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Background. Chlorine dioxide (ClO2) and its related compounds have been proposed as a treatment for several diseases; their popularity increased during the COVID-19 pandemic. This study aimed to identify, characterize, and synthesize the existing publications regarding ClO2 and its related compounds' toxicity and efficacy as a treatment. Material and Methods. A scoping systematic review of animal and human studies was carried out in PubMed and EMBASE from their origin 1946 to October 20, 2020. Outcomes of interest were toxicity and efficacy of ClO2 and related compounds. After title, abstract, and full-text peered-review screening, data was extracted and synthesized. Methodological and reporting bias was analyzed in order to identify low-quality studies. Results. We identified 15 animal and 19 human studies out of 752 articles found in academic literature. The latter selection included 13 toxicity case reports and 6 clinical studies reporting on the topical and systemic administration of ClO2. Animal studies hinted at the possibility of reproductive, developmental, thyroid, hematological, and nephrotic damage in different species. Most studies displayed methodological bias and low quality in reporting. On the human side, several case reports described mild and severe intoxications with ClO2 and related compounds at different doses in healthy and comorbid individuals. Clinical studies revealed no conclusive evidence on ClO2 as an effective systemic treatment. Conclusions. The principle of precaution should be called upon until quality evidence is provided; new and more comprehensive pre-clinical studies are needed before carrying out human trials. Meanwhile, tighter regulations on this substance could prevent adverse toxicological events.
Antecedentes. El dióxido de cloro (ClO2) y otros compuestos derivados del cloro se han propuesto como tratamiento para varias enfermedades; su popularidad aumentó durante la pandemia de COVID-19. Este estudio pretende identificar, caracterizar y sintetizar la evidencia y la calidad de las publicaciones existentes acerca de la toxicidad y la eficacia del ClO2 como tratamiento. Material y métodos. Se realizó una revisión sistemática de estudios en animales y humanos en PubMed y EMBASE desde su origen hasta el 20 de octubre, 2020. Los resultados de interés fueron la toxicidad y la eficacia del ClO2. Se identificaron las publicaciones, se extrajeron los datos y se analizó el sesgo metodológico y de reporte para identificar estudios de baja calidad. Resultados. De 752 artículos de literatura académica, se seleccionaron 15 estudios en animales y 19 en humanos. Los últimos incluyeron 13 reportes de toxicidad y 6 estudios clínicos sobre la administración tópica y sistémica de ClO2. Los estudios en animales sugirieron la posibilidad de daños reproductivos y de desarrollo, tiroideos, hematológicos y renales en diferentes especies. La mayoría de los estudios mostró sesgo metodológico y baja calidad. En cuanto a los seres humanos, diversos reportes de toxicidad describieron intoxicaciones leves y graves con ClO2 y compuestos relacionados con diferentes dosis en individuos sanos y comórbidos. En los estudios clínicos no se halló alguna prueba concluyente sobre sobre el ClO2 como un tratamiento sistémico eficaz. Conclusiones. La evidencia de toxicidad sistémica en animales y humanos advierte la necesidad de desarrollar nuevos estudios preclínicos, más modernos y de calidad suficiente, en diferentes especies, antes de llevar a cabo ensayos clínicos. Mientras tanto, se debe apelar al principio de precaución y promover regulaciones más estrictas acerca de esta sustancia para prevenir eventos toxicológicos adversos.
Documented use of chlorine dioxide (ClO2) in academic literature dates back to 19461 when ClO2 began to be used for paper bleaching and to purify water because of its oxidative power to eliminate pollutants and remove the unpleasant taste and odor from water.2 In the 60s, several studies began to explore the kinetics, mechanisms, and effectiveness of ClO2 as a disinfectant against bacteria, viruses, and protozoa.3,4
Furthermore, hypotheses identifying ClO2 as a possible therapeutic agent based on its oxidative properties began to emerge, and studies on the acute and chronic toxicology of ClO2 and its metabolites in animals began to be published.5 Since then, several patents concerning the use of ClO2 and its derivatives as a treatment for several diseases (including HIV) were published without solid evidence support.6
In 2006, a book claimed that a product made of a sodium chlorite solution in combination with citric or hydrochloric acid (known as a "Miracle Mineral Solution" or MMS) was able to cure malaria and other diseases.7 These claims on MMS were later amplified on the internet, particularly as a treatment for cancer and autism.8 Nevertheless, the increase in reports of adverse events linked to the consumption of MMS —including vomiting and diarrhea— resulted in warnings against its use issued by the Food and Drug Administration (FDA) in 2010 and by the regulatory agencies of other countries.9
In 2020, with the surge of the COVID-19 pandemic, the use of products made of ClO2 and related compounds as a treatment for the disease gained popularity on social media platforms. A group of supporters, such as the World Health and Life Coalition (COMUSAV, allegedly integrated by health professionals, mainly from Spain and Latin American countries), argued in favor of its innocuity and efficacy, lobbying governments and promoting "treatment protocols" for the use of a chlorine dioxide solution (CDS), gaining thousands of followers.10
Given this renewed interest in ClO2, some authors have collected information regarding the available evidence of this compound as a human treatment. In their 2020 systematic review, Burela et al.11 did not find publications evaluating ClO2 and its derivatives as prophylactic or curative agents for COVID-19 or other coronavirus infections. Authors reported not having found sufficient clinical evidence to support the effectiveness of ClO2 against COVID-19; however, other research groups kept arguing the opposite.12
Due to the conflicting evidence, in this scoping review, we systematically identified, characterized, and synthesized the available evidence (animal and human studies) associated with the toxicity of ClO2, their related compounds, and their efficacy as a treatment for diseases. This study aims to provide comprehensive answers for the scientific public and lay people regarding which information can be relied upon on the issue of ClO2 consumption at the moment.
Literature Source and Search Strategy
A scoping systematic review of academic literature following an adapted version of the PRISMA guidelines was developed to integrate academic literature on chlorine dioxide's efficacy and toxicity outcomes in animal and human studies.
The systematized search collected English, Spanish, French, Portuguese, and German records from MEDLINE (PubMed) and EMBASE from the databases' origins to October 20, 2020. The search strategy included MeSH terms and keywords focusing on chlorine dioxide's therapeutic use and toxicity (Suppl. Table 1).
Screening
Peered-review screening (IR, IL, LM) was subsequently performed by title, abstract, and full-text.
Inclusion and Exclusion Criteria
This study included academic articles (indexed in journals, including letters to the editor) but not grey literature (press publications and reports lacking peer review). Systematic reviews were screened for single pertinent articles, which were included manually.
Studies were only included if ClO2 or its precursors (MMS in particular) were part of the studied substances; byproducts were only considered when resulting from the exposure or administration of the first. There was no predefined study design limitation for the inclusion of studies regarding toxicity and efficacy outcomes (no disease target was specified either).
For animal studies, only the systemic route of administration was considered (it was deemed the closest to oral and parenteral use, which was our outcome of interest in humans). For human studies, the administration route included systemic (oral and parenteral), topical, and buccopharyngeal administration.
Publications regarding uses for water bleaching, surface cleaning (disinfectant properties), or purifying properties of ClO2 were excluded. In vitro, plant, and insect studies were not part of the scope of the study. Protocols and articles with unavailable full-text were also excluded.
Extraction and Data Synthesis
Four researchers extracted relevant data on the publication and study characteristics.
The studied variables for animal studies included the type and number of animals, study type, administration route, tested substances, exposure and dosage, control group, measurements, and outcomes of interest.
Human case reports described individuals involved, exposure context and formulation, toxic or adverse effects, treatment, monitoring, and mechanism behind toxicity. Clinical studies included information on the study design, participants, intervention (formulation, route of administration, and dosage), results, and conclusions.
Methodological Quality and Risk of Bias
Each of the selected animal studies was evaluated for potential sources of selection, performance, detection, attrition, and reporting bias (Suppl. Table 2) using elements adapted from the CAMARADES13 and SYRCLE14 risk of bias tools (A. Animal allocation & randomization, B. Blinding, C. Population size, D. Outcome reporting, complete follow-up, and E. Compliance with animal welfare requirements).
Two critical appraisers evaluated clinical studies using the Joanna Briggs Institute (JBI) risk bias evaluation tools15 for case reports, case-controls, case series, quasi-experiments, and randomized controlled trials (RCT). JBI appraisal final scoring can be found in Supplementary Tables 3 (A-E).
A total of 752 articles were identified through the systematized search. After duplicate removal and screening (title, abstract, and full text), a total of 34 studies were included: 15 in animals and 19 in humans (Figure 1).

Animal Studies
A total of 15 in vivo studies in animals published between 1980 and 2020 were identified (Table 1). Chlorine dioxide (n=10) and sodium chlorite (NaClO2) (n=9) were more frequently tested in animal studies, followed by other chloride species.
Most studies were performed in rats (n=8) and mice (n=5); however, there were also other ones on monkeys (n=2) and chicken embryos (n=1). The majority of animal studies (14 out of 15) aimed to investigate the systemic toxicity of ClO2.
| Tabla 1. Animal studies reporting on efficacy or toxicological outcomes derived from chlorine dioxide exposure | |
|---|---|
Moore, G. S et al., 198016 | |
| POPULATION Animal data | 10-12-weeks old A / J female mice with “normal” levels of G6PD activity; randomly mated with A / J males of a similar age. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Reproductive and developmental toxicity study (oral exposure). Test substance: NaClO2 in drinking water. Dose for the treatment group: 100 pm, (plugging, gestation, parturition and lactation). |
| CONTROL Control group | Negative control: distilled water. |
| Measurements | Live litter size, number of alive at weaning, gestation time, average live birth litter weight, birth weights and weights until weaning at 28 days, number of dead at birth, number of survivors dying before weaning. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | There were no effects derived from the ingestion of chlorite ion (100 ppm) on pregnant dams when measuring gestation time, breeding weight, or age at parturition. However, the conception rate of the exposed dams was reduced 17% compared to controls. The growth rate of A/J pups through weaning was also retarded. |
Bercz, J P et al., 198217 | |
| POPULATION Animal data | African Green monkeys (Cercopithecus aethiops), adults, 5 males and 7 females, body weight range 3-5.7 kg, mean RBC G6PD activities of 8.8 IU/g Hb. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Hematologic and thyroid toxicity study (subchronic toxicity; oral exposure) Test substances: ClO2, NaClO2, NaClO3, NH2Cl. Exponentially rising step doses (30-60 days). Doses of ClO2: 30, 100 and 200 ppm. Doses of NaClO2 and NaClO3: 25, 50, 100, 200 and 400 ppm. Doses of NH2Cl: 100 ppm. Estimated mean daily dose at higher concentration stages: 9 mg / kg / day. |
| CONTROL Control group | Between chemicals, animals rested for 6-9 weeks until re-establishment of baseline clinical parameters. Each animal served as its own control. |
| Measurements | Exhaustive hematology tests (19 clinical parameters measured twice) as well as weight differences were performed. Experiments of in vitro deactivation of ClO2 by animal saliva and in vivo deactivation in the gastric space were also carried out. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | The most significant toxic effect was selectively elicited by ClO2 since this substance inhibited thyroid metabolism. Dose-dependent T4 deficiency developed progressively after 4 weeks, and was reversible after cessation of exposure. NaClO2 caused alterations in Hb levels, RBC count, mHb content and serum transaminase. NaClO3 and NH2Cl did not induce hematologic alterations. |
Moore GS. et al., 198218 | |
| POPULATION Animal data | Two strains of mice, either with “normal” (A /J) and with low levels of G6PD activity (C57L / J). a) Hematologic toxicity: i) 20 A / J and 20 C57L / J mice, ii) 63 A / J and 59 C57L / J mice b) Reproductive toxicity: ten 10-12-weeks old previously-mated A / J females a) Renal toxicity: i) 55 mice, ii) 55 mice and iii) 60 mice |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | a) Hematologic, b) reproductive and c) renal toxicity study, (subacute and subchronic toxicity; oral exposure) A) Test substances: i. ClO2 and ii: NaClO2 i: ClO2: each group was divided into two subgroups of 10 mice exposed to 0 ppm and 100 ppm in drinking water (for 30 days). ii: NaClO2: each group was divided into four subgroups exposed to 0, 1, 10 and 100 ppm in drinking water (for 30 days) B) Females were randomly assigned to either a control (distilled water) or a treatment group (100 ppm NaClO2) C) Each group was divided into 5 dose-response subgroups (100 ppm NaCl control, and 0 ppm, 4 ppm, 20 ppm and 100 ppm NaClO2). Groups were exposed for different time periods (i) 30 days, (ii) 90 days, and iii) 180 days). |
| CONTROL Control group | Negative control: drinking water without the test substance. Positive control: 100 ppm of NaCl as a high salt control for the renal effects control group. |
| Measurements | Changes in body weight, water volume consumption per day, 11 hematological parameters, G6PD activity, glutathione assay, effect on conception rate and litters of A/J strain mice (growth rate, mortality and development), effects on kidney structure. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | No hematologic, conception or kidney structure changes were observed in mice exposed to ClO2. NaClO2 did not cause kidney structure changes at 100 ppm for up to 120 days; but there was increased osmotic fragility of RBC, mean corpuscular volume and G6PD activity. A / J mice showed decreased conception rate, weight of pups and a lower average growth rate due to NaClO2. |
Suh DH et al., 198319 | |
| POPULATION Animal data | Sprague-Dawley female rats (weight 150-170 g) and their fetuses exposed in utero. Pregnant rats: 6 control; 21 ClO2; 17 ClO2-; 18 ClO3-. Litters examined: 6 control; 20 ClO2; 16 ClO2-; 17 ClO3-. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Developmental and reproductive toxicity study (oral and in utero exposure). Test substances: ClO2 and its metabolites ClO2- and ClO3- Daily doses: 0, 1, 10 and 100 ppm (ClO2); 1 and 10 ppm (ClO2- and ClO3-) in drinking water for 2.5 months prior to and throughout gestation. Females were bred with untreated males. |
| CONTROL Control group | Negative control: drinking water without the test substance. 50% of the total population in each group was assigned to intervention group (bred and pregnant) and 50% was assigned to control group (bred and pregnant). |
| Measurements | Pregnant dams, weight gain, number of implants, live fetuses, resorption's, dead fetuses, fetal body weight and length, skeletal & visceral anomalies parameters in fetuses |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | None of the test substances exhibited apparent maternal toxicity. Decreases in the numbers of implants and live fetuses per dam were observed with ClO2 treatment (100 ppm). Fetal weight was significantly increased as well. The presentation of incompletely ossified interparietal bone was also increased (10 and 100 ppm ClO2 doses). Fetal length was increased (10 ppm ClO2- and ClO3- groups). Few cases of hypoplastic kidney, hydronephrosis and dextrocardia were observed. |
Moore, GS et al., 198420 | |
| POPULATION Animal data | Sprague-Dawley rats, 85 males, 6-weeks old. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Renal toxicity study (subchronic toxicity; oral exposure). Test substance: NaClO2 Doses: 31.2, 125 and 500 ppm for periods of 30, 90 and 180 days (15 animals per dose group). |
| CONTROL Control group | Negative control (15 rats): drinking water without NaClO2.Positive control (5): a single dose of 1.5 mg / kg mercuric chloride. Sodium control (20): 500 ppm of NaCl in drinking water. |
| Measurements | Water consumption, mortality, renal microscopy, urinalysis, body weight change, kidney weight, and percent kidney to body weight ratio. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | No evidence of kidney damage was observed after NaClO2 administration (31.2 ppm - 500 ppm) which is higher than that present in water treatment systems (< 5 ppm). |
Meier JR. et al., 198521 | |
| POPULATION Animal data | Micronucleus assay: 5 male and 5 female Swiss CD-I mice (8-11-weeks old) per treatment group. Bone Marrow Aberration Assay: 4 male and 4 female Swiss CD-I mice (8-11-weeks old) per treatment group. Sperm-head Abnormality Assay: 10 hybrid B6C 3F1 male mice (8-11-weeks old) per treatment group. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Genotoxicity study (acute and subchronic toxicity; oral exposure). Test substances: Chlorine at pH 6.5 (OCl- << HOCl) and 8.5 (OCl- >> HOCl) and NH2Cl solutions: 40, 100 and 200 ppm in chlorine equivalents. ClO2 solutions: 400, 200 and 100 ppm Cl equivalents in distilled H20. NaClO2 and NaClO3 solutions: 200, 500 and 1000 ppm. Animals were dosed by oral gavage with 1 ml of test solution on a subchronic regimen (five daily administrations; 24 hr apart). |
| CONTROL Control group | Negative control: deionized water. Positive control: intraperitoneal triethylenemelamine (1 mg / kg) in 0.9% SS for micronucleus and bone marrow aberration assays; intraperitoneal 200 mg / kg ethyl methanesulfonate in deionized water for sperm-head abnormality assay. |
| Measurements | Induction of chromosomal aberrations and micronuclei in bone marrow of CD-1 mice and induction of spermhead abnormalities in B6C 3F1 mice. Formation of halogenated acetonitriles was also tested. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | OCl- (main component of chlorine) in normal drinking water pH may represent a mutagenic hazard based on the sperm-head abnormalities observations at 3 weeks following treatment at dose levels equivalent to approximately 4 and 8 mg / kg / day (the estimated adult human exposure dose would be approx. 0.03 to 0.06 mg / kg / day). Other disinfectants and haloacetonitriles tested did not exhibit evidence of genetic toxicity effects. |
Orme J. et al., 198522 | |
| POPULATION Animal data | Spraque-Dawley female rats (60-days old); 103 litters born to exposed and unexposed groups. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Reproductive and thyroid toxicity study (oral and in utero exposure). Test substance: ClO2 in drinking water Doses for pups born to unexposed dams: 14 mg / kg / day (age: 5 to 20 days postpartum). Doses for females: 2, 20 and 100 ppm (2 weeks prior to mating until pups weaning at 21 days of age). |
| CONTROL Control group | Negative control: distilled water. Positive control: propylthiouracil (PTU) at 5 mg / L in drinking water. |
| Measurements | Behavioral (locomotor activity of the pups) and thyroid function in dam and pup serum (T3 and T4 levels). |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | A highly significant correlation was found between locomotor activity and T4 levels in gavaged pups, which showed a significant T4 depression. Neonatal thyroid function showed to be more sensitive to the antithyroid effects of ClO2 and PTU in the indirectly exposed pups. The T4 levels of the 21-days old pups was significantly depressed in the 100-ppm ClO2 group. |
Harrington, RM et al., 198623 | |
| POPULATION Animal data | Six African green adult female monkeys (weight 3.2-5.5 kg). 36 male Sprague-Dawley rats (∼2 months old; weight 200-250 g); 12 animals per dose group. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Thyroid toxicity study (subchronic toxicity; oral exposure). Test substance: ClO2, in drinking water for 8 weeks. Monkey dose: 100 ppm ClO2 (two equal experiments separated by a period of one year). Rat doses: 0, 100 and 200 ppm ClO2. |
| CONTROL Control group | Negative control monkeys: no 0 ppm ClO2 group; the same monkeys from the preliminary experiment were used as a control for the same experiment one year later. Negative control, rats (12 animals): drinking water without ClO2. |
| Measurements | Measurements (at 0, 4 and 8 weeks of treatment): in rats: T4 levels, radioactive iodine uptake, body weight. In monkeys: T4 levels, radioactive iodine uptake, serum estradiol. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | In both species ClO2 had an effect on thyroid parameters. In monkeys: decrease in T4 levels after 4-week exposure; after 8 week of treatment T4 levels rebounded to pretreatment levels and thyroid radioiodide uptake increased. In rats: dose-dependent decrease in T4 levels during the 8-week treatment period and no rebound effect observed; iodide uptake was not affected. |
Hayashi M. et al., 198824 | |
| POPULATION Animal data | Eight-week-old ddY mice; 108 males. 1000 polychromatic erythrocytes per mouse. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Genotoxicity study, in vivo micronucleus test (intraperitoneal and oral exposure) Test substances: ClO2, NaClO2, NaClO and 44 other chemicals Intraperitoneal doses: 3.2, 6.3, 12.5 and 25 mg / kg ClO2; 7.5, 15, 30 and 60 mg / kg NaClO2; and, 312.5, 625, 1250 and 2500 mg / kg of NaClO, in one injection. Oral doses: 37.5, 75, 150 and 300 mg / kg of NaClO2. |
| CONTROL Control group | Negative control (6 mice): SS or water. Positive control (6 mice): 2 mg / kg intraperitoneal mitomycin C, one dose only. |
| Measurements | Number of micronucleated polychromatic erythrocytes (observed through a high-power objective microscope), proportion among total erythrocytes. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | ClO2 (from 3.2 to 12.5 mg / kg) and NaClO2 (from 7.5 to 30 mg / kg) induced micronuclei in the bone marrow erythrocytes after a single intraperitoneal injection. Both substances could be potential genotoxins. |
Toth GP et al., 199025 | |
| POPULATION Animal data | Virgin female Long-Evans hooded rats and their 937 male and female pups. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Thyroid and neurodevelopmental toxicity study (subacute toxicity; oral exposure- intubation). Test substance: ClO2. Pups: 14 mg / kg / day of ClO2 (postnatal day 1 to 20). |
| CONTROL Control group | Positive control: propylthiouracil (PTU) 20 mg / kg / day (postnatal day 1-20). Negative control: distilled water (postnatal day 1-20). |
| Measurements | Olfactory bulbs, cerebellum, forebrain and liver were analyzed at birth. General parameters of maturation were measured. T4 and T3 levels, and T3 uptake were measured as well as the hepatic mitochondrial a-glycerophosphate dehydrogenase (a-GPD) activity. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | Decreases in body weight and dendritic spine counts (specific area of the cerebral cortex) were observed in ClO2-treated rats. Reductions in forebrain weight, protein content and cell proliferation were indicative of neurotoxic lesions in the developing forebrain following direct postnatal ClO2 exposure. Serum thyroid hormone levels were unchanged relative to controls. |
Carlton, BD et al., 199126 | |
| POPULATION Animal data | Twelve male and 24 female Long-Evans rats (4-6 weeks of age) per dose group. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Hematologic, thyroid and reproductive and developmental toxicity study (subchronic toxicity; oral exposure). Test substance: ClO2, administered by gavage in deionized water. ClO2 doses (once per day): 0, 2.5, 5, or 10 mg / kg (10 ml / kg). Males: 7 days per week for 56 days prior to breeding and throughout the 10-day breeding period. Females: 14 days prior to breeding; and throughout breeding, gestation, and lactation to weaning of the F1 offspring on lactation day 21. |
| CONTROL Control group | Negative control (36 F0 animals): deionized water without ClO2. |
| Measurements | Complete blood count, thyroid hormone levels, complete gross necropsy, histopathology of reproductive tract; sperm motility and velocity; fertility, length of gestation, body weight gain, maternal behavior; for litters, viability, size, day of eye opening, weight, abnormalities, hormones. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | No presence of adverse effects or clinical signs of reproductive toxicity in parental animals. Parameters remained unaltered in litters. Vaginal weight in female weanlings was significantly decreased in the high dose group (10 mg / kg) relative to controls. Observed changes in thyroid hormone parameters were not attributable to ClO2 treatment. |
Harrington, RM et al., 199527 | |
| POPULATION Animal data | Male and female Crl: CD (SD) BR rats (∼4 weeks old). 50 rats were used for a preliminary 14-day study to calibrate doses and 120 rats were used in the 13-week study. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Toxicity study in all systems (subchronic toxicity; oral exposure). Test substance: NaClO2 Doses: 15 males and 15 females per dose group-10, 25 and 80 mg / kg / day by gavage (for 13 weeks). |
| CONTROL Control group | Negative control (15 males and 15 females): drinking water without NaClO2. |
| Measurements | Complete hematology and blood chemistry evaluations, urinalysis and exhaustive microscopic examinations were performed on more than 40 different tissues. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | In the 14-day preliminary study, mean mHb levels at 100 mg / kg / day were almost twice as high as in the control group. In the 13-week study, mHb levels increased in males with the highest doses, whereas in females mHb concentration was significantly lower at the highest dose level tested. NaClO2 (80 mg / kg / day) induced a decrease in RBC in males and females and a decrease in Hb concentration in males. Morphological changes in erythrocytes were also observed. Splenic extramedullary hematopoiesis and increased spleen weights were present in both sexes. |
Gill MW et al., 200028 | |
| POPULATION Animal data | Thirty male and 30 female OFA (SD) IOPS-Caw Sprague-Dawley rats of the F0 generation (6 weeks old at the prebreed exposure period); 25 males and 25 females of the F1 generation. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Reproductive, hematologic, thyroid and neuro-developmental toxicity study (subchronic toxicity; oral and in utero exposure). Test substance: NaClO2 in drinking water. Doses for F0 and F1 generations: 0, 35, 70 and 300 ppm (10-weeks during the prebreed period, as well as during mating, gestation, parturition and lactation-a 90-day exposure in total). |
| CONTROL Control group | Negative control (F0 generation; 30 of each gender; F1 generation, 25 of each gender): drinking water without NaClO2. |
| Measurements | Body weight, body weight changes, viability and survival indicators, landmarks of pup development and sexual maturation, gross external evaluation. Hematological, thyroid hormone and neurotoxicological evaluations; vision, motor activity, coordination and learning evaluations and gross signs of central and peripheral nervous system dysfunction. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | Decreased water and food consumption and body weight in all the 70 and 300 ppm treatment groups. 300 ppm group: decreased pup body weight, small delays in preputial separation and vaginal opening, mild hemolytic anemia for male and female rats and mild methemoglobinemia. Day-25 pups (70 and 300 ppm NaClO2): changes to the nervous system (small decreases in amplitude of auditory startle response); day-11 pups (300 ppm group): small decrease in absolute brain weight. No evidence of reproductive toxicity. Thyroid hormone levels were not affected by treatment. The study reported a NOEL of 300 ppm of NaClO2 for effects on reproduction and on thyroid toxicity biomarkers, a NOAEL of 70 ppm for hematological toxicity (mild hemolytic anemia and mild methemoglobinemia) and a NOAEL of 300 ppm for neurotoxicity (brain weight and auditory startle response). |
Karrow NA et al., 200129 | |
| POPULATION Animal data | B6C 3F1 mice, 56 females-8 per treatment group-(4–6 weeks old) |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Immunomodulatory effects study (subacute toxicity; oral exposure). Test substance: NaClO2 Doses: 0, 0.1, 1, 5, 15 and 30 ppm in drinking water for 28 days. |
| CONTROL Control group | Negative control: drinking water without NaClO2. Positive control: 50 mg / kg intraperitoneal cyclophosphamide, on days 25-28. |
| Measurements | Water consumption, body and organ weights, hematological parameters; spleen T cell, B cell, NK cell, and macrophage enumeration; spleen IgM antibody response and ELISA serum IgM antibody titers to sheep erythrocytes; spleen cell mixed leukocyte response to stimulator DBA / 2 spleen cells; peritoneal macrophage activation assay; basal and augmented natural killer cell activity in the spleen |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | With the exception of a slight increase in the percentage of reticulocytes in the 15 ppm NaClO2 treatment group, hematological changes were not observed. Overall, NaClO2 in drinking water produced minimal immunotoxic effects in mice and does not appear to significantly alter cellular, humoral and innate immune responses. Mice tolerated doses ranging from 0.1 to 30 ppm / day without any adverse effects. |
Zambrano, X et al., 202030 | |
| POPULATION Animal data | Thirty SPF RossxRoss chick embryos (10-day old)-5 embryos per experimental group-inoculated with avian infectious bronchitis coronavirus. |
| INTERVENTION Study type (administration route) Test substances, exposure, and doses | Efficacy study, in vivo assessment of the antiviral effect (inoculation into the allantoic cavity). Test substance: ClO2 Doses: 30 and 300 ppm (in sterile 0.9% SS). Six experimental groups: 1) experimental control; 2) 30 ppm ClO2; 3) 300 ppm ClO2; 4) resuspended avian coronavirus vaccine and 30 ppm ClO2; 5) resuspended avian coronavirus vaccine and 300 ppm ClO2; 6) resuspended live attenuated avian coronavirus vaccine and sterile 0.9% SS. |
| CONTROL Control group | Negative control: sterile 0.9% SS. |
| Measurements | Macroscopic body lesions typically caused by avian coronavirus (cutaneous bleeding, stunting, curving, urate deposits in the kidney and feather alterations); mortality markers. |
| OUTCOMES Most significant findings based on efficacy / toxicity parameters measured | Viral titres were 2.4-fold lower and mortality was reduced by half in infected embryos that were treated with ClO2. Lesions typical of avian coronavirus infections were observed in all inoculated embryos, but severity tended to be significantly lower in ClO2-treated embryos. No gross or microscopic evidence of toxicity caused by ClO2 was observed. |
| ClO2: chlorine dioxide; ClO2-: chlorite; ClO3-: chlorate; G6PD: glucose-6-phosphate dehydrogenase; Hb: hemoglobin; HOCl: hypochlorous acid; IU: international units; NaClO: sodium hypochlorite; NaClO2: sodium chlorite; NaClO3: sodium chlorate; NH2Cl: monochloramine; OCl-: hypochlorite; mHb: methemoglobin; NOAEL: no-observable-adverse-effect-level; NOEL: no-observable-effect-level; RBC: red blood cell count; SS: saline solution; T3: triiodothyronine; T4: thyroxine. | |
Seven studies assessed reproductive and developmental toxicity; six studies investigated toxic effects on thyroid function; four studies evaluated hematologic biomarkers of toxicity, and one studied genotoxicity (n=2), nephrotoxicity (n=2), and immunotoxicity (n=1). Harrington et al.27 ran the most comprehensive study (1995) where practically all organs, systems, and tissues were examined after testing oral exposure to NaClO2 in a rat model.
Regarding ClO2, only Moore et al. 198218 found no effects on the reproduction or development of mice, while other studies found a wide range of abnormalities at different concentrations (Table 1). Sodium chlorite also demonstrated detrimental effects in mice by decreasing the conception rate and affecting pups' weight and growth rate.
Chlorine dioxide affected the thyroid function at different doses in rats and monkeys in studies published in the 80s. Nevertheless, studies in rats and mice in the early 90s and 2000s did not replicate these findings for ClO2 or NaClO2.
Hematological toxic effects were not observed in monkeys, mice, or rats exposed to ClO2. Nonetheless, other studies in mice and monkeys reported that NaClO2 did derive in hematological alterations. Only Gill et al.28 formally reported a "no observable effect level" (NOEL) of NaClO2 regarding the effects on reproduction and thyroid toxicity biomarkers and a "no observed adverse effect level" (NOAEL) for hematological and neurotoxicity.
Chlorine dioxide and NaClO2 were found to be potential genotoxins; however, they were not identified as a cause of nephrotoxicity in mice or rats. In addition, slight immunotoxic effects were observed after exposure to NaClO2, and only OCl-, one of the byproducts of chlorine at normal drinking water pH, showed to be a potential mutagenic chemical. No studies investigated immunotoxicity caused by ClO2.
Solely one pre-clinical efficacy study was found and included in our scoping review. Zambrano-Estrada et al.30 infected 30 chick embryos with avian coronavirus. After treating them with ClO2, they observed lower viral titers, decreased mortality, and significantly less severe lesions without evidence of ClO2 toxicity.
After assessing the selected study-quality items, most studies showed satisfactory quality (Suppl Table 2). Population size and outcome reporting were described by most, but not all of the studies; others did not inform drop-outs, deviations from the protocol, or how they were handled. Regarding the risk of bias, 7 out of 15 studies did not specify animal allocation and randomization. Moreover, the blinding of study personnel and outcome assessors were not stated in any studies.
Case Reports
The review identified 13 case reports in humans (Table 2). Most of them (85%) were published between 2012 and 2020, involving seven men, four women, and three children. Four reports were related to a ClO2 product exposure, nine referred to a NaClO2 exposure, and one referred to both. At least six reports identified the ingestion of a commercially-developed product. Oral exposure was the most frequent one (77%); other exposures included inhalation, topical exposure, and oral exposure in combination with intravenous administration.
Most of the exposures to these substances were intentional (69.2%). In some cases, different concentrations, presentations, and dilutions of NaClO2 and ClO2 (Table 2) were used/consumed to treat diseases such as prostate cancer, a cutaneous fungal infection, gastroenteritis in a patient with idiopathic thrombocytopenic purpura, hypertension with concomitant COVID-19, or for unspecified reasons.
Specifically, in the context of COVID-19, there was a fatal case due to the intentional ingestion of complementary therapy (ClO2 solution with intravenous saline solution and NaClO2). Likewise, during the pandemic, two 8- and 9-year-old siblings accidentally ingested an undiluted sodium chlorite solution; the youngest had mild symptoms, but the oldest suffered severe poisoning that kept him hospitalized for several weeks until he recovered.
Adverse events were reported in five out of seven voluntary consumption cases; three of seven experienced toxic effects due to an erroneous dosage consumption.
Additionally, there were six accidental exposures and two suicide attempts. Only in 5 out of 13 cases was possible to know or estimate the amount of ClO2 or NaClO2 the patients consumed. In such cases, it was evident that the doses were much higher than permissible or recommended by the manufacturers of the products.
Overall, all case reports showed good methodological quality after critical appraisal using the corresponding JBI checklist (Supp. Table 3-A); almost two-thirds (62%) of them reached the highest possible score.
| Tabla 2. Case reports on the toxicological outcomes of chlorine dioxide consumption in humans | |
|---|---|
Exner-Freisfeld et al., 1986 (Germany)31 | |
| Individuals involved | 49-year-old woman |
| Exposure context and formulation (compound or metabolite) | Accidental inhalation when generating chlorine dioxide (ClO2) gas from a bleach solution preparation mix sodium chlorite (NaClO2) to bleach dry flowers. Presumably, ClO2 gas concentration in the room was > 0.1 ppm |
| Toxic or adverse effects reported | Main system / organ affected: lungs, cough, throat irritation, headache, tachypnea, tachycardia, rales, marked leukocytosis, hypoxemia, decreased vital capacity and forced expiratory volume. Two months after: pulmonary function values were normalized; mild coughing and shortness of breath continue occasionally. |
| Treatment, monitoring & resolution | Corticosteroids and ipratropium bromide with fenoterol resulted in significant relief of symptoms and improved lung function with stabilization to a normal range, as confirmed by follow-up examination two years later. |
| Mechanism (hypothesis behind toxicity) | The exposure referred to by the patient was reproduced in a chemical laboratory (2.5 liters of 15% NaClO2 with 250 mL of 50% HCOOH and 20 L of boiling water in a 16 m2 room). Authors concluded that poisonous ClO2 gas can be generated at high concentrations (greater than the permissible exposure limits in workplaces (> 0.3 mg / m3) even with open doors and windows. |
Lin et al., 1993 (Taiwan)32 | |
| Individuals involved | 25-year-old man |
| Exposure context and formulation (compound or metabolite) | Suicide attempt (poisoning): oral ingestion of 10g NaClO2 dissolved in 100 mL of water |
| Toxic or adverse effects reported | Main system / organ affected: blood, renal and gastro-intestinal systems. Methemoglobinemia (59%), generalized cyanosis, abdominal cramps, nausea, vomiting, irritability, confusion, respiratory failure, hemolysis, disseminated intravascular coagulation. Several days later: cardiac arrest, septicemia, acute renal failure and fluid overload. |
| Treatment, monitoring & resolution | Hyperbaric oxygen therapy, IV methylene blue (250 mg), continuous arteriovenous hemofiltration to remove chlorite, antibiotics, hemodialysis, steroids. The patient reached recovery and was discharged about 2 months after admission. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that the patient´s acute reversible interstitial nephritis could be potentially attributed to NaClO2 poisoning and emphasized the importance of early management. |
Romanovsky, et al., 2013 (Canada)33 | |
| Individuals involved | 65-year-old man |
| Exposure context and formulation (compound or metabolite) | Accidental oral ingestion of a mouthful of 28% NaClO2 (the solution was previously diluted in a cup with an unmeasured amount of water), while using the solution as a fruit disinfectant |
| Toxic or adverse effects reported | Main system / organ affected: blood and renal systems. G6PD inhibition and severe oxidative hemolysis despite mild methemoglobinemia. Disseminated intravascular coagulation and anuric acute kidney injury; nausea, vomiting, diarrhea and hematuria; gastric upset, lactic acidosis and hypotension. |
| Treatment, monitoring & resolution | Hemodialysis, hemofiltration, high-dose N-acetylcysteine infusion, IV fluid resuscitation, norepinephrine 10 mcg / min, RBC and plasma infusions. The patient reached recovery and was discharged 17 days after admission to hospital; two months follow-up showed recovered normal renal function. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that in the absence of severe methemoglobinemia, the patient’s acute kidney injury was likely due to a combination of tubular Hb toxicity and renal ischemia (derived from poor oxygen supply). |
Bathina et al., 2013 (India)34 | |
| Individuals involved | 20-year-old man |
| Exposure context and formulation (compound or metabolite) | Oral ingestion of 250 mL of a commercial product called “Stable ClO2 Gold” (ClO2 solution -chlorite, chloride and chlorate- of unknown / not reported concentration) |
| Toxic or adverse effects reported | Main system / organ affected: kidneys. Anuria, blood urea 188 mg / dL, serum creatinine 7.2 mg / dL, urine analysis with bland sediment, and severe renal failure. Renal biopsy showed features suggestive of acute tubular necrosis. Acute kidney injury occurred in the absence of methemoglobinemia, hemolysis and disseminated intravascular coagulation. |
| Treatment, monitoring & resolution | Hemodialysis. The patient reached recovery and was discharged at day 15 after admission. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that acute tubular necrosis remains one of the important causes of reversible acute kidney injury in ClO2 poisoning. |
Burke et al., 2014 (USA)35 | |
| Individuals involved | 75-year-old man |
| Exposure context and formulation (compound or metabolite) | Overdose derived from oral ingestion of 100 drops (recommended dose of 10 drops) of alternative medicine, commercial product, Miracle Mineral Solution (MMS) based on an aqueous solution of 28% NaClO2 that yields chlorine dioxide with the addition of citric acid (ClO2). MMS was purchased online for the treatment of prostate cancer. |
| Toxic or adverse effects reported | Main system affected: blood, exertional dyspnea, malaise, dark urine, hemolytic anemia (self-limited). |
| Treatment, monitoring & resolution | Four units of packed RBC. Normal G6PD levels during the acute hemolytic phase. The patient reached recovery and was discharged four days after hospitalization. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that the patient overdosed because the EPA had set a maximum level of ClO2 to 0.8 mg / L in drinking water; however, a single drop of MMS contains 2-8 mg of ClO2. Authors also concluded that MMS can cause hemolytic anemia in patients with or without G6PD deficiency. |
Gebhardtova et al., 2014 (Slovak Republik)36 | |
| Individuals involved | 55-year-old man |
| Exposure context and formulation (compound or metabolite) | Suicide attempt with oral ingestion of about 100 ml of 28% NaClO2 solution (severe poisoning). Concomitant ingestion of 0.75 L of whiskey and 12 ibuprofen tablets of 400 mg |
| Toxic or adverse effects reported | Main systems / organs affected: blood, renal and gastro-intestinal. Methemoglobinemia (40%), anuric acute renal failure, hemolytic anemia, disseminated intravascular coagulation, hypotension, gastric, esophageal and duodenum ulceration, edema of the pylorus. Days later: bronchopneumonia and sepsis. |
| Treatment, monitoring & resolution | Early antidote therapy with IV methylene blue (0.5 mg / kg) to manage methemoglobinemia prior to hemolysis is recommended for chlorite poisoning management. Patient also received renal replacement therapy to manage acute kidney injury and to remove chlorite from circulation. The patient reached recovery and was discharged from hospital on day 64. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that methemoglobinemia formation is dependent on the amount of chlorite ingested and that chlorite-induced Hb oxidation is dose-dependent. |
Loh et al., 2014 (Singapore)37 | |
| Individuals involved | 41-year-old woman |
| Exposure context and formulation (compound or metabolite) | Intentional oral ingestion of a glassful of MMS- 28% NaClO2 solution- diluted in water, presumably as a preventive treatment (a relative of the patient prepared the solution; therefore, the number of drops applied remained unknown). |
| Toxic or adverse effects reported | Main systems / organs affected: lymph nodes, systemic (inflammatory response). Fever (40°C), left-sided level II, III, IV and V cervical lymphadenopathy with perinodal fat stranding, chills, rigors and dry cough. Diagnosis of Kikuchi-Fujimoto disease (KFD) was made on excisional lymph node biopsy. |
| Treatment, monitoring & resolution | The patient did not show acute signs of chlorite toxicity; therefore, she was initially treated for a presumed upper respiratory tract infection with oral paracetamol and antibiotics. Firstly, the patient was admitted 11 days after onset of symptoms. Authors applied the Naranjo algorithm and obtained a “possible” causality regarding the likelihood of adverse drug reaction. The patient reached recovery. Two weeks-follow-up showed no recurrence of fever. |
| Mechanism (hypothesis behind toxicity) | Authors hypothesized that the exuberant lymphocytic response was the product of an inflammatory cascadecaused by mild local oxidative damage in the oropharyngeal and gastrointestinal mucosa due to chlorite ions. Since KFD is a rare cause of fever and lymphadenopathy of unknown aetiology, authors concluded that morecases need to be reported to determine if MMS is a possible cause of KFD. |
Sorigué et al., 2015 (Spain)38 | |
| Individuals involved | 46-year-old man with idiopathic thrombocytopenic purpura |
| Exposure context and formulation (compound or metabolite) | Intentional oral ingestion of a ClO2 preparation (obtained through the internet), presumably as a treatment for gastroenteritis (ingested volume and concentration were not reported) |
| Toxic or adverse effects reported | Main systems / organs affected: blood systems. Coluria, jaundice, Hb 92 g / L, LDH 1620 U / L, indirect bilirubin 9 mg / dL, haptoglobin 0.07 g / L and direct antiglobulin test positive for IgG y C 3d. Autoimmune hemolytic anemia was diagnosed. |
| Treatment, monitoring & resolution | IV immunoglobulins 1g / kg / day for 2 days, IV prednisone 2 mg / kg / day, packed RBC and urgent splenectomy. Authors applied the Naranjo algorithm and obtained a “possible” causality regarding the likelihood of adverse drug reaction. The patient reached recovery. A 9-month follow-up showed no further symptoms and normal Hb and platelets values. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that the hemolysis presented after the ingestion of the ClO2 preparation support the hypothesis that this substance could have played a role in the development of the hemolytic crisis in this patient with idiopathic thrombocytopenic purpura. |
Hagiwara et al., 2015 (Japan)39 | |
| Individuals involved | 1-year-old boy |
| Exposure context and formulation (compound or metabolite) | Accidental oral ingestion of a small quantity (not estimated / not reported) of a ClO2-based household product containing a gelling agent (chlorite and chlorate ions) |
| Toxic or adverse effects reported | Main systems / organs affected: blood, gastrointestinal and respiratory. Vomiting, poor complexion, 85-88% oxygen saturation, tachypneic, elevated methemoglobinemia (8%). |
| Treatment, monitoring & resolution | Oxygen therapy; patient required endotracheal intubation and mechanical ventilation. The patient reached recovery; discharged from hospital on day 6, no evidence of further damage checked 3 months after the event. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that the clinical features of the patient were consistent with the development of methemoglobinemia caused by the chlorite ions formed from the household product. |
Alcántara et al., 2016 (Spain)40 | |
| Individuals involved | 42-year-old man |
| Exposure context and formulation (compound or metabolite) | Intentional topical application of MMS,- 28% solution of NaClO2 (ClO2)- and citric acid in distilled water was prepared and sprayed on the patient’s trunk. (pH mixture: 2.5-3; conc. NA) on a suspected cutaneous fungal infection |
| Toxic or adverse effects reported | Main systems / organs affected: skin. Lesions on the sprayed area (trunk): diffuse erythema with dusky areas. After histopathologic examination: toxic irritant contact dermatitis (epidermal hyperplasia with hyperkeratosis, apoptotic keratinocytes, fibrosis of papillary dermis). |
| Treatment, monitoring & resolution | Unspecified corticoesteroids for one week. The patient reached recovery and lesions cleared. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that it is important that dermatologists take into consideration that MMS may cause skin lesions. |
Arnold et al., 2018 (USA)41 | |
| Individuals involved | 27-year-old woman |
| Exposure context and formulation (compound or metabolite) | Accidental oral ingestion (poisoning) of approximately 75 mL of MMS-28% NaClO2 mixed in water (ClO2)- Estimated amount of NaClO2 ingested: 21 g (patient’s daughter mixed 2.5 ounces instead of 2 drops of the solution as instructed on the bottle) |
| Toxic or adverse effects reported | Main systems / organs affected: gastrointestinal, systemic, blood. Within minutes: diaphoresis, intractable vomiting. At the hospital: 80% oxygen saturation, methemoglobinemia, decreased hematocrit, hypotension (without the development of significant hemolytic anemia or acute kidney injury) |
| Treatment, monitoring & resolution | Oxygen, intubation, single dose of methylene blue (0.7 mg / kg), vasopressors. The patient reached recovery and was extubated after day two. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that it was possible that the patient ingested less than the reported dose, since there was no presentation of severe hemolysis or renal toxicity. |
Aguilar et al., 2020 (Mexico)42 | |
| Individuals involved | 58-year-old woman; hypertensive for 15 years; 14-days history of confirmed COVID-19 disease- treated at home with only 1 day of emergency room stay. |
| Exposure context and formulation (compound or metabolite) | Intentional oral ingestion of 1000 mL of ClO2 solution plus intravenous administration of 500 mL of 0.9% SS with 28% NaClO2 (chlorite, chloride, chlorate). |
| Toxic or adverse effects reported | Main systems / organs affected: respiratory, cardiovascular, hepatic, renal. Sudden respiratory deterioration, decreasing oxygen saturation up to 60%, uncontrolled hypertension, tachypnea, tachycardia, excoriations of the lips, diffuse bilateral rales with dullness to percussion, hippocratic fingers. Hours later: fluid-refractory hypotension, bilateral diffuse alveolar pattern (secondary chemical pneumonitis), acute liver failure findings, leukocytosis, acute kidney injury AKIN III, death. |
| Treatment, monitoring & resolution | Mechanical ventilation, sedation, norepinephrine, anticoagulation, broad spectrum antibiotic, hydrocortisone 50 mg IV every 6 hours. Patient died 5 days after the ingestion of ClO2. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that patient’s respiratory failure was secondary to oral and intravenous use of ClO2, leading to multiple organ failure and death. |
Zhen et al., 2021(USA)43 | |
| Individuals involved | 9-year-old boy and his 8-year-old brother |
| Exposure context and formulation (compound or metabolite) | Accidental oral ingestion of a small volume of undiluted MMS (22.4% NaClO2) by two siblings simultaneously (pediatric age) |
| Toxic or adverse effects reported | Main systems / organs affected: gastrointestinal, blood, respiratory, renal. Methemoglobinemia, renal failure and hemolytic anemia. Both siblings, immediately: nausea, vomiting, dyspnea. 9-year-old boy: cyanotic, 71% oxygen saturation, cyanosis, minimal urine output; subsequent oliguric acute renal failure, hemolytic anemia, mild thrombocytopenia, hypercoagulability. 8-year-old boy: frequent emesis and loose stools, 4.7% methemoglobinemia. |
| Treatment, monitoring & resolution | Treatments (9-year-old): intubation, methylene blue (1 mg / kg IV), hemodialysis, renal replacement therapy, packed RBC, erythropoietin, platelets, anticoagulants. The patient reached recovery and was discharged some weeks later (not specified). Treatments (8-year-old): not reported. Patient reached recovery and was discharged on day 2 after admission. |
| Mechanism (hypothesis behind toxicity) | Authors concluded that these were the second and third reported cases of NaClO2’s toxicity by ingestion in children. Because of COVID-19 pandemic, MMS was sold as a natural cure posing people at risk of life-threatening consequences. |
| AKI: acute kidney injury; AKIN III: Acute Kidney Injury Network classification-stage III; ClO2: chlorine dioxide; EPA: Environmental Protection Agency; G6PD: glucose-6-phosphate dehydrogenase; Hb: hemoglobin; HCCOH: formic acid; IV: intravenous; KFD: Kikuchi Fujimoto disease; LDH: lactate dehydrogenase; mHb: methemoglobin; MMS: Miracle Mineral Solution; NA: not available; NaClO2: sodium chlorite; RBC: red blood cell; NaClO2: sodium chlorite; SS: saline solution | |
Clinical Studies
The review identified six clinical studies: one case series, two case controls, one quasi-experimental study, and two RCTs (Table 3).
Four studies employed topical administration of ClO2, and only two referred to systemic administration.
Regarding topical treatment, the case series consisted of a descriptive study on female patients with keratosis pilaris who were given a ClO2-based commercial foam cleanser. This study scored very low in terms of quality and reliability of the validity of its results (Suppl. Table 3). No control group was included, and the total duration of treatment for each patient was not clearly explained.
Likewise, unstandardized reports of variability in size and resolution time of the corporal papules were employed as confirmation of some patients who showed improvements.
Furthermore, inclusion/exclusion criteria, patient demographics, validated methods for diagnosing the condition and assessing outcomes, and information about the consecutive and complete inclusion of participants were missing or not clearly stated.
| Tabla 3. Clinical studies concerning the outcome of efficacy & tolerability of chlorine dioxide | |
|---|---|
Lubbers et al. 1982 (USA)44 | |
| Type of study design | Case-control study, three-phase tolerability study |
| Participants | Phases I and II: 60 adult male volunteers each (21-35 years old, ±10% of normal body weight). Phase III: 3 G6PD-deficient subjects (otherwise healthy; similar characteristics as Phases I and II individuals) |
| Intervention (formulation and administration dose) | Phases I and II: ten people randomly assigned to orally receive each of the 5 disinfectants (freshly prepared stock solutions of 1) chlorine dioxide (ClO2), 2) sodium chlorite (NaClO2), 3) sodium chlorate, 4) chlorine, and 5) chloramine; all diluted with demineralized deionized water to variable concentrations: 0.01-24 mg / L) and the control untreated water. Phase I: the solutions were administered in a series of six sequences of three days each, with disinfectant concentration increasing for each treatment (for each concentration, two daily portions of 500 mL each administered at 4-hr intervals, at days 1, 4, 7, 10, 13 and 16.). Phases II and III: daily oral administration of 500 mL of solutions (5 mg / L for Phases II and III) to each volunteer for 12 weeks. Phase III: the three subjects received 5 mg / L NaClO2 solution. |
| Objective of the study | To assess the relative safety of chronically administered chlorine water disinfectants in man. |
| Results | For some biochemical parameters (BUN, creatinine, uric acid, total bilirubin, mHb, free thyroxine index and others), statistical analyses indicated a high probability of change which could be attributed to ingestion of a specific disinfectant, but none were judged to have immediate physiological consequences. |
| Conclusions | Authors concluded that oral ingestion of ClO2 and its metabolites, chlorite and chlorate, demonstrated relative safety. They also stated that it is not possible to rule out that, over a longer treatment period, some biochemical of physiological parameters could show alterations of clinical relevance. |
Paraskevas et al., 2008 (The Netherlands)45 | |
| Type of study design | Examiner-masked, two-groups parallel experiment of compared efficacy |
| Participants | 77 healthy subjects (43 females and 34 males), 18-48 years old |
| Intervention (formulation and administration dose) | Subjects were randomly assigned to the test or control group. Experimental period was of 3 days of non-brushing where the test group used ClO2 mouthrinse (Quist-forte containing 100-ppm free ClO2; for activation: 5 mL base solution + 5 mL activator solution) and the control group used chlorhexidine mouthrinse (Corsodyl -0.20% chlorhexidine digluconate). Topical (mouthrinse) was employed twice a day, morning and evening (10 mL solution for 60 seconds), after which they expectorated. After 3 days subjects’ plaque was assessed. |
| Objective of the study | To investigate the inhibiting effect of a ClO2 mouthrinse versus a chlorhexidine-based mouthrinse during three days of plaque accumulation. |
| Results | There was a significant difference in plaque levels between the two groups (taking into account different jaws, surfaces and tooth types). ClO2 showed a less potent plaque inhibition than chlorhexidine. |
| Conclusions | Authors concluded that chlorhexidine was significantly more effective in reducing plaque in the mouth compared to the ClO2 mouthrinse, but subjects preferred the taste of ClO2 and experienced less taste alterations compared to chlorhexidine. |
Shinada et al., 2008 (Japan)46 | |
| Type of study design | Randomized, double-blind, crossover, placebo-controlled clinical trial; exploratory study on efficacy. |
| Participants | 15 healthy male volunteers, 19-38 years old; test group: 8 subjects; control group: 7 subjects. |
| Intervention (formulation and administration dose) | Participants were instructed to rinse with 10 mL of the corresponding mouthwash for 30 seconds (topical administration); the test group used a mouthwash containing 0.16% NaClO2 (with an efficacy of 0.1% ClO2), glycerin, mint oil, 1.13% citric acid and distilled water, while the control group used a placebo consisting in: glycerin, mint oil, distilled water. After one-week washout period, each subject rinsed in the same way with the opposite mouthwash. |
| Objective of the study | To assess the effects of a mouthwash containing ClO2 on morning oral odor using organoleptic measurements and gas chromatography analysis of volatile sulphur compounds. |
| Results | The mouthwash containing ClO2 improved morning bad breath based on organoleptic measurements and on the reduced concentrations of volatile sulphur compounds (hydrogen sulphide, methyl mercaptan, dimethyl sulphide) in mouth air for up to 4 hours after mouth rinsing. * No measurable side effects reported |
| Conclusions | Authors concluded that future studies are needed to examine long-term effects of the mouthwash in halitosis patients. |
Shinada et al., 2010 (Japan)47 | |
| Type of study design | Efficacy randomized, double-blind, crossover, placebo-controlled clinical trial. |
| Participants | 15 healthy male volunteers, 19-38 years old; test group: 8 subjects; control group: 7 subjects. |
| Intervention (formulation and administration dose) | Participants were instructed to rinse with 10 mL of the corresponding mouthwash for 30 seconds (topical administration) twice per day (after waking and before sleeping) for 7 days (topical administration); the test group used a mouthwash containing 0.16% NaClO2 (with an efficacy of 0.1% ClO2), glycerin, mint oil, 1.13% citric acid and distilled water, while the control group used a placebo consisting in: glycerin, mint oil, distilled water. After oneweek washout period, each subject rinsed in the same way with the opposite mouthwash. |
| Objective of the study | To assess the inhibitory effects of a mouthwash containing ClO2 on morning oral malodor and on salivary periodontal and malodorous bacteria. |
| Results | The mouthwash containing ClO2 improved morning bad breath based on organoleptic measurements and on the reduced concentrations of volatile sulphur compounds (hydrogen sulphide, methyl mercaptan, dimethyl sulphide) measured by gas chromatography in mouth air. Also, plaque accumulation, tongue coating index and the counts of Fusobacterium nucleatum in saliva showed a significant inhibition. No measurable side effects reported. |
| Conclusions | Authors concluded that future studies should examine more long-term effects of the mouthwash in halitosis patients as well as effects on periodontal diseases and plaque accumulation in broader population samples. |
Zirwas et al. 2018 (USA)48 | |
| Type of study design | Case series (efficacy determination) |
| Participants | 5 female participants of 11, 12, 13, 20 and 28 years of age with keratosis pilaris in anterior thighs, cheeks, posterior arms, cheeks and posterior arms, respectively. |
| Intervention (formulation and administration dose) | All patients used the foam facial cleanser (topical administration of Aseptic MD, a ClO2 complex wash developed by Frontier Pharmaceutical) and were instructed to wash once a day, gently rubbing the affected area for 5 to 10 seconds with a soft cotton cloth (estimated dose was not reported) |
| Objective of the study | To report a case series demonstrating the efficacy of a complexed form of ClO2 as a cleanser in keratosis pilaris. |
| Results | Papules resolved 90-100% in 2 days to 1 month with minimal effect on erythema. Rapid, nearly complete resolution of keratosis pilaris in the reported patients. |
| Conclusions | Authors concluded that ClO2’s rapid keratolytic activity stems from its reaction with cysteine residues in keratin and with disulfide bonds between and within keratin chains. |
Insignares-Carrione et al., 2021 (Switzerland)12 | |
| Type of study design | A phase IIa study, multicenter quasi-experimental clinical trial in various countries from Central and South America |
| Participants | 40 patients (23 male and 17 females; 36-72 years of age) with active infection with COVID-19 (RT-PCR positive). Test group: 20 patients; control group: 20 patients |
| Intervention (formulation and administration dose) | Test group (initial protocol): oral ingestion, 10 mL of 3000 ppm ClO2 (base preparation produced by electrolysis with an ultrapure ClO2 generating equipment and standardized components) added to 1 L of water; this was taken within 2 hrs divided into 8 equal doses (30 mg per day for 21 days); this group voluntarily decided not to receive medications. The maintenance protocol consisted in 10 mL ClO2 3000 ppm added to 1 L of water, which was taken divided into 10 equal doses during the day, every hour. Control group: ibuprofen (200-400 mg every 8 hr), azythromycin (500 mg daily for 5 days), hydroxyzine (5 mg every 12 hr), methylprednisolone (40 mg every 12 hr for 3 days, then 20 mg every 12 hr for 3 days) and supportive measures. Patients received the supplies and written instructions to prepare their ClO2 solution at home. |
| Objective of the study | To determine the effectiveness of oral ClO2 in the treatment of COVID-19. |
| Results | On the seventh day post symptom manifestation, all test patients presented a negative RT-PCR. Also, a significant difference was found in the test group regarding fever, cough, chills, dyspnea, pain, platelets, PC reactive, LDH, AST, D-dymer, lactate; at day 14 all the biochemical parameters decreased significantly in the test group with respect to the control group. Baseline severity of the COVID-19 disease and viral load was not reported. Though measured, results of the measurement of oxygenation were not reported. 2 patients reported a self-limited light gastritis 7 days after treatment. |
| Conclusions | Authors concluded that their research validated the effectiveness of ClO2 in COVID-19 and recommend conducting further double-blind studies. |
| AST: aspartate aminotransferase; BUN: blood urea nitrogen; ClO2: chlorine dioxide; G6PD: glucose-6-phosphate dehydrogenase; LDH: lactate dehydrogenase; mHb: methemoglobin; NA: not available; NaClO2: sodium chlorite; RBC: red blood cell. | |
Regarding topical treatment, two RCTs conducted by the same research team and reporting outcomes for the same group of 15 male volunteers aimed to assess the efficacy of rinsing with a mouthwash based on ClO2 (single dose) in order to inhibit morning oral malodor (halitosis). The 7-day trial study also measured the effect of mouthwash on plaque accumulation and in other biomarkers of periodontal diseases; both showed significant improvements.
The two RCTs obtained the highest score in terms of methodological quality and analysis of the risk of bias according to the corresponding JBI checklist.
Paraskevas et al. 200845 also evaluated a ClO2 mouth rinse product in the form of a case-control study with 77 subjects. They concluded that it could reduce plaque accumulation; however, it was less effective than a chlorhexidine-based control product.
Lubbers et al. 198244 conducted a case-control study of acute and subchronic toxicity in a total of 123 male volunteers to assess tolerability to ClO2 and four other disinfectants diluted in water for oral ingestion.
Several biochemical parameters showed changes possibly related to the ingestion of one of the disinfectants in the different phases of the study. Still, in general terms, no physiologically relevant alterations were observed in any of the study phases. The authors emphasized the need for further studies assessing extended treatment periods and broader group sizes.
The two case-control studies included in our review also obtained the highest score after evaluating them with the corresponding JBI checklist.
Finally, the most recent quasi-experimental efficacy study by Insignares-Carrione et al.12 sought to demonstrate the effectiveness of oral ingestion of ClO2 in the complementary management of 40 patients with COVID-19; twenty of them decided to ingest the self-prepared experimental treatment in comparison with other 20 control patients who disagreed.
The study groups had different follow-up periods and displayed unclear or unspecified inclusion/exclusion criteria.
Specific outcomes were assessed through laboratory tests (Table 3) and subjective scales such as the Likert and visual analog scales.
Patient oxygenation levels were missing despite the authors stating that they did measure them.
The authors concluded that ClO2 effectively managed COVID-19 without relevant adverse effects and that future double-blind studies were required. According to the JBI checklist for quasi-experimental studies, this study had a moderate methodological design quality and risk of bias.
A total of 34 toxicological and clinical efficacy studies on the use of ClO2 and related compounds as treatment in animals and humans were identified. Almost half of the studies (47%) were more than 20 years old. Most human studies were toxicity case reports (68%), and only 6 were clinical studies. Regarding methodological quality and risk of bias, 56% (19 out of 34 studies) of the total animal and human studies displayed good quality (upper quintile). In contrast, the others did not comply with the quality elements considered necessary in each type of study.
Toxicological Evidence on Animals Should Be Noted
Chlorine dioxide and NaClO2 were the most studied chemicals in animals, presenting relevant findings on toxicity. However, since 1991 there have been no new publications concerning these studies.
Given the progress in technology and scientific development, better pre-clinical evidence (including non-rodent mammalian models) regarding ClO2 toxicity will undoubtedly be needed to update procedures, biomarkers employed to investigate various forms of toxicity, different routes of administration, pharmacokinetic profiles, and parameters. The latter, such as the NOAEL values obtained in pre-clinical studies, should be divided by uncertainty factors to scale the safety margins from the "most sensitive" of the tested species to human dose levels.
Such escalation is fundamental to either developing clinical efficacy studies (if safe for human consumption) or establishing reference consumption doses (in case of accidental ingestion).49 This should not be done conversely, without scaling to design or justify dosage regimens directly in humans, such as the presented cases in which ClO2 promoters justify its use in humans (specifically for COVID-19 treatment) by arguing that a NOAEL (after oral ingestion) reported in a reproduction toxicity study in rats can be extrapolated to a "safe" human consumption dose in adults.50,51
Additionally, the authors of this review believe that information on routes of administration in animals is still incomplete, as only a few studies of oral and intravenous administration were identified. Besides, knowledge of potential target organs and systems is needed, which can be complemented with a more comprehensive panel of animal tests for this substance (in different species), such as carcinogenicity studies, specific genetic toxicology assays, and immunotoxicity studies, which were absent in the reviewed literature.
Our review also identified specific gaps in outcome reporting in the included animal studies, which decreases the strength of the generated evidence and the interpretations that can derive from the experimental outcomes.
We identified that randomization, allocation concealment, and blinded outcome assessments to eliminate potential bias in individual experiments52 were rarely reported in animal studies.
The absence of these elements can be partially explained by the fact that guidelines for quality reporting are relatively recent in animal experimentation. Most likely, some of these publications cannot be taken as solid evidence until these issues are fully taken care of.53
Only one modern animal study aimed to report the efficacy outcomes of ClO2 as a treatment for COVID-1930, and successfully complied with quality reporting elements. Nevertheless, it is still only available as a pre-print, potentially indicating that it has not been peer-reviewed.
In addition, out of the time frame of this review, a recent study in mice, intended as a safety evaluation of a commercial product liberating aqueous ClO2 and used to treat halitosis, concluded that if ingested, this product could cause multiorgan failure (the quality of this study, however, could not be evaluated).54
In this review, animal studies demonstrated increasingly higher critical appraisal scores as the years of publication approached the present, potentially meaning they had a more careful experimental design. Nevertheless, this does not always apply, as we found a newly published low-quality narrative review citing in vitro, animal, and human studies to justify the nasal irrigation of ClO2 for the prevention of COVID-19.55 This publication did not account for any of the JBI critical appraisal checklist points.
Animal studies represent the critical step before translation to clinical studies; therefore, researchers lacking complete and reliable data reports on animals (mainly basing themselves on data from older studies) should refrain from continuing with human trials.56
How Much Is Enough, and Under What Circumstances?
Chlorine dioxide may not be as toxic to humans as other substances. Still, as seen in this review, there is always a possibility of accidentally reaching a threshold of ClO2 toxicity (overdose) by deviating from the product preparation indications, such as not diluting ClO2 in water.
Additionally, cumulative exposure to ClO2 through disinfected water consumption should be reviewed. It is also possible that preconditions may play a role in exacerbating potential toxic effects after the ingestion of miracle cures for illnesses despite not exceeding the toxicity thresholds calculated by the manufacturers.
Particular attention should be paid to warning labels since products based on ClO2 or NaClO2 are used as disinfectants or acquired for therapeutic purposes. These represent a latent risk of accidental ingestion for children, which could derive in severe or even lethal consequences.
Clinical efficacy studies for any substance should always emphasize the need to collect and analyze toxicity outcomes, as some authors have noted that this data is sometimes overlooked in studies in progress.57
Our review also includes evidence for the management of exposure/intoxication due to ClO2 in different circumstances, which may be of use to guide clinical decision-making in similar situations.
This information can be beneficial during the COVID-19 pandemic due to the booming demand for prophylactic or curative products based on ClO2 and other chlorine derivatives, sometimes resulting in adverse events.58 Of note, other human toxicity reports added to the piling evidence amid the COVID-19 pandemic.59-62
An Effective Treatment?
In general, three clinical studies displayed high methodological quality scores and were focused on investigating the topical use of ClO2 for oral health management.45-47 However, only two studies dealt with the systemic use of ClO2; this also excluded high-quality clinical safety study (according to the JBI tool) by Lubbers et al., 1982.44 The latter should be replicated and expanded, focusing on ClO2; likewise, it should measure a broader panel of biomarkers using different doses and more extensive exposure periods.
Recent reviews and meta-analyses of RCTs concerning the daily use of ClO2 to effectively treat halitosis have been published. They conclude that this remedy is effective and does not present adverse effects63, but they are also cautious, suggesting longer follow-up times in similar experimental designs.64
Finally, the quasi-experimental clinical study by Insignares-Carrione et al.12, seeking to demonstrate the effectiveness of ClO2 in managing COVID-19 patients, displayed numerous methodological and overall quality deficiencies.
It is worth mentioning that the sample of participants was small and that since COVID-19 can be a self-limiting disease in non-severe cases, any assertion of improvement due to ingested substances must be taken with caution.
Likewise, the study does not objectively specify the severity of the COVID-19 disease experienced by participants (neither in the case group nor in the controls), which introduces a high probability of bias. The fact that participants prepared their ClO2 solution at home might have introduced variability in exposure conditions.
Despite denying any conflicts of interest, the authors, at the end of the article, thank Andreas Kalcker, the leading promoter of CDS consumption, with whom they have published other works directly.65
Out of the time scope of our review, but worth mentioning in 2021, Aparicio et al.51 published a retrospective observational study in which ClO2 is administered as prophylaxis treatment to family members of individuals with COVID-19 (confirmed by PCR).
Exposed family members with no COVID-19 symptoms were considered a success; however, this statement ignores the asymptomatic presentation of the disease, which the appropriate laboratory tests can only identify. It is noteworthy that this study did not undergo an Institutional Review Board (IRB) process review, and the first author's clinic (most probably supplying the ClO2 preparation) was closed by health authorities due to non-compliance with sanitary requirements.66
Implications for Public Health
As confirmed in this study, evidence concerning ClO2 is inconclusive. Advocates of this substance have defended its use, arguing the existence of registered clinical trials which have not reported results yet and lack a national regulatory authorization of execution.67 As a matter of fact, a recent exploration of the website https://clinicaltrials.gov yielded 18 clinical trials using ClO2 as an intervention, most of them addressing mouth conditions and 3 concerning COVID-19; none of the latter reported results.
Additionally, it is worrisome that decision-makers have delivered this substance to their people, and, in some countries, the Senate has authorized its production.68,69 Supporters have even filed applications in order to consider the Helsinki declaration for the compassionate use of this substance for COVID-19 treatment in the absence of other solutions, despite its discussed toxicity and lack of evidence on effectiveness.70
Public health should call on the precautionary principle to prevent toxicity cases derived from the use of this substance as a treatment as long as there is no conclusive evidence. Most importantly, tight advertising, sales, and consumption regulations should be enforced until further evidence is published.
Limitations
Despite careful search strategy design, the present scoping review may have missed academic articles due to search engines' inherent restrictions and online unavailability, while case reports are usually published in grey literature such as national databases71 and the press. Finally, excluded in vitro studies could help understand the kinetics of ClO2.
Chlorine dioxide has been proposed as a treatment for several diseases; thus, its popularity has increased in recent years; compiled quality evidence has not been adequately analyzed.
This study found moderate literature on the subject, including pre-clinical and clinical studies.
Animal studies hint at the possibility of multiorgan damage; consequently, there is a need to update the experiments to modern approaches. In humans, several case reports of ClO2 toxicity have been published.
Regarding ClO2 efficacy as a treatment, there is still insufficient and non-compelling data about efficacy studies in humans. If intending to demonstrate or rule out that ClO2 can work as an active therapeutic principle, the quality of studies and reporting should be improved in pre-clinical studies before translation and escalation to human trials. Public health should call on the precautionary principle to prevent toxicity cases as long as there is no conclusive evidence on this substance.
| Supplemmentary Table 1. Final search strategy | ||
|---|---|---|
| Concept | Term | Search Strategy Syntaxis |
| A | Chlorine dioxide | ((“chlorine dioxide” [Supplementary Concept]) OR (“chlorine dioxide”)) OR (miracle mineral solution) |
| B | Usage & outcomes | (((“therapeutic use” [Subheading]) OR (“Therapeutics”[Mesh])) OR (“Treatment Outcome”[Mesh]) |
| C | Toxicity | (“toxicity” [Subheading]) (“Toxicity Tests, Subchronic”[Mesh] OR “Toxicity Tests, Chronic”[Mesh] OR “Toxicity Tests, Acute”[Mesh] OR “Toxicity Tests, Subacute”[Mesh] OR “Toxicity Tests”[Mesh]) |
| Final search | (A AND (B OR C)) | |
| Supplemmentary Table 2. Risk of Bias in Animal Studies | |||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Publications | Moore, GS | Bercz, JP | Moore GS | Suh DH | Moore, GS | Meier JR | Orme J | Harrington, RM | Hayashi M | Toth GP | Carlton, BD | Harrington, RM | Gill MW | Karrow NA | Zambrano, X |
| 5 elements of critical appraisal | Risk of bias evaluation | ||||||||||||||
| Animal allocation & randomization | Y | N | Y | U | Y | U, NE | N | U, NE | U | Y | U, NE | Y | Y | Y | Y |
| Reports blinding | N | N | N | N | N | N | N | N | N | N | U, NE | N | N | N | N |
| Reports population size | Y | Y | Y | Y | Y | Y | N | Y | Y | U | Y | Y | Y | Y | Y |
| Reports complete outcomes and follow-up | Y | U, I | Y | Y | Y | U, I | Y | U, I | Y | Y | Y | Y | Y | Y | Y |
| Compliance with animal welfare requirements | U, NE | U, NE | Y | N | U, NE | U, NE | U, NE | U, NE | U, NE | U, NE | U, NE | U, NE | Y | U, NE | Y |
| Overall appraisal (number of YES out of 5) | 3 | 1 | 4 | 2 | 3 | 1 | 1 | 1 | 2 | 2 | 2 | 3 | 4 | 3 | 4 |
| Y: yes; N: no; NE: not explicit; U: unclear; I: incomplete Henderson VC, Kimmelman J, Fergusson D, Grimshaw JM, Hackam DG. Threats to validity in the design and conduct of preclinical efficacy studies: a systematic review of guidelines for in vivo animal experiments. PLoS Med. 2013; 10(7):e1001489. Hooijmans CR, Rovers MM, de Vries RBM, Leenaars M, Ritskes-Hoitinga M, Langendam MW. SYRCLE’s risk of bias tool for animal studies. BMC Med Res Methodol. 2014; 14: 43. The Edinburgh CAMARADES Group. Collaborative Approach to Meta Analysis and Review of Animal Data from Experimental Studies (CAMARADES). The University of Edinburgh. Available from URL: https://www.ed.ac.uk/clinical-brain-sciences/research/camarades | |||||||||||||||
| Supplemmentary Table 3. JBI critical appraisal checklist | |||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| A. For case reports | |||||||||||||
| 8 elements of critical appraisal | Risk of bias evaluation | ||||||||||||
| Publications | Exner-Freisfeld | Lin | Bathina | Romanovsky | Burke | Gebhardtova | Loh | Hagiwara | Sorigué | Alcantara | Arnold | Aguilar | Zhen |
| 1. Were patient’s demographic characteristics clearly described? | Y | Y | N | Y | Y | Y | Y | Y | Y | U | U | Y | U |
| 2. Was the patient’s history clearly described and presented as a timeline? | Y | Y | Y | Y | U | Y | Y | Y | Y | U | Y | Y | Y |
| 3. Was the current clinical condition of the patient on presentation clearly described? | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y |
| 4. Were diagnostic tests or assessment methods and the results clearly described? | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y |
| 5. Was the intervention(s) or treatment procedure(s) clearly described? | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y |
| 6. Was the post-intervention clinical condition clearly described? | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y |
| 7. Were adverse events (harms) or unanticipated events identified and described? | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y |
| 8. Does the case report provide takeaway lessons? | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y | Y |
| Overall appraisal (number of YES out of 8) | 8 | 8 | 7 | 8 | 7 | 8 | 8 | 8 | 8 | 6 | 7 | 8 | 7 |
| B. For case-control studies | ||
|---|---|---|
| 10 elements of critical appraisal | Risk of bias evaluation | |
| Lubbers et al., 1982 | Paraskevas et al., 2008 | |
| 1. Were the groups comparable other than the presence of disease in cases or the absence of disease in controls? | Y | Y |
| 2. Were cases and controls matched appropriately? | Y | Y |
| 3. Were the same criteria used for identification of cases and controls? | Y | Y |
| 4. Was exposure measured in a standard, valid and reliable way? | Y | Y |
| 5. Was exposure measured in the same way for cases and controls? | Y | Y |
| 6. Were confounding factors identified? | Y | Y |
| 7. Were strategies to deal with confounding factors stated? | Y | Y |
| 8. Were outcomes assessed in a standard, valid and reliable way for cases and controls? | Y | Y |
| 9. Was the exposure period of interest long enough to be meaningful? | Y | Y |
| 10. Was appropriate statistical analysis used? | Y | Y |
| Overall appraisal (number of YES out of 10) | 10 | 10 |
| C. For case series | |
|---|---|
| 10 elements of critical appraisal | Risk of bias evaluation |
| Zirwas et al., 2018 | |
| 1. Were there clear criteria for inclusion in the case series? | N |
| 2. Was the condition measured in a standard, reliable way for all participants included in the case series? | U |
| 3. Were valid methods used for identification of the condition for all participants included in the case series? | U |
| 4. Did the case series have consecutive inclusion of participants? | U |
| 5. Did the case series have complete inclusion of participants? | Y |
| 6. Was there clear reporting of the demographics of the participants in the study? | N |
| 7. Was there clear reporting of clinical information of the participants? | U |
| 8. Were the outcomes or follow-up results of cases clearly reported? | Y |
| 9. Was there clear reporting of the presenting site(s)/clinic(s) demographic information? | Y |
| 10. Was statistical analysis appropriate? | N |
| Overall appraisal (number of YES out of 10) | 3 |
| D. For quasi-experimental studies | |
|---|---|
| Publications | Insignares-Carrione et al., 2021 |
| 9 elements of critical appraisal | Risk of bias evaluation |
| 1. Is it clear in the study what is the ‘cause’ and what is the ‘effect’ (i.e. there is no confusion about which variable comes first)? | Y |
| 2. Were the participants included in any comparisons similar? | U |
| 3. Were the participants included in any comparisons receiving similar treatment/care, other than the exposure or intervention of interest? | N |
| 4. Was there a control group? | Y |
| 5. Were there multiple measurements of the outcome both pre and post the intervention/exposure? | Y |
| 6. Was follow-up complete; if not, were differences between groups in terms of their follow-up adequately described and analyzed? | U |
| 7. Were the outcomes of participants included in any comparisons measured in the same way? | Y |
| 8. Were outcomes measured in a reliable way? | N |
| 9. Was appropriate statistical analysis used? | Y |
| Overall appraisal (number of YES out of 9) | 5 |
| E. For randomized-controlled trials | ||
|---|---|---|
| 13 elements of critical appraisal | Risk of bias evaluation | |
| Shinada et al., 2008 | Shinada et al., 2010 | |
| 1. Was true randomization used for assignment of participants to treatment groups? | Y | Y |
| 2. Was allocation to treatment groups concealed? | Y | Y |
| 3. Were treatment groups similar at the baseline? | Y | Y |
| 4. Were participants blind to treatment assignment? | Y | Y |
| 5. Were those delivering treatment blind to treatment assignment? | Y | Y |
| 6. Were outcomes assessors blind to treatment assignment? | Y | Y |
| 7. Were treatment groups treated identically other than the intervention of interest? | Y | Y |
| 8. Was follow-up complete; if not, were differences between groups in terms of their follow-up adequately described and analyzed? | Y | Y |
| 9. Were participants analyzed in the groups to which they were randomized? | Y | Y |
| 10. Were outcomes measured in the same way for treatment groups? | Y | Y |
| 11. Were outcomes measured in a reliable way? | Y | Y |
| 12. Was appropriate statistical analysis used? | Y | Y |
| 13. Was the trial design appropriate, and any deviations from the standard RCT design (individual randomization, parallel groups) accounted for in the conduct and analysis of the trial? | Y | Y |
| Overall appraisal (number of YES out of 13) | 13 | 13 |
| Y: yes; N: no; U: unclear Joanna Briggs Institute (JBI). Critical Appraisal Tools. University of Adelaide. Available from URL: https://jbi.global/critical-appraisal-tools | ||
| Supplemmentary Table 4. PRISMA 2020 Checklist | |||
|---|---|---|---|
| Section and topic | Item # | Checklist item | Location where item is reported (page #) |
TITLE | |||
| Title | 1 | Identify the report as a systematic review. | 64 |
ABSTRACT | |||
| Abstract | 2 | See the PRISMA 2020 for abstracts checklist. | 64-65 |
INTRODUCTION | |||
| Rationale | 3 | Describe the rationale for the review in the context of existing knowledge. | 65 |
| Objectives | 4 | Provide an explicit statement of the objective(s) or question(s) the review addresses. | 65 |
METHODS | |||
| Eligibility criteria | 5 | Specify the inclusion and exclusion criteria for the review and how studies were grouped for the syntheses. | 66, Figure 1 |
| Information sources | 6 | Specify all databases, registers, websites, organisations, reference lists and other sources searched or consulted to identify studies. Specify the date when each source was last searched or consulted. | 66, Figure 1 |
| Search strategy | 7 | Present the full search strategies for all databases, registers and websites, including any filters and limits used. | 66, Supplementary Table 1 |
| Selection process | 8 | Specify the methods used to decide whether a study met the inclusion criteria of the review, including how many reviewers screened each record and each report retrieved, whether they worked independently, and if applicable, details of automation tools used in the process. | Figure 1 |
| Data collection process | 9 | Specify the methods used to collect data from reports, including how many reviewers collected data from each report, whether they worked independently, any processes for obtaining or confirming data from study investigators, and if applicable, details of automation tools used in the process. | 66 |
| Data items | 10a | List and define all outcomes for which data were sought. Specify whether all results that were compatible with each outcome domain in each study were sought (e.g. for all measures, time points, analyses), and if not, the methods used to decide which results to collect. | 66 |
| 10b | List and define all other variables for which data were sought (e.g. participant and intervention characteristics, funding sources). Describe any assumptions made about any missing or unclear information.List and define all other variables for which data were sought (e.g. participant and intervention characteristics, funding sources). Describe any assumptions made about any missing or unclear information. | 66 | |
| Study risk of bias assessment | 11 | Specify the methods used to assess risk of bias in the included studies, including details of the tool(s) used, how many reviewers assessed each study and whether they worked independently, and if applicable, details of automation tools used in the process. | 66, Supplementary Tables 2 and 3 |
| Effect measures | 12 | Specify for each outcome the effect measure(s) (e.g. risk ratio, mean difference) used in the synthesis or presentation of results. | Not applicable |
| Synthesis methods | 13a | Describe the processes used to decide which studies were eligible for each synthesis (e.g. tabulating the study intervention characteristics and comparing against the planned groups for each synthesis (item #5)). | 66 |
| 13b | Describe any methods required to prepare the data for presentation or synthesis, such as handling of missing summary statistics, or data conversions. | 66 | |
| 13c | Describe any methods used to tabulate or visually display results of individual studies and syntheses. | 66 | |
| 13d | Describe any methods used to synthesize results and provide a rationale for the choice(s). If meta-analysis was performed, describe the model(s), method(s) to identify the presence and extent of statistical heterogeneity, and software package(s) used. | Not applicable | |
| 13e | Describe any methods used to explore possible causes of heterogeneity among study results (e.g. subgroup analysis, meta-regression). | Not applicable | |
| 13f | Describe any sensitivity analyses conducted to assess robustness of the synthesized results. | Not applicable | |
| Reporting bias assessment | 14 | Describe any methods used to assess risk of bias due to missing results in a synthesis (arising from reporting biases). | 66, Supplementary Tables 2 and 3 |
| Certainty assessment | 15 | Describe any methods used to assess certainty (or confidence) in the body of evidence for an outcome. | 66, Supplementary Tables 2 and 3 |
RESULTS | |||
| Study selection | 16a | Describe the results of the search and selection process, from the number of records identified in the search to the number of studies included in the review, ideally using a flow diagram. | 66, Figure 1 |
| 16b | Cite studies that might appear to meet the inclusion criteria, but which were excluded, and explain why they were excluded. | 66-83, Figure 1 | |
| Study characteristics | 17 | Cite each included study and present its characteristics. | 66-83, Tables 1, 2 and 3 |
| Risk of bias in studies | 18 | Present assessments of risk of bias for each included study. | Supplementary Tables 2 and 3 |
| Results of individual studies | 19 | For all outcomes, present, for each study: (a) summary statistics for each group (where appropriate) and (b) an effect estimate and its precision (e.g. confidence / credible interval), ideally using structured tables or plots. | Not applicable |
| Results of syntheses | 20a | For each synthesis, briefly summarise the characteristics and risk of bias among contributing studies. | 66-83, Tables 1, 2 and 3, Supplementary Tables 2 and 3 |
| 20b | Present results of all statistical syntheses conducted. If meta-analysis was done, present for each the summary estimate and its precision (e.g. confidence / credible interval) and measures of statistical heterogeneity. If comparing groups, describe the direction of the effect. | Not applicable | |
| 20c | Present results of all investigations of possible causes of heterogeneity among study results. | Not applicable | |
| 20d | Present results of all sensitivity analyses conducted to assess the robustness of the synthesized results. | Not applicable | |
| Reporting biases | 21 | Present assessments of risk of bias due to missing results (arising from reporting biases) for each synthesis assessed. | Not applicable |
| Certainty of evidence | 22 | Present assessments of certainty (or confidence) in the body of evidence for each outcome assessed. | Not applicable |
DISCUSSION | |||
| Discussion | 23a | Provide a general interpretation of the results in the context of other evidence. | 83-85 |
| 23b | Discuss any limitations of the evidence included in the review. | 85 | |
| 23c | Discuss any limitations of the review processes used. | 85 | |
| 23d | Discuss implications of the results for practice, policy, and future research. | 85 | |
OTHER INFORMATION | |||
| Registration and protocol | 24a | Provide registration information for the review, including register name and registration number, or state that the review was not registered. | - |
| 24b | Indicate where the review protocol can be accessed, or state that a protocol was not prepared. | - | |
| 24c | Describe and explain any amendments to information provided at registration or in the protocol. | - | |
| Support | 25 | Describe sources of financial or non-financial support for the review, and the role of the funders or sponsors in the review. | 93 |
| Competing interests | 26 | Declare any competing interests of review authors. | 93 |
| Availability of data, code and other materials | 27 | Report which of the following are publicly available and where they can be found: template data collection forms; data extracted from included studies; data used for all analyses; analytic code; any other materials used in the review. | Supplementary Tables 1, 2 and 3 |
| Taken from Page MJ, McKenzie JE, Bossuyt PM, Boutron I, Hoffmann TC, Mulrow CD, et al. The PRISMA 2020 statement: An updated guideline for reporting systematic reviews. BMJ 2021; 372:n71. DOI: 10.1136/bmj.n71 For more information, visit: http://www.prisma-statement.org/ | |||
We thank Noelia Del Castillo and Luis Germán Ruiz Maytorena for their valuable research assistance.
The authors declare no competing interests.
This research received no specific grant from any funding agency in the public, commercial, or not-for-profit sectors.
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