Next Article in Journal
Alcohol Consumption on the Heaviest Drinking Occasion and Hangovers during the First Dutch COVID-19 Lockdown
Previous Article in Journal
Association of Plasma Carotenoid and Malondialdehyde Levels with Physical Performance in Korean Adolescents
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Cleaning Products Commonly Used in Oklahoma Family Child Care Homes: Implications for Respiratory Risk and Children’s Health

1
Department of Health Promotion Sciences, Hudson College of Public Health, University of Oklahoma Health Sciences Center, 801 N.E. 13th Street, Oklahoma City, OK 73104, USA
2
Department of Nutritional Sciences, College of Allied Health, University of Oklahoma Health Sciences Center, 1200 N. Stonewall Ave., Oklahoma City, OK 73114, USA
3
Department of Nutrition and Exercise Physiology, Elson S. Floyd College of Medicine, Washington State University Health Sciences Spokane, 412 E. Spokane Falls Blvd., Spokane, WA 99202, USA
4
Department of Occupational and Environmental Health, Hudson College of Public Health, University of Oklahoma Health Sciences Center, 801 N.E. 13th Street, Oklahoma City, OK 73104, USA
5
Department of Pediatrics, College of Medicine, University of Oklahoma Health Sciences Center-Tulsa, 4444 E. 41st Street, Tulsa, OK 74135, USA
6
Department of Biostatistics and Epidemiology, Hudson College of Public Health, University of Oklahoma Health Sciences Center, 801 N.E. 13th Street, Oklahoma City, OK 73104, USA
7
Institute for Research on Equity and Community Health (iREACH), Christiana Care, Avenue North, 4000 Nexus Drive, CEI-300, Wilmington, DE 19803, USA
8
Department of Human Development and Family Sciences, University of Delaware, 111 Alison Hall West, Newark, DE 19716, USA
*
Author to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2022, 19(7), 4299; https://doi.org/10.3390/ijerph19074299
Submission received: 18 March 2022 / Revised: 1 April 2022 / Accepted: 1 April 2022 / Published: 3 April 2022

Abstract

:
Little is known about the cleaning products used by early care and education programs that contribute to childhood asthma, particularly in Oklahoma where rates of uncontrolled asthma are higher than national rates (60.0% vs. 50.3%, respectively). We conducted a cross-sectional study of cleaning products used by Oklahoma-licensed family child care homes (FCCHs) (n = 50) to characterize and identify potential respiratory-health risks associated with chemical contents. Overall, 386 chemicals were abstracted from the 132 reported products. Of these, 100 unique chemicals were identified. Four percent (4.2%) of providers used a product with a sensitizer that may cause allergy or asthma symptoms if inhaled and 35.4% used a product with an irritant that may cause irritation to the respiratory tract. Most (62.5%) reported using a product with a chemical that had a C=C double bond in its molecular structure that may make it highly reactive with other substances in the air and produce secondary air pollutants and 83.3% reported using a sodium hypochlorite containing product. Twenty-three percent reported products that contain carcinogens. Policy, educational, and technical assistance interventions are needed to promote the use of safer products and reduce respiratory and other health risks posed by chemicals in Oklahoma FCCHs.

1. Introduction

Early care and education (ECE) programs, also known as child care, play a critical role in shaping children’s health and development. Approximately 61% of children under the age of five in the United States (US) receive regular care in ECE programs [1], with some spending up to 50 h per week in these environments [2,3]. State licensing regulations require ECE programs to prevent and control disease transmission, primarily through cleaning, sanitizing, and disinfecting [4]; however, products used for these purposes may routinely expose children to environmental toxicants [3,5,6,7]. Although effectively disinfecting and sanitizing is important for ensuring hygienic ECE environments, products such as bleach may pose a risk to children’s respiratory and overall health [8]. Children are especially vulnerable to environmental toxicants due to their (i) higher respiratory rates that cause them to breathe a larger volume of air per unit body weight [9]; (ii) increased physical exertion that causes them to breathe in more through their mouths, resulting in a greater volume of harmful chemicals to be inhaled [10]; and (iii) developing organ systems, with their lungs remaining undeveloped until adolescence [11,12]. Children’s small stature also puts their breathing zone closer to the floor where toxic gases tend to collect, resulting in higher inhalation of toxicants. Frequent use of cleaning products in ECE environments may increase children’s exposure to a variety of harmful environmental toxicants including volatile organic compounds (VOCs), particulate matter (PM), and nitrogen dioxide, which have been associated with decreased lung function, inflammation, airway obstruction, increased allergen sensitization, and the exacerbation of asthma symptoms [13,14,15,16,17,18,19].
According to the US Environmental Protection Agency (EPA), cleaners are intended to be used for removing dirt and organic matter from surfaces using detergents; sanitizers are intended to be used for killing or inactivating bacteria using chemicals; and disinfectants are intended to be used for killing or inactivating viruses and bacteria using chemicals [20]. Sanitizing and disinfecting products are regulated by the US EPA and registered as antimicrobial pesticides. Cleaning products are only required to be registered with the US EPA if they sanitize or disinfect (i.e., contain antimicrobial pesticides); therefore most are not registered. Cleaning products, particularly sprays, contain a complex mixture of hazardous chemicals including VOCs [21]. Aerosols or pump sprays also emit chemicals as gases and aerosols that may interact with other compounds in the indoor air, creating secondary toxicants such as PM [22,23,24]. Most state licensing regulations require ECE programs to use bleach or an EPA-registered disinfectant [25]. Bleach, which is the most commonly used product in ECE settings [5,26], contains chlorine-releasing antimicrobial agents (i.e., sodium hypochlorite). These agents can interact with toxicants in other cleaning products such as ammonia and acids to create nitrogenated compounds (e.g., chloramines and others) that may cause respiratory irritation [27,28]. Formaldehyde, which is another disinfecting byproduct of bleach [29], is a known irritant of the eyes, nose, throat, and lungs, and can act as a trigger of asthma symptoms; prolonged exposures can cause cancer [30]. Bleach also emits small amounts of chloroform, another known carcinogen, and at high temperatures, can emit up to twice as much chloroform [29].
ECE licensing regulations require many surfaces to be sanitized or disinfected daily and others, such as changing tables, to be disinfected after each use, frequently exposing children to toxicants. To illustrate, healthy infants have eight or more diaper changes a day, so changing tables at ECE programs caring for multiple infants may be used numerous times an hour [31] and disinfected after each use, usually with bleach or bleach-containing sprays, while children are present. VOCs are known to stay in the air for up to 20 min after a cleaning task is completed [32]. ECEs that maintain a rigid cleaning schedule that allows bleach the appropriate dwell time of 10 min before each diaper change could potentially expose children to lingering VOCs in the air for at least 30 min per diaper change [29]. Although limited, environmental sampling studies have documented the presence of environmental toxicants in ECE settings [3,5,26,33]. All four US studies [3,5,26,33], documented the presence of VOCs such as chloroform, benzene, and ethylbenzene, some above health-based limits. Studies conducted outside of the US have also documented the presence of environmental toxicants in ECE settings [34,35,36,37]. Notably, a study of nurseries in Portugal found high levels of formaldehyde and VOCs with levels peaking at the beginning of the morning, during or immediately after lunch, and in the afternoon [34], suggesting that toxicants originated from indoor sources such as cleaning products [34].
Understanding the types of cleaning products used in ECEs and the potential health impacts of the chemicals found in these products is critical to developing interventions to reduce children’s risk and create healthier ECE environments. Yet, little is known about the types of cleaning products that are used by ECE providers. Most studies conducted to date have measured air quality or chemical residues or assessed ECE providers’ general cleaning practices [3,5,26,33]. Most of this research has been conducted in child care centers (i.e., community or center-based child care and Head Start), which are usually located in large facilities with multiple classes, large class sizes, and multiple staff members [4]. Little research has been conducted in family child care homes (FCCHs) or home-based child care, which are located in residences, usually have a single provider, and care for no more than 12 children at a time [38]. To the best of our knowledge, only one study, which was conducted outside of the US, examined cleaning products used in ECEs and their potential health impacts [6]. This nationwide survey of more than 300 nurseries, kindergartens, and elementary schools across France found that 584 different cleaning products were used; safety data sheets (SDSs) were available for 218 products. Of the 152 chemicals abstracted from the products’ SDSs, more than half of the chemicals were respiratory irritants and seven percent were reactive chemicals containing a C=C double bonds that can react easily with environmental ozone to produce secondary air pollutants that may pose respiratory and other health risks, such as aldehydes and PM [6,22,23,39]. In this study, conducted among Oklahoma City metropolitan area licensed FCCH providers (n = 50), we characterized cleaning products used and identified potential health risks associated with their chemical contents, while in Oklahoma, licensed FCCHs and centers are bound to the same requirements, prior research conducted by our research team in Oklahoma indicates that FCCHs’ reported cleaning and other related practices differ from those reported by centers [7].

2. Materials and Methods

2.1. Study Design

This study used baseline data collected in Happy Healthy Homes, a randomized, matched-attention, controlled intervention trial aimed at FCCH providers (n = 50); a detailed study protocol has been previously published [40] and the trial is registered with Clinicaltrials.gov (NCT03560050). FCCH providers were: (i) licensed FCCHs serving at least one 2-to-5-year-old child; (ii) caring for low-income children and participating in the Child and Adult Care Food Program; (iii) located within the Oklahoma City metropolitan area (approximately a 60-mile radius); and (iv) planning to remain in business for at least 12 months. Providers were recruited through sponsor organizations and direct phone calls. A total of 370 eligible FCCH providers were originally contacted, of which 74 providers were screened and consented; 50 providers completed baseline data collection. Trained research staff visited participating FCCHs to collect baseline data, including provider surveys, environmental observations and product label abstraction, from October 2017 through October 2018. The study was approved by the University of Oklahoma Health Sciences Center Institutional Review Board.

2.2. Measures

2.2.1. Participant Characteristics

Providers reported sociodemographic characteristics such as age, gender, race, ethnicity, education, and income via survey and also provided information about their program including the number of years in business, number of children in care, number of hours spent cleaning each day, whether the building was rented and built before 1978, and whether any children in their care had asthma.

2.2.2. Cleaning Products

Items from the Environmental Exposures in Child Care Facilities Study [26] and the Children’s Environmental Health Network’s Eco-Healthy Child Care® Checklist [41] were adapted to measure product information. Participants reported the three products that they used most often to clean, sanitize, or disinfectant the indoor areas where children are cared for. They then showed research staff these three products. Research staff abstracted the following information from the product label: (i) brand name; (ii) intended use of the product (i.e., a cleaner for removing dirt from surfaces using detergents; a sanitizer for killing bacteria using chemicals; and or a disinfectant for killing bacteria and viruses using chemicals [20]); and (iii) presence of green product certifications (i.e., Greenseal, Ecologo, US EPA Safer Choice, or Design for the Environment). A photograph was taken of the products and their labels.

2.2.3. Chemical Ingredients

Product brand names and the top three chemicals listed as active ingredients were abstracted from the product labels or from photos taken on site. When exact chemical ingredients were not listed on product labels, this information was obtained through the Consumer Product Information Database (CPID) [42], manufacturer websites, and/or SDSs (formerly MSDSs or Material Safety Data Sheets).

2.2.4. Chemical Designation

The US Department of Labor Occupational Safety and Health Administration Hazard Communication Standard requires product labels and SDSs to classify chemicals using the Global Harmonized System (GHS) of Classification and Labeling of Chemicals [43]. The GHS classifies chemicals into hazard classes and allows for easy identification of those hazard classes using its designated pictograms. For the purpose of the current study, we were concerned with chemicals labeled with an Exclamation Mark Irritant GHS07 and Health Hazard GHS08 pictograms. Chemical ingredients that had these pictograms were further evaluated based on its GHS hazard class, statements, codes, and molecular formula structure. Molecular formulas were evaluated using the US National Library of Medicine’s ChemIDplus [44]. A set of seven chemical designations were adapted from a nationwide survey on indoor air quality in nurseries and schools in France [6] to identify chemical ingredients that pose a potential health concern (Figure 1).
A chemical ingredient was considered a potential concern if: (i) it may cause allergic sensitization of the respiratory tract, as defined by the GHS hazard code H334; (ii) it may cause irritation to the respiratory tract, defined by the GHS hazard code H335; (iii) it has a C=C double bond that is highly reactive with ozone and may produce secondary air pollutants such as aldehydes and PM [6,22,23,39]. Sodium hypochlorite, the chemical active ingredient for bleach, and its byproducts (e.g., chloroform, chloramines, and formaldehyde) are associated with respiratory irritation and a potential trigger of asthma symptoms [8,27,28,29,30]; however, the GHS does not consider the byproducts of the chemical. Thus, we noted sodium hypochlorite during our abstraction process. In addition, given the severity of health implications, we also noted any product that was designated as a carcinogen defined by the GHS hazard codes H350 and H350i.

2.3. Data Analyses

Descriptive statistics were conducted for all measures, including mean and standard deviation (SDs) for continuous variables and frequencies and percentages for categorical or nominal variables. All analyses were performed in Microsoft® Excel® for Microsoft 365 MSO (Version 2112, Microsoft, Redmond, WA, USA).

3. Results

3.1. Participant Characteristics

FCCH provider and program characteristics are presented in Table 1. The average age of providers was 44 years (SD = 13). All participating FCCH providers were female. Nearly all were non-Hispanic (95.7%) and most identified as white (60.5%), with the majority having some college or vocational training (63.3%). Approximately one third (31.3%) of providers had a degree in early childhood education or development. The average number of years programs were in business was 11 years (SD = 10). FCCH programs cared for an average of seven (SD = 4) children ranging from birth to five years of age. The average number of self-reported daily hours providers spent cleaning their FCCH was 3 (SD = 3). Over a third (36.7%) of providers reported that children in their care had asthma. An additional 34.7% did not know whether children in their care had asthma.

3.2. Cleaning Products

Of the 132 cleaning products reported by FCCH providers, 77 distinct products were identified. The top three products reported were (i) Clorox Bleach 1, Concentrated, Regular (43.8%); (ii) Young Living Thieves Essential Oil Infused (12.5%); and (iii) Clorox Performance Bleach 2 with Cloromax (10.4%). Among the 77 distinct cleaning products, 68.8% were intended to be used as cleaners; 24.7% were intended to be used as sanitizers; and 48.1% were intended to be used as disinfectants. As noted previously, sanitizers and disinfectants contain pesticides, which may be more harmful than the detergents found in cleaners. None of the cleaning products reported had a green product certification. The 20 most commonly reported cleaning products and their intended use are presented in Table 2. The other reported products can be found in the Appendix A Table A1.

3.3. Chemical Usage at the Provider-Level

Of the 386 chemicals abstracted, 100 distinct or unduplicated chemicals were identified. Overall, 4.2% of providers used a product with a known sensitizer that may cause allergy or asthma symptoms or breathing difficulties if inhaled. Over a third (35.4%) of providers used a product with a known irritant that may cause irritation to the respiratory tract. Most (62.5%) providers reported using a product with a chemical that had a C=C double bond in its molecular structure that may make it highly reactive with other substances in the air to produce secondary air pollutants. Overall, most (83.3%) FCCH providers reported using a sodium hypochlorite containing product. Almost a quarter (22.9%) of providers reported using a product that contained a carcinogen. Chemical designation and class of chemical ingredients found in reported products are presented in Table 3.

4. Discussion

Understanding the cleaning products used in ECEs and the potential health impacts of the chemicals found in these products is critical for assessing risk and developing policies and interventions to protect children’s health. Our study provides insight into the potential health impacts of the chemicals found in cleaners used by Oklahoma FCCHs and indicates a need for improvement. FCCH providers commonly reported using chemical cleaners that contain US EPA-listed chemicals of concern for environmental exposure and asthma control, particularly products containing irritants and reactive chemicals. We found that 13% of the chemical ingredients abstracted from the cleaning products used by FCCH providers were respiratory irritants. This is lower than the previously mentioned study of 310 nurseries and schools in France that found that 49% of chemicals identified in cleaning products used were irritants. [6]. In contrast, we found much higher reactive chemical ingredients than this French study (15.0% versus 7.2%, respectively) [6]. While these differences may be due to the lack of uniformity in safety regulations or product preferences across countries, both studies found substantial use of products with irritants and reactive chemical ingredients. Similar to a study of ECEs in Washington, D.C. [5], most FCCH providers in our study (83.3%) reported using bleach or sodium hypochlorite-containing products to clean, sanitize, and disinfect. In Oklahoma, ECEs are required under the Oklahoma Administrative Code 340:110-3-304 to use a household bleach solution or a product registered with the US EPA to sanitize and disinfect. Our recent statewide survey of Oklahoma ECEs, found similar rates to the current study: 86% of centers and 92% of FCCHs reported regularly using bleach [7]. While bleach-containing-products are popular and may be effective sanitizers and disinfectants, they pose a potential respiratory concern. The byproducts (i.e., chloroform, chloramines, and formaldehyde) of bleach’s active ingredient sodium hypochlorite are associated with respiratory irritation and may trigger asthma symptoms [8,27,28,29,30]. Alternative products that have lower respiratory risk than bleach or quaternary ammonias, such as fragrance-free, non-chlorine, hydrogen peroxide-containing products [29], may result in overall healthier ECE environments for children. Hydrogen peroxide, at the concentrations found in cleaning products, presents a low risk of toxicity to humans [29] and based on a review of disinfectant efficacy covers at least 70% of ECE-relevant organisms [29]. Ready-to-use peroxide products are preferred over bleach for cleaning because they do not need to be diluted daily, have not been associated with asthma, do not cause nasal irritation, and are US EPA-registered disinfectants with the shortest dwell time, thus resulting in reduced exposure [8].
None of the providers in our study used products with a third party or green product certification, an indication that the product’s chemical ingredients are safer or less toxic. Some green product certifications, such as the US EPA Safer Choice label, require that all of the product’s chemical ingredients meet the US EPA’s safety criteria for human health and the environment including carcinogenicity, reproductive/development toxicity, and persistence in the environment without compromising specific performance standards [45]. Thus, cleaning products with a Safer Choice label are safer for: (i) individuals, families, and pets; (ii) worker’s health; and (iii) fish and the environment [45]. Educating providers about third-party certifications may influence their product purchases and reduce exposure. The recent Lifting Up Communities with Interventions and Research Study [46] conducted with women at home, found that switching to safer cleaning products decreased objectively-measured indoor air concentrations of multiple VOCs including chloroform and benzene. The promotion and provision of safer products may reduce exposures to asthma triggers and increase asthma control and warrant further investigation as an intervention for ECEs. Educating providers about green product certification may help to improve purchasing and product use behaviors.
While not the major focus of this paper, our findings regarding carcinogens is important. Almost a quarter (22.9%) of providers reported using one or more products that contained a carcinogen. Furthermore, 8.3% of reported cleaning products in our study contained a carcinogen. This is slightly higher than the previously mentioned French study, which found that 6.8% of products used contained at least one chemical identified as carcinogenic to humans by the International Agency for Research on Cancer (IARC) [6]. The differences in our findings may be due to differing standards set by the governing bodies responsible for evaluating the chemical contents of cleaning products. To illustrate, ethanol, a common chemical found in both studies, was identified as a carcinogen by the IARC, while the GHS classified ethanol as a highly flammable eye irritant. While the origins of pediatric cancer are only partly known, children have increased susceptibility to environmental carcinogens due to their unique patterns of exposure, rapid growth and development, and life expectancy [47]. Interventions to reduce children’s exposures to carcinogens in ECEs are needed.
To our knowledge, this is the first in the US to identify and characterize the chemicals in cleaning products used in FCCHs, a unique childcare setting. Nonetheless, there are limitations to note. We only studied a portion (i.e., the top three) cleaning products used to clean, sanitize, or disinfect indoor areas used for childcare. Thus, we have a limited perspective about the range of products used and may have likely underestimated the chemical burden faced by children in these facilities. Similarly, the chemical ingredients abstracted from product labels and SDSs only included the top three active chemical ingredients, excluding inactive ingredients and chemicals such as fragrances, which are complex mixtures of chemicals that are proprietary in nature. Therefore, our assessment of chemical ingredients is not comprehensive and may underestimate potential health concerns. While we observed the reported products and their labels, we did not objectively measure indoor toxicants and as a result, cannot categorize the full range of toxicants present nor determine whether levels exceed US EPA and the World Health Organization’s indoor air quality guidelines [48]. Finally, our study findings may not be generalizable since it only included 50 FCCHs in the Oklahoma City metropolitan area. Nonetheless, findings from this study underscore the need for interventions that will reduce the presence of chemicals and promote the use of alternative products that have lower respiratory and overall health risks, such as ready-to-use hydrogen peroxide products or products with green product certifications. Educating child care providers and policymakers about the potential health concerns posed by chemical ingredients in commonly used cleaning products and identifying safer cost-effective alternative products for cleaning, sanitizing and disinfection may increase environmental literacy and lead to improved policies and behaviors, and ultimately, safer childcare environments.

5. Conclusions

This study identified several threats to children’s respiratory and overall health posed by chemicals contained in commonly used cleaning products in Oklahoma FCCHs. While additional study is needed to better understand the chemical burdens and exposures faced by children in ECE environments, effective interventions to safeguard children’s health in ECEs are needed now.

Author Contributions

Conceptualization, C.D.Q., M.S.W. and A.L.S.; Data curation, C.D.Q. and H.S.; Formal analysis, C.D.Q., K.A., J.C. and A.L.S.; Funding acquisition, S.B.S. and A.L.S.; Methodology, C.D.Q., K.A. and A.L.S.; Supervision, M.S.W. and A.L.S.; Writing—original draft, C.D.Q., M.S.W. and A.L.S.; Writing—review and editing, M.S.W., S.B.S., H.S., B.W., K.A., J.C., N.R.I. and A.L.S.; Project administration, B.W. and M.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the Agriculture and Food Research Initiative grant no. 2017-68001-26355 from the USDA National Institute of Food and Agriculture and the National Institute of General Medical Sciences of the National Institutes of Health under award number U54GM104938. Any opinions, findings, conclusions, or recommendations expressed in this publication are those of the authors and do not necessarily reflect the views of the US Department of Agriculture or the National Institutes of Health. Additional support for Cassandra D. Querdibitty was provided by the Hudson Fellowship Program awarded to the University of Oklahoma Hudson College of Public Health. The content is solely the responsibility of the authors and does not necessarily represent the official views of the Hudson College of Public Health or the Hudson Fellowship Program.

Institutional Review Board Statement

All study procedures were approved by the University of Oklahoma Health Sciences Center Institutional Review Board (#7551).

Informed Consent Statement

All participants provided voluntary informed consent prior to participation.

Data Availability Statement

The data presented in this study are available on request from the corresponding author. The data are not publicly available.

Acknowledgments

We acknowledge the support and contributions of Chelsea Kracht, Cady Merchant, Sara-Fortin Miller, Sara Patel, Jana Cornelius, Felecia Jones, Colette Vartanian, Holly Davis, and Johana Jarosova, who all contributed to study data collection. We would also like to acknowledge contributions of our community partners, including Felecia Jones, LuAnn Faulkner-Schneider, Denise Anderson, Jennifer Weber, Rainbow Fleet, Worker Assistance Program Food Program, and Helping Hands Food Program as well as Deana Hildebrand. We are deeply grateful for the providers who allowed us into their homes, shared their experiences with us, and wished to create healthier spaces for young children.

Conflicts of Interest

The authors declare no conflict of interest and the funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

Appendix A

Table A1. Other products reported by family child care home (FCCH) providers and product’s intended use, Happy Healthy Homes Baseline Survey, Oklahoma, 2017–2018.
Table A1. Other products reported by family child care home (FCCH) providers and product’s intended use, Happy Healthy Homes Baseline Survey, Oklahoma, 2017–2018.
Product Brand NameCleaner 1Sanitizer 2Disinfectant 3Total FCCHs (n = 48) 4
Ajax With Bleach Cleanser, PowderX 1 (2.08)
Best choice Glass Cleaner with AmmoniaX 1 (2.08)
Bona Tile and Floor CleanerX 1 (2.08)
Clorox Anywhere Hard Surface Daily Sanitizing, Pump Spray X 1 (2.08)
Clorox Bleach Gel Cleaner + Bleach, Pump SprayX 1 (2.08)
Clorox Bleach Splash-Less RegularXXX1 (2.08)
Clorox Bleach with Pine-SolX 1 (2.08)
Clorox Commercial Solutions Germicidal Bleach 4, Regular, Professional UseXXX1 (2.08)
Clorox Fraganzia Multi-Purpose Cleaner, Spring (Primavera)X X1 (2.08)
Clorox Healthcare Bleach Germicidal Wipes, Professional UseXXX1 (2.08)
Clorox Splash-Less Bleach, Concentrated, Fresh Meadow XX1 (2.08)
Comet with Bleach Disinfectant CleanserX X1 (2.08)
Dawn Simply Clean Dishwashing Liquid Dish Soap, Original ScentX 1 (2.08)
Dawn Ultra Dishwashing Liquid Dish Soap, Original X 1 (2.08)
DG Home Disinfectant Spray Fresh Linen Scent X1 (2.08)
Fabuloso Multi-Purpose Cleaner, LavenderX 1 (2.08)
Fresh Scent Disinfecting WipesXXX1 (2.08)
Freshine Disinfecting Wipes Lemon Scented X1 (2.08)
Good & Clean disinfecting wipes X1 (2.08)
Great Value Cleaning BleachXXX1 (2.08)
Great Value Lavender Low-Splash Bleach XX1 (2.08)
Home Select ultra dish soap (cherry blossom)X 1 (2.08)
* Kustom Kleen---1 (2.08)
Lysol Brand Clean & Fresh Multi-Surface Cleaner, Sparkling Lemon & SunflowerX 1 (2.08)
Lysol Brand II Disinfecting Wipes, Lemon & Lime Blossom X1 (2.08)
Lysol Brand II Disinfecting Wipes, Ocean Fresh X1 (2.08)
Lysol Brand Multi-Purpose Cleaner with Hydrogen Peroxide, Citrus Sparkle Zest, Pump SprayX 1 (2.08)
Lysol Clean and Fresh Multi Surface cleaner (Cherry blossom & Pomegranate)XXX1 (2.08)
Lysol Max Cover Disinfectant Mist, Lavender Field, Aerosol X1 (2.08)
Lysol Power & Free Multi-Purpose Cleaning Wipes with Hydrogen Peroxide, Oxygen SplashX 1 (2.08)
Lysol Power Toilet Cleaner XX1 (2.08)
Lysol Professional Disinfectant Spray, Fresh, Aerosol, Professional Use X1 (2.08)
Melaleuca-Clear Power Glass CleanerX 1 (2.08)
Member’s Mark Commercial Lemon Fresh CleanerX X1 (2.08)
Member’s Mark Disinfectant Wipes Lemon ScentXXX1 (2.08)
Method Cleaning Products Squirt + Mop Wood Floor Cleaner AlmondX 1 (2.08)
Mop & Glo Multi-Surface Floor Cleaner, Fresh Citrus ScentX 1 (2.08)
Mr. Clean Multi-Purpose Cleaner with Febreze Meadows and RainX 1 (2.08)
Mrs. Meyers Multi-Surface Cleaner-GeraniumX 1 (2.08)
OdoBan Eliminates Odors, Continuous Spray, Disinfectant Fabric & Air Freshener, Eucalyptus Scent-10001, Aerosol X1 (2.08)
Palmolive Ultra Oxy, Power Degreaser, Dishwashing Hand LiquidX 1 (2.08)
Pine-Sol Multi-Surface Cleaner, Lemon Fresh ScentX 1 (2.08)
Pine-Sol Multi-Surface Cleaner, Sparkling Wave ScentX 1 (2.08)
Pledge Commercial Line, Lemon Clean, Aerosol, Professional UseX 1 (2.08)
Purell Foodservice Surface Sanitizer, Pump Spray, Professional Use XX1 (2.08)
Rejuvenate Floor CleanerX 1 (2.08)
Resolve Large Area Carpet Cleaner Machine Solution—2X ConcentrateX 1 (2.08)
Simple Green Stone Cleaner & Polish, Pump SprayX 1 (2.08)
Soft Scrub Commercial Cleanser with Bleach, Professional UseXXX1 (2.08)
Sol-u-guard Botanical X1 (2.08)
Sol-u-mel stain remover (lemon blossom)X 1 (2.08)
Streak Free Glass Cleaner MPCX 1 (2.08)
Swiffer disposable mopping padX 1 (2.08)
Swiffer Sweeper Wet Mopping Cloths with Febreze Freshness, Lavender Vanilla & Comfort, 24 countX 1 (2.08)
The Home Store glass cleanerX 1 (2.08)
ThievesX 1 (2.08)
Windex Multisurface Disinfectant Cleaner, Glade Rain shower Scent, Pump Spray X1 (2.08)
1 Cleaners defined by the US EPA remove dirt and organic matter from surfaces using detergents; 2 Sanitizers defined by the US EPA kill bacteria on surfaces using chemicals; 3 Disinfectants are defined by the US EPA kills viruses and bacteria on surfaces using chemicals; Definitions found at: https://www.epa.gov/coronavirus/whats-difference-between-products-disinfect-sanitize-and-clean-surfaces (accessed on 12 August 2021); 4 n = 2 missing; * Could not access product label information.

References

  1. Laughlin, L. Who’s Minding the Kids? Child Care Arrangements: Spring 2011; U.S. Census Bureau: Washington, DC, USA, 2013; pp. 70–135.
  2. Donoghue, E.A.; Lieser, D.; DelConte, B.; Donoghue, E.; Earls, M.; Glassy, D.; Mendelsohn, A.; McFadden, T.; Scholer, S.; Takagishi, J. Quality Early Education and Child Care From Birth to Kindergarten. Pediatrics 2017, 140, 2. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Hoang, T.; Castorina, R.; Gaspar, F.; Maddalena, R.; Jenkins, P.L.; Zhang, Q.; McKone, T.E.; Benfenati, E.; Shi, A.Y.; Bradman, A. VOC exposures in California early childhood education environments. Indoor Air 2017, 27, 609–621. [Google Scholar] [CrossRef] [PubMed]
  4. Oklahoma Department of Human Services. Licensing Requirements for Child Care Programs. Available online: http://www.okdhs.org/OKDHS%20Publication%20Library/14-05.pdf (accessed on 25 March 2020).
  5. Quiros-Alcala, L.; Wilson, S.; Witherspoon, N.; Murray, R.; Perodin, J.; Trousdale, K.; Raspanti, G.; Sapkota, A. Volatile organic compounds and particulate matter in child care facilities in the District of Columbia: Results from a pilot study. Environ. Res. 2016, 146, 116–124. [Google Scholar] [CrossRef]
  6. Wei, W.; Boumier, J.; Wyart, G.; Ramalho, O.; Mandin, C. Cleaning practices and cleaning products in nurseries and schools: To what extent can they impact indoor air quality? Indoor Air 2016, 26, 517–525. [Google Scholar] [CrossRef] [PubMed]
  7. Querdibitty, C.D.; Williams, B.; Wetherill, M.S.; Sisson, S.B.; Campbell, J.; Gowin, M.; Stephens, L.; Salvatore, A.L. Environmental Health-Related Policies and Practices of Oklahoma Licensed Early Care and Education Programs: Implications for Childhood Asthma. Int. J. Environ. Res. Public Health 2021, 18, 8491. [Google Scholar] [CrossRef] [PubMed]
  8. Agana, L.; Melgoza, C. Bleach Exposure in Child Care Settings: Strategies for Elimination or Reduction; Asthma Community Network: San Francisco, CA, USA, 2011. [Google Scholar]
  9. Agency for Toxic Substances and Disease Registry. Toxicological Profile for Carbon Tetrachloride. Available online: https://www.atsdr.cdc.gov/toxprofiles/tp30.pdf (accessed on 12 January 2021).
  10. Anderson, M.; Glynn, T.; Enache, A. EPA Region 2 Pesticides in Child Care Initiative 2010 Staten Island Pilot Project Final Report. Available online: https://www.epa.gov/sites/production/files/documents/StatenPilot2010.pdf (accessed on 12 November 2020).
  11. De Luca, G.; Olivieri, F.; Melotti, G.; Aiello, G.; Lubrano, L.; Boner, A.L. Fetal and early postnatal life roots of asthma. J. Matern. Fetal Neonatal. Med. 2010, 23 (Suppl. S3), 80–83. [Google Scholar] [CrossRef] [PubMed]
  12. Pinkerton, K.E.; Joad, J.P. The mammalian respiratory system and critical windows of exposure for children’s health. Environ. Health Perspect. 2000, 108 (Suppl. S3), 457–462. [Google Scholar] [CrossRef]
  13. Salvi, S. Health effects of ambient air pollution in children. Paediatr. Respir. Rev. 2007, 8, 275–280. [Google Scholar] [CrossRef]
  14. Goldizen, F.C.; Sly, P.D.; Knibbs, L.D. Respiratory effects of air pollution on children. Pediatr. Pulmonol. 2016, 51, 94–108. [Google Scholar] [CrossRef]
  15. Harving, H.; Dahl, R.; Mølhave, L. Lung Function and Bronchial Reactivity in Asthmatics during Exposure to Volatile Organic Compounds. Am. Rev. Respir. Dis. 1991, 143, 751–754. [Google Scholar] [CrossRef]
  16. Koren, H.S.; Graham, D.E.; Devlin, R.B. Exposure of Humans to a Volatile Organic Mixture. III. Inflammatory Response. Arch. Environ. Health Int. J. 1992, 47, 39–44. [Google Scholar] [CrossRef] [PubMed]
  17. Mortimer, K.; Neugebauer, R.; Lurmann, F.; Alcorn, S.; Balmes, J.; Tager, I. Air pollution and pulmonary function in asthmatic children: Effects of prenatal and lifetime exposures. Epidemiology 2008, 19, 550–557. [Google Scholar] [CrossRef] [PubMed]
  18. Norbäck, D.; Björnsson, E.; Janson, C.; Widström, J.; Boman, G. Asthmatic symptoms and volatile organic compounds, formaldehyde, and carbon dioxide in dwellings. Occup. Environ. Med. 1995, 52, 388–395. [Google Scholar] [CrossRef] [PubMed]
  19. Hollenbach, J.P.; Cloutier, M.M. Childhood Asthma Management and Environmental Triggers. Pediatric Clin. N. Am. 2015, 62, 1199–1214. [Google Scholar] [CrossRef]
  20. United States Environmental Protection Agency. What’s the Difference between Products that Disinfect, Sanitize, and Clean Surfaces? Available online: https://www.epa.gov/coronavirus/whats-difference-between-products-disinfect-sanitize-and-clean-surfaces (accessed on 12 August 2021).
  21. Gerster, F.M.; Vernez, D.; Wild, P.P.; Hopf, N.B. Hazardous substances in frequently used professional cleaning products. Int. J. Occup. Environ. Health 2014, 20, 46–60. [Google Scholar] [CrossRef] [Green Version]
  22. Morawska, L.; He, C.; Johnson, G.; Guo, H.; Uhde, E.; Ayoko, G. Ultrafine particles in indoor air of a school: Possible role of secondary organic aerosols. Environ. Sci. Technol. 2009, 43, 9103–9109. [Google Scholar] [CrossRef]
  23. Nazaroff, W.W.; Weschler, C.J. Cleaning products and air fresheners: Exposure to primary and secondary air pollutants. Atmos. Environ. 2004, 38, 2841–2856. [Google Scholar] [CrossRef]
  24. Singer, B.C.; Coleman, B.K.; Destaillats, H.; Hodgson, A.T.; Lunden, M.M.; Weschler, C.J.; Nazaroff, W.W. Indoor secondary pollutants from cleaning product and air freshener use in the presence of ozone. Atmos. Environ. 2006, 40, 6696–6710. [Google Scholar] [CrossRef]
  25. The Environmental Law Institute; The Children’s Environmental Health Network. Reducing Environmental Expsoures in Child Care Facilities: A Review of State Policy; The Children’s Environmental Health Network: Washington, DC, USA, 2015; pp. 1–153. [Google Scholar]
  26. Bradman, A.; Gaspar, F.; Castorina, R.; Tong-Lin, E.; Mckone, T. Environmental Exposures in Early Childhood Education Environments. Available online: https://ww2.arb.ca.gov/sites/default/files/classic//research/apr/past/08-305.pdf (accessed on 15 November 2020).
  27. Thickett, K.M.; McCoach, J.S.; Gerber, J.M.; Sadhra, S.; Burge, P.S. Occupational asthma caused by chloramines in indoor swimming-pool air. Eur. Respir. J. 2002, 19, 827–832. [Google Scholar] [CrossRef] [Green Version]
  28. PubChem. Chloramine. Available online: https://pubchem.ncbi.nlm.nih.gov/compound/Chloramine (accessed on 17 September 2021).
  29. Holm, S.M.; Leonard, V.; Durrani, T.; Miller, M.D. Do we know how best to disinfect child care sites in the United States? A review of available disinfectant efficacy data and health risks of the major disinfectant classes. Am. J. Infect. Control 2019, 47, 82–91. [Google Scholar] [CrossRef] [Green Version]
  30. PubChem. Formaldehyde. Available online: https://pubchem.ncbi.nlm.nih.gov/compound/712 (accessed on 17 September 2021).
  31. Holt, K.A.; Pediatrics, A.A.O. Bright Futures: Nutrition; American Academy of Pediatrics: Itasca, IL, USA, 2011. [Google Scholar]
  32. Bello, A.; Quinn, M.M.; Perry, M.J.; Milton, D.K. Quantitative assessment of airborne exposures generated during common cleaning tasks: A pilot study. Environ. Health 2010, 9, 76. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  33. Beamer, P.; Castano, A.; Leckie, J. Vertical profile particulate matter measurements in a California daycare. Indoor Air 2002, 1, 103–108. [Google Scholar]
  34. Branco, P.T.; Nunes, R.A.; Alvim-Ferraz, M.C.; Martins, F.G.; Sousa, S.I. Children’s exposure to indoor air in urban nurseries—Part II: Gaseous pollutants’ assessment. Environ. Res. 2015, 142, 662–670. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  35. St-Jean, M.; St-Amand, A.; Gilbert, N.L.; Soto, J.C.; Guay, M.; Davis, K.; Gyorkos, T.W. Indoor air quality in Montréal area day-care centres, Canada. Environ. Res. 2012, 118, 1–7. [Google Scholar] [CrossRef] [PubMed]
  36. Hwang, S.H.; Seo, S.; Yoo, Y.; Kim, K.Y.; Choung, J.T.; Park, W.M. Indoor air quality of daycare centers in Seoul, Korea. Build. Environ. 2017, 124, 186–193. [Google Scholar] [CrossRef]
  37. Ruotsalainen, R.; Jaakkola, N.; Jaakkola, J.J.K. Ventilation and indoor air quality in Finnish daycare centers. Environ. Int. 1993, 19, 109–119. [Google Scholar] [CrossRef]
  38. Oklahoma Department of Human Services. Licensing Requirements for Family Child Care Homes and Large Child Care Homes. Available online: http://www.okdhs.org/OKDHS%20Publication%20Library/86-104.pdf (accessed on 20 November 2020).
  39. Bello, A.; Quinn, M.M.; Perry, M.J.; Milton, D.K. Characterization of occupational exposures to cleaning products used for common cleaning tasks—A pilot study of hospital cleaners. Environ. Health 2009, 8, 11. [Google Scholar] [CrossRef] [Green Version]
  40. Sisson, S.B.; Salvatore, A.L.; Hildebrand, D.; Poe, T.; Merchant, C.; Slawinski, M.; Kracht, C.L.; Stoner, J.A.; Alcala Lazarte, N.; Schneider, L.A.F.; et al. Interventions to promote healthy environments in family child care homes in Oklahoma-Happy Healthy Homes: Study protocol for a randomized controlled trial. Trials 2019, 20, 541. [Google Scholar] [CrossRef] [Green Version]
  41. Children’s Environmental Health Network. Eco-Healthy Child Care Checklist. Available online: https://cehn.org/wp-content/uploads/2015/11/EHCC-Checklist-Home-Print-3.2016-Final.pdf (accessed on 17 July 2017).
  42. United States National Institute of Environmental Health Sciences. Consumer Product Information Database Health Effects of Consumer Products. Available online: https://www.whatsinproducts.com/ (accessed on 6 June 2021).
  43. United States National Institute of Health. GHS Classification. Available online: https://pubchem.ncbi.nlm.nih.gov/ghs/ (accessed on 15 September 2021).
  44. United States National Library of Medicine. ChemIDplus. Available online: https://chem.nlm.nih.gov/chemidplus/ (accessed on 20 March 2021).
  45. United States Environmental Protection Agency. Learn about the Safer Choice Label. Available online: https://www.epa.gov/saferchoice/learn-about-safer-choice-label (accessed on 10 October 2021).
  46. Harley, K.G.; Calderon, L.; Nolan, J.E.S.; Maddalena, R.; Russell, M.; Roman, K.; Mayo-Burgos, S.; Cabrera, J.; Morga, N.; Bradman, A. Changes in Latina Women’s Exposure to Cleaning Chemicals Associated with Switching from Conventional to “Green” Household Cleaning Products: The LUCIR Intervention Study. Environ. Health Perspect. 2021, 129, 97001. [Google Scholar] [CrossRef]
  47. Reynolds, P.; Von Behren, J.; Gunier, R.B.; Goldberg, D.E.; Hertz, A.; Smith, D.F. Childhood cancer incidence rates and hazardous air pollutants in California: An exploratory analysis. Environ. Health Perspect. 2003, 111, 663–668. [Google Scholar] [CrossRef] [Green Version]
  48. Al-Hemoud, A.; Al-Awadi, L.; Al-Khayat, A.; Behbehani, W. Streamlining IAQ guidelines and investigating the effect of door opening/closing on concentrations of VOCs, formaldehyde, and NO2 in office buildings. Build. Environ. 2018, 137, 127–137. [Google Scholar] [CrossRef]
Figure 1. Chemical designation criteria for chemical ingredients found in cleaning products reported by family child care home (FCCH) providers. This information was adapted from the United Nation’s Global Harmonized System of Classification and Labelling of Chemicals found at: https://unece.org/transport/standards/transport/dangerous-goods/ghs-rev9-2021 (accessed on 2 March 2020).
Figure 1. Chemical designation criteria for chemical ingredients found in cleaning products reported by family child care home (FCCH) providers. This information was adapted from the United Nation’s Global Harmonized System of Classification and Labelling of Chemicals found at: https://unece.org/transport/standards/transport/dangerous-goods/ghs-rev9-2021 (accessed on 2 March 2020).
Ijerph 19 04299 g001
Table 1. Participant characteristics, Happy Healthy Homes (n = 50), Oklahoma, 2017–2018.
Table 1. Participant characteristics, Happy Healthy Homes (n = 50), Oklahoma, 2017–2018.
Provider CharacteristicsMean (SD)
Age (years) 144 (12.6)
n (%)
Female50 (100)
Hispanic, Latino/a, or of Spanish origin 2
Yes2 (4.35)
No44 (95.65)
Race 3
White26 (60.47)
Black or African American15 (34.88)
American Indian or Alaska Native2 (4.65)
Highest level of education 4
High school graduate or GED4 (8.16)
Some college or vocational training31 (63.27)
4-year college graduate or higher14 (28.57)
Degree in early childhood education or development 5
Yes15 (31.25)
No33 (68.75)
Household income 6
USD 15,000 to 34,9999 (20.45)
USD 35,000 to 49,9998 (18.18)
USD 50,000 to 74,9999 (20.45)
USD 75,000 or more18 (40.91)
Program CharacteristicsMean (SD)
Years FCCH in business11 (9.6)
Number of children in care9.5 (4.2)
Number of children in care ≤ 5 years old6.8 (3.6)
Number of hours spend cleaning FCCH each day3.2 (2.6)
n (%)
Renting building used for FCCH12 (24.00)
FCCH building built before 197818 (36.00)
Children in care have asthma 7
Yes18 (36.73)
No14 (28.57)
Don’t know17 (34.69)
1 n = 6 missing; 2 n = 4 missing; 3 n = 7 missing; 4 n = 1 missing; 5 n = 2 missing; 6 n = 6 missing; 7 n = 1 missing.
Table 2. Top cleaning products reported by family child care home providers and product’s intended use, Happy Healthy Homes, Oklahoma, 2017–2018.
Table 2. Top cleaning products reported by family child care home providers and product’s intended use, Happy Healthy Homes, Oklahoma, 2017–2018.
Product Brand NameCleaner 1Sanitizer 2Disinfectant 3Total FCCHs (n = 48) 4
Clorox Bleach 1, Concentrated, Regular XX21 (43.75)
Young Living Thieves Essential Oil InfusedX 6 (12.50)
Clorox Performance Bleach 2 with Cloromax XX5 (10.42)
Pine-Sol Multi-Surface Cleaner, OriginalX 4 (8.33)
Clorox Disinfecting Wipes 1 (Citrus and Fresh Blend) X4 (8.33)
Lysol All Purpose Cleaner, Complete Clean, Lemon Breeze/Cherry Blossom and Pomegranate, Pump SprayX 4 (8.33)
Lysol brand III Disinfectant Spray, Citrus Meadows/Crisp Linen Scent, Aerosol X4 (8.33)
Clorox Bleach Wipes, 35 Count Canister X3 (6.25)
Dawn Ultra Dishwashing Liquid, Original ScentX 3 (6.25)
Bona Hardwood Floor Cleaner Refill Soft PackageX 2 (4.17)
Clorox Commercial Solutions Clean-Up Cleaner + Bleach, Pump Spray, Professional UseXXX2 (4.17)
Clorox Splash-Less Bleach, Concentrated, Clean LinenXXX2 (4.17)
Lysol All-Purpose CleanerX 2 (4.17)
Lysol Disinfecting Wipes, Lemon and Lime Blossom X2 (4.17)
Member’s Mark Disinfecting Wipes Fresh ScentXXX2 (4.17)
Mr. Clean Multi-Purpose Cleaner with Gain Original Fresh ScentX 2 (4.17)
Pinalen Original Multi-Purpose CleanerX 2 (4.17)
Pine-Sol Multi-SurfaceX X2 (4.17)
Clorox Clean-Up Cleaner with Bleach, Original/Fresh Scent, Pump SprayX X2 (4.17)
Great Value Disinfectant Spray (citrus/fresh linen scent) X2 (4.17)
1 Cleaners defined by the US EPA remove dirt and organic matter from surfaces using detergents; 2 Sanitizers defined by the US EPA kill bacteria on surfaces using chemicals; 3 Disinfectants are defined by the US EPA kills viruses and bacteria on surfaces using chemicals; Definitions found at: https://www.epa.gov/coronavirus/whats-difference-between-products-disinfect-sanitize-and-clean-surfaces (accessed on 12 August 2021); 4 n = 2 missing.
Table 3. Chemical designation and class of chemical ingredients found in products reported by family child care home providers, Happy Healthy Homes, Oklahoma, 2017–2018.
Table 3. Chemical designation and class of chemical ingredients found in products reported by family child care home providers, Happy Healthy Homes, Oklahoma, 2017–2018.
Chemical DesignationCAS No.Chemical IngredientChemical ClassificationTotal Products (n = 132)Total FCCHs (n = 48) 1
Sensitizer 2 n (%)n (%)
141-43-5MonoethanolamineVolatile organic compound1 (0.76)1 (2.08)
7647-01-0Hydrochloric acidInorganic substance1 (0.76)1 (2.08)
Irritant 3
000079-14-1Hydroxy acetic acidOrganic compound4 (3.03)4 (8.33)
068081-81-2Sodium dodecylbenzene sulfonateHydrogen carbons4 (3.03)4 (8.33)
000629-25-4Sodium laurateOrganic compound2 (1.52)2 (4.17)
007722-84-1Hydrogen peroxideInorganic substance2 (1.52)2 (4.17)
68037-49-0Sodium 1-tetradecanesulfonateHydrocarbon2 (1.52)2 (4.17)
001300-72-7Sodium xylene sulfonateHydrocarbon1 (0.76)1 (2.08)
100-79-8Isopropylidene glycerolHeterocyclic compound1 (0.76)1 (2.08)
107-21-1Ethylene glycolAlcohols1 (0.76)1 (2.08)
111-76-2Ethylene glycol monobutyl etherAlcohols1 (0.76)1 (2.08)
1336-21-6Ammonium hydroxideAmmonia1 (0.76)1 (2.08)
151-21-3Sodium lauryl sulfateAlcohols1 (0.76)1 (2.08)
7647-01-0Hydrochloric acidInorganic substance1 (0.76)1 (2.08)
87-90-1Trichloroisocyanuric acidHeterocyclic compound1 (0.76)1 (2.08)
Reactive 4
068424-85-1Alkyl(C12-16) dimethyl benzyl ammonium chlorideQuaternary ammonium compounds11 (8.33)11 (22.92)
085409-23-0n-Alkyl (68% C12, 32% C14) dimethyl ethyl benzyl ammonium chlorideQuaternary ammonium compounds7 (5.30)7 (14.58)
068989-01-5Benzenemethanaminium, N, N-dimethyl-N-tetradecyl-, saccharinateQuaternary ammonium compounds6 (4.55)6 (12.50)
000770-35-4Propylene glycol phenyl etherAlcohols5 (3.79)5 (10.42)
063449-41-2C8-18-Alky dimethyl benzyl ammonium chloridesQuaternary ammonium compounds5 (3.79)5 (10.42)
068081-81-2Sodium dodecylbenzene sulfonateHydrogen carbons4 (3.03)4 (8.33)
025155-30-0Benzenesulfonic acidOrganic compound2 (1.52)2 (4.17)
026062-79-3Polyquaternium-6Quaternary ammonium compounds2 (1.52)2 (4.17)
001300-72-7Sodium xylene sulfonateHydrocarbon1 (0.76)1 (2.08)
001328-53-6Phthalocyanine greenHeterocyclic compound1 (0.76)1 (2.08)
026172-55-4MethylchloroisothiazolinoneOrganic compound1 (0.76)1 (2.08)
027176-87-0Dodecyl benzene sulfonic acidHydrocarbon1 (0.76)1 (2.08)
3844-45-9FD&C BlueHydrocarbon1 (0.76)1 (2.08)
68391-01-5n-Alkyl (60% C14, 30% C16, 5% C12, 5% C18) dimethyl benzyl ammonium chlorideQuaternary ammonium compounds1 (0.76)1 (2.08)
89-83-8ThymolPhenols1 (0.76)1 (2.08)
Carcinogen 5
068424-85-1Alkyl(C12-16) dimethyl benzyl ammonium chlorideQuaternary ammonium compounds11 (8.33)11 (22.92)
1 n = 2 missing; 2 Chemicals that may cause allergy or asthma symptoms or breathing difficulties if inhaled, as defined by the Global Harmonization System (GHS) hazard code H334 on the chemical’s safety data sheet (SDS); 3 Chemicals may cause irritation to the respiratory tract, as defined by GHS hazard code H335 on the chemical’s SDS; 4 Chemicals with a double bonded carbon in its molecular structure that may make it highly reactive with other substances in the air to produce secondary air pollutants; 5 Chemicals may cause cancer, as defined by the GHS hazard code H350 and H350i on the chemical’s SDS.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Querdibitty, C.D.; Wetherill, M.S.; Sisson, S.B.; Williams, B.; Aithinne, K.; Seo, H.; Inhofe, N.R.; Campbell, J.; Slawinski, M.; Salvatore, A.L. Cleaning Products Commonly Used in Oklahoma Family Child Care Homes: Implications for Respiratory Risk and Children’s Health. Int. J. Environ. Res. Public Health 2022, 19, 4299. https://doi.org/10.3390/ijerph19074299

AMA Style

Querdibitty CD, Wetherill MS, Sisson SB, Williams B, Aithinne K, Seo H, Inhofe NR, Campbell J, Slawinski M, Salvatore AL. Cleaning Products Commonly Used in Oklahoma Family Child Care Homes: Implications for Respiratory Risk and Children’s Health. International Journal of Environmental Research and Public Health. 2022; 19(7):4299. https://doi.org/10.3390/ijerph19074299

Chicago/Turabian Style

Querdibitty, Cassandra D., Marianna S. Wetherill, Susan B. Sisson, Bethany Williams, Kan Aithinne, Haeyn Seo, Nancy R. Inhofe, Janis Campbell, Megan Slawinski, and Alicia L. Salvatore. 2022. "Cleaning Products Commonly Used in Oklahoma Family Child Care Homes: Implications for Respiratory Risk and Children’s Health" International Journal of Environmental Research and Public Health 19, no. 7: 4299. https://doi.org/10.3390/ijerph19074299

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop