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Optimizing hierarchical tree dissection parameters using historic epidemiologic data as ‘ground truth’

  • David Jacobson ,

    Roles Data curation, Formal analysis, Investigation, Validation, Visualization, Writing – original draft, Writing – review & editing

    quh7@cdc.gov

    Affiliations Parasitic Diseases Branch, Division of Parasitic Diseases and Malaria, Centers for Disease Control and Prevention, Atlanta, Georgia, United States of America, Oak Ridge Institute of Science and Education, Oak Ridge, Tennessee, United States of America

  • Joel Barratt

    Roles Conceptualization, Formal analysis, Investigation, Visualization, Writing – original draft, Writing – review & editing

    Affiliation Parasitic Diseases Branch, Division of Parasitic Diseases and Malaria, Centers for Disease Control and Prevention, Atlanta, Georgia, United States of America

Abstract

Hierarchical clustering of pathogen genotypes is widely used to complement epidemiologic investigations of outbreaks. Investigators must dissect trees to obtain genetic partitions that provide epidemiologists with meaningful information. Statistical approaches to tree dissection often require a user-defined parameter to predict the optimal partition number and augmenting this parameter can drastically impact resultant partition memberships. Here, we demonstrate how to optimize a given tree dissection parameter to maximize accuracy irrespective of the tree dissection method used. We hierarchically clustered 1,873 genotypes of the foodborne pathogen Cyclospora spp., including 587 possessing links to historic outbreaks. We dissected the resulting tree using a statistical method requiring users to select the value of a ‘stringency parameter’ (s), with a recommended value of 95% to 99.5%. We dissected this hierarchical tree across s-values from 94% to 99.5% (at increments of 0.25%), to identify a value that maximized partitioning accuracy, defined as the degree to which genetic partitions conform to known epidemiologic groupings. We show that s-values of 96.5% and 96.75% yield the highest accuracy (> 99.9%) when clustering Cyclospora sp. isolates with known epidemiologic linkages. In practice, the optimized s-value will generate robust genetic partitions comprising isolates likely derived from a common food source, even when the epidemiologic grouping is not known prior to genetic clustering. While the s-value is specific to the tree dissection method used here, the optimization approach described could be applied to any parameter/method used to dissect hierarchical trees.

Introduction

Hierarchical clustering is widely used in the field of molecular epidemiology to detect groups of genetically related pathogen isolates. However, an important limitation of hierarchical clustering is that hierarchical clusters are nested, meaning that small clusters comprising closely related isolates exist within larger clusters that get progressively larger as genetic relationships become increasingly distant. Consequently, investigators must dissect hierarchical trees into discrete genetic groupings (i.e., partitions) to facilitate prioritization of discrete genetic groups for subsequent epidemiologic investigation. Usually, the value of some tree-dissection parameter (e.g., a SNP distance threshold) is empirically selected by investigators to facilitate tree dissection, hopefully yielding partitions where all (or most) grouped isolates are representatives of the same strain [13]. In epidemiologic contexts, the objective is always to select a parameter value for tree dissection that groups isolates with a high likelihood of belonging to the same strain, and thus, have a high probability of being associated with a common source.

Various statistical methods exist that can be used to guide tree dissection by predicting an optimal partition number [4], yet these methods usually require users to select a value for one or more input parameters that can have a significant impact on the resulting partition memberships. As such, the value of any user-defined parameter for tree dissection should be set with careful consideration. Values yielding too few partitions can link dissimilar isolates together, making it difficult to identify suspected food vehicles. Alternatively, values yielding too many partitions may separate genetically similar isolates, causing outbreaks to be overlooked. Empirical selection of a user-defined input parameter value during tree dissection may yield accurate partitions, particularly for pathogens for which a large volume of robust historical molecular epidemiologic data is available. This is because historical genetic data can inform molecular epidemiologists of how genetically similar isolates of the same strain typically are; however, for many human parasites, including the foodborne parasite Cyclospora spp. [5], historic knowledge of circulating strains may be limited or absent, and the concept of what constitutes a strain may be complicated by sexual reproduction [6].

The intersect of an epidemiologically-defined cluster and its analogous genetic cluster will ideally be approaching 100%: this principle forms the basis of molecular epidemiology [7]. For example, a recently described tool based on multi-locus-sequence-typing (MLST) and hierarchical clustering for genotyping Cyclospora spp., generally displays approximately 90% concordance with epidemiologic data [8, 9]. However, routine Cyclospora spp. genotyping only began in the United States in 2018 [8], so the volume historic molecular data available for this pathogen is limited compared to available data for foodborne bacterial pathogens such E. coli O157 or Salmonella [1, 10, 11]. For the latter two bacterial pathogens, data on intra-strain genetic variation is available to inform selection of certain partitioning thresholds such as species-specific SNP-difference threshold [1, 10, 11].

Alternatively, the methods used for identification of discrete partitions within hierarchically clustered Cyclospora spp. data requires continued optimization. Given the current lack of historic ‘strain’ information for Cyclospora spp., we propose here that historic outbreak-linked genotypes could be used to optimize tree dissection parameters, by maximizing the degree to which genetic partitions conform to known epidemiologic groupings (i.e., maximizing partitioning accuracy against an epidemiologic gold standard). Importantly, the outbreak-linked, ‘gold standard’, genotypes used in this optimization must be confidently linked to an epidemiologic cluster, as speculative epidemiologic groupings may misrepresent true algorithmic performance. Subsequently, following optimization, these historic genotypes could be hierarchically clustered alongside genotypes from isolates of unknown linkage. On partitioning of the resultant hierarchical tree using optimized parameter values, resultant partitions comprising isolates with unknown linkage have a high likelihood of being derived from a common source and should be prioritized for epidemiologic follow-up. Optimization with gold standard epidemiologically linked genotypes has already proved successful in identifying high performing genetic distance calculation algorithms to use in Cyclospora spp. genotyping. We previously clustered matrices generated using common distance calculation approaches (e.g., Jaccard, Bray-Curtis, Manhattan, and Euclidean) as well as novel haplotype-based algorithms designed for sexually reproducing parasites (Barratt’s heuristic and Plucinski’s Bayesian), with Barratt’s heuristic outperforming all other methods when evaluating how accurately genetic clusters reflect gold standard epidemiologic clusters [12], as we propose to do here.

In a recent study, dissection of hierarchically clustered Cyclospora spp. MLST data to identify discrete partitions comprising closely related isolates, was performed using a statistical framework that requires selecting a value for the user-defined ‘stringency’ parameter [4]. In that study [4], we recommended that the stringency parameter be set to a value above 95% and below 100%, though we justified the use of the maximum recommended s-value of 99.5% to dissect a hierarchically clustered dataset of more than 1,000 Cyclospora spp. MLST genotypes [4]. Setting the stringency to 99.5% resulted in the delimitation of genetic partitions where 90.8% of epidemiologically linked isolates were also linked genetically (i.e., 90.8% sensitivity) [4]. We also advised that users should consider optimizing the stringency parameter (s) to maximize performance, though specific details on how this may be achieved were not provided [4]. Therefore, the aim of this study was to demonstrate how a given tree dissection parameter–in this case, the value of the stringency parameter—can be optimized using historic epidemiologic data to improve tree dissection accuracy. Ultimately, we show that compared to when tree dissection parameter values are empirically selected, optimization of parameters in the way described does result in genetic partitions that more accurately reflect the epidemiologic linkage of clustered genotypes.

Materials and methods

Genotyping data

We utilized a publicly available MLST dataset for Cyclospora spp. generated by the United States (U.S.) Centers for Disease Control and Prevention (CDC), the Public Health Agency of Canada, and certain U.S. State public health departments, as part of ongoing Cyclospora spp. genotyping performed during 2018, 2019, 2020, and 2021 [8, 9, 1318]. To maximize the diversity of isolates included this analysis, we also included genotypes from persons who became infected in China and Indonesia, and from persons presenting with cyclosporiasis in the UK after returning from travel. Briefly, this dataset comprised 1,873 Cyclospora sp. genotypes. These isolates had been sequenced at eight markers as previously described [8, 9, 18], including six nuclear markers and two mitochondrial markers. Illumina data from these isolates were accessed under NCBI BioProject Number PRJNA578931. Each isolates’ genotype had been ascertained using bioinformatic workflows previously described [8].

Epidemiologic information

Epidemiologic information for a subset of these 1,873 genotypes was collected prior to this study through Cyclosporiasis National Hypothesis Generating Questionnaires (CNHGQ) during routine US public health surveillance. Each CNHGQ included information on a case-patient’s food consumption history during a two-week period before becoming ill. Using this information, 587 isolates included in this analysis had been confidently linked to an outbreak or event that occurred in the USA, for which more than one isolate was genotyped (Table 1). Genotypes possessing clear epidemiologic links represented a reference for expected (i.e., ‘ground truth’) clustering outcomes when assessing clustering performance (see below). Isolates that could not be linked confidently to an outbreak cluster were designated as possessing “unknown epidemiologic linkage”. Isolates in this “unknown” category also included all isolates from outside the USA as CNHGQs were not collected for cyclosporiasis patients outside the USA.

Distance calculation and partition number selection

A pairwise distance matrix was calculated from these Cyclospora spp. genotypes using Barratt’s heuristic definition of genetic distance as previously described [3, 19, 20]. This matrix was hierarchically clustered using Ward’s method implemented via the agnes function in the R package ‘cluster’ [21]. Next, we applied Plucinski and Barratt’s framework as previously described [4] to dissect the resulting hierarchical tree into a k number of discrete partitions across 23 different stringency values (s-values): those ranging from 94% to 99.5%, at intervals of 0.25%. The number of discrete partitions (k) predicted using each of these 23 s-values was recorded. We subsequently dissected the hierarchical tree into the number of partitions (k) predicted for each s-value using the cutree R function [22]. The partition memberships resulting from each of these 23 tree dissection iterations was used to assess partitioning performance for each of the corresponding 23 s-values. All hierarchical trees in this manuscript were generated using ggtree in R [23].

Assessment of partitioning performance

For each of the 23 s-values tested, we classified clustering results obtained for each genotype as either a true positive (TP), false positive (FP), true negative (TN), or false negative (FN), using the definitions described below. From these classifications we calculated various performance metrics including sensitivity, specificity, positive predictive value (PPV), negative predictive value (NPV), and accuracy, as previously described [8]. The calculations were weighted by the ratio of genotyped isolates in each epidemiologic cluster to the total number of genotyped isolates with epidemiologic links (n = 587) so that larger epidemiologic clusters (i.e., with more genotyped isolates) would contribute more to the final values. Given that accuracy is a measure of proximity of results from the true value, we proposed that the optimal stringency setting would be the value of k that results in maximum accuracy, as determined by the equation:

After identifying the stringency setting that maximized accuracy, we assessed the discriminatory power of obtained using this setting by calculating Simpson’s index of diversity (D) as described elsewhere [7]. The value of D was determined by: where N is the total number of isolates (n = 1,873), S is the number of partitions (i.e., equal to k), and nj represents the number of isolates within the jth partition. D is calculated with all isolates, not just those with epidemiological linkages. Simpson’s index assesses a method’s ability to distinguish between unrelated strains sampled randomly from a given species [7], where values of D close to 1.0 generally indicate good discriminatory power. We therefore considered this an indicator of whether the optimal stringency value (i.e., the one that maximizes accuracy) also provides useful strain discrimination.

Classification of epidemiologically-linked isolates after clustering

To compute partitioning accuracy, each of the 587 isolates with epidemiologic links were classified as a TP, TN, FP, or FN based on whether they were correctly assigned to the same partition as their epidemiologically-linked partners or not. Previous investigations showed that most epidemiologically-linked isolates included in this analysis possess a similar genetic signature [8, 9, 18]. Therefore, each epidemiologic cluster would have a partition number (i.e., a genetic cluster) to which the majority of its epidemiologically-linked isolates would be assigned. For the purposes of classification, we refer to this as the ‘mode’ partition number for an epidemiologic cluster. True positives would comprise isolates that were correctly assigned to the mode partition number for their epidemiologic cluster. Next, if we consider a fictitious epidemiologic cluster called “Outbreak A”, true negatives for the “Outbreak A” cluster would include all isolates from Outbreaks X, Y, and Z that were not assigned to the mode partition for outbreak A. False negatives would include isolates that were not assigned to the mode partition number for their epidemiologic cluster. False positives would include isolates with a particular epidemiologic linkage that were assigned to a different partition to that of their epi-linked partners, and to a partition alongside isolates with a different epidemiologic linkage. Importantly, isolates belonging to different epidemiologic clusters can share the same mode partition number (i.e., unrelated outbreaks caused by the same strain). Therefore, isolates with the same mode partition number but possess a distinct epidemiologic linkage were not classified as false positive linkages for the purposes of our analysis. The classifications were performed for each epidemiologic cluster separately and the sum of all TP, TN, FP, and FN classifications for each epidemiologic cluster was used to compute an overall value of clustering accuracy for each stringency setting used, in addition to other performance metrics.

Ethics

Ethics approval for the use of clinical specimens was reviewed by the CDC Center for Global Health Human Research Protection Office under project determination number 2018–123. The need for patient informed consent was waived because the specimens were de-linked from any personal identifiers prior to submission to CDC.

Results

Stringency values of 96.5% and 96.75% produced identical performance results (Table 2) and were established as optimal for partitioning our hierarchically clustered dataset. All s-values ≥ 96.5% resulted in partitions with zero false positive links, yielding a specificity and PPV of 1 (Table 2). Conversely, all values ≤ 96.75% resulted in partitions with the fewest false negatives (n = 6), which maximized sensitivity and NPV (Table 2). Consequently, the optimal s-values of 96.5% and 96.75% meant we minimized both false positives and false negatives, which yielded partitions with the highest accuracy (99.96%). At the optimal s-values, the 1,873 genotyped isolates were distributed across 30 partitions (i.e., k = 30) (Tables 2 and 3). The optimal stringency setting also maximized the number of partitions that isolates with epidemiologic links (n = 587) were distributed across (17 partitions, Table 2). Sub-optimal accuracy was observed at an s-value of 99.5%, which maximized the number of false negatives (n = 39) as a consequence of dividing many linked isolates across different partitions (Table 2). Conversely, an s-value of 94% (the minimum value evaluated) yielded 73 false positives, due to assignment of many unrelated isolates to the same partition.

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Table 2. Clustering performance for each stringency (s) value.

https://doi.org/10.1371/journal.pone.0282154.t002

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Table 3. Impact of stringency setting on the partition (k) membership of genotypes linked to various epidemiologic clusters.

https://doi.org/10.1371/journal.pone.0282154.t003

The higher number of false positives at lower stringency values is a consequence of isolates from different epidemiologic clusters being assigned to the same partition. Specifically, this included isolates from cyclosporiasis case-patients linked to the 2018 Temporospatial Cluster A (Epi Cluster Number [E.C.N] - 07), 2021 Florida Italian-style restaurant (E.C.N—24), 2020 Salad Chain A (E.C.N.–22), and 2019 Distributor A Type 3 (E.C.N.–16) epidemiologic clusters; isolates from these four distinct outbreaks were assigned to the same partition at a stringency of 94% (Fig 1). At optimal s-values, only isolates linked to the 2020 Salad Chain A (E.C.N.–22) and 2019 Distributor A (E.C.N.–16) epidemiological clusters remained in the same partition (Fig 2), supporting that these two outbreaks were caused by the same strain. In contrast isolates linked to 2018 Temporospatial Cluster A (E.C.N—07), and the 2021 FL Italian-style restaurant (E.C.N—24) cluster were divided across two distinct genetic partitions at higher stringency values (Fig 2). At stringency values above the established optima, some isolates were incorrectly separated from their epidemiologically linked partners (i.e., false negatives). For example, out of the 132 genotyped isolates linked to the pre-packaged salad mix 2020_001 cluster, all 132 belonged to a single genetic cluster at the optimal settings, while 11 isolates were split into other partitions at a stringency of 99.5% (Fig 3, S1 File). Likewise, 6 of the 94 specimens belonging to 2018 Vendor A split from their epi-linked partners at 99.5% stringency (Fig 3).

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Fig 1. Impact of minimum stringency (s) value on genetic linking of epidemiologically-linked isolates.

The hierarchical tree generated from our distance matrix was dissected into the minimum value of k (k = 21) predicted using the 94% s-value. The outer circle of colored bars indicates the boundary between each partition predicted and the inner circle of colored bars represents the epidemiologic linkage of various isolates, where each bar color represents a distinct epidemiologic cluster (grey represents isolates of unknown epidemiologic linkage). Epidemiological clusters of interest are labeled in the colored boxes. (A) At k = 21, we observe that the labeled epidemiologic clusters on the top right of the tree all belong to a single genetic partition, indicating that different epidemiologic clusters are being unnecessarily grouped into a single genetic partition.

https://doi.org/10.1371/journal.pone.0282154.g001

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Fig 2. Impact of optimal stringency (s) value on genetic linking of epidemiologically-linked isolates.

The hierarchical tree generated from our distance matrix was dissected into the optimal value of k (k = 30) predicted using the 96.5% and 96.75% s-value. The outer circle of colored bars indicates the boundary between each partition predicted and the inner circle of colored bars represents the epidemiologic linkage of various isolates, where each bar color represents a distinct epidemiologic cluster (grey represents isolates of unknown epidemiologic linkage). Epidemiological clusters of interest are labeled in the colored boxes. (A) At k = 30, we observe that the labeled epidemiologic clusters on the top right of the tree are split between three different genetic partitions, while the two epidemiologic clusters on the bottom of the tree have 100% of isolates belonging to a single genetic partition.

https://doi.org/10.1371/journal.pone.0282154.g002

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Fig 3. Impact of maximum stringency (s) value on genetic linking of epidemiologically-linked isolates.

The hierarchical tree generated from our distance matrix was dissected into the optimal value of k (k = 67) predicted using the 99.5% s-value. The outer circle of colored bars indicates the boundary between each partition predicted and the inner circle of colored bars represents the epidemiologic linkage of various isolates, where each bar color represents a distinct epidemiologic cluster (grey represents isolates of unknown epidemiologic linkage). Epidemiological clusters of interest are labeled in the colored boxes. (A) At k = 99.5%, we observe that the labeled epidemiologic clusters on the bottom of the tree have isolates split across multiple genetic partitions, suggesting that the maximum stringency value is unnecessarily splitting epidemiologic clusters between partitions.

https://doi.org/10.1371/journal.pone.0282154.g003

Simpson’s index of diversity ranged from 0.9100 at k = 15 (s-values of 94% through 94.5%) to 0.9335 at k = 67 (s = 99.5%) (Table 2). At the optimal stringency values, k = 30 and Simpson’s index of diversity was 0.9210, which is indicative of good discriminatory power.

Discussion

We recently described a framework for dissecting hierarchically clustered genetic data that requires investigators to provide a user-defined stringency value that impacts downstream genetic partition memberships [4]. We recommended that the stringency parameter be set to a value between 95% and 100% and here we describe a process by which the selection of this parameter can be refined. While this seems like a small range of values, we demonstrate that even minor adjustments to the s-value can have a major impact on the resultant genetic partitions and subsequently, the perceived genetic linkages. This underpins the need for investigators to optimize user-defined parameters that impact the process of hierarchical tree dissection, regardless of the method employed.

Specifically, our results highlight the importance of selecting parameter values that maximize partitioning accuracy. In our investigation, all stringency values evaluated resulted in partitioning at an accuracy greater than 99%; however, at more relaxed stringency values (i.e., < 95%) greater than 70 false positives were observed, while at higher stringency values (i.e., > 98.5%) more than 30 false negatives were observed. At the optimal value established here, 0 false positives and only 6 false negatives were observed. Therefore, arbitrarily selecting a given tree dissection parameter without a systematic evaluation across a range of potential values may result in a loss of performance by inflating the number of false positives or false negatives.

An important characteristic of any molecular epidemiologic tool is that the intersect between epidemiologically-defined clusters and their analogous genetic partitions should be nearing 100% [7]. Optimization of tree dissection parameters in this context should include computation of accuracy using epidemiologically defined clusters as a ‘ground truth’ reference for expected clustering outcomes. These reference genotypes of known epidemiologic linkage should be clustered alongside isolates of unknown epidemiologic linkage that represent possible candidates for downstream epidemiologic investigation. Resulting partitions identified using optimized parameter values that containing isolates with an unknown epidemiologic linkage will subsequently have a high likelihood of being derived from a common source, and thus represent robust candidates for epidemiologic follow-up. This is because their assignment to the same partition was based on parameters optimized to an internal reference of expected genetic links.

For epidemiologic investigations of cyclosporiasis outbreaks, patients complete a CNHGQ that collects information on the foods they recall consuming days to weeks prior to falling ill. Cyclosporiasis often presents as intermittent, non-specific symptoms many days to weeks after consumption of contaminated produce, meaning that weeks may elapse between illness onset and CNHGQ interview. This delay can make it difficult for patients to recall specific meal components, potentially introducing noise to epidemiologic datasets [9]. Regardless, our experience with Cyclospora spp. has consistently demonstrated good concordance (~90% or more) between linkages identified via CNHGQ and genetic clustering. Accuracy of 100% may never be observed when assuming epidemiologic data as a true representative of ‘ground truth’, due to various sources of noise [9]. However, given the generally strong concordance between genotyping and these epidemiologic methods [8, 9], selecting parameter values that maximize accuracy seems warranted, as this–- in our experience—will usually yield partitions of unknown linkage that are more likely derived from a common source.

The discriminatory power of our dissected tree, determined by Simpson’s index of diversity (D), was 0.9210 at the optimal s-values which resulted in 30 partitions. This is slightly lower than the value of D = 0.95 recommended elsewhere as an indicator of good discriminator power [7]. None of the stringency values evaluated here exceeded 0.95 (we observed a maximum D = 0.9335 at stringency = 99.5%), which is likely the result of a confluence of multiple factors. First, our dataset is heavily weighted to isolates from cyclosporiasis case patients residing in the United States (U.S.) between 2018 and 2021, which is unlikely to reflect the full genetic diversity of Cyclospora spp. (i.e., only genotypes causing U.S. infections during these periods were analyzed). Second, the current MLST-based genotyping approach captures only a portion of the ~45 megabase Cyclospora spp. genome [6]; the MLST method involves sequencing 8 genetic markers each less than 1 kilobase in length each. Finally, Simpson’s index of diversity is a formula where datasets with greater richness (i.e., high number of clusters) and evenness (i.e., every cluster has a similar number of isolates) will have greater D-values compared to those with less richness and/or evenness. Our dataset consists of isolates from numerous cyclosporiasis outbreaks of varying sizes (Table 1), meaning richness and evenness are constrained by outbreak history, which impacts the value of D. Novel Cyclospora spp. types are identified each year [8, 9, 18] and work is being done to increase the number of markers used to genotype Cyclospora spp., thus discriminatory power will likely increase in response to these updates.

The sequencing of additional/different Cyclospora spp. MLST markers would warrant a re-assessment of the optimal s-value, as subsequent tree structures may be impacted by the inclusion of the additional genetic information. Likewise, a large increase in the number of outbreaks caused by novel Cyclospora spp. genetic types, may also augment the resultant tree topology and thus be an impetus for re-evaluating the optimal value of the stringency parameter. Generally, when factors impact tree structure (e.g., new markers) or when the gold standard epidemiologic references do not encompass the observed genetic diversity (e.g., outbreaks from novel types) it is highly recommended that tree dissection parameters (i.e., SNP distance thresholds, or the stringency parameter in this case) be re-optimized. Nevertheless, the presently evaluated epidemiologic clusters represent the currently observed genetic diversity fairly well (Fig 1). Our optimal s-value (i.e., 96.5 to 96.75) was determined using a set of genotypes with gold-standard epidemiologic groupings, plus approximately 1,300 isolates without epidemiologic linkages. The optimal s-value described here remains a robust choice when applied to Cyclospora spp. that include the same gold-standard genotypes and a selection of the 1,300 additional isolates used here, in addition to any clinical isolates of interest to the investigator. A suggested reference dataset is provided (S2 File).

To conclude, we describe a simple approach that has proven useful for optimizing hierarchical tree dissection parameters to facilitate subsequent epidemiologic investigations. While the present example applies specifically to optimization of the stringency parameter for a particular tree dissection framework, this same approach could easily be used to optimize parameter values that are applicable to any tree dissection approach. We anticipate that other molecular epidemiologists will find this work useful, especially in contexts where optimized parameters for tree dissection have not yet been established for certain pathogens.

Supporting information

S1 File. Complete clustering results.

This excel file contains a full list of calculation and results for accuracy and Simpson’s D at each s-value.

https://doi.org/10.1371/journal.pone.0282154.s001

(XLSX)

S2 File. Analysis support files.

This excel file includes the list of the suggested reference isolates, as well as the haplotype sheet and distance matrix used for clustering in this manuscript. The file also includes the epidemiologic linkages for each isolate.

https://doi.org/10.1371/journal.pone.0282154.s002

(XLSX)

Acknowledgments

We thank Yueli Zheng for bioinformatic support and Lauren Ahart and Marion Rice for assistance with epidemiologic classifications.

References

  1. 1. Stimson J, Gardy J, Mathema B, Crudu V, Cohen T, Colijn C. Beyond the SNP Threshold: Identifying Outbreak Clusters Using Inferred Transmissions. Mol Biol Evol. 2019;36(3):587–603. Epub 2019/01/29. pmid:30690464
  2. 2. Szarvas J, Bartels MD, Westh H, Lund O. Rapid Open-Source SNP-Based Clustering Offers an Alternative to Core Genome MLST for Outbreak Tracing in a Hospital Setting. Front Microbiol. 2021;12:636608. Epub 2021/04/20. pmid:33868194
  3. 3. Plucinski MM, Barratt JLN. Nonparametric Binary Classification to Distinguish Closely Related versus Unrelated P. falciparum Parasites. Am J Trop Med Hyg. 2021. Epub 2021/04/06. pmid:33819175
  4. 4. Barratt JLN, Plucinski MM. Epidemiologic utility of a framework for partition number selection when dissecting hierarchically clustered genetic data evaluated on the intestinal parasite Cyclospora cayetanensis. American Journal of Epidemiology. 2022;(in press).
  5. 5. Barratt JLN, Shen J, Houghton K, Richins T, Sapp SG, Cama V, et al. Cyclospora cayetanensis comprises at least 3 species that cause human cyclosporiasis. Parasitology. 2022:1–17. pmid:36560856
  6. 6. Barratt JLN, Park S, Nascimento FS, Hofstetter J, Plucinski M, Casillas S, et al. Genotyping genetically heterogeneous Cyclospora cayetanensis infections to complement epidemiological case linkage. Parasitology. 2019;146(10):1275–83. Epub 2019/06/01. pmid:31148531
  7. 7. van Belkum A, Tassios PT, Dijkshoorn L, Haeggman S, Cookson B, Fry NK, et al. Guidelines for the validation and application of typing methods for use in bacterial epidemiology. Clin Microbiol Infect. 2007;13 Suppl 3:1–46. Epub 2007/11/06. pmid:17716294.
  8. 8. Nascimento FS, Barratt J, Houghton K, Plucinski M, Kelley J, Casillas S, et al. Evaluation of an ensemble-based distance statistic for clustering MLST datasets using epidemiologically defined clusters of cyclosporiasis. Epidemiol Infect. 2020;148:e172. Epub 2020/08/04. pmid:32741426
  9. 9. Barratt J, Houghton K, Richins T, Straily A, Threlkel R, Bera B, et al. Investigation of US Cyclospora cayetanensis outbreaks in 2019 and evaluation of an improved Cyclospora genotyping system against 2019 cyclosporiasis outbreak clusters. Epidemiology and Infection. 2021;149:e214; In press. Epub 20210913. pmid:34511150
  10. 10. Coipan CE, Dallman TJ, Brown D, Hartman H, van der Voort M, van den Berg RR, et al. Concordance of SNP- and allele-based typing workflows in the context of a large-scale international Salmonella Enteritidis outbreak investigation. Microb Genom. 2020;6(3). Epub 2020/02/27. pmid:32101514
  11. 11. Dallman TJ, Byrne L, Ashton PM, Cowley LA, Perry NT, Adak G, et al. Whole-genome sequencing for national surveillance of Shiga toxin-producing Escherichia coli O157. Clin Infect Dis. 2015;61(3):305–12. Epub 2015/04/19. pmid:25888672
  12. 12. Jacobson D, Zheng Y, Plucinski MM, Qvarnstrom Y, Barratt JL. Evaluation of various distance computation methods for construction of haplotype-based phylogenies from large MLST datasets. Molecular Phylogenetics and Evolution. 2022;177:107608. pmid:35963590
  13. 13. Casillas SM, Bennett C, Straily A. Notes from the Field: Multiple Cyclosporiasis Outbreaks—United States, 2018. MMWR Morb Mortal Wkly Rep. 2018;67(39):1101–2. Epub 2018/10/05. pmid:30286055
  14. 14. Anonymous. Outbreak of Cyclospora Infections Linked to Fresh Basil from Siga Logistics de RL de CV of Morelos, Mexico: Centers for Disease Control and Prevention; 2019 [cited 2020]. https://www.cdc.gov/parasites/cyclosporiasis/outbreaks/2019/weekly/index.html.
  15. 15. Domestically Acquired Cases of Cyclosporiasis—United States, May–August 2018: Centers for Disease Control and Prevention; 2018 [cited 2020]. https://www.cdc.gov/parasites/cyclosporiasis/outbreaks/2018/c-082318/index.html.
  16. 16. Domestically Acquired Cases of Cyclosporiasis—United States, May–August 2019: Centers for Disease Control and Prevention; 2019 [cited 2020]. https://www.cdc.gov/parasites/cyclosporiasis/outbreaks/2019/a-050119/index.html.
  17. 17. Domestically Acquired Cases of Cyclosporiasis—United States, May–August 2020: Centers for Disease Control and Prevention; 2020 [cited 2021]. https://www.cdc.gov/parasites/cyclosporiasis/outbreaks/2020/seasonal/index.html.
  18. 18. Barratt J, Ahart L, Rice M, Houghton K, Richins T, Cama V, et al. Genotyping Cyclospora cayetanensis from multiple outbreak clusters with an emphasis on a cluster linked to bagged salad mix—United States, 2020. J Infect Dis. 2021. Epub 2021/10/05. pmid:34606577.
  19. 19. Barratt JLN, Sapp SGH. Machine learning-based analyses support the existence of species complexes for Strongyloides fuelleborni and Strongyloides stercoralis. Parasitology. 2020;147(11):1184–95. Epub 2020/06/17. pmid:32539880
  20. 20. Jacobson D, Zheng Y, Plucinski MM, Qvarnstrom Y, Barratt JLN. Evaluation of various distance computation methods for construction of haplotype-based phylogenies from large MLST dataset. Mol Phylogenet Evol. 2022:107608. Epub 2022/08/14. pmid:35963590.
  21. 21. Maechler M, Rousseeuw P, Struyf A, Hubert M, Hornik K. Cluster: cluster analysis basics and extensions. R package version. 2012;1(2):56.
  22. 22. Team RC. R: A language and environment for statistical computing. 2013.
  23. 23. Yu G, Smith DK, Zhu H, Guan Y, Lam TTY. ggtree: an R package for visualization and annotation of phylogenetic trees with their covariates and other associated data. Methods in Ecology and Evolution. 2017;8(1):28–36.