless, other studies suggests that adult D. citri barely moved once they had colonized a host plant (Kobori et al., 2011). Therefore, differentiating between D. citri adults coming from organic and conventional orchards by δ15N values would be of immediate practical benefit in making appropriate strategic decisions on Integrated Pest Management (IPM) citrus programs. In addition, inferring the origin of HLB-infected insects with δ15N values would facilitate narrowing the zones with HLB infected trees at a local scale. Such a method would have a low-cost (around $6 per specimen) in the actual cost of the techniques used to monitor the pest movement and it could better inform where they are feeding in a specific season to apply prospective treatment options against the pest. Finally, this technique may improve food quality control studies, since being completely able to differentiate between organic and conventional crops may have a high impact on market prices and competitivity of the citrus industry (Camin et al., 2011; Rapisarda et al., 2005; Rogers, 2008).

In this study we hypothesize that i) δ15N values acquired during the nymphal stages of D. citri will be conserved in the final developmental stage (adult), ii) δ15N values from young citrus leaves will be highly correlated with the δ15N values from the pest, D. citri and iii) citrus orchard fertilization management can be traced using δ15N values of young leaves. If the three hypotheses are correct, we may be able to trace the citrus orchard (or area) of origin of individual specimens of D. citri. To test the first hypothesis, we conducted a laboratory experiment with D. citri using different fertilization treatments on the citrus relative host plant Murraya koenigii (L.) Sprengel (Sapindales: Rutaceae), which is commonly used for mass rearing of this insect. To test the second hypothesis, we performed a field experiment in four citrus orchards to correlate the δ15N values of the D. citri and the δ15N values of the plant material where the insects were feeding. Lastly, to test the third hypothesis we sampled leaves from a large number of commercial citrus orchards from Southern California labeled as organic or conventional production (Table 1).

Table 1:
Citrus orchards information.
Dates in bold indicates that the orchads were sampled in two sampling dates and “-” indicates unknown information.
Management Variety Orchard number Sampling dates Nitrogen resource Fertilizer (dosage) [N-P-K] Size (ha) Location
Conventional Navel C1 Mar-17/Jul-17 Urea, Ca(NO3)2 403.51 kg/ha of Ca(NO3)2 spread. Foliar treatments of 56.04 kg/ha of urea in August and 11.21 kg/ha in November 3.642 Redlands
C2 Mar-17 Urea, Ca(NO3)2 403.51 kg/ha of Ca(NO3)2 spread. Foliar treatments of 56.04 kg/ha of urea in August and 11.21 kg/ha in November 4.047 Redlands
C3 Dec-16/Mar-17 UN-32 (15-5-5) 4.261 Riverside
C4 Dec-16/Mar-17 UN-32 (15-5-5) 8.176 Riverside
C5 Mar-17/Oct-17 UN-32 1.94 Redlands
Valencia C6 Mar-17 Urea, KNO3 22,42 kg/ha of urea and 22,42 kg/ha of KNO3 in May 19.425 Loma Linda
C7 Mar-17 Ca(NO3)2 403.51 kg/ha of Ca(NO3)2 spread. 22.42 kg/ha of urea and 22.42 kg/ha of KNO3 in May 3.642 Redlands
C8 Mar-17 Urea, Ca(NO3) 2,KNO3 403.51 kg/ha of Ca(NO3)2 spread. 22.42 kg/ha of urea and 22.42 kg/ha of KNO3 in May 6.070 Loma Linda
C9 May-18 1.509 Lindsay
C10 May-18 3.365 Lindsay
Organic Navel O1 Mar-17/Jul-17 Manure Chicken pellets once a year 0.809 San Diego
O2 Mar-17 True (10-2-8) blended organic fertilizer in July, Oct and March 0.809 Temecula
O3 Dec-16/Mar-17 Urea Urea (56.04 kg/ha), Phosphorous acid (2.24 kg/ha), Zinc Manganese (5.6 kg/ha) 8.357 Riverside
O4 Mar-17/Oct-17 Urea, manure, feather meal (4-4-2)/(16-0-0) 0.887 Redlands
Valencia O5 May-17 Vegetable matter, manure and aquaculture residuals Pyganic (MGK), Oro Boost, Entrust SC, Compost (American Organics), Earthworm Organics Vermigrow tea 1.214 Salton Sea
O6 Urea, soy protein hydrolase, seaweed extract, (NH4)2SO4, NH4NO3, (NH4)2HPO4, KNO3 Explorer, Nutra Plus, Acadian seaweed, OMG, N-Texx, Ferticel (5-10-10) 6.741 Lindsay
O7 3.977 Lindsay
O8 May-18 3.963 Lindsay
O9 4.053 Lindsay
O10 5.863 Lindsay
O11 7.206 Strathmore
DOI: 10.7717/peerj.8807/table-1

Material and Methods

Impact of developmental stage on Diaphorina citriδ15N values incorporation

Diaphorina citri adults 4 to 7 days old (age of D. citri adults referred as days after emergence) were obtained from a colony established at the University of California Riverside (UCR). This colony has been reared on M. koenigii plants since 2011 in environmental rooms (∼27 °C, ∼50% RH, 8:16 D:L, light source; Sylvania Octron 4100k fo32/741 32 w) in the Insectary and Quarantine Facility at UCR. Collected D. citri adults were sorted with a 1:1 sex ratio in a mating cage that contained M. koenigii seedlings on an environmental room with the same conditions specified above. These seedlings were sown and grown in approximately 1g mixture of Vermiculite and Pearlite (2:1) without fertilization treatment inside of an 18 × 150 mm borosilicate glass culture tube (Fisher Scientific, Hampton, NH, USA). Seedlings developed until their stem reached approximately 8 cm in height with more than 5 leaves. 100 D. citri adults 9 to 11 days-old were confined inside the cages for mating and oviposition for four days. After the confinement period, the adults were removed, and their offspring developed until adult stage on the seedlings. The resulting D. citri adults were used as the initial population (F0) for the experiment. Seeds of M. koenigii were collected from two trees of the UCR Citrus Variety Collection. Upon collection, seeds were extracted from the fruit and washed to remove most of the extraneous flesh before being sterilized in a 2% NaClO solution. Thereafter, 300 seeds were split evenly into two groups in a greenhouse: the first group labeled as “organic” being fertilized with an organic OMRI certified bone meal fertilizer (Jobe’s Organics, 2-14-0 NPK), while the other group labeled as “conventional” was treated with Osmocote (14-14-14 NPK). The assigned fertilizer was applied (52 mg/pot) to the seeds upon sown and every three months until the M. koenigii plants were 6 to 8 months old.

The F0 D. citri adults were divided equally between organic and conventional treatments and were exposed to six M. koenigii plants (initial plants) from each fertilization treatment for five days (in environmental rooms at ∼27 °C; ∼50% RH, 8:16 D:L, light source; Sylvania Octron 4100k fo32/741 32 w). After oviposition, the insects were removed and stored at −20 °C. The resultant offspring growing on each plant were removed from their initial plant/treatment at different stages of development (2nd instar nymphs, 4th instar nymphs and adults 0 to 1, 0 to 3 and 0 to 7 days old [∼20 D. citri nymphs or adults on each of the three plants assigned to a specific “D. citri stage/age transferred” namely as “group of psyllids” and treatment for a total of n = 30 plants]) and randomly transferred to a new M. koenigii plant with the opposite fertilization treatment (the individuals that hatch on the plants with organic treatment were transferred to plants with conventional treatment and the opposite) (Fig. S1). After being transferred to their new host plat/treatment, all D. citri individuals from the 30 M. koenigii plants developed to adulthood and continued to feed for 12 days after emergence on the last plant/treatment. On day 12, they were removed from the plant and stored at −20  °C. From each plant, two to six adults were selected to perform δ15N analyses (see ‘Plan material and D. citri sample δ 15N analysis). Three leaves per plant for a total of 42 plants (12 plants where the F0 oviposited and 30 plants to which the insects were transferred) were processed to analyze the δ15N (see Plant material and D. citri sample δ 15 N analysis).

Relationship between the citrus leaf and D. citriδ15N values

Four citrus orchards (C1, C4, O1 and O4) (Table 1) were surveyed for the presence of D. citri populations, during the summer of 2017 (May-August), when D. citri populations usually peak in Southern California (Milosavljević et al., 2018). Ten to 20 trees in each grove with at least two D. citri colonies per tree were selected. White paint filter bags of 3.8 L (Workforce, China) were used as exclusion bags and secured with a zip-tie over each infested flush to isolate D. citri colonies with a maximum of three colonies per tree. Exclusion bags were checked weekly until more than 50% of the nymphs were either deceased or emerged as adults (71 exclusion bags with adults obtained), then the full branch was trimmed and stored at −20  °C until δ15N analyses of plant and insect material (see ‘Plant material and insect sample δ15N analysis’).

Field sampling for citrus leaf δ15N analysis

A total of 21 citrus orchards were sampled in the South and Central regions of California for δ15N analysis, consisting of 12 Valencia and 9 Navel sweet orange groves (Citrus sinensis (L.) Osbeck) all with Carrizo citrange as the rootstock (Table 1). Out of these 21 orchards, 11 were managed according to USDA organic guidelines and 10 were managed according to conventional methods (not organic) (Table 1). At each grove, a transect was selected to best encompass the presence of D. citri (checked by visual inspection) and the range in soil and environmental differences (a diagonal transect of the grove selecting a tree every other row when the D. citri presence allow it). Ten to 18 trees that fell upon this transect were randomly selected, and five young leaves (leaves from the most recent flushing period, light-dark green and fully expanded leaves) on different branches were collected at eye level (1.5 to 2 m above soil level) and stored at −20 °C until processed (see Plant material and D. citri sample δ15N analysis). Of these, we selected five trees randomly and three leaves for each were analyzed to compare leaves values of δ15N between conventional and organic orchards. Values of δ15N obtained from the plant material in the same citrus orchards but in different experiments from this study were also included in this analysis (see Relationship of the citrus leaf and D. citri δ15N values).

Six orchards (C1, C3, C4, O1, O3 and O4) were sampled on different seasons to assess seasonal variation of δ15N values of citrus leaves (Table 1). The six orchards were surveyed on March of 2017 (Spring). Additionally, the orchards C3, C4 and O3 were surveyed in December of 2016 (Winter) and C1, O1 and O4 were surveyed in July of 2017 (Summer).

Field experiments of this and the previous section were approved by the United States Department of Agriculture’s Animal and Plant Health Inspection Service (APHIS) (project number: #16-8130-0668-CA).

Plant material and D. citri sample δ15N analysis

Citrus and M. koenigii leaves were rinsed with deionized water three times before being dried at 60 °C in an Isotemp hybridization incubator (Fisher Scientific, Hampton, NH, USA) for 48 h. D. citri individuals were dried at 55  °C for 24 h or constant dry weight in the same incubator as the plant material. Leaves were individually ground into a fine powder using a mortar and pestle. D. citri samples were not ground and all material was stored separately in 2 mL microtubes. Target sample mass was calculated according to University of California, Davis Stable Isotope Facility (SIF) standards. Each sample was weighted in a 0.0001 g resolution scale (Intelligent Weighing Technology, Camarillo, CA, USA) then enclosed in 9 × 5 mm tin capsules (Elemental microanalysis, Okehampton, UK) and sealed to prevent leakage or contamination during the shipment. Samples were shipped to the University of California, Davis SIF in 96 well plates and analyzed using a PDZ Europa ANCA-GSL elemental analyzer interfaced to a PDZ Europa 20–20 isotope ratio mass spectrometer (Sercon Ltd., Cheshire, UK).

Statistics

All the statistical analyses described below were done in R (http://www.R-project.org). The difference between fertilization management on the δ15N values of the plant material in the experiment of δ15N values incorporation on the different D. citri stages were compared by one way ANOVA followed by Bonferroni’s posthoc tests for multiple comparison for all group of psyllids. The δ15N values for the insects in the same experiment were not independent since the source of all the insects for each treatment was from the same group of plants. Therefore, these values were analyzed using a linear mixed effects model with developmental stage (group of psyllids) as random factor with the “R” packages “car” and “nlme”. After this we ran pairwise comparisons between fertilizations for each group of psyllids using estimated marginal means with Tukey’s adjustment with the “R” package “emmmeans”. The average δ15N values of the citrus leaves and D. citri individuals from each exclusion cage installed on the citrus canopies were related with a linear regression. The citrus leaf δ15N values between seasons within the orchard were analyzed by Student’s t-test (see Citrus leaf δ 15N values on different seasons result). Finally, the δ15N values by leaf of the 21 citrus orchards sampled to assess differences between fertilization managements were analyzed by ANOVA, and the average of the citrus leaf δ15N values by orchard data were modeled using a kernel density estimation for the distribution of between-group (conventional and organic) variability with the “R” packages ggplot2, plyr and sm.

Results

Impact of developmental stage on Diaphorina citriδ15N values incorporation

The average δ15N values of the 41 M. koenigii plants grown with organic (8.139 ± 0.199‰) and conventional (2.867 ± 0.197‰) fertilization treatments were significantly different (F1,124 = 355.23, P < 0.001) (Fig. 1A, note that the initial M. koenigii plants, where the F0 oviposit, for each treatment are included in the analysis but not in the figure). The plants from the organic treatment assigned to each group of psyllids did not differ significantly on its δ15N values (F5,57 = 2.166, P = 0.071). However, the δ15N values from the plants with conventional treatment assigned to each group of psyllids differed significantly (F5,57 = 6.989, P  < 0.001) (Fig. 1A).

Impact of developmental stage on D. citriδ15N values incorporation.

Figure 1: Impact of developmental stage on D. citriδ15N values incorporation.

Average δ15N values (±SE) for (A) leaf tissue from M. koenigii plants (with two fertilization treatments: conventional and organic) used to feed D. citri transferred from the opposite fertilization treatment (different letters indicate significant differences between group of psyllids (transference time) on the same fertilization treatment) (B) D. citri adults transferred from the opposite fertilization treatment plants on different stages (2nd instar: when the D. citri nymphs were 2nd instar nymphs and successively). Black circles indicate those D. citri raised on conventional and transferred to organic on that specific transference time and white triangles the opposite (“ns” indicates no significant differences between fertilization treatments of the same group of psyllids). Note that all the adult individuals from each groups of psyllids were analyzed for its δ15N values at 12 days after their emergence.

The δ15N values from the F0 D. citri adult population (those psyllids raised on non-fertilized plants and that laid the eggs on the fertilized initial M. koenigii plants) did not significantly differ after being fed, as adults, on conventionally or organically fertilized M. koenigii plants for five days (F1,18 = 2.659, P = 0.12). However, their offspring, which spent some time feeding on fertilized plants as nymphs, had higher δ15N values (F0 D. citri adults δ15N = 0.945 ± 0.307‰; n = 20).

The values of δ15N on the D. citri adults obtained were not influenced by the fertilization treatment (χ 2 = 0.453, df = 1, P = 0.501) or the group of psyllids (χ2 = 2.794, df = 4, P = 0.593), but the interactions between these two variables was significant (χ2 = 123.384, df = 4, P < 0.001). The average δ15N values of D.citri adults raised on M. koenigii plants with conventional fertilization and transferred to plants with organic fertilization during the 2nd and 4th nymphal stages were higher (6.356 ± 0.551 and 7.154  ± 0.156‰  for 2nd and 4th respectively) compared to those same stage transferred from organically to conventionally managed plants (3.629 ±  0.247‰ and 4.752 ±  0.335‰ for 2nd and 4th respectively) (2nd: P < 0.001; 4th: P < 0.001) (Fig. 1B). However, D. citri adults that spent their entire nymphal period feeding on conventional or organic plants prior to being transferred to the opposite treatment 0–1 and 0–3 days after emerging as adults and feeding on their new hosts for 12 days, did not differ in the δ15N values between fertilization treatments (0–1 days: P = 1; 0–3 days: P = 0.844) (Fig. 1B). Conversely, D. citri adults transferred from organic plants to conventional plants at the stage “0–7 days old” had an average value of δ15N, 7.914 ± 0.274‰, higher than those transferred from conventional plants to organic plants at the same stage [5.098 ± 0.156‰, P  <  0.001] (Fig. 1B).

Relationship between the citrus leaf and D. citriδ15N values

The δ15N values for D. citri adults obtained in each exclusion cage were positively correlated with the δ15N values of the young citrus leaves from the same exclusion bag (Fig. 2). However, there were no significant influence of the fertilization managements (conventional vs. organic) on either the δ15N values of the leaves from the exclusion bags (avg. 6.774 ± 0.178‰, n = 271; F1,67 = 0.623, P = 0.433) or on the δ15N values of the D. citri adult individuals reared inside those exclusion bags (avg. 7.272 ± 0.169‰  n = 258; F1,67 = 1.379, P = 0.245). Therefore, it was not possible to trace the origin of the individuals. The difference between the average δ15N values of the leaves and the δ15N values of the D. citri adults per cage showed and an increase of 0.471 ± 0.125 (n = 71).

Relationship of the citrus leaf and D. citriδ15N values.

Figure 2: Relationship of the citrus leaf and D. citriδ15N values.

Positive correlation of average δ15N values (±SE) on citrus young leaves and the average δ15N values (±SE) of the D. citri feeding on each exclusion cage from four citrus orchards (C1, C4, O1 and O4) with two different fertilization managements (white marker for conventional and black marker for organic). Linear regression (dotted line): (δ15N D. citri) = 0.854 * (δ15N citrus leaf) + 1.479, R2 = 0.88, P < 0.001.

Citrus leaf δ15N values in different seasons

No significant differences were found in the citrus leaf δ15N values between seasons within orchards (C1; t(36) = 0.91, P = 0.437, C3; t(28) = 1.39, P = 0.176, C4; t(21) = 0.63, P = 0.534, O1; t(23) = 1.36, P = 0.186, O3; t(21) = 0.08, P = 0.936, O4; t(16) = 0.9, P = 0.381). The δ15N values of the 239 young citrus leaves analyzed from six orchards (C1, C3, C4, O1, O3 and O4) varied between a minimum of 2.352 ‰ in O1 in Summer of 2017 and a maximum of 18.393‰ in the same orchard in Spring of 2017. From the citrus orchards compared in winter (December 2016) and spring (March 2017) (C3, C4 and O3), O3 had the highest average citrus leaf δ15N value with 9.589 ± 0.261‰ and 9.557 ± 0.143‰ in winter and spring respectively (Fig. 3). From the citrus orchards compared in spring (March 2017) and summer (July 2017) seasons (C1, O1 and O4), the highest average citrus leaf δ15N values were obtained from O1 with 8.212 ± 1.035‰ and 9.029 ± 1.179‰ in Spring and Summer respectively (Fig. 3).

Citrus leaf δ15N values in different seasons.

Figure 3: Citrus leaf δ15N values in different seasons.

δ15N (‰) average values (±SE) of young citrus leaf tissue from six citrus orchards (C1, C3, C4, O1, O3 and O4) in three different seasons; Winter of 2016 (December), Spring of 2017 (March) and Summer of 2017 (July). C3, C4 and O3 sampled in December of 2016 and March of 2017 (all orchards and periods n = 5). C1, O1 and O4 sampled in March of 2017 (all orchards n = 5) and July of 2017 (C1 and O1 n = 9, O4 n = 17). No significant differences were found in each orchard between seasons.

Citrus leaf δ15N values in conventional and organic groves

Significant differences were found in the δ15N values between fertilization managements (F1,548 = 79.244, P < 0.001). On average, the organic and the conventional orchards had a δ15N value of 8.158  ± 1.038‰ and 5.185 ± 0.561‰ respectively. The maximum δ15N value (20.103‰) was detected in an organic orchard (O2) and the minimum δ15N value (1.215‰) was obtained from a conventional orchard (C8) (Fig. 4). Modeled Kernel distribution density curves for the citrus leaf δ15N values for the organic and conventional orchards showed that data from conventional orchards followed a normal distribution (Shapiro–Wilk normality test = 0.978, P = 0.956) and data from organic orchards followed a bimodal distribution (Fig. 5). Although there was a definite tendency for conventional citrus orchards to have lower δ15N values, there was overlap between the δ15N values for the organic and conventional citrus orchards (Fig. 5). Ninety-nine percent (p = 0.01) of the modeled conventional δ15N values would be expected to have a δ15N value below 10‰. This means that δ15N values above 10 ‰  could be expected to be obtained from organic citrus orchards, whereas δ15N values below 10 ‰ could not be unambiguously identified as organic or conventional.

Citrus leaf δ15N values in conventional and organic groves.

Figure 4: Citrus leaf δ15N values in conventional and organic groves.

Average δ15N (‰) values (±SE) of 21 citrus orchards under different fertilization managements (Table 1) (dark grey for organic orchards: n = 11; white for conventional: n = 10; black points indicate the outliers).
Probability density for average δ15N values for citrus orchards.

Figure 5: Probability density for average δ15N values for citrus orchards.

Modeled kernel density estimation curves and histogram of the raw data for the organic (light grey; n = 11) and conventional (black curve and dark grey; n = 10) average citrus leaf δ15N values per orchard. The dashed lines show the average for each data group.

Discussion

Our data indicate significant differences in the citrus leaf δ15N values between organic and conventional citrus orchards. Despite this difference, given the high variability of the δ15N values, mostly in organic citrus orchards, it would be impractical to use a single analysis of the δ15N values in the citrus leaves to discriminate or confirm if an orchard has been following organic or conventional fertilization managements. However, the tendency for conventional citrus to have lower δ15N values allows us to define a limit value of 10 ‰ above which the young citrus leaves δ15N values obtained could be considered organic at 99% confidence level, whereas citrus leaves with δ15N values below 10‰ could not be confidently assigned to either fertilization treatment. The application of δ15N analysis to discriminate between organic and conventional cultivation has been discussed in detail in previous studies (Bateman, Kelly & Woolfe, 2007; Rogers, 2008). Here we present the first analysis of δ15N from young citrus leaves as an indicator of the orchard fertilization management. We found that the average δ15N values per orchard do not vary between seasons (Fig. 3), which makes the sampling season a non-critical factor for future studies. Our study also shows a high variability in the δ15N values from plant tissues sampled within citrus orchards with the same fertilization management, especially in organic orchards (Fig. 4). These differences in the 21 citrus orchards tested may be due to different reasons, all of them influenced directly by biochemical processes during fixation of N in the soil (Handley & Raven, 1992). The high variation in the δ15N values obtained within the organic treatments may be due to differences of treatments in their fertilization regimens (Table 1). Additionally, the irrigation frequency has an important effect on the decomposition of the organic matter and this may influence the N of organic origin available for the plant in the soil (Amundson et al., 2003). The citrus orchards used in this study belong to different growers that use different irrigation frequency and were located in areas with different soil types and structure. All these factors may add variability to δ15N values. Previous studies already showed a greater variability in the δ15N values in the organic groves (Bateman, Kelly & Woolfe, 2007). Remarkably, Legaz et al. (1982) found that N in citrus goes from old tissues to new tissues and is replaced, in those old tissues, by the N that comes from fertilization every growing season. Therefore, the δ15N measured in young leaves in this study comes mostly from the N reserve in old leaves which their N supply was replenished with N coming from the fertilizer applied the previous year, that means that is not replenished with the N from the last fertilization. Consequently, the time passed since each citrus orchard first adopted an organic fertilization management may be key to identify that orchard based on δ15N value. The average δ15N value obtained in this study for the conventional citrus orchards (∼5.2 ‰ for young leaves) was slightly higher than the average δ15N values obtained in previous studies in citrus with the same fertilization management (∼4.4‰ for fruit pulp) (Rapisarda et al., 2005). This slight increase may be due to the contribution of reactive nitrogen deposition in the soil from the traffic-derived NO2 (Ammann et al., 1999; Redling et al., 2013). It is widely known the high intensity traffic in the highways of Southern California, and it had been demonstrated that the plant material close to road traffic increase its δ15N by assimilating the nitrogen deposition from the traffic-derived NO2 (Ammann et al., 1999; Redling et al., 2013). The effect of this nitrogen deposition on the δ15N values is not adequately studied in commercial crops, even so this effect cannot explain the wide range in the δ15N values found in this and previous studies in organic crops (Bateman, Kelly & Woolfe, 2007; Rogers, 2008).

We found a significant correlation between the D. citri adults and host plant δ15N values in the field study on citrus trees and in the lab experiment on M. koenigii plants (Figs. 1 and 2). However, because of the high variability in the δ15N values between citrus orchards with the same fertilization management, especially in the organic ones, it has proved difficult to pinpoint D. citri nymphal natal origin using δ15N insect values. On average, the δ15N values for D. citri increased 0.4‰ for each unit increase in the values from the plant material where they were feeding on until they reached adult stage (young citrus leaves from the same exclusion cage). This result is consistent with the typical trend of δ15N values in animal tissues (second trophic level), which shows considerable enrichment compared to the δ15N values from the plants (first trophic level) (Rossmann, 2001).

In the laboratory experiments, we were able to establish the origin (organic or conventional treatment) of D. citri adults when the insects were feeding on plants with the same fertilization treatment throughout all nymphal stages. The δ15N values of D. citri adults that were transferred to the opposite fertilization treatment in the 2nd or 4th nymphal stage, had the δ15N values correlated with the δ15N values of leaves of the last fertilization treatment where they were feeding on (Fig. 1B). There were no significant differences in the δ15N values of D. citri adults that were switched from one fertilization treatment to another before they were three days old (Fig. 1B). Those D. citri adults that switched diet after ∼seven days old had δ15N values similar to those of the plants that they were feeding on as nymphs (Fig. 1B). In addition, the D. citri adults used as initial population (F0) in the assay “Impact of developmental stage on Diaphorina citri δ15 N incorporation” had no significantly different δ15N values after being fed on plant of different fertilization treatment for five days (oviposition period). All these results suggest that D. citri acquire the δ15N values mostly at the nymphal stage, and as newly emerged adults (less than three days old) (Fig. 1B). This may be due to the sclerotization process after adult emergence. The isotope label is fixed into structural body tissue of the organism at different moments depending if there are metabolically active or inert tissues (Rubenstein & Hobson, 2004). During the sclerotization process of the insect that happens after emergence, it may take high quantities of N from the plant and this N may fix in the exoskeleton of the insect, leaving the δ15N imprint of the last meal before sclerotization (Andersen, 2010).

Conclusion

Stable isotopes have been proven to accurately reflect sources of nutrients in food webs and to unravel the migratory movements of insects. However, it does require a clear understanding of these isotopic patterns in nature and these studies should include the following steps. First, select a tissue that represents the appropriate temporal period of integration of geographical information, isotopically characterizing and differentiating among populations of interest, and finally linking populations by inferring geographical (or plant) origins based on isotopic similarity (Rubenstein & Hobson, 2004). Here, we selected a tissue, the young citrus leaves, which represents the appropriate temporal period and niche of D. citri. We tried to differentiate among organic vs. conventional fertilization managements and we linked the D. citri populations by inferring plant origin based on δ15N similarity (with positive results in the laboratory). However, we were not able to correlate all these data to pinpoint the origin of D. citri due to the enormous variability in the fertilization managements used in citrus orchards, especially in the organic fertilization management.

Supplemental Information

Workflow chart of the experiment on the impact of developmental stage on Diaphorina citri δ15N values incorporation

Draw credit: Francesc Gomez Marco.

DOI: 10.7717/peerj.8807/supp-1

N isotope values for all the experiments

DOI: 10.7717/peerj.8807/supp-2
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