Abstract
Background:
Uranium exposure remains an important environmental legacy and physiological health concern, with hundreds of abandoned uranium mines located in the Southwestern United States largely impacting underserved indigenous communities. The negative effects of heavy metals on barrier permeability and inhibition of intestinal epithelial healing have been described; however, transcriptomic changes within the intestinal epithelial cells and impacts on lineage differentiation are largely unknown.
Objectives:
Herein, we sought to determine the molecular and cellular changes that occur in the colon in response to uranium bearing dust (UBD) exposure.
Methods:
Human colonoids from three biologically distinct donors were acutely exposed to UBD then digested for single cell RNA sequencing to define the molecular changes that occur to specific identities of colonic epithelial cells. Validation in colonoids was assessed using morphological and imaging techniques.
Results:
Human colonoids acutely exposed to UBD exhibited disrupted proliferation and hyperplastic differentiation of the secretory lineage cell, enteroendocrine cells (EEC). Single-cell RNA sequencing also showed more EEC subtypes present in UBD-exposed colonoids.
Discussion:
These findings highlight the significance of crypt-based proliferative cells and secretory cell differentiation using human colonoids to model major colonic responses to uranium-bearing particulate dust exposure. https://doi.org/10.1289/EHP13855
Introduction
Uranium mining in the United States arose in the 1940s, peaked in the 1970s, and subsided in the late 1980s, with extensive activity concentrated in Navajo, Puebloan, and other indigenous lands in the Southwest.1 To date, over 500 mines in this region are considered abandoned uranium mines (AUM).2 Heavy metals from AUMs transfer into the sediment and groundwater,3,4 with nonfissile uranium (238U) levels in surrounding communities exceeding maximum contamination levels () dictated by the US Environmental Protection Agency.5 For example, well water in Nambe Pueblo (Santa Fe, New Mexico) once contained 238U.6 Even partially remediated uranium mines degrade over time and cause heavy metal contamination of the surrounding sediment and groundwater.7 This has led to unacceptable 238U levels found in community water sources throughout the US, even in aquifers that are not near uranium mines.8,9
Although 238U is weakly radioactive, it primarily negatively influences human health as a chemotoxicant and can accumulate in various organs.10–12 The communities that reside near AUMs are chronically exposed to particulate dust with varying levels of uranium [referred to as uranium-bearing dust (UBD)] via inhalation and ingestion,13,14 increasing their overall health risks. Studies in rodents found that chronic environmental exposure to UBD was linked to impaired neurological function,15 pulmonary damage,16 hepatotoxicity,17 and reproductive defects.18 Epidemiological studies in humans have found that uranium exposure correlated with renal damage.19
Specific to the gut, chronic exposure to environmental toxicants and heavy metals has been linked to intestinal inflammation,20 increased susceptibility to pathogen-induced diseases,21,22 circulating inflammatory potential,23 and colorectal cancer.24 Additionally, heavy metal exposure has been shown to negatively impact the microbiota,25 immune cells,26,27 and the intestinal epithelial barrier28 in both rodent and Caco-2 cell studies. Yet, the molecular changes that can lead to these pathologies are undefined. The 238U, via UBD, enters the intestine via ingestion or inhalation. Inhaled sedimentary particles are transported to the epiglottis by tracheobronchial cilia, then swallowed.29 Reported amounts and rate of uranium absorption in the digestive tract were fairly low, from 0.1 to 7%,30 bringing into question how systemic health impacts arise from direct toxicity to the gut. In mice, ingested uranium was primarily absorbed in the lower intestinal tract (colon),26 suggesting 238U-related cellular changes may originate in the colon.
The intestine is the largest immune organ in humans31 and directly communicates with the brain via hormone-secreting enteroendocrine cells (EECs) and the enteric nervous system.32,33 Thus, detrimental effects to the intestine can indirectly affect systemic health. The UBD utilized in this study was environmentally relevant, as it was obtained from a church attic in Paguate, NM, a village in the Laguna Pueblo located next to one of the largest open-pit uranium mines in the United States, the Jackpile Mine.34
Human colonoid cultures are a tractable, epithelial-only model that can indefinitely proliferate due to the presence of adult intestinal stem cells,35 making them a valuable model to study how the epithelium responds to intestinal injury and the factors involved in epithelial regeneration. The current lack of understanding on how heavy metals, specifically in particulate form like UBD, affect intestinal epithelia suggest a novel approach is needed.
Enteroendocrine cells are rare hormone-producing cells in the gut.36,37 They are distributed throughout the intestinal epithelium, making up only of the epithelial cell population. Thus, EEC function is difficult to study in whole animals. Recent studies showed that intestinal organoids are a physiologically relevant model to study EEC differentiation and function.38,39 Intestinal organoids produce the various EEC subtypes, retain regional specificity to the gut hormones produced, and respond to a variety of physiological stimuli.40
In this study, we used single-cell RNA sequencing (scRNA-seq) to characterize UBD-induced changes to intestinal epithelial cell lineages. We used human colonoids as a relevant model of human intestine to characterize UBD-induced transcriptomic changes and present them as a relevant pathophysiological model for studies in host–toxicant interactions.
Methods
Tissue Collection and Colonoid Generation
Human colonoid studies were reviewed and approved by the Johns Hopkins University School of Medicine institutional review board (IRB number NA_00038329) and University of New Mexico institutional review board (IRB number 18-171). Colonic biopsies were obtained from healthy individuals undergoing screening colonoscopies who had given informed written consent. All colonoids were generated from proximal colonic biopsies from patients undergoing routine, screening colonoscopy and with no pathophysiology. Colonic crypt isolation and colonoid generation were prepared as previously reported.41,42 Isolated crypts were resuspended in Matrigel (Corning) and droplets were plated in a 24-well plate (Corning). After polymerization at 37°C, of organoid expansion media was added for 2 d [Advanced Dulbecco’s modified Eagle medium (DMEM)/Ham’s F-12 (ThermoFisher), penicillin/streptomycin (Quality Biological), HEPES (ThermoFisher), and 1× GlutaMAX (ThermoFisher), with 50% vol/vol WNT3A conditioned medium (ATCC CRL-2647), 15% vol/vol R-spondin1 conditioned medium (cell line kindly provided by Calvin Kuo, Stanford University, currently available through Sigma-Aldrich), 10% vol/vol Noggin conditioned medium (cell line kindly provided by Gijs van den Brink, Tytgat Institute for Liver and Intestinal Research, and described in Heijmans et al.43), 1× B27 supplement (ThermoFisher), N-acetylcysteine (MilliporeSigma), human epidermal growth factor (ThermoFisher), (Leu-15) gastrin (AnaSpec), A83-01 (Tocris), SB202190 (MilliporeSigma), primocin (InvivoGen), CHIR99021 (Tocris), and Y-27632 (Tocris)]. All conditioned media were generated following, in precise detail, the protocol from the vendor or initial publication. Briefly, cells for conditioned media were grown to 80% confluency, upon which the media was replaced with Advanced DMEM with fetal bovine serum (FBS) (WNT3A) or without FBS (R-spondin1 and Noggin). Media were not changed until collection. Conditioned media from WNT3A cells were collected on days 4 and 7, combined, filtered through a filter, aliquoted, and stored at for up to 6 months. Conditioned media from R-spondin1 and Noggin cells were collected on day 7, filtered through a filter, aliquoted, and stored at for up to 6 months.
After 2 d, the organoid expansion media (without CHIR99021 and Y-27632) was replaced every other day. Colonoids were passaged every 10–14 d by harvesting in Cultrex Organoid Harvesting Solution (Bio-Techne, Minneapolis, MN) at 4°C with shaking for 45 min, as previously described.44 All colonoid cultures were maintained at 37°C and 5% . Unless noted, colonoid lines have been passaged times.
Brightfield Imaging
Colonoids plated in Matrigel in 24-well plates were imaged during experiments on a Zeiss Axio Observer A1 inverted microscope (Zeiss) with images captured on CellSense imaging software (Olympus). As shown in previous intestinal organoid studies, propidium iodide (PI) was used to quantify changes in cell death.44–47 PI and DAPI (ThermoFisher) were added at a final concentration of and , respectively. Colonoids were placed at 37°C for 1 h before imaging. Images were viewed and processed using OlyVia (Olympus). Total cells and PI+ cells were counted in ImageJ. independent experiments were performed, with at least 1,000 cells counted in each condition.
Uranium-Bearing Dust Analysis
UBD was obtained from a church attic on indigenous lands that lie adjacent to the 3,000-acre Jackpile mine in New Mexico. Permission was granted by the Environmental and Natural Resources Department of the Laguna Pueblo with assistance in obtaining the sample from the Southwest Information and Research Center. Samples of the collected dust were sieved using a filter. Transmission electron microscopy (TEM) analyses of the dust were carried out on all particulates size fraction for an unbiased analysis. Particulates from this fraction, suspended in acetone, were deposited onto holey carbon film supported on Cu TEM grids using pipettes. For the TEM analysis, five TEM grid squares were studied in detail. The samples were air dried and then analyzed using a JEOL 2010F FEG TEM/STEM (JEOL USA) operating at . The samples were imaged using a variety of different TEM and scanning transmission electron microscopy (STEM) techniques, including bright-field TEM and high-angle annular dark-field STEM imaging. Uranium-bearing particulates were identified on the JEOL 2010F by energy dispersive X-ray spectroscopy (EDS) using an Oxford Instruments AZtecEnergy EDS system (Oxford Instruments) coupled to an Oxford X-Max silicon drift detector (SDD). The detailed distribution of U-bearing phases and their association with other minerals was obtained using STEM EDS spectral X-ray mapping. TEM and STEM images of two examples of these U-bearing grains are shown in Figure S1.
Treatment and Preparation of Single Cells from 3D Colonoids for Single-Cell RNA Sequencing
Colonoids used for sequencing are described in Table S1. UBD was diluted in organoid expansion media, then colonoids in Matrigel were treated overnight (18 h) with UBD, with control colonoids receiving the same volume/volume of organoid expansion medium as the vehicle. Dosage was chosen based on prior studies26,48–51 that showed molecular changes to cells or animals exposed to uranium, but with minimal cytotoxic damage, since acute uranium exposure is not linked to cytotoxicity. Next day, colonoids were harvested from Matrigel using Cultrex Organoid Harvesting Solution, then resuspended in TrypLE enzyme solution (ThermoFisher), transferred to a 24-well plate and spun at at 37°C for 45 min in a spinoculator (Mixer HC; USA Scientific) to digest into single cells. Single cells were washed in of Advanced DMEM/F12, pelleted again, resuspended in of organoid expansion media and filtered with Flowmi cell strainers (SP Bel-Art). Cells were transported to the UNM Analytical and Translational Genomics Core in the UNM Comprehensive Cancer Center for counting and processing. Average processing time from colonoids to library preparation was hours, and the cells were highly viable ().
Single Cell and Library Preparation
Using the Cell Countess II FL (ThermoFisher), single cells and viability were counted by Trypan Blue exclusion. All reagents for single cell and library preparation were purchased from 10X Genomics and provided by the UNM Comprehensive Cancer Center. The Next GEM Chip G was loaded and put into the Chromium Controller for processing, creating the GEMs (gel beads-in-emulsion). cDNA synthesis of the GEMs was completed per the 10X Chromium Next GEM 3’ protocol. Synthesized cDNA was evaluated for quality and quantity on a DNA High-Sensitivity Chip on the Agilent BioAnalyzer machine. Next, cDNA was fragmented, adaptor ligated, and sample indexed (barcoded) with PCR. Once the libraries were completed, they were processed on a DNA High-Sensitivity Chip with the Agilent BioAnalyzer to ensure that the final libraries were bp in size. They were also processed with the KAPA Library quantification kit to verify the concentration of final libraries.
Pooling and Sequencing Quality Control
Sample concentration was determined using Agilent Tape Station 4200 and Invitrogen Qubit 4.0. Samples were diluted with molecular grade water, normalized, and pooled at , according to Illumina protocol, prior to quantitative real-time polymerase chain reaction (qPCR) to determine cluster efficiency. Samples were loaded onto an Illumina NovaSEQ 6000 instrument and sequenced on S4 Flow cells at specified read length. Data were delivered in FASTQ file format.
Processing FASTQ Reads into Gene Expression Matrices
Raw FASTQ reads from sequencing were processed using Cell Ranger (version 2.0.0) software from 10X Genomics. In brief, sequencing reads were demultiplexed, unique molecular identifiers (UMI) were collapsed, and reads aligned to the human transcriptome GRCh38-3.0.0 as the reference.52
scRNA-Seq Quality Control and Processing of 10X Sequencing Data
The raw data created by Cell Ranger was read into the Seurat R package for quality control and downstream processing. Low-quality cells expressing genes and genes expressed in fewer than three cells were filtered out. After looking at the violin plots of the number of counts, features (genes), and percent mitochondria per sample, we further filtered cells expressing genes in control samples and cells expressing genes in UBD-treated samples to avoid probable doublets. Cells expressing of mitochondrial genes were filtered out in control and UBD samples. To account for differences in sequencing depth across samples, the data was log-normalized and scaled.
Clustering, Visualization, and Cell Annotation
For cell clustering, we sorted the top 2,000 highly variable genes that differed from cell to cell for downstream analysis. The dimensionality of the data was reduced by principal component analysis (PCA) on the highly variable genes. Since Seurat clusters cells based on their PCA scores, the elbow plot was used to determine the top principal components (PCs) for use in clustering the data. From the elbow plot, the top 15 PCs were used in clustering. Cells were divided into unsupervised clusters using a shared-nearest-neighbor modularity optimization-based clustering algorithm. Cells were clustered at a resolution of 0.4 and visualized using Uniform Manifold Approximation and Projection (UMAP) plots.53 Differentially expressed genes per cluster were calculated using the Seurat Wilcoxon signed-rank test. Cluster annotation was based off the top genes (log2 fold change and ) and marker genes described in literature. Control and UBD-treated samples were annotated together to draw direct comparisons. Marker gene expression was visualized using violin plots and dot-plots (size of the dot reflects the percentage of cells expressing the gene, and color indicates relative expression). R version 4.0.4 was used for all data plotting and analysis.
Differences between Treatment
For comparisons between control and UBD-treated samples, the samples from the same subject were log normalized and scaled separately and were merged into one dataset for downstream analysis. Where necessary, all control samples were merged into one dataset, and all UBD-treated samples were merged into another dataset.
Percentage of Cells and Statistical Analysis
The relative abundance of each cell type was calculated as percentage of cells per condition (control and UBD). We tested for statistical significance using two-tailed -test (GraphPad Prism 9.0).
Pathway Analysis
Differentially expressed (DE) genes among clusters or samples were ranked according to their expression with the upregulated ones at the top of the list and the downregulated ones at the bottom. The ranked gene list was imported onto gProfiler (Ensembl 109). Pathway analysis was done using gene ontology (GO) biological process and Reactome (version 84). After running the analysis, the gProfiler data was downloaded as a GMT file, while the results file was downloaded in the Generic Enrichment Map format. Both types of files were then imported into Cytoscape (version 3.9.1) where the EnrichmentMap app was used to generate the enrichment map. We used a -value cutoff and q-value cutoff of 1 and an Overlap Coefficient cutoff of 0.5. Using DE genes from Seurat as input, protein–protein interactions of upregulated genes in the UBD-treated enteroendocrine cluster were determined using the STRING app on Cytoscape.
Immunofluorescence, RNAscope, and Confocal Imaging
Colonoids were harvested from Matrigel using Cultrex Organoid Harvesting Solution, then fixed for 40 min in 4% paraformaldehyde (Electron Microscopy Sciences). Immunostaining was performed as previously described.44 In brief, fixed colonoids were permeabilized and blocked and incubated with primary antibodies at 4 degrees overnight. After washing, organoids were incubated with fluorescent secondary antibodies and DAPI for 1 h at room temperature, washed, and mounted. Primary and secondary antibodies used are listed in Table S2.
Fixed colonoids were prepared for whole-mount staining with RNAscope Multiplex Fluorescent version 2 using probes Hs-CHGA and Hs-PROX1 (Table S3). Sample preparation and labeling were performed according to the manufacturer’s protocol (Advanced Cell Diagnostics) with slight modifications as previously described.54 Opal fluorophores (Perkin Elmer) and DAPI were used for visualization. Confocal imaging was carried out in the UNM Comprehensive Cancer Center Fluorescence Microscopy Shared Resource using an LSM 800 AiryScan confocal microscope (Zeiss) and UNM AIM Center using an LSM 900 AiryScan confocal microscope (Zeiss). Total cells and antibody- or oligo-positive cells were counted in ImageJ. Immunofluorescence and RNAscope were independent experiments, with at least 1,000 cells counted in each condition.
Statistics
Data were represented as . Statistical significances were calculated using Student’s -test. Significance was represented as at least . All experiments were performed on a minimum of three different colonoid lines derived from separate normal human subjects, with a total of seven different colonoid lines used throughout these studies for validation. refers to numbers of independent replicates performed. All analyses were performed on GraphPad Prism 9.0.
Additional Software
All graphical schematics within this manuscript were generated in BioRender.com under an academic plan and includes a publication license.
Results
Mineralogy Analysis of the UBD
Mineralogy of the size fraction in the UBD was based on an analysis of individual mineral grains or grain clusters and is shown in Figure S1. This fraction consisted of a variety of minerals that are commonly present in aeolian dust in arid environments including quartz, feldspar, micas/clay minerals, calcite, and gypsum.55 Rare minerals included baryte, rutile, and iron oxides such as hematite and magnetite. In addition to these minerals, extensive searching of the TEM grids revealed the presence of submicron grains of U-bearing minerals. Mineralogy of two of the five TEM grid square areas showed no U-bearing minerals, but in the three other grid squares, several grains were found, often in close spatial association. Of relevance, a) no U-bearing grains were found with grain sizes , b) the grains always occurred in clusters intimately mixed with other minerals—no individual isolated grains were found, and c) the individual U-bearing minerals were as small as in size or less. Estimating the abundance of these grains was very challenging from TEM data, but our estimate was . The mass fraction was significantly lower, because the grains were all submicron, a characteristic that is unique to the U-bearing minerals.56,57
Cytotoxicity Assay of Colonoids Post-Acute UBD Exposure
To determine if UBD induced cell death or morphological changes in human colonoids, three biologically distinct human colonoid cultures were treated with vehicle (control, organoid expansion media) or UBD (resuspended in organoid expansion media) overnight ( h). Brightfield imaging of both conditions showed no differences in gross morphology after acute UBD exposure (Figure 1A). Propidium iodide (PI) staining was used to visualize dead cells with DAPI as the nuclear counterstain. No significant difference in PI-positive cells was observed between control (Figure 1B) and UBD-treated colonoids (Figure 1C) or found when PI-positive cells were quantified (Figure 1D).
Figure 1.
Effect of acute uranium-bearing dust exposure on human colonoids. (A–D) Human colonoids were treated with vehicle (control) or uranium-bearing dust (UBD) overnight; . (A) Representative brightfield images of control and UBD-treated colonoids; . (B and C) Representative confocal images of control (B) and UBD (C) colonoids stained with propidium iodide (PI) (dead cells); . (D) Quantification of PI-positive cells relative to total cell populations in control and UBD-treated colonoids. (not significant) based on Student’s -test; . Source data can be found in Excel Table S1. (E) Representative violin plots for gene expression numbers per cell shows control colonoids express while some UBD-exposed express .
scRNA-Seq Analysis of Colonoids Post-Acute UBD Exposure
To understand if UBD was changing specific cell lineages, we performed droplet-based single-cell RNA sequencing (scRNA-seq) on three biologically unique colonoid lines (Table S1) under control or UBD treated conditions. Despite the lack of changes in cell death and overall morphology, computationally there was a stark difference in cellular gene expression. Cells in control colonoids expressed genes while some UBD-treated cells expressed genes (Figure 1E).
Graph-based clustering using the Louvain algorithm and marker-gene analysis revealed few clusters in control colonoids that primarily represented cells founds in the deep crypt, as shown in the representative control colonoid UMAP (Figure 2A). Clusters were manually identified using marker genes and published datasets58–60 as cycling transit amplifying (TA) cells, stem cells, and two clusters of secretory progenitor cells (Excel Tables S2–S4). The colonoids represented nondifferentiated epithelia since they were maintained in organoid expansion media that contained WNT3A/Rspo-1/Noggin.
Figure 2.

Comparison of epithelial cell lineages in control and uranium-bearing dust (UBD)-treated colonoids using single-cell RNA sequencing. (A) Control and (B) UBD-treated colonoids were initially analyzed separately to determine differences between the biological controls. Putative cluster identification is listed below each representative Uniform Manifold Approximation and Projection (UMAP). Source data for the Seurat pipeline can be found in Excel Tables S2–S7. (C) Representative UMAP of merged control and UBD-treated colonoids to perform direct comparison analysis between each cell cluster. (D) Comparison of relative cell percentages for each cluster between control and UBD-treated colonoids. Proliferative clusters (0, 1, 3) are circled. Source data for merged analysis can be found in Excel Table S8, and source data for cluster percentages can be found in Excel Table S9. Note: TA, transit amplifying.
In contrast, UBD-treated colonoids maintained in identical media, had a higher degree of cell type variability, as shown in the representative UBD-treated colonoid UMAP. They grouped into clusters (Excel Tables S5–S7) that included differentiated cell types and were identified as secretory progenitors, goblet cells, absorptive colonocytes, cycling TA cells, absorptive progenitors, stem cells, and enteroendocrine (EEC)–enterochromaffin cells and EEC–L cells (Figure 2B). Since the three colonoid lines were from biologically unique donors, differential gene and clustering analysis was performed on each control and UBD-treated colonoid set to first determine if there were major differences due to genetic variability. Similar clustering patterns and differentially expressed genes were seen in all three colonoid lines for control (mainly deep crypt cells) and UBD-treated (mainly differentiated cells) conditions. Thus, control and UBD-treated colonoid datasets were merged to directly compare cell proportions in each cluster (Figure 2C; Excel Table S8). There was an increase in all types of differentiated cells but a decline in proliferative (stem and cycling TA) cells in the UBD-treated compared to control colonoids (Figure 2D).
To visualize differences within clusters between control and UBD-treated colonoids, the datasets were merged, clustered, and split according to treatment. UBD-treated cells (blue) did not entirely overlap with control cells (red) (Figure S2). Volcano plots of control and UBD-treated colonoids for all three colonoid lines showed significantly upregulated (red) and downregulated (blue) genes by treatment (Figure S3). In UBD-treated colonoids, genes associated with secretory lineage (such as TFF3, CHGA, PCSK1N, MUC2, FCGBP) were upregulated, while cell cycle and mitochondrial genes were downregulated (in relation to control). In contrast, mitochondrial genes were downregulated in UBD-treated colonoids (in relation to control colonoids).
Measurement of EECs in UBD-Treated Human Colonoids
Disruption of EECs and hormones have been reported in various gut-related and systemic metabolic diseases.61–63 Among the cell type differences observed in UBD-treated colonoids, there was an expansion in EECs (Figure 2C, cluster 6). Since EECs are rare and control colonoids did not show major biological variation when clustered independently, we merged the control and -treated colonoids for downstream analysis. We identified EECs by the expression of chromogranin A (CHGA) and chromogranin B (CHGB), both well characterized pan-EEC markers. Feature plots and dot plots were used to identify CHGA- and CHGB-expressing cells (Figure 3A) and to quantify CHGA and CHGB expression (Figure 3B), respectively. Total number of EECs were 3.6-fold higher, with higher transcript levels of CHGA (4.4 fold) and CHGB (6.3 fold) in UBD-treated colonoids compared to controls (Figure 3C). These differences were quantified via immunostaining of CHGA-expressing cells (Figure 3D,E). Additionally, detection of RNA oligos via RNAscope in situ hybridization showed a significant difference in CHGA+ oligos per cell in UBD-treated colonoids compared to controls (Figure 3F,G).
Figure 3.

Expression of enteroendocrine cell markers in control and uranium-bearing dust (UBD)-treated colonoids. (A) Feature plot of pooled control (left) and UBD-treated (right) colonoids () with cells differentially expressing Chromogranin A (CHGA) (top) and Chromogranin B (CHGB) (bottom) indicated by black arrows. (B) Dot plot of enteroendocrine cell (EEC) markers CHGA and CHGB. (C) Quantification of total EECs and EEC markers CHGA and CHGB compared between the pooled control and UBD-exposed colonoids. At least 10,000 cells were analyzed for each condition. * (total EE), 0.07 (CHGA), and 0.03 (CHGB). Source data for EEC cluster quantification can be found in Excel Table S10. Source data for the Seurat pipeline for the merged analysis can be found in Excel Table S8. (D) Representative immunostaining for CHGA in control and UBD-treated colonoids. CHGA, green; phalloidin, white; nuclei, blue; . (E) Quantification of percent CHGA+ cells in total cell populations in control and UBD-treated colonoids. *; . Source data found in Excel Table S11. (F) Representative RNAscope fluorescence staining of CHGA in colonoids to validate scRNA-seq. CHGA, red; nuclei, blue; . (G) Quantification of RNAscope staining of CHGA dots per cell in total cell populations in control and UBD-treated colonoids. *; . Data are presented as . Source data found in Excel Table S11. -Values based on Student’s -test. Note: SEM, standard error of the mean.
Evaluation of Serotonin Producing-Enterochromaffin Cells and Peptide YY-Producing L Cells upon UBD Exposure
Enterochromaffin (EC) and L cells are the two most abundant EEC subtypes in the colon; however, there are at least 12 subtypes described in the small bowel and colon.64 We further analyzed these two major EEC subtypes in our scRNA-seq datasets. EC cells were marked by expression of tryptophan hydroxylase 1 (TPH1), the enzyme that catalyzes the rate-limiting step in synthesis of serotonin (5-HT) from tryptophan,65 while L cells were marked by expression of peptide tyrosine tyrosine (PYY).66 Feature plots of merged control and UBD-treated colonoids showed a 5.4-fold expansion of EC cells and a 3.4-fold expansion of L cells following UBD treatment (Figure 4A–C). A scatter plot of average gene expression in EECs by treatment showed that PYY was nearly absent in control colonoids but, like CHGA, was highly expressed in UBD-treated colonoids (Figure S4).
Figure 4.

Expression of enterochromaffin and L cell markers in control and uranium-bearing dust (UBD)-treated colonoids. (A) Feature plot of pooled control (left) and UBD-treated (right) colonoids () with cells differentially expressing tryptophan hydroxylase 1 (TPH1) (top) and peptide tyrosine tyrosine (PYY) (bottom) shown in orange and indicated with arrows. (B) Quantification of cells differentially expressing TPH1 compared between the pooled control and UBD-treated colonoids. *. (C) Quantification of cells differentially expressing PYY compared between the pooled control and UBD-treated colonoids. *. Source data for TPH1 and PYY quantification can be found in Excel Table S12. Source data for the Seurat pipeline for the merged analysis can be found in Excel Table S8. (D) Representative immunostaining for serotonin (5-HT) in control and UBD-treated colonoids. 5-HT, red; nuclei, blue; . (E) Quantification of percent 5-HT+ cells in total cell populations in control and UBD-treated colonoids. *; . Source data found in Excel Table S13. (F) Representative immunostaining for PYY in control and UBD-treated colonoids. White arrows indicate PYY+ basolateral extensions. PYY, red; nuclei, blue; . (G) Quantification of percent PYY+ cells in total cell populations in control and UBD-treated colonoids. *; . Data are presented as . Source data found in Excel Table S14. -Values are based on Student’s -test. Note: SEM, standard error of the mean.
We validated EC and L cell expansion upon acute UBD exposure by immunostaining for 5-HT (Figure 4D) and PYY (Figure 4F), respectively. Quantification of 5-HT showed that there were higher numbers of EC cells in UBD-treated colonoids compared to controls (Figure 4E). Similarly, the proportion of PYY expressing L cells were also higher in UBD-treated colonoids when compared to controls (Figure 4G). Interestingly, we observed PYY+ basal extensions (Figure 4F, arrows) from UBD-treated L cells that were absent in control colonoid L cells.
Subclustering of EECs in Control and UBD-Treated Colonoids
To further determine the spectrum of EECs that results from acute UBD exposure, we reanalyzed the EEC clusters from the combined control and UBD-treated colonoids. The EEC clusters were subclustered at a higher resolution of 1 instead of 0.4, then identified by comparing the differentially expressed genes (Excel Tables S15 and S16) with published EEC datasets.59,67 This resulted in the control colonoid EECs separating into three clusters identified as EEC progenitors, X cells, and EC cells (Figure 5A, left UMAP). The UBD-treated EECs subclustered into eight distinct clusters identified as EEC progenitors, X cells, EC cells, N cells, K cells, L cells, and enterochromaffin-late cells (Figure 5A, right UMAP). Subclustering also identified two subtypes of L cells in the UBD-treated colonoids. A small group of L cells expressed both GCG (proglucagon) and PYY (circled cluster, solid arrow) while a larger group of L cells expressed only PYY (circled cluster, dashed arrow) (Figure 5B).
Figure 5.

Higher resolution subclustering of enteroendocrine cells in control and uranium-bearing dust (UBD)-treated colonoids. (A) Representative Uniform Manifold Approximation and Projection (UMAP) of enteroendocrine cells (EECs) in control and UBD-treated colonoids subclustered at a higher resolution and identified. (B) Feature plots of UBD-treated EECs separated by glucagon (GCG) or peptide tyrosine tyrosine (PYY) differential expression. Some L cells express both GCG and PYY (solid arrow), but a subset of L cells express only PYY (dashed arrow). Source data for the Seurat pipeline can be found in Excel Tables S15–S16.
Gene Expression Profile Analysis of EECs in Control and UBD-Treated Colonoids
We evaluated the transcriptome of the newly formed UBD-induced EECs compared to control colonoid EECs. We compared gene profiles of the three common EEC clusters between control and UBD-treated colonoids [progenitors (control, 0; UBD, 6), X cells (control, 1; UBD, 1), and EC cells (control, 2; UBD, 0)] (Figure 6A). The most notable differences were observed in the EEC progenitor clusters. The topmost expressed genes in the EEC progenitor cluster in control (Figure 6A, cluster 0) were associated with secretory cells. In contrast, genes in EEC progenitors in UBD-treated cells (Figure 6A, cluster 6) were associated with the cell cycle.
Figure 6.


Gene expression profile analysis of enteroendocrine cells. (A) Heatmap of pooled enteroendocrine cells (EECs) from control colonoids (left) and uranium-bearing dust (UBD)-treated colonoids (right) comparing the gene profiles of EEC progenitors, X cells, and enterochromaffin cells between the two conditions. (B) Heatmap of selected EEC genes [chromogranin A (CHGA), tryptophan hydroxylase 1 (TPH1), regenerating family member 4 (REG4), anterior gradient 2 (AGR2), peptide tyrosine tyrosine (PYY), and fatty acid binding protein 1 (FABP1)] are denoted with arrows in control (left) and UBD-treated (right) colonoids. (C) Network analysis of top upregulated genes in UBD-treated EECs. (D) Enrichment map of higher WNT signaling in UBD-treated EECs. Source data for the Seurat pipeline can be found in Excel Tables S15–S16.
Comparing relative expression amounts of select EEC-associated genes, we found that CHGA, TPH1, REG4, AGR2, PYY, and FABP1 transcripts had higher expression in the UBD-treated colonoids compared to control colonoids (Figure 6B, arrows). We performed differential gene analysis on EECs from UBD-treated colonoids to further characterize the transcriptomic changes. Over 700 genes were differentially expressed in EECs upon UBD treatment, of which 67% were upregulated compared to control. Network analysis of top upregulated genes in UBD-treated EECs showed interactions between mitochondrial and ribosomal genes (Figure 6C). We performed pathway analysis in gProfiler using the genes that were upregulated in UBD-treated EECs. Upregulated pathways from gProfiler were imported into Cytoscape for enrichment analysis. The enrichment map of UBD treated EECs shows upregulation of multiple pathways related to WNT signaling (Figure 6D).
Analysis of EEC Differentiation Transcription Factors
Based on our result indicating that EEC hyperplasia in UBD-treated colonoids may be related to upregulated WNT signaling, we sought to understand the mechanism of EEC differentiation in the context of UBD treatment. NEUROG3 and NEUROD1 are the early and late transcription factors that drive EEC differentiation in mammals.68 Both transcription factors are considered WNT-independent, which is contrary to our network analysis of EECS in UBD-treated colonoids. Dot plot analysis showed that transcript levels of NEUROG3 and NEUROD1 were not very different between UBD treatment and control (Figure 7A).
Figure 7.

Analysis of transcription factor genes in control and uranium-bearing dust (UBD)-treated colonoids. (A) Dot plot of transcription factors prospero homeobox 1 (PROX1), atonal bHLH transcription factor 1 (ATOH1) (goblet cells), neuronal differentiation 1 (NEUROD1) (EECs), and neurogenin 3 (NEUROG3) (EECs) from control (blue line) and UBD-treated (orange line) colonoids. (B) Schematic of potential EEC differentiation regulation in Drosophila (Prospero, top) and human colon (PROX1, bottom). Created with Biorender.com with an academic license. (C) Feature plot of cells differentially expressing PROX1 (arrows) in pooled control and UBD-treated colonoids (). (D) Quantification of cells differentially expressing PROX1 compared between the pooled control and UBD-treated colonoids. *. Source data for PROX1 quantification can be found in Excel Table S12. Source data for the Seurat pipeline for the merged analysis can be found in Excel Table S8. (E) Representative immunostaining for PROX1 in control and UBD-treated colonoids. PROX1, red; nuclei, blue; . (F) Quantification of percent PROX1+ cells in total cell populations in control and UBD-treated colonoids. *; . Source data found in Excel Table S15. (G) Representative RNAscope fluorescence staining of PROX1 in colonoids to validate scRNA-seq. PROX1, red; nuclei, blue; . (H) Quantification of RNAscope staining of PROX1 dots per cell in total cell populations in control and UBD-treated colonoids. *; . Data are presented as . Source data found in Excel Table S16. -Values are based on Student’s -test. Note: SEM, standard error of the mean.
Thus, we searched for a possible WNT-dependent transcription factor that may be driving UBD-induced EEC differentiation. In Drosophila, the transcription factor Prospero drives differentiation of midgut stem cells into EECs.69 The mammalian homolog of Prospero is PROX1 and is WNT-dependent.70 Therefore, we hypothesized that UBD treatment leads to activation of WNT signaling and upregulates PROX1 expression, driving EEC differentiation from secretory progenitor cells (Figure 7B). From our scRNA-seq analysis, PROX1-expressing cells were higher in number in UBD-treated colonoids compared to control colonoids (Figure 7C,D). Additionally, in UBD-treated colonoids, PROX1 transcripts were higher in cycling TA and secretory progenitor cells (Figure 7A). This PROX1 difference was validated via immunostaining (Figure 7E,F) and RNAscope (Figure 7G,H).
Discussion
Gut exposure to environmental toxins and heavy metals has been linked to intestinal and systemic diseases, as well as inhibition of intestinal epithelial healing.21,22,24 However, transcriptomic changes within intestinal epithelial cells due to these environmental toxicants are largely unknown. UBD was used to model environmental exposure of 238U to human colonoids (a simplified, yet physiologically relevant intestinal model). EEC numbers were higher and differentiated into de novo EEC subtypes as determined by droplet based scRNA sequencing. We also observed higher expression of genes associated with WNT signaling but lower expression of genes associated with proliferative cells and identified a potential noncanonical mechanism of EEC differentiation upon UBD treatment.
The mammalian intestinal epithelium regenerates continuously by a proliferative pool of stem and transient amplifying cells.71 These proliferative cells give rise to various mature cell types required for an intact and properly functioning epithelial barrier. Thus, a decrease in proliferative cells, as seen with acute UBD exposure, can hamper the ability of the gut to repair its epithelium with potentially severe downstream consequences. Impairment of epithelium regeneration augments access of luminal toxins, antigens, and microbes to deeper layers of the mucosa. This can lead to recruitment of immune cells and subsequent inflammation.72 We used PI to determine if acute UBD exposure causes cell death and found no significant differences with control. However, PI staining does not mark cells initiating early stage apoptosis.73 Further studies are needed to determine if UBD exposure triggered apoptotic events.
Another major observation was the expansion of hormone-producing EECs, which are typically rare and make up of the total gut epithelium.74 The intestine is the largest endocrine organ in humans75 and communicates with the brain via EECs and the enteric nervous system.32,33 Gut–brain communication is partially attributed to EEC neuropods that directly synapse with enteric nerves.33,76 Therefore, modulation of the intestine via environmental toxicants can indirectly affect systemic health. An important caveat is that communities living near abandoned uranium mines are being chronically exposed to UBD. The long-term implications and EEC changes to chronic exposures are not yet known.
In this study, UBD-treated colonoids exhibited a 5-fold higher expression of genes known to be markers of EC cells, suggesting expansion of 5-HT-producing EC cells. In the gut, 5-HT stimulated motility and secretion,77,78 enhanced mucosal immunity, and was implicated in wound healing. Peripheral 5-HT can circulate systemically via platelets and acted as a mitogen in injured organs.79,80 In a murine model of liver injury, 5-HT promoted liver regeneration after partial hepatectomy, while mice lacking TPH1 could not fully regenerate their liver.81 These findings suggested that EECs can undergo adaptive reprogramming during injury and provided insights for potential new regenerative therapeutics in the gut. Despite the beneficial effects of 5-HT, high levels can be detrimental. As a vasoconstrictor, sustained 5-HT release elevated blood pressure with risk of severe fluctuations in hypertensive individuals,82 decreased bone mineral density,83 and dysregulated metabolic processes like gluconeogenesis and lipolysis which may predispose individuals to diabetes and obesity.84
Acute UBD exposure also led to a 3-fold higher expression of L-cell-associated genes, suggesting an expansion in L cells, the second most abundant EEC subtype in the colon. The major peptides secreted by L cells [PYY, glucagon-like peptide 1 (GLP-1), and glucagon-like peptide 2 (GLP-2)] are associated with intestinal motility, protection against inflammation, and regeneration.85–87 Based on the known function of L cell peptides, this suggested that UBD-induced L cell expansion may be beneficial by stimulating mitogenesis essential for regeneration.
We identified EEC subtypes (N and K cells) in the UBD-treated EEC subclusters that were not present in control colonoids. In homeostatic conditions, K cells are primarily found in the small bowel.88 Their appearance in the colon was unexpected. K cells produce glucose-dependent insulinotropic peptide (GIP), which inhibits gastric acid secretion and gastrointestinal motility.89 It is counter-intuitive to slow gut motility, as we would expect an increase in gut motility and secretion to flush away toxicants from the gut. Again, this suggested that we do not have a full understanding of EECs and the functional roles of their specific hormones and peptides. Neurotensin produced by N cells stimulates colonic regeneration, gut motility,90,91 and can facilitate exit of toxicants from the body. De novo differentiation of N cells during UBD exposure may be beneficial.
There has been strong evidence that implicated EECs as facultative stem cells that promote plasticity and regeneration of the gut.88,92 However, EEC expansion can also contribute to the rise of small intestinal neuroendocrine tumors.93 EECs can revert to stem cells following injury with high intensity radiation (12 Gy) that causes massive cell death and ablation of crypt-based stem cells.94 On the contrary, UBD exposure in colonoids was not associated with massive cell death. Instead, UBD exposure resulted in differences in lineage differentiation, particularly expansion of de novo and mature EECs. These opposing observations suggest EEC response to injury or toxicants might depend on severity of damage, further exemplifying the plasticity of these cells.
Downstream analysis of our scRNA-seq datasets found enrichment of genes involved in WNT signaling pathways in UBD-induced EECs. However, neither NEUROG367,68 nor NEUROD1,68,95 the canonical transcription factors that drive EEC differentiation,68,95 are WNT dependent. Instead, our scRNA-seq data found PROX1 transcripts, a WNT-dependent transcription factor,96 were higher in cycling TA and secretory progenitor cells in UBD-treated colonoids. PROX1 is the mammalian homolog of Prospero, the Drosophila transcription factor69,96 that drives differentiation of midgut stem cells into EECs.69 Since PROX1 is a WNT-dependent transcription factor and given that WNT signaling was enriched in UBD-induced EECs, we hypothesized that toxicant exposure led to increased WNT signaling, which upregulated PROX1 and drove secretory progenitor cells into noncanonical EEC differentiation.
The UBD used in this study was obtained from a church attic located on Laguna Pueblo, from the edge of a now dormant 3,000 acre open-pit uranium mine. A caveat to this study is the lack of knowledge on the causal factors in the UBD, such as physical and chemical interactions of uranium or other heavy metals and particulates. Since this study focused on assessing transcriptional and cell differentiation effects between control and UBD-exposed colonoids, extensive investigation into the physicochemical properties of UBD would not enable further insights into this putative toxicant. Another limitation to this study is the lack of immune cells in the culture. Coculturing intestinal enteroids with primary human macrophages has been shown to augment the intestinal barrier and promote maturation compared to enteroid mono-cultures.97 While this current study focused on the epithelial response to UBD, the colonoid model builds the foundation for future studies of UBD exposure on intestinal immune cells and colonoids-immune cocultures.
In summary, using a real-world environmental toxicant, we showed differences following UBD exposure that suggest human colonoids develop a pathophysiological response that shifts epithelial cell lineages. Proliferative cells were decreased while secretory lineage differentiation was increased, most notably EECs between UBD and control cells. Importantly, UBD exposure led to the development of EEC subtypes that were not present in control colonoids. Further investigation is required to determine if this expansion is mostly beneficial or detrimental. Understanding changes to EEC differentiation in toxicant exposure, injury, and regeneration will provide the basis for better understanding of systemic changes and dysfunction that can originate from enterohormones in the gut.
Supplementary Material
Acknowledgments
M.J.C., E.F.C., and J.G.I. conceived of experiments. R.A., L.L.A., and J.G.I. designed experiments. A.B. characterized and analyzed uranium-bearing dust composition. R.A., L.L.A., M.N.T., and F.T.L. performed the experiments. R.A., L.L.A., A.B., E.F.C., M.J.C., and J.G.I. analyzed the data. R.A., L.L.A., and J.G.I. wrote the manuscript with critical edits from M.N.T., F.T.L., A.B., M.J.C., and E.F.C. All authors reviewed the final version.
We thank Michael L. Paffett, Jamie L. Padilla, and Kathryn J. Brayer (University of New Mexico Comprehensive Cancer Center, Albuquerque, NM, USA) for technical assistance with confocal microscopy, single cell sequencing, and bioinformatics, respectively. We also thank Jeff Gaco from the Environment and Natural Resources Department of the Laguna Pueblo and Chris Shuey from the Southwest Information and Research Center for their permission and assistance, respectively, in obtaining the UBD used in this study.
This work was supported by NIH grants K01DK106323 (J.G.I.), R56ES034400 (J.G.I.), P42ES025589 (E.F.C. and J.G.I.), P20GM121176 (E.F.C. and J.G.I.), P20GM130422 (M.J.C.), and P50MD15706 (J.G.I.), and American Gastroenterological Association-Aman Armaan Ahmed Family Summer Undergraduate Research Fellowship (L.L.A.). This research was partially supported by the UNM Comprehensive Cancer Center Support Grant NCI P30CA118100.
Further information and requests for resources and reagents should be directed to the Lead Contact, Julie G. In (jgin@salud.unm.edu).
All unique reagents generated in this study are available from the Lead Contact without restriction.
All scRNA-seq datasets are available in Gene Expression Omnibus (GEO GSE239584).
Conclusions and opinions are those of the individual authors and do not necessarily reflect the policies or views of EHP Publishing or the National Institute of Environmental Health Sciences.
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