Skip to main content
Toxicology Reports logoLink to Toxicology Reports
. 2021 Mar 9;8:511–519. doi: 10.1016/j.toxrep.2021.03.007

Absence of genotoxicity of purified Aloe vera whole leaf dry juice as assessed by an in vitro mouse lymphoma tk assay and an in vivo comet assay in male F344 rats

Jiang Hu a,*, Mel Lloyd b, Cheryl Hobbs c, Peter Cox b, Keith Burke c, Gareth Pearce b, Michael A Streicker c, Quanyin Gao a, Vasilios Frankos a
PMCID: PMC7973126  PMID: 33747796

Graphical abstract

graphic file with name ga1.jpg

Keywords: Aloe vera, Hydroxyanthracene derivatives, Decolorization, Mutant frequency, % tail DNA, Mutagenicity

Abstract

Hydroxyanthracene derivatives (HAD) are naturally present in the latex layer of Aloe vera leaf, predominantly as aloins A, B and aloe-emodin. HAD are typically removed from commercial ingestible aloe products through activated charcoal filtration (decolorization). Current research aimed to evaluate genotoxic potential of a purified aloe whole leaf dry juice containing 0.3 ppm of total aloins and non-detectable aloe-emodin (LOD =0.01 ppm) in the L5178Y mouse lymphoma assay (MLA; OECD 490) and in vivo comet assay (OECD 489). No marked increases in mutant frequency at the tk locus were observed in the MLA at concentrations up to 5000 μg/mL for 3 h and 24 h (-S9), and up to a precipitating concentration of 3000 μg/mL for 3 h (+S9) compared to concurrent vehicle control. Relative total growth at the highest analyzable concentrations at 3 h (±S9) and 24 h (-S9) ranged from 64 to 133 %. In the comet assay, no statistically significant increases in DNA strand breaks were detected in the colon or kidney following oral gavage of 500, 1000 or 2000 mg/kg/day in male F344 rats for 2 days compared to concurrent vehicle control. Overall, these findings demonstrated the test article containing minimal HAD is not genotoxic under the described experimental conditions.

1. Introduction

Aloe vera (L.) Burm. f. has a long history of traditional use for its medicinal properties, with documented records dating back to the 4th century B.C. [1,2]. Various preparations from aloe leaves have reportedly been used internally for indications such as colds, sore throat, indigestion, gastrointestinal irritations and constipation [[2], [3], [4], [5]]. More recent studies have shown that Aloe vera may have antioxidant, immunostimulatory and anti-inflammatory properties, and its consumption has been linked to potential health benefits, such as increasing absorption of vitamins, alleviating gastroesophageal reflux symptoms, lowering serum LDL-cholesterol and glucose levels, and improving skin elasticity [4,[6], [7], [8], [9], [10]]. Aloe vera food and supplement market has grown rapidly in recent years, likely owing to increasing consumer awareness of these purported health benefits.

Hydroxyanthracene derivatives (HAD) are a class of compounds naturally present in plants and with an anthraquinone backbone structure, including rhein, chrysophanol, aloe-emodin, physcion, dianthrone, and anthrone, along with their glycosides [11]. Because these compounds have potent laxative effects, plant extracts with high levels of these compounds are commonly used in traditional herbal medicine or food supplements to improve bowel function [[12], [13], [14]]. Aloe vera leaves contain small amounts (< 1%) of HAD, mainly as aloin (or barbaloin) A, B and aloe-emodin (Fig. 1), which are located in the rind (outer green skin protecting the gel) and latex (yellowish exudate from the rind), but not in the inner leaf (clear fleshy gel) [15,16]. Aloins and aloe-emodin in aloe leaves have been found to be genotoxic in bacterial mutation and mammalian cell assays in vitro as well as in several in vivo genotoxicity assays [[17], [18], [19]], and are considered to be the main contributing agents to the colonic carcinogenicity observed in a 2-year cancer bioassay of an orally administered Aloe vera whole leaf extract (containing approximately 6400 ppm aloin A and 71 ppm aloe-emodin) in F344 N rats [18,20].

Fig. 1.

Fig. 1

Chemical Structures of Aloin A, Aloin B and Aloe-emodin.

Due to concerns related to the potential genotoxicity and carcinogenicity risk associated with HAD in Aloe vera, the process for aloe production has undergone continuous improvement [21]. It is now a common practice to remove HAD through a multi-step purification process in the commercial production of aloe products [22]. Aloe vera whole leaf (rind, inner leaf and latex) and inner leaf gel are typically subjected to a series of filtration steps using activated charcoal, a process known as decolorization, to remove pigmented substances and HAD, resulting in a purified product with only residual amounts of HAD as unavoidable impurities. The International Aloe Science Council (IASC), a self-regulating trade association, has set a quality standard of less than 10 ppm of total aloins for all Aloe vera leaf juice products intended for oral consumption [23]. These purified (a.k.a. decolorized) aloe products are not known to have any laxative properties linked to HAD due to their insignificant levels. Most recently, the European Commission (EC) has proposed regulatory measures to prohibit the use of preparations from the leaf of Aloe species containing HAD in foods and food supplements, and set the level of 1 ppm for aloe-emodin/emodin and the level of 1 ppm for the sum of aloins A and B as the threshold for its harmonized risk management approach [24].

Numerous published studies have shown that Aloe vera leaf preparations with < 10 ppm of aloins were not mutagenetic in prokaryotic and eukaryotic test systems [20,[25], [26], [27]]. These studies were considered in the International Agency for Research on Cancer (IARC) evaluation of Aloe vera and summarized in Table 1 [18]. However, results from one study by Guo et al. [28] that was not included in the IARC evaluation have generated some uncertainty regarding the genotoxic potential of decolorized aloe material. In that study, a decolorized aloe whole leaf extract with 63 ppm of aloins was tested positive for mutagenic effect in a mouse lymphoma tk assay after 24 h treatment in the absence of metabolic activation [28]. Notably, positive mutagenicity was found only at dosing concentrations of 6–8 mg/mL, which is higher than the maximum of 5 mg/mL as typically recommended in regulatory testing guidelines for MLA. This decolorized aloe whole leaf extract significantly increased reactive oxygen species (ROS) levels in the cell culture system, and induced a mutation spectrum different from that of the non-decolorized aloe whole leaf extract tested in the same study. These findings have led to the concern that constituents other than HAD might be present in aloe leaves and contribute to mutagenic activities [17,28]. Since in vivo evidence of genotoxicity for purified Aloe vera preparations is scarce, the question remains as to whether commercial preparations derived from Aloe vera whole leaves that adhere to the IASC quality standard and contain only insignificant amounts of HAD are genotoxic.

Table 1.

Reported Genetic and Related Effects of Aloe vera Inner Leaf, Gel and Decolorized Whole Leaf Materials (Adapted from IARC Aloe vera Monograph, Table 4.1, 2016).

Test system Results
Dose (LED or HID) Aloe vera preparation Reference
Without exogenous metabolic system With exogenous metabolic system
Salmonella typhimurium, TA100, reverse mutation negative negative NR Stabilized gel; aloin A and B ≤ 10 ppm Sehgal et al. [29]
Salmonella typhimurium, TA98, TA100, TA1535, TA 1537, reverse mutation negative negative 10 mg/plate Qmatrix® inner leaf fillet; aloins < 10 ppm Williams et al. [27]
Salmonella typhimurium, TA98, TA100, reverse mutation negative negative 6 mg/plate Decolorized whole leaf extract, aloin A at 60–200 ppm Boudreau et al. [20]
Salmonella typhimurium, TA97, TA98, TA100, TA1535, reverse mutation negative negative 10 mg/plate Gel, aloin A at 1100–1400 ppm Boudreau et al. [20]
Salmonella typhimurium, TA98, TA100, reverse mutation negative negative 21 × initial concentrationa Decolorized whole leaf extract; aloin A at 0.868 ppm, aloin B at 1.335 ppm, and aloe-emodin at 0.2 ppm Sehgal et al. [26]
Escherichia coli, WP2 uvrA/pKM101 negative negative 6 mg/plate Decolorized whole leaf extract, aloin A at 60–200 ppm Boudreau et al. [20]
Escherichia coli, WP2 uvrA/pKM101 negative negative 3 mg/plate Gel, aloin A at 1100–1400 ppm Boudreau et al. [20]
Escherichia coli, SOS DNA damage repair assay negative negative 10 × initial concentrationa Stabilized gel; aloin A and B ≤ 10 ppm Sehgal et al. [29]
Escherichia coli, SOS DNA damage repair assay negative negative 21 × initial concentrationa Decolorized whole leaf extract; aloin A at 0.868 ppm, aloin B at 1.335 ppm, and aloe-emodin at 0.2 ppm Sehgal et al. [26]
Chromosomal aberrations, Chinese hamster lung cells negative negative 10 mg/plate Qmatrix® inner leaf fillet; aloins < 10 ppm Williams et al. [27]
Mouse lymphoma L5178Y/TK+/−cells positive negative 6 mg/mL Decolorized whole leaf extract; aloin A at 63 ppm Guo et al. [28]
Male ICR mice, micronucleus formation in bone-marrow cells negative 5000 mg/kg bw, po Qmatrix® inner leaf fillet; aloins < 10 ppm Williams et al. [27]

LED, lowest effective dose; HID, highest ineffective dose; NR, not reported; po, per oral.

a

Dosing concentrations as reported in the original publication, and dosing concentrations in mg/mL or mg/plate cannot be deduced based on the information reported.

In view of contradictory genotoxicity evidence on decolorized (a.k.a. purified) Aloe vera preparations in the literature, further studies conducted in accordance with internationally recognized genotoxicity testing recommendations [[30], [31], [32]], are warranted to assess whether the genotoxic effect observed in vitro is of toxicological relevance to human health. The present research aimed to evaluate the mutagenic and clastogenic potential of a purified Aloe vera whole leaf preparation containing trace HAD as unavoidable impurities in the MLA. Furthermore, a comet assay was conducted in F344 N rats to examine its genotoxic potential in vivo.

2. Materials & methods

Both the comet and mouse lymphoma assays were conducted following applicable Good Laboratory Practice (GLP) regulations and in accordance with OECD Test Guidelines 489 and 490 [33,34], respectively. All chemicals were purchased from Sigma-Aldrich (St. Louis, MO, USA), unless otherwise stated.

2.1. Test article

A commercially available purified Aloe vera whole leaf dry juice (Lot# 715HB10YK03) was used in both studies. The test article was supplied by Herbalife Nutrition (Torrance, CA, USA) and manufactured by Pharmachem, LLC (Descoto, TX, USA) from fresh harvested Aloe vera leaves. In brief, aloe whole leaves were washed and then macerated mechanically into a slurry, which was subsequently pasteurized and filtered to remove insoluble components and contaminants. The resulting juice was treated with food-grade activated charcoal, a process known as decolorization, to remove chlorophylls and anthraquinones. After removal of activated charcoal, the resulting material was subjected to additional filter presses to produce a clarified juice, which was further concentrated and dried to produce the purified Aloe vera whole leaf dry juice powder. The test article was a light tan color dry powder comprised of naturally occurring polysaccharides (aloe acemannan), minerals, glucose, malic acid and other organic acids. The identity of the test article was confirmed by proton nuclear magnetic resonance (1H NMR) spectrometry. Quantitation of aloin A, aloin B and aloe-emodin in the test article was carried out using the validated AOAC Official Method 2016.09 with reverse-phase high performance liquid chromatography (RP-HPLC) [35]. Chemical composition of the test article is summarized in Table 2.

Table 2.

Chemical Composition of Purified Aloe vera Whole Leaf Dry Juice.

Test Result
Appearance Light tan free flowing powder
pH 4.59
Moisture content (w/w%) 4%
Polysaccharides (w/w%) 5.01 %
Malic acid (w/w%) 13.98 %
Citric acid (w/w%) 9.0 %
Isocitric acid lactone (w/w%) 4.6 %
Lactic acid (w/w%) 5.22 %
Glucose (w/w%) 9.82 %
Fructose (w/w%) 3.37 %
Potassium (mg/g) 66.69
Calcium (mg/g) 61.05
Total of aloin A and Ba (ppm) 0.3
Aloe-emodina (ppm) ND
Cadmium (ppm) < 0.1
Arsenic (ppm) 1.7
Lead (ppm) 0.01
Mercury (ppm) < 0.5

ND, not detected; a LOD =0.01 ppm, LOQ =0.02 ppm.

2.2. Mouse lymphoma tk assay

Test article stock solutions were prepared under subdued lighting in purified water at the maximum limit concentration of 50 mg/mL. Purified water diluted 10-fold in the culture medium was used as the negative vehicle control. The positive controls methyl methanesulphonate (MMS) in the absence of S9 and benzo[a]pyrene (B[a]P) in the presence of S9 were formulated in anhydrous analytical grade dimethyl sulphoxide (DMSO) and protected from light. The mammalian liver post-mitochondrial fraction (S9) used for metabolic activation was acquired from Molecular Toxicology Inc. (Boone, NC, USA) and prepared from male Sprague Dawley rats induced with Aroclor 1254. Lyophilized (Mutazyme™) S9 mix was reconstituted with purified water to provide a 10 % S9 mix just prior to use, and the final concentration of S9 fraction was 1% (v/v) for all cultures treated in the presence of S9. The master stock of L5178Y tk+/− (3.7.2C) mouse lymphoma cells originated from Dr. Donald Clive (Burroughs Wellcome Co., Research Triangle, NC, USA) and were stored as frozen working stocks in liquid nitrogen. Each batch of frozen cells was purged of tk-/- mutants and checked for spontaneous mutant frequency (MF) and affirmed that they were mycoplasma free. For each experiment, frozen stocks were thawed rapidly, the cells were maintained in Roswell Park Memorial Institute medium (RPMI-1640; Life Technologies, Carlsbad, CA, USA) containing L-glutamine and HEPES supplemented with heat-inactivated horse serum, penicillin and streptomycin, pluronic and sodium pyruvate and incubated at 37 ± 1 °C under 5% (v/v) CO2 in air for growth.

The test article was assessed in a cytotoxicity range-finder and a mutation experiment, each conducted under three test conditions, 3 h with and without S9 and 24 h without S9. In the range-finder experiment, the final concentrations of test article ranged from 156.3–5000 μg/mL. Only single cultures were used for test article and vehicle treatment controls and no positive controls were included. In the mutation experiment, the final concentrations of test article ranged from 250 to 5000 μg/mL. Duplicate cultures were used except for positive controls, for which single cultures were used at two independent concentrations. During the exposure period of both experiments, approximately 1 × 107 cells were placed in sterile centrifuge tubes for the 3 h treatments and approximately 4 × 106 cells were placed in sterile tissue culture flasks for the 24 h treatment. For treatment cultures, 2 mL of vehicle or test article formulation or 0.2 mL of positive control solution (plus 1.8 mL of purified water) were added. For 3 h treatments, S9 mix or 150 mM KCl was added. After the exposure period, cells were centrifuged (200 x g), washed with tissue culture medium and resuspended in RPMI 10 with an adjusted density of 2 × 105 cells/mL. Solubility of the test article in culture medium was assessed at the beginning and end of each treatment by the observation of visible precipitation. Osmolality and pH measurements in pre- and post-treatment media were taken in the cytotoxicity range-finder experiment.

During the mutation expression period, cells were transferred to tissue culture flasks (where necessary) and incubated for two days during which the tk−/− mutations were expressed. At the end of the expression period, cytotoxicity was assessed in the range-finder experiment by measuring suspension growth (SG) and relative suspension growth (RSG). In the mutation experiment, cytotoxicity was measured by relative total growth (RTG). Cell densities in the cultures were adjusted to 1 × 104 cells/mL, and then plated for viability and trifluorothymidine (TFT) resistance. Viability was evaluated by plating 0.2 mL cell suspension at 8 cells/mL of each culture into each well of two 96-well microtitre plates (an average of 1.6 cells/well), which were incubated at 37 ± 1 °C in a humidified atmosphere with 5% CO2 until scoreable (12–13 days). Mutation (TFT resistance) was assessed by plating 0.2 mL cell suspension at 1 × 104 cells/mL into each culture of four 96-well microtitre plates (an average of 2000 cells/well) in medium containing TFT at a final concentration of 3 μg/mL; the plates were incubated until scoreable (14 days).

The total number of wells containing a colony were scored initially for viability and mutation. For the mutation plates, the number of wells containing large colonies and those containing small colonies were scored for the negative and positive control cultures, and for any test article concentrations that induced an MF exceeding the sum of the vehicle control MF plus the Global Evaluation Factor (GEF). For microwell assays, the GEF is defined as 126 mutants per 106 viable cells according to Moore et al. [36]. The relevance of increases in MF (total wells with colonies) by comparison with concurrent controls and the GEF was evaluated according to the recommendations of the Mouse Lymphoma Assay Workgroup [36]. Linear regression was performed on the ranked MF against ranked dosing concentrations to test for a linear trend. The assay acceptance and evaluation criteria were applied in adherence to OECD Guideline 490.

2.3. Comet assay

Seven to eight-week-old male Fischer 344/N Hsd rats (Envigo Laboratories, Frederick, MD, USA) were used in the comet assay. The male animals of this model was selected because 1) F344/N rats were tested in the National Toxicology Program (NTP) 2-year carcinogenicity study previously which found clear evidence of carcinogenicity in the colon for the orally administered non-decolorized Aloe vera whole leaf extract; and 2) a more pronounced effect was observed in males as compared to females in the study [20]. The colon and kidney were selected as target organs for comet analysis. The kidney was examined because orally administered aloe-emodin was previously shown to cause increases in DNA strand breaks in male Oncins France 1(OF1) mice [37]. Systemic exposure to the test article or HAD was not measured because 1) the levels of aloins and aloe-emodin in the test article were very low and non-detectable, respectively; 2) in vivo carcinogenicity associated with ingestion of Aloe vera and its HAD has only been detected in the colon (the site of direct contact) in the F344 rat model; and 3) ingested aloins have very low oral bioavailability [38,39].

Animals were housed with two to three per cage, fed Certified Purina Pico Chow No. 5002 (Ralston Purina Co., St. Louis, MO, USA) with access to reverse osmosis treated tap water ad libitum in a controlled-temperature room (23 ± 1 °C) with a 12-h dark/light cycle. All husbandry procedures were in compliance with the United States Department of Agriculture’s (USDA 2017) Animal Welfare Act Regulations, 9 CFR 1, and animals were handled and treated according to the Guide for the Care and Use of Laboratory Animals [40].

The oral doses of purified Aloe vera whole leaf dry juice tested were 500, 1000 and 2000 mg/kg bw/day. Dose selection was based on the results of a 90-day oral toxicity study of the same material (different lot) in F344 rats in which the no-observed-adverse-effect-level (NOAEL) was found to be >1845 mg/kg bw/day, the highest dose tested [41], and designed to meet the limit dose requirement for non-toxic test materials as per OECD Guideline 489. The dose formulations were prepared in deionized water at concentrations of 50, 100, and 200 mg/mL. Deionized water was used as the vehicle control. The positive control, ethyl methanesulphonate (EMS), was prepared in 0.9 % saline daily at a concentration of 15 mg/mL and administered at an oral dose of 150 mg/kg bw/day.

After a 7-day acclimation period, 25 animals were randomly assigned to one of the five groups (n = 5/group) using a stratification procedure to ensure that mean body weight was not statistically different among the groups. Dose formulations were administered via oral gavage at a dose volume of 10 mL/kg body weight for two consecutive days. Animals were monitored twice daily for mortality and moribundity. Clinical observations were performed daily prior to dose administration and at termination. Cage side observations were performed at 1 h ± 30 min post dose. Body weights of individual animals were measured within two days of arrival, for allocation, prior to daily dose administration, and at termination. Approximately 3 h ± 30 min after the final dose administration on Day 2, animals were euthanized for tissue collection.

For the colon tissue collection, the entire colon was removed from each animal. Cold mincing solution (magnesium- and calcium-free Hanks Balanced Salt Solution, 10% v/v DMSO, and 20 mM EDTA, pH 7.4–7.7, Invitrogen, Carlsbad, CA, USA) was injected into the colon to facilitate the removal of fecal material. A 4–5 cm length of colon was removed from the distal end and flushed extensively with mincing solution from both directions. The distal section of colon was cut longitudinally and placed in cold mincing solution, then transferred to a dish, scraped lightly and rinsed into the same dish with 1–2 mL of mincing solution. The tissue was transferred to a new dish and scraped with more pressure to harvest the epithelium. The scraped colon epithelial tissue was rinsed over the dish with ∼500 μL of mincing solution and the spatula was rinsed with ∼500 μL to remove any adhering cells. The mincing solution in the dish containing the epithelial cells was pipetted up and down several times to break up clumps of cells, then aliquoted into two microfuge tubes and placed on ice. For the kidney tissue collection, a section was collected from the center of the right kidney of each animal. Two small sections of kidney tissue were placed in separate microcentrifuge tubes containing 1 mL of cold mincing solution and rapidly minced to generate duplicate samples. All tissue samples were flash frozen in liquid nitrogen and stored at or below −80 °C in a freezer until processed.

For each animal, one of the duplicate tubes containing frozen tissue samples was transferred from the −80 °C freezer to dry ice, thawed in room temperature water bath, and then placed immediately on wet ice. Samples remained on wet ice for the duration of the slide making process. A portion of the cell suspension of each tissue sample was diluted with 0.5 % NuSieve GTG low melting point agarose (Lonza, Morristown, NJ, USA), dissolved in phosphate buffer at 37 °C, and layered onto duplicate commercially available Flare™ slides (Trevigen, Gaithersburg, MD, USA). The volume of the cell suspension did not decrease the percentage of low melting point agarose by more than 10% (i.e., not below 0.45%). The slides were immersed in chilled lysing solution (2.5 M NaCl, 100 mM Na2EDTA, 10 mM Tris, pH 10, with 10 % DMSO and 1% Triton X-100 added fresh) overnight in a refrigerator under a light proof condition. After this incubation period, the slides were rinsed in neutralization solution (0.4 M Trizma base, pH 7.5) to remove residual detergent and salts prior to the alkali unwinding step. Slides were randomly placed onto the platform of a submarine-type electrophoresis unit and submerged in cold alkaline electrophoresis solution (300 mM NaOH, 1 mM Na2EDTA; pH > 13). The slides were left to unwind under refrigerated conditions for 20 min, then electrophoresed at 4 °C for 20 min at 25 V (0.7 V/cm) with a current of approximately 300 mA. After electrophoresis, slides were neutralized with 0.4 M Trizma base (pH 7.5) for 5 min and then dehydrated by immersion in absolute ethanol (≥ 99.6 %, Pharmco-AAPER, Shelbyville, KY, USA) for 5 min and allowed to air dry. Slides were stored at room temperature in a desiccator until stained and scored.

Air-dried slides were stained with SYBR™ Gold (Invitrogen, Carlsbad, CA, USA) and 150 cells were scored per sample at 200x total magnification using Comet IV Image Analysis Software (Version 4.3.2, Instem, UK). Slides were coded and scored for the percentage of migrated DNA (% tail DNA) without knowledge of their identity. The % tail DNA endpoint measurement was used to characterize the extent of DNA migration, calculated as the intensity of all tail pixels divided by the total intensity of all pixels in the comet, expressed as a percentage. “Hedgehogs” (i.e., small or no visible head, or the head and tail appear separate) were tabulated but not scored.

The final body weight, body weight gain, and DNA damage results were analyzed using Statistical Analysis System version 9.2 (SAS institute, Cary, NC, USA). Homogeneity of variance was analyzed using the Levene’s test, and normality was assessed using the Shapiro-Wilk test. Homogeneous data were analyzed using one-way analysis of variance (ANOVA) and test article-treated groups were compared to the concurrent vehicle control group using a one-tailed Dunnett’s test. Dose-dependent changes were evaluated using a linear regression model. Data that were not homogeneous and normally distributed were transformed using a log transformation and then reanalyzed. Positive control data were analyzed by the Student t-test. The body weight and body weight gain data are presented as mean ± standard deviation (SD) for each group. For % tail DNA, the median value from the 150 cells scored was calculated for each animal, and then group means and standard deviations were calculated. The assay acceptance and evaluation criteria were applied in adherence to OECD Guideline 489.

3. Results

3.1. Mouse lymphoma tk assay

The MLA performed under the described experimental conditions met the acceptance criteria in accordance with OECD 490. For the concurrent vehicle controls, the proportions of small colony mutants in the absence and presence of S9 ranged from 33% to 46%, and mean MF were 76.48, 107.05 and 87.73 per 106 viable cells for the 3 h treatments in the absence and presence of S9 and 24 h treatment in the absence of S9, respectively. Substantial increases in the number of both small and large colony mutants were observed following the treatment with positive control chemicals MMS and B[a]P, with the mean total MF rising above 300 per 106 viable cells. The values from negative and positive control groups were concordant with the laboratory’s historical control data under similar experimental conditions. No marked changes in osmolality or pH were observed in the culture medium treated with the test article at the highest concentration (5000 μg/mL) compared to the concurrent vehicle control. The results of cytotoxicity range-finder experiment and mutation experiment are presented in Table 3, Table 4, respectively.

Table 3.

Relative Suspension Growth in Range-Finder Experiment.

Concentration 3 h Treatment – %RSG
Concentration 24 h Treatment – %RSG
(μg/mL) −S9 +S9 (μg/mL) −S9
0 100 100 0 100
156.3 90 95 19.53 91
312.5 92 98 39.06 90
625 89 87 78.13 90
1250 92 90 156.3 89
2500 88 91 pp 312.5 82
5000 88 NE pp 625 87
1250 85
2500 87
5000 81

%RSG, percent relative suspension growth; pp, precipitation noted at end of treatment incubation period.

NE, not evaluated due to observation of precipitate.

Table 4.

Relative Total Growth and Mutant Frequency in Main Exepriment.

3 h Treatment –S9
3 h Treatment + S9
24 h Treatment –S9
Concentration %RTG MF Concentration %RTG MF Concentration %RTG MF
(μg/mL) (μg/mL)a (μg/mL)
0 100 76.48 0 100 107.05 0 100 87.73
250 81 87.52 250 138 93.42 250 111 69.15
500 84 70.84 500 123 89.19 500 85 107.51
1000 74 91.14 750 118 91.16 1000 97 85.55
2000 83 94.26 1000 114 86.08 2000 92 89.27
3000 80 89.06 1500 135 88.50 3000 86 86.39
4000 73 97.10 2000 163 77.43 4000 75 103.28
5000 67 82.73 2500 134 73.32 5000 64 91.63
MMS 15 44 437.21 3000pp 133 72.99 MMS 5 44 811.51
MMS 20 38 539.00 B[a]P 2 60 615.15 MMS 7.5 33 980.42
B[a]P 3 43 1110.29

MF, mutant frequency; RTG, relative total growth; pp, precipitation observed at end of treatment incubation period.

a

A concentration of 5000 μg/mL was tested in the presence of S9 but discarded following the treatment incubation period due to precipitation; Linear trend test on MF for 3 h treatment –S9: p-value = 0.1165, not significant; Linear trend test on MF for 3 h treatment +S9: p-value = not significant (negative trend); Linear trend test on MF for 24 h treatment: p-value = 0.1759, not significant.

In the range-finder experiment, among six tested concentrations ranging from 156.3–5000 μg/mL, no post-treatment precipitate was observed in the absence of S9, but post-treatment precipitate was observed at the two highest concentrations in the presence of S9 (2500 and 5000 μg/mL) for the 3 h treatment. No post-treatment precipitate was observed after the 24 h treatment in the absence of S9 for nine tested concentrations ranging from 19.53–5000 μg/mL. The test article was not cytotoxic, as indicated by the 3 h treatment RSG values of 88% and 91% for the highest analyzable concentrations of 5000 and 2500 μg/mL in the absence and presence of S9, respectively. The RSG value for the highest concentration tested (5000 μg/mL) was 81 % after the 24 h treatment in the absence of S9 (Table 3).

In the mutation experiment, following the 3 h treatment period, post-treatment precipitate was observed at the two highest concentrations in the presence of S9 (3000 and 5000 μg/mL) but no post-treatment precipitate was observed in the absence of S9. Therefore, the highest analyzable concentrations for the 3 h treatment were 5000 μg/mL in the absence of S9 and 3000 μg/mL (the lowest precipitating concentration) in the presence of S9. Following the 24 h treatment in the absence of S9, no post-treatment precipitate was observed at any concentration and 5000 μg/mL was the highest concentration analyzed. The RTG values were 67 % and 133% at the highest analyzable concentrations following the 3 h treatments in the absence and presence of S9, respectively. The RTG value following the 24 h treatment in the absence of S9 was 64 % at 5000 μg/mL. Under each treatment condition, the MF at the test article concentrations plated, with or without S9, were all less than the sum of the mean MF of the vehicle control plus the GEF, and the linear trend tests on MF were non-significant (Table 4), indicating a negative result under each treatment condition.

3.2. Comet assay

All animals survived to the scheduled termination without showing signs of moribundity. There were no abnormal observations in the animals that received the test article or 150 mg/kg bw/day EMS except for one animal in the 2000 mg/kg bw/day dose group that had diarrhea at 1 h post-dose on Day 2. No statistically significant changes were observed in final body weight or body weight gain of the groups administered purified aloe dry juice compared to the concurrent vehicle control, while EMS resulted in a statistically lower mean body weight gain compared to the vehicle control group (Table 5).

Table 5.

Body Weight and Changes in Male F344 Rats.

Dose Level (mg/kg bw/day) Initial Body Weight (g, mean ± SD)a Final Body Weight (g, mean ± SD)a Body Weight Change (g, mean ± SD)a
0 160.7 ± 5.4 167.0 ± 5.9 6.3 ± 1.2
500 159.9 ± 6.5 165.1 ± 8.5 5.2 ± 3.0
1000 160.4 ± 5.7 163.8 ± 6.9 3.4 ± 3.6
2000 163.7 ± 5.9 168.7 ± 5.1 5.0 ± 1.3
EMS – 150 162.0 ± 6.5 158.2 ± 7.0 −3.9 ± 2.7b

SD, standard deviation.

a

Calculated from individual animal data.

b

Statistically significant difference compared to the concurrent vehicle control (p < 0.0001).

The % tail DNA results for the colon and kidney are presented in Fig. 2. EMS as the positive control resulted in a statistically significant increase in % tail DNA with respect to the vehicle control (p < 0.05) in both tissues. Orally administered purified Aloe vera whole leaf dry juice up to 2000 mg/kg bw/day did not cause a statistically significant induction of DNA strand breaks in the colon epithelial cells or kidney cells compared to the concurrent vehicle control (p > 0.05). A statistically significant decrease in DNA damage was observed in the kidney cells of the group that received 1000 mg/kg bw/day (p = 0.01). This decrease in DNA damage in the mid-dose group coupled with the lack of any dose response is not deemed to be biologically relevant. Since none of the test article treated groups exhibited a statistically significant increase in DNA damage for either kidney or colon, there was no dose-related response, and the values were consistent with laboratory’s historical control data, the comet assay was interpreted as negative in these tissues under the experimental condition.

Fig. 2.

Fig. 2

Comet assay mean % tail DNA (mean ± SD) in male F344N rats (n = 5 animals/group; 750 cells/group/tissue) after oral exposure to purified aloe whole leaf dry juice. * P < 0.05 compared to the concurrent vehicle control.

4. Discussion

Mutagenic and genotoxic potential of various Aloe vera preparations (whole leaf or inner leaf) has been investigated in prokaryotic and eukaryotic test systems with and without metabolic activation [18]. Non-decolorized aloe whole leaf preparation as well as aloe HAD were found to be mutagenic in both in vitro and in vivo assays [[17], [18], [19],42,43,37,44,45]. With regard to aloe preparations containing trace or no anthraquinones; such as purified aloe whole leaf preparations, inner leaf gel and aloe acemannan; bacterial mutation assays have consistently shown negative outcomes [20,26,27,29,46]. However, results of in vitro studies in mammalian cell models appear to be limited and inconsistent. Williams et al. [27] demonstrated that an Aloe vera inner leaf gel material with <10 ppm aloins (Qmatrix®) did not induce chromosomal aberrations in Chinese hamster lung cells, whereas a decolorized aloe whole leaf extract with 63 ppm of aloin A was found to be mutagenic in a MLA at dosing concentrations of 6000–8000 μg/mL in the absence of S9 [28]. Of note, the level of aloin impurities in the material tested by Guo et al. [28] was ∼6 times higher than the industry standard set by IASC for Aloe vera leaf juice preparations intended for oral consumption.

In light of the discrepancies in the outcome among in vitro genotoxicity assays of decolorized Aloe vera preparations in the literature, we evaluated a purified Aloe vera whole leaf dry juice following the EFSA (2012) and OECD [32] recommended genotoxicity testing strategy, which included the OECD guideline compliant in vitro MLA and in vivo comet assay with an appropriate animal model and target organs. The MLA was intentionally selected in lieu of other in vitro mammalian cell assays because of the positive mutagenicity found by Guo et al. [28] in the same assay. The present study demonstrated that the purified Aloe vera whole leaf dry juice with 0.3 ppm of total aloins and non-detectable aloe-emodin did not induce mutations in the MLA at concentrations up to 5000 μg/mL (the maximum concentration recommended for testing mixtures according to OECD 490) in the absence of S9 and up to the precipitating concentration of 3000 μg/mL in the presence of S9 under the experimental conditions. This negative finding is consistent with that of Guo study in which no mutagenicity was detected for its decolorized aloe whole leaf extract up to 5000 μg/mL. Nevertheless, there are notable differences between the two studies. The purified aloe whole leaf dry juice in the present study contained substantially lower levels of aloins than the extract in the Guo study (0.3 vs. 63 ppm). The decolorized aloe extract in the Guo study markedly reduced pH and raised osmolality in the culture medium, whereas the test article in the present study did not cause these effects at similar dosing concentrations. Additionally Guo et al. found that its decolorized aloe extract induced substantial ROS in the culture system, which appeared to coincide with increases in MF at very high dosing concentrations. Emodin, a structural related HAD, was found to increase ROS levels and cause DNA damage in the cultured human peripheral blood lymphocytes (HPBLs) in vitro [47], suggesting that aloe HAD-induced ROS may contribute to the genotoxic effect in the test system. This raises further questions as to whether mutagenic response observed by Guo et al. is, at least in part, an indirect outcome of excessive oxidative stress, a condition known to compromise genome stability and cause damage of DNA and chromosomes in the cell culture system [48].

Considering that cell culture systems have inherent deficiencies (impaired DNA repair capability, lack of antioxidant enzymes and ADME) and are more susceptible to false positive outcomes, in vivo tests offer more relevant evidence for extrapolation to humans with respect to cancer risk. An appropriately performed comet assay is regarded as a useful tool to evaluate in vivo genetic toxicity as a follow-up to positive or equivocal in vitro findings and as a secondary measure of genotoxicity in a tissue other than bone marrow to inform potential carcinogenicity risk in humans [30,[49], [50], [51]]. In vivo evidence related to genotoxic effects of Aloe vera material is scarce. A search of the literature yielded only one published study, an in vivo micronucleus assay evaluating orally administered Aloe vera inner leaf gel with < 10 ppm aloins (Qmatrix®) in the Institute for Cancer Research (ICR) mice [27], which found a negative outcome for induction of micronuclei in bone marrow cells. Since ingested aloins and aloe-emodin have very poor bioavailability, and systemic exposure to the test article or aloins was not measured by Williams et al., its negative findings could be due to a lack of exposure in the bone marrow compartment [17,52]. The comet assay is increasingly being used to evaluate DNA damaging or protective effects of natural botanicals added to food products [[53], [54], [55]]. In the present comet assay, purified Aloe vera whole leaf dry juice at oral doses of up to 2000 mg/kg bw/day (the limit dose for nontoxic materials according to OECD 489) did not induce DNA strand breaks in the cells isolated from either the kidney or colon epithelium of male F344 rats. It should be noted that comet assays conducted in F344 rats and reporting data in the colon and kidney tissues are dearth in the literature, so do the historical control data. O’Donoghue et al. [55] reported a comet assay in F344 rats, in which the % tail DNA values for the colon and kidney appear to be slightly lower for the vehicle control, and are comparable for the EMS treated positive control when compared to the values observed in the present assay. Since within-assay variance is very small for both studies, different methods and procedures of tissue sampling and handling could conceivably account for the discernable variability between different laboratories. Nevertheless, the results from the present comet assay clearly corroborate the negative findings from the MLA performed using the same batch of test material, and provide further evidence that oral exposure to purified aloe preparation may not cause genetic toxicity in vivo.

In the NTP carcinogenicity study exposure to non-decolorized Aloe vera whole leaf extract via drinking water significantly increased the incidence of adenoma and carcinoma in the large intestine of F344 rats [20]. This carcinogenic effect on the colon was later reproduced in the 13-week study using the same animal model in which preneoplastic lesions in the mucosal and goblet cells of the large intestine were observed following the oral administration of aloins [52]. Notably, no treatment-related cancerous lesions were observed in any internal organs in these studies of non-decolorized aloe whole leaf extract. Coupled with the findings from Guo et al. [28] showing that mutagenic activity only occurred in the absence of metabolic activation, the evidence strongly suggests that the genotoxic target organ linked to aloe whole leaf is the site of contact. Typically, the stomach and upper intestinal tract would be considered suitable target organs for evaluation in the comet assay for orally administered substances that may act at the site of direct contact [33]. However, these sites do not appear to be the carcinogenic targets as evidenced by the absence of neoplastic lesions in the forestomach and small intestine of F344 rats in the NTP carcinogenicity study. Moreover, there is no evidence that other structurally related HAD compounds (e.g., emodin, sennosides, danthron) exhibited carcinogenic effect on the stomach or small intestine when administered orally in rodent cancer bioassays [[56], [57], [58], [59], [60]]. These findings support that the colon, rather than the stomach and small intestine, is the most relevant target organ in the present comet assay.

With respect to the kidney, Nesslany et al. [37] found that oral administration of aloe-emodin at 2000 mg/kg bw/day induced DNA damage in kidney cells of male OF1 mice. In our comet assay no genotoxicity was detected in the kidney of male F344 rats treated with the purified aloe whole leaf dry juice. This is not surprising considering that the test article did not contain any detectable level of aloe-emodin. The negative outcome from the present study supports that oral exposure to purified aloe preparation may not pose carcinogenic risk for the kidney. This appears to corroborate with the observations in the NTP carcinogenicity study in which aloe whole extract containing aloe-emodin as high as 71 ppm did not induce any neoplastic lesions in the kidney of F344 rats.

One potential limitation in our research is related to the maximum dosing concentration employed in the MLA. The OECD Guideline 490 recommends the limit dose concentration in the MLA to be the lower of 10 mM, 2 mg/mL, or 2 μL/mL, or determined by a precipitating or limiting cytotoxicity concentration. However, for mixtures of uncertain composition, the top concentration may need to be higher (e.g., 5 mg/mL) in the absence of sufficient cytotoxicity in order to increase the exposure to individual components of the test article. In our work, the purified aloe whole leaf dry juice was tested only up to 5 mg/mL in the absence of S9, at which level it did not induce significant cytotoxicity or cause interfering precipitation in the cell culture. Since Guo et al. [28] found that positive responses in the absence of S9 occurred only at higher concentrations (6 mg/mL and above) of the decolorized aloe extract, the data from the present MLA alone might not be sufficient to rule out the effects observed at higher dosing concentrations by Guo et al. Instead of testing higher dose concentrations in the MLA, we opted to perform in vivo comet assay to assess genotoxicity potential in a relevant rat model and at target organs germane to carcinogenic effects of aloe whole leaf to assure that an outcome with clinical relevance to human exposure could be achieved.

5. Conclusions

In summary, the results from current research demonstrate the absence of genotoxicity for a purified Aloe vera whole leaf dry juice containing insignificant amount of HAD in the mouse lymphoma tk assay under testing conditions compliant with the OECD 490 guideline. Furthermore, in vivo comet assay conducted per the OECD 489 guideline confirms that this material did not induce DNA damage in the colon and kidney of male F344 rats, reflecting an appropriate in vivo model and target organs relevant to human cancer risk associated with consumption of aloe whole leaf and/or its HAD constituents. The evidence generated herein is of important value in informing hazard identification and carcinogenicity risk assessment pertaining to purified aloe leaf preparations containing very low levels of HAD as technically unavoidable impurities. Nonetheless, further research is likely warranted to elucidate the mechanism(s) of the carcinogenic effect of non-decolorized Aloe vera whole leaf preparation or aloe HAD observed in the rat model in order to fully comprehend their relevance to dietary exposure to Aloe vera products and to devise appropriate risk mitigation strategies.

CRediT authorship contribution statement

Jiang Hu: conceptualization, methodology, original manuscript preparation. Mel Lloyd: study director, methodology, data interpretation and reporting for the mouse lymphoma assay, manuscript reviewing and editing. Cheryl Hobbs: methodology and execution, data interpretation for the comet assay, manuscript reviewing and editing. Peter Cox: formulation analysis for the mouse lymphoma assay. Keith Burke: formulation analysis for the comet assay. Gareth Pearce: methodology and execution for the mouse lymphoma assay. Michael A. Streicker: study director for comet assay. Quanyin Gao: test article characterization. Vasilios Frankos: conceptualization, methodology.

Transparency document

Transparency document
mmc1.zip (504.6KB, zip)

Declaration of Competing Interest

The authors report no declarations of interest.

Acknowledgement

Funding for this research was provided by Herbalife Nutrition, a manufacturer of nutritional products that contain purified Aloe vera whole leaf dry juice. The conduct, data collection and interpretation of the mouse lymphoma tk and comet assays were carried out independently by Covance Laboratories and Integrated Laboratory Systems, respectively.

Edited by Dr. A.M Tsatsaka

References

  • 1.Mehta I. “History of Aloe vera” – (a magical plant) IOSR J. Humanities and Soc. Sci. 2017;22(8):4. [Google Scholar]
  • 2.Upton R. American Herbal Pharmacopoeia; Scotts Valley, CA: 2012. American Herbal Pharmacopoeia Monograph: Aloe vera Leaf, Aloe vera Leaf Juice, Aloe vera Inner Leaf Juice. [Google Scholar]
  • 3.Eshun K., He Q. Aloe vera: a valuable ingredient for the food, pharmaceutical and cosmetic industries - a review. Crit. Rev. Food Sci. Nutr. 2004;44(2):91–96. doi: 10.1080/10408690490424694. [DOI] [PubMed] [Google Scholar]
  • 4.Nandal U., Bhardwaj R.L. Aloe vera for human nutrition, health and cosmetic use - a review. Int. Res. J. Plant Sci. 2012;3(3):38–46. [Google Scholar]
  • 5.Reynolds T., Dweck A.C. Aloe vera leaf gel: a review update. J. Ethnopharmacol. 1999;68(1–3):3–37. doi: 10.1016/s0378-8741(99)00085-9. [DOI] [PubMed] [Google Scholar]
  • 6.Kaithwas G., Singh P., Bhatia D. Evaluation of in vitro and in vivo antioxidant potential of polysaccharides from Aloe vera (Aloe barbadensis miller) gel. Drug Chem. Toxicol. 2014;37(2):135–143. doi: 10.3109/01480545.2013.834350. [DOI] [PubMed] [Google Scholar]
  • 7.Pressman P., Clemens R., Hayes A.W. Aloe vera at the frontier of glycobiology and integrative medicine: health implications of an ancient plant. SAGE Open Medicine. 2019;7 doi: 10.1177/2050312119875921. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Sadoyu S., Rungruang C., Wattanavijitkul T., Sawangjit R., Thakkinstian A., Chaiyakunapruk N. Aloe vera and health outcomes: an umbrella review of systematic reviews and meta-analyses. Phytother. Res. 2020;35(2):1–22. doi: 10.1002/ptr.6833. [DOI] [PubMed] [Google Scholar]
  • 9.Sánchez M., González-Burgos E., Iglesias I., Gómez-Serranillos M.P. Pharmacological update properties of Aloe vera and its major active constituents. Molecules (Basel, Switzerland) 2020;25(6):1324. doi: 10.3390/molecules25061324. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Suksomboon N., Poolsup N., Punthanitisarn S. Effect of Aloe vera on glycaemic control in prediabetes and type 2 diabetes: a systematic review and meta-analysis. J. Clin. Pharm. Ther. 2016;41(2):180–188. doi: 10.1111/jcpt.12382. [DOI] [PubMed] [Google Scholar]
  • 11.Fouillaud M., Caro Y., Venkatachalam M., Grondin I., Dufossé L. Anthraquinones. In: Nollet L.M.L., Gutierrez-Uribe J.A., editors. Phenolic Compounds in Food - Characterization and Analysis. CRC Press; 2018. p 131. [Google Scholar]
  • 12.EFSA Panel on Dietetic Products Nutrition and Allergies Scientific opinion on the substantiation of a health claim related to hydroxyanthracene derivatives and improvement of bowel function pursuant to article 13(5) of regulation (EC) No 1924/2006. EFSA J. 2013;11(10):3412. doi: 10.2903/j.efsa.2013.3412. [DOI] [Google Scholar]
  • 13.EMA . In: European Union Herbal Monograph on Aloe barbadensis Mill. and on Aloe (Various Species, Mainly Aloe ferox Mill. and Its Hybrids), folii Succus Siccatus. Agency E.M., editor. 2017. p 9. [Google Scholar]
  • 14.Health Canada . In: Natural Health Product Monograph - Aloe vera Oral. Health Canada, editor. 2018. [Google Scholar]
  • 15.Park M.K., Park J.H., Kim N.Y., Shin Y.G., Choi Y.S., Lee J.G., Kim K.H., Lee S.K. Analysis of 13 phenolic compounds in Aloe species by high performance liquid chromatography. Phytochem. Anal. 1998;9(4):186–191. [Google Scholar]
  • 16.Saccù D., Bogoni P., Procida G. Aloe exudate: characterization by reversed phase HPLC and headspace GC-MS. J. Agric. Food. Chem. 2001;49(10):4526–4530. doi: 10.1021/jf010179c. [DOI] [PubMed] [Google Scholar]
  • 17.EFSA Panel on Food Additives and Nutrient Sources added to Food Safety of hydroxyanthracene derivatives for use in food. EFSA J. 2018;16(1):e05090. doi: 10.2903/j.efsa.2018.5090. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.IARC . vol 108. International Agency for Research on Cancer; 2016. (Aloe Vera - Carcinogenicity of Some Drugs and Herbal Products). [Google Scholar]
  • 19.Lanouar F., Boughattas I., Mkhinini M., Bousserrhine N., Banni M. Evidence of the genotoxic effect of aloin on earth worms Eisenia andrei. Focus on Sci. 2017;3:1–6. doi: 10.21859/focsci-03041467. [DOI] [Google Scholar]
  • 20.Boudreau M.D., Beland F.A., Nichols J.A., Pogribna M. Toxicology and carcinogenesis studies of a nondecolorized [corrected] whole leaf extract of Aloe barbadensis miller (Aloe vera) in F344/N rats and B6C3F1 mice (drinking water study) Nat. Toxicol. Program Tech. Rep. Ser. 2013;577:1–266. [PubMed] [Google Scholar]
  • 21.Ahlawat K.S., Khatkar B.S. Processing, food applications and safety of Aloe vera products: a review. J. Food Sci. Technol. 2011;48(5):525–533. doi: 10.1007/s13197-011-0229-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.IASC . 2012. Aloe vera Processing.https://www.iasc.org/Resources/AloeVeraProcessing.aspx [Google Scholar]
  • 23.IASC . 2019. Certification Program - Policies & Operational Procedures.https://www.iasc.org/Portals/19/Documents/Certification/19_0730_IASC%20Certification%20Program_SOP%20Final.pdf?ver=2019-07-30-161006-300 [Google Scholar]
  • 24.European Commission . 2020. Draft COMMISSION REGULATION (EU) Amending Annex III to Regulation (EC) No 1925/2006 of the European Parliament and of the Council as Regards Botanical Species Containing Hydroxyanthracene Derivatives. Comitology Register https://ec.europa.eu/transparency/comitology-register/screen/documents/067676/3/consult?lang=en. Accessed December 15, 2020. [Google Scholar]
  • 25.Guo X., Mei N. Aloe vera: a review of toxicity and adverse clinical effects. J. Environ. Sci. Health Part C Environ. Carcinog. Ecotoxicol. Rev. 2016;34(2):77–96. doi: 10.1080/10590501.2016.1166826. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Sehgal I., Winters W.D., Scott M., Kousoulas K. An in vitro and in vivo toxicologic evaluation of a stabilized Aloe vera gel supplement drink in mice. Food Chem. Toxicol. 2013;55:363–370. doi: 10.1016/j.fct.2013.01.012. [DOI] [PubMed] [Google Scholar]
  • 27.Williams L.D., Burdock G.A., Shin E., Kim S., Jo T.H., Jones K.N., Matulka R.A. Safety studies conducted on a proprietary high-purity Aloe vera inner leaf fillet preparation, qmatrix®. Regul. Toxicol. Pharm. 2010;57(1):90–98. doi: 10.1016/j.yrtph.2010.01.002. [DOI] [PubMed] [Google Scholar]
  • 28.Guo X., Zhang S., Dial S.L., Boudreau M.D., Xia Q., Fu P.P., Levy D.D., Moore M.M., Mei N. In vitro investigation of the mutagenic potential of Aloe vera extracts. Toxicol. Res. 2014;3(6):487–496. doi: 10.1039/C4TX00053F. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 29.Sehgal I., Winters W.D., Scott M., David A., Gillis G., Stoufflet T., Nair A., Kousoulas K. Toxicologic assessment of a commercial decolorized whole leaf Aloe vera juice, lily of the desert filtered whole leaf juice with aloesorb. J. Toxicol. 2013 doi: 10.1155/2013/802453. 12. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.EFSA Scientific Committee Scientific opinion on genotoxicity testing strategies applicable to food and feed safety assessment. EFSA J. 2011;9(9):2379. doi: 10.2903/j.efsa.2011.2379. [DOI] [Google Scholar]
  • 31.EFSA Scientific Committee Genotoxicity assessment of chemical mixtures. EFSA J. 2019;17(1):e05519. doi: 10.2903/j.efsa.2019.5519. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.OECD . 2015. Guidance Document on Revisions to OECD Genetic Toxicology Test Guidelines. 58. [Google Scholar]
  • 33.OECD . 2016. Test No. 489: In Vivo Mammalian Alkaline Comet Assay. [Google Scholar]
  • 34.OECD . 2016. Test No. 490: In Vitro Mammalian Cell Gene Mutation Tests Using the Thymidine Kinase Gene. [Google Scholar]
  • 35.Kline D., Ritruthai V., Babajanian S., Gao Q., Ingle P., Chang P., Swanson G. Quantitative analysis of aloins and aloin-emodin in Aloe vera raw materials and finished products using high-performance liquid chromatography: single-laboratory validation, first action 2016.09. J. AOAC Int. 2017;100(4):1154–1157. doi: 10.5740/jaoacint.2016_09. [DOI] [PubMed] [Google Scholar]
  • 36.Moore M.M., Honma M., Clements J., Bolcsfoldi G., Burlinson B., Cifone M., Clarke J., Delongchamp R., Durward R., Fellows M., Gollapudi B., Hou S., Jenkinson P., Lloyd M., Majeska J., Myhr B., O’Donovan M., Omori T., Riach C., San R., Stankowski L.F., Jr., Thakur A.K., Van Goethem F., Wakuri Isao, Yoshimura I. Mouse lymphoma thymidine kinase gene mutation assay: follow-up meeting of the International workshop on genotoxicity testing--Aberdeen, Scotland, 2003--assay acceptance criteria, positive controls, and data evaluation. Environ. Mol. Mutagen. 2006;47(1):1–5. doi: 10.1002/em.20159. [DOI] [PubMed] [Google Scholar]
  • 37.Nesslany F., Simar-Meintières S., Ficheux H., Marzin D. Aloe-emodin-induced DNA fragmentation in the mouse in vivo comet assay. Mutation Res. Genetic Toxicol. Environ. Mutagenesis. 2009;678(1):13–19. doi: 10.1016/j.mrgentox.2009.06.004. [DOI] [PubMed] [Google Scholar]
  • 38.Park M.Y., Kwon H.J., Sung M.K. Plasma, tissue and urinary levels of aloin in rats after the administration of pure aloin. Nutr. Res. Practice. 2008;2(1):17–21. doi: 10.4162/nrp.2008.2.1.17. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39.Yu C.P., Shia C.S., Lin H.J., Hsieh Y.W., Lin S.P., Hou Y.C. Analysis of the pharmacokinetics and metabolism of aloe-emodin following intravenous and oral administrations in rats. Biomed. Chromatogr. 2016;30(10):1641–1647. doi: 10.1002/bmc.3735. [DOI] [PubMed] [Google Scholar]
  • 40.National Research Council . Guide for the Care and Use of Laboratory Animals. 8th ed. National Academies Press; 2011. [PubMed] [Google Scholar]
  • 41.Shao A., Broadmeadow A., Goddard G., Bejar E., Frankos V. Safety of purified decolorized (low anthraquinone) whole leaf Aloe vera (L) burm. F. juice in a 3-month drinking water toxicity study in F344 rats. Food Chem. Toxicol. 2013;57:21–31. doi: 10.1016/j.fct.2013.03.002. [DOI] [PubMed] [Google Scholar]
  • 42.Li Y., Luan Y., Qi X., Li M., Gong L., Xue X., Wu X., Wu Y.F., Chen M., Xing G.Z., Yao J., Ren J. Emodin triggers DNA double-strand breaks by stabilizing topoisomerase II-DNA cleavage complexes and by inhibiting ATP hydrolysis of topoisomerase II. Toxicol. Sci. 2010;118(2):435–443. doi: 10.1093/toxsci/kfq282. [DOI] [PubMed] [Google Scholar]
  • 43.Mueller S.O., Stopper H. Characterization of the genotoxicity of anthraquinones in mammalian cells. Biochimica et Biophysica Acta (BBA) - General Subjects. 1999;1428(2–3):406–414. doi: 10.1016/S0304-4165(99)00064-1. [DOI] [PubMed] [Google Scholar]
  • 44.Müller S.O., Eckert I., Lutz W.K., Stopper H. Genotoxicity of the laxative drug components emodin, aloe-emodin and danthron in mammalian cells: topoisomerase II mediated? Mutation Res. Genetic Toxicol. 1996;371(3–4):165–173. doi: 10.1016/S0165-1218(96)90105-6. [DOI] [PubMed] [Google Scholar]
  • 45.Wolfle D., Schmutte C., Westendorf J., Marquardt H. Hydroxyanthraquinones as tumor promoters: enhancement of malignant transformation of C3H mouse fibroblasts and growth stimulation of primary rat hepatocytes. Cancer Res. 1990;50(20):6540–6544. [PubMed] [Google Scholar]
  • 46.Fogleman R.W., Shellenberger T.E., Balmer M.F., Carpenter R.H., McAnalley B.H. Subchronic oral administration of acemannan in the rat and dog. Vet. Hum. Toxicol. 1992;34(2):144–147. [PubMed] [Google Scholar]
  • 47.Brkanac S.R., Gerić M., Gajski G., Vujčić V., Garaj-Vrhovac V., Kremer D., Domijan A.M. Toxicity and antioxidant capacity of Frangula alnus Mill. bark and its active component emodin. Regul. Toxicol. Pharm. 2015;73(3):923–929. doi: 10.1016/j.yrtph.2015.09.025. [DOI] [PubMed] [Google Scholar]
  • 48.Halliwell B. Cell culture, oxidative stress, and antioxidants: avoiding pitfalls. Biomedical Journal. 2014;37(3):99–105. doi: 10.4103/2319-4170.128725. [DOI] [PubMed] [Google Scholar]
  • 49.Brendler-Schwaab S., Hartmann A., Pfuhler S., Speit G. The in vivo comet assay: use and status in genotoxicity testing. Mutagenesis. 2005;20(4):245–254. doi: 10.1093/mutage/gei033. [DOI] [PubMed] [Google Scholar]
  • 50.EFSA Panel on Food Contact Materials Enzymes Flavourings and Processing Aids Guidance on the data required for the risk assessment of flavourings to be used in or on foods. EFSA J. 2010;8(6):1623. doi: 10.2903/j.efsa.2010.1623. [DOI] [Google Scholar]
  • 51.ICH . 2012. International Conference on Harmonisation; Guidance on S2(R1) Genotoxicity Testing and Data Interpretation for Pharmaceuticals Intended for Human Use. [PubMed] [Google Scholar]
  • 52.Boudreau M.D., Olson G.R., Tryndyak V.P., Bryant M.S., Felton R.P., Beland F.A. From the cover: aloin, a component of the Aloe vera plant leaf, induces pathological changes and modulates the composition of microbiota in the large intestines of F344/N male rats. Toxicol. Sci. 2017;158(2):302–318. doi: 10.1093/toxsci/kfx105. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 53.Fawzy E.I., El Makawy A.I., Mahmoud El-Bamby M., Elhamalawy H.O. Improved effect of pumpkin seed oil against the bisphenol-a adverse effects in male mice. Toxicol. Rep. 2018;5:857–863. doi: 10.1016/j.toxrep.2018.08.014. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 54.Hobbs C.A., Koyanagi M., Swartz C., Davis J., Maronpot R., Recio L., Hayashi S. Genotoxicity evaluation of the naturally-derived food colorant, gardenia blue, and its precursor, genipin. Food and Chem. Toxicol. 2018;118:695–708. doi: 10.1016/j.fct.2018.06.001. [DOI] [PubMed] [Google Scholar]
  • 55.O’Donoghue J.L., Beevers C., Buard A. Hydroquinone: assessment of genotoxic potential in the in vivo alkaline comet assay. Toxicol. Rep. 2021;8:206–214. doi: 10.1016/j.toxrep.2021.01.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 56.Lydén-Sokolowski A., Nilsson A., Sjöberg P. Two-year carcinogenicity study with sennosides in the rat: emphasis on gastro-intestinal alterations. Pharmacology. 1993;47(Suppl 1):209–215. doi: 10.1159/000139860. [DOI] [PubMed] [Google Scholar]
  • 57.Mitchell J.M., Mengs U., McPherson S., Zijlstra J., Dettmar P., Gregson R., Tigner J.C. An oral carcinogenicity and toxicity study of senna (Tinnevelly senna fruits) in the rat. Arch. Toxicol. 2006;80(1):34–44. doi: 10.1007/s00204-005-0021-9. [DOI] [PubMed] [Google Scholar]
  • 58.Mori H., Sugie S., Niwa K., Takahashi M., Kawai K. Induction of intestinal tumours in rats by chrysazin. Br. J. Cancer. 1985;52(5):781–783. doi: 10.1038/bjc.1985.257. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 59.Mori H., Sugie S., Niwa K., Yoshimi N., Tanaka T., Hirono I. Carcinogenicity of chrysazin in large intestine and liver of mice. Jpn. J. Cancer Res. Gann. 1986;77(9):871–876. [PubMed] [Google Scholar]
  • 60.National Toxicology Program Toxicology and carcinogenesis studies of emodin (CAS NO. 518-82-1) feed studies in F344/N rats and B6C3F1 mice. Nat. Toxicol. Program Tech. Rep. Ser. 2001;493:1–278. [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Transparency document
mmc1.zip (504.6KB, zip)

Articles from Toxicology Reports are provided here courtesy of Elsevier

RESOURCES