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ABSTRACT: The role of natural aeroallergen exposure in modulating allergen-specific immune responses is not well understood.
We sought to examine relationships between mouse allergen exposure and mouse-specific immune responses.
New employees (n = 179) at a mouse facility underwent repeated assessment of mouse allergen exposure, skin prick tests (SPTs), and measurement of mouse-specific IgG levels. Relationships between the mean level of exposure, variability of exposure (calculated as log deviation), and time to development of immunologic outcomes were examined by using Cox proportional hazards models.
By 24 months, 32 (23%) participants had experienced a positive SPT response, and 10 (8%) had mouse-specific IgG₄. The incidence of a positive SPT response increased as levels of exposure increased from low to moderate, peaking at 1.2 ng/m³, and decreased beyond this point (P = .04). The more variable the exposure was across visits, the lower the incidence of a positive SPT response (hazard ratio [HR], 0.17; 95% CI, 0.07-0.41). Variability of exposure was an independent predictor of a positive SPT response in a model that included both exposure metrics. In contrast, the incidence of mouse-specific IgG₄ increased with increasing levels of mouse allergen exposure (HR, 2.9; 95% CI, 1.4-6.0), and there was evidence of a higher risk of mouse-specific IgG₄ with greater variability of exposure (HR, 6.3; 95% CI, 0.4-95.2).
Both the level and variability of mouse allergen exposure influence the humoral immune response, with specific patterns of exposure associated with specific immunophenotypes. Exposure variability might be a more important predictor of a positive SPT response, whereas the average exposure level might be a more important predictor of mouse-specific IgG₄.
The Journal of allergy and clinical immunology 06/2011; 128(2):390-396.e7. · 9.17 Impact Factor
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ABSTRACT: This study assessed mouse allergen exposure across a range of jobs, including non-mouse handling jobs, at a mouse facility. Baseline data from 220 new employees enrolled in the Jackson Laboratory (JAXCohort) were analyzed. The baseline assessment included a questionnaire, allergy skin testing, and spirometry. Exposure assessments consisted of collection of two full-shift breathing zone air samples during a 1-week period. Air samples were analyzed for mouse allergen content, and the mean concentration of the two shifts represented mouse allergen exposure for that employee. The mean age of the 220 participants was 33 years. Ten percent reported current asthma and 56% were atopic. Thirty-eight percent were animal caretakers, 20% scientists, 20% administrative/support personnel, 10% materials/supplies handlers, and 9% laboratory technicians. Sixty percent of the population handled mice. Eighty-two percent of study participants had detectable breathing zone mouse allergen, and breathing zone mouse allergen concentrations were 1.02 ng/m³ (0.13-6.91) (median [interquartile range (IQR)]. Although mouse handlers had significantly higher concentrations of breathing zone mouse allergen than non-handlers (median [IQR]: 4.13 ng/m³ [0.69-12.12] and 0.21 ng/m³ [below detection (BD)-0.63], respectively; p < 0.001), 66% of non-handlers had detectable breathing zone mouse allergen. Mouse allergen concentrations among administrative/support personnel and materials/supplies handlers, jobs that generally do not entail handling mice, were median [IQR]: 0.23 ng/m³ [BD-0.59] and 0.63 ng/m³ [BD-18.91], respectively. Seventy-one percent of administrative/support personnel, and 68% of materials/supplies handlers had detectable breathing zone mouse allergen. As many as half of non-mouse handlers may have levels of exposure that are similar to levels observed among mouse handlers.
Journal of Occupational and Environmental Hygiene 12/2010; 7(12):726-34. · 1.19 Impact Factor
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Peyton A Eggleston
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ABSTRACT: Pediatric asthma has many causes and can manifest differently in different children and at different times. Understanding the many factors related to the development and exacerbation of asthma is complicated by the complexity of the many environmental exposures related to asthma development and morbidity. Furthermore, the same environmental exposures that may cause increased symptoms at 1 point in time may be protective when the exposure occurs earlier or at high enough levels. We know that environmental exposures such as allergens, irritants, and pollutants are quite complex in their composition; further examination of this complexity may improve our understanding of this complex and highly prevalent disease.
PEDIATRICS 03/2009; 123 Suppl 3:S160-7. · 4.47 Impact Factor
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ABSTRACT: Guidelines recommend allergen avoidance for patients with allergic asthma, but direct measurements of home allergen levels are not available to most physicians. Parent report of indoor allergen exposure is a potentially convenient and inexpensive surrogate measure of exposure, although validity of parent report to estimate indoor allergen levels is not well established.
To determine if parent-reported pest and pet exposures can identify patients with clinically relevant allergen exposure.
Parents of 300 inner-city children completed a survey about pests (cockroaches and mice) and furred pets (dogs and cats). Settled dust samples were obtained for Bla g 1, Mus m 1, Can f 1, and Fel d 1 from kitchens and bedrooms.
Parent reports were associated with clinically relevant levels of Bla g 1, Mus m 1, Can f 1, and Fel d 1 (P < .001 for all). For example, when parents reported cockroaches were present, 86% of homes had settled dust Bla g 1 levels of 1 U/g or higher, and when they reported mice were present, 90% had Mus m 1 levels greater than 500 ng/g. Report of pets was also predictive of clinically meaningful allergen levels. Parent-reported absence of pets provided assurance that allergen levels were below relevant thresholds (negative predictive value, 80%-98%). However, parent-reported absence of pests did not provide assurance of low levels of these allergens (negative predictive value, 38%-75%).
Since direct measurement of indoor allergens is not always feasible, especially in the inner city, parent report of pests and pets may be sufficient to recommend environmental control practices for sensitized children. Negative parent reports of pests are not sufficient evidence of low pest allergen exposure.
Annals of allergy, asthma & immunology: official publication of the American College of Allergy, Asthma, & Immunology 12/2008; 101(5):517-23. · 2.83 Impact Factor
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ABSTRACT: Prior studies have related community violence to depression among children, but few studies have examined this relationship among adults. We hypothesized that victimization, awareness, and fear of neighborhood violence would increase the odds of depression among adult caregivers of children with asthma. We surveyed caregivers in the Baltimore Indoor Environment Study of Asthma in Kids (BIESAK), USA. The primary outcome was screening positive for depression on the Center for Epidemiological Studies Depression index. We assessed victimization, awareness, and fear of neighborhood violence, and conducted spatial analysis identifying subject homes within 500 ft of a homicide to validate survey measures of neighborhood violence. A multilevel logistic model with clustering by neighborhood estimated odds ratios and 95% confidence intervals. Survey responses about fear of neighborhood violence were strongly predicted by having a home within 500 ft of a homicide. Of 150 caregivers of children with asthma, 49% were aware of a neighborhood violent event, 36% were fearful of neighborhood violence, 22% reported victimization, and 27% had a homicide within 500 ft of the home. In our multilevel model, fear of violence increased the odds of depression by 6.7. Victimization was associated with a possible trend towards depression, and awareness of neighborhood violence did not increase the odds of depression. Based on our findings, personal experience with neighborhood violence may be more important than simple awareness. Health care workers should consider screening for depression among patients exposed to community violence.
Social Science [?] Medicine 08/2008; 67(1):31-7. · 2.70 Impact Factor
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ABSTRACT: Asthma disproportionately affects inner-city, minority children in the U.S. Outdoor pollutant concentrations, including particulate matter (PM), are higher in inner-cities and contribute to childhood asthma morbidity. Although children spend the majority of time indoors, indoor PM exposures have been less extensively characterized. There is a public health imperative to characterize indoor sources of PM within this vulnerable population to enable effective intervention strategies. In the present study, we sought to identify determinants of indoor PM in homes of Baltimore inner-city pre-school children. Children ages 2-6 (n=300) who were predominantly African-American (90%) and from lower socioeconomic backgrounds were enrolled. Integrated PM(2.5) and PM(10) air sampling was conducted over a 3-day period in the children's bedrooms and at a central monitoring site while caregivers completed daily activity diaries. Homes of pre-school children in inner-city Baltimore had indoor PM concentrations that were twice as high as simultaneous outdoor concentrations. The mean indoor PM(2.5) and PM(10) concentrations were 39.5+/-34.5 and 56.2+/-44.8 microg/m(3), compared to the simultaneously measured ambient PM(2.5) and PM(10) (15.6+/-6.9 and 21.8+/-9.53 microg/m(3), respectively). Common modifiable household activities, especially smoking and sweeping, contributed significantly to higher indoor PM, as did ambient PM concentrations. Open windows were associated with significantly lower indoor PM. Further investigation of the health effects of indoor PM exposure is warranted, as are studies to evaluate the efficacy of PM reduction strategies on asthma health of inner-city children.
Environmental Research 03/2008; 106(2):148-55. · 3.40 Impact Factor
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Peyton A Eggleston
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ABSTRACT: Poor, minority children living in US inner cities have increased rates of asthma morbidity and mortality. Factors that contribute to these increased rates are varied and complex, with current evidence suggesting that the environment is an important causative factor. Respiratory morbidity is often the result of allergens and air pollutants. Additionally, for children living in urban environments, underlying societal susceptibility factors specific to the inner city serve to increase asthma morbidity. Even though ambient pollutants have been declining in US cities, asthma morbidity and mortality rates have been increasing. Indoor pollutants are closely linked to increased asthma prevalence and morbidity. While the understanding of environmental influences is still relatively limited, we can say that indoor exposures are more important than ambient pollutants, and we know that bioaerosols containing allergenic proteins are especially important. Additionally, certain particulate aerosols and ozone cause inflammation individually and may act synergistically to enhance the acute and chronic IgE-mediated inflammation. The purpose of this article is to review the data relating exposure to environmental pollutants and airborne allergens, and the relationship of this exposure to asthma prevalence and morbidity in order to inform plans for public health programs to reduce an asthma burden.
Chest 12/2007; 132(5 Suppl):782S-788S. · 5.25 Impact Factor
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ABSTRACT: Factors predictive of future asthma must be identified among young inner-city children, who suffer disproportionately from asthma. We investigated whether current asthma control predicts future asthma-related health care use among inner-city preschool-aged children with asthma.
A total of 150 inner-city preschool-aged children with asthma were followed prospectively for 6 months. At baseline, symptom frequency and reliever-medication use were assessed to classify children into National Asthma Education and Prevention Program-derived control categories. Long-term controller-medication use was also assessed, as well as asthma-related health care use at baseline and at 3 and 6 months.
The mean age was 4.4 years, 92% were black, and 39% reported long-term controller use. At baseline, 37% were classified as having mild-intermittent, 17% had mild-persistent, 21% had moderate-persistent, and 25% had severe-persistent asthma control. Significant changes in asthma control were observed over time, including 46% of children originally categorized with mild-intermittent asthma who had worsened asthma control by 3 months. Asthma control significantly predicted future health care use 3 months later but not 6 months later. Multivariate analyses showed that, once control status was known, reported use of long-term controller medication added little additional predictive value.
Among inner-city preschool-aged children, significant fluctuations in asthma control occur as early as 3 months after assessment. Poor control but not long-term controller-medication use is an independent predictor of future asthma-related health care use at 3 months but is not significantly predictive of 6-month outcomes. Therefore, clinicians caring for inner-city children with asthma should consider reassessing asthma control at least every 3 months to identify those at highest future risk and to provide early interventions.
PEDIATRICS 12/2007; 120(5):e1174-81. · 4.47 Impact Factor
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ABSTRACT: Evidence for environmental causes of asthma is limited, especially among African Americans. To look for systematic differences in early life domestic exposures between inner-city preschool children with and without asthma, we performed a study of home indoor air pollutants and allergens.
Children 2-6 years of age were enrolled in a cohort study in East Baltimore, Maryland. From the child's bedroom, air was monitored for 3 days for particulate matter <or= 2.5 and <or= 10 microm in aerodynamic diameter (PM(2.5), PM(10)), nitrogen dioxide, and ozone. Median baseline values were compared for children with (n = 150) and without (n = 150) asthma. Housing characteristics related to indoor air pollution were assessed by caregiver report and home inspection. In addition, indoor allergen levels were measured in settled dust.
Children were 58% male, 91% African American, and 88% with public health insurance. Housing characteristics related to pollutant exposure and bedroom air pollutant concentrations did not differ significantly between asthmatic and control subjects [median: PM(2.5), 28.7 vs. 28.5 microg/m(3); PM(10), 43.6 vs. 41.4 microg/m(3); NO(2), 21.6 vs. 20.9 ppb; O(3), 1.4 vs. 1.8 ppb; all p > 0.05]. Settled dust allergen levels (cat, dust mite, cockroach, dog, and mouse) were also similar in bedrooms of asthmatic and control children.
Exposures to common home indoor pollutants and allergens are similar for inner-city preschool children with and without asthma. Although these exposures may exacerbate existing asthma, this study does not support a causative role of these factors for risk of developing childhood asthma.
Environmental Health Perspectives 11/2007; 115(11):1665-9. · 7.04 Impact Factor
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Journal of Allergy and Clinical Immunology 11/2007; 120(4):956-9. · 11.00 Impact Factor
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ABSTRACT: We conducted this study to compare environmental exposures in suburban homes of children with asthma to exposures in inner city homes of children with asthma, to better understand important differences of indoor pollutant exposure that might contribute to increased asthma morbidity in the inner city. Indoor PM(10), PM(2.5), NO(2), O(3), and airborne and dust allergen levels were measured in the homes of 120 children with asthma, 100 living in inner city Baltimore and 20 living in the surrounding counties. Home conditions and health outcome measures were also compared. The inner city and suburban homes differed in ways that might affect airborne environmental exposures. The inner city homes had more cigarette smoking (67% vs. 5%, p < .001), signs of disrepair (77% vs. 5%, p < .001), and cockroach (64% vs. 0%, p < .001) and mouse (80% vs. 5%, p < .001) infestation. The inner city homes had higher geometric mean (GM) levels (p < .001) of PM(10) (47 vs. 18 microg/m(3)), PM(2.5) (34 vs. 8.7 microg/m(3)), NO(2) [19 ppb vs. below detection (BD)], and O(3) (1.9 vs. .015 ppb) than suburban homes. The inner city homes had lower GM bedroom dust allergen levels of dust mite (.29 vs. 1.2 microg/g, p = .022), dog (.38 vs. 5.5 microg/g, p < .001) and cat (.75 vs. 2.4 microg/g, p = .039), but higher levels of mouse (3.2 vs. .013 microg/g, p < .001) and cockroach (4.5 vs. .42 U/g, p < .001). The inner city homes also had higher GM airborne mouse allergen levels (.055 vs. .016 ng/m(3), p = .002). Compared with the homes of suburban children with asthma, the homes of inner city Baltimore children with asthma had higher levels of airborne pollutants and home characteristics that predispose to greater asthma morbidity.
Journal of Urban Health 07/2007; 84(4):577-90. · 2.13 Impact Factor
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ABSTRACT: Although mouse allergen exposure is common in inner-city homes, little is known about the relationships between exposure and humoral immune responses to mouse allergen in this population.
To examine relationships between mouse allergen exposure and allergen-specific IgE and IgG responses in inner-city children with asthma.
Inner-city children with asthma underwent skin testing and venipuncture for determination of mouse allergen-specific IgE and IgG levels. Settled dust samples were collected from their homes for allergen analysis.
The study population (n = 112) was predominantly African American (92%) with a mean age of 4.4 years. The prevalence rate of mouse sensitization was 25% and did not consistently increase with increasing Mus m 1 levels. Instead, the prevalence rate was lowest among those exposed to <2 microg/g, increased among those exposed to 2-7.9 microg/g and 8-29.9 microg/g, and then decreased among participants exposed to >29.9 microg/g (14%, 20%, 40%, and 28%, respectively). Similarly, the prevalence rates of mouse allergen-specific IgG and IgG(4) did not increase across increasing exposure categories. Mouse allergen-specific IgG and IgG(4) were strongly associated with IgE sensitization (odds ratios [95% CI], 82.8 [20.5-334.4] and 50.4 [14.0-181.7], respectively).
High-level exposure to mouse allergen in children may be associated with attenuated humoral responses of all isotypes rather than selective attenuation of IgE.
Protection against allergic sensitization by high-dose allergen exposure may not be mediated by preferential production of IgG over IgE.
Journal of Allergy and Clinical Immunology 04/2007; 119(4):910-5. · 11.00 Impact Factor
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ABSTRACT: Room characteristics predicting indoor allergen exposure in suburban homes have not been clearly identified.
To examine relationships between room characteristics and concentrations of indoor allergens in homes of suburban asthmatic patients.
The homes of 339 asthmatic children ages 6 to 17 years were studied. Home inspections were conducted by a trained technician, and dust samples were analyzed for indoor allergen content. A high allergen concentration was defined as 8 microg (U)/g or more of fine dust.
Infrequent sheet washing and wall-to-wall carpet were risk factors for high bedroom dust mite concentrations. Infrequent sheet washing was also a risk factor for high Fel d 1 concentrations. Food remains in the bedroom was a risk factor for high bedroom Bla g 1 levels, and exposed food, leaks, and dirty pots were all risk factors for high kitchen Bla g 1 levels. The combination of lack of mattress or pillow encasements, infrequent sheet washing, and carpeting was associated with a 24-fold increase in odds of a high dust mite concentration (odds ratio [OR], 24.1; 95% confidence interval [CI], 3.2-181.4). Among non-cat owners, the combination of stuffed toys on the bed, lack of mattress or pillow encasements, and infrequent sheet washing was associated with a 49-fold increase in odds of a high Fel d 1 level (OR, 49.4; 95% CI, 2.8-887.3). The combination of leaks, exposed food, and dirty pots was associated with a high kitchen Bla g 1 concentration (OR, 10.6; 95% CI, 2.8-40.5).
Specific room characteristics predict high indoor allergen exposure among children with asthma, and a combination of these characteristics may further increase the risk of high allergen exposure.
Annals of allergy, asthma & immunology: official publication of the American College of Allergy, Asthma, & Immunology 12/2006; 97(5):628-35. · 2.83 Impact Factor
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ABSTRACT: Asthma guidelines recommend environmental control practices (ECPs) to improve asthma health. In the inner city, where asthma morbidity is high, it is not known whether children's health status affects the use of ECPs.
To investigate health status determinants of ECPs in the homes of children with asthma.
Caregivers of children aged 2 to 6 years with (n = 150) and without (n = 150) asthma completed a survey about ECPs. Atopic status was determined by means of skin prick testing.
Most ECPs were similarly practiced, regardless of whether the child had asthma. Only pet avoidance was more common in children with asthma (30% vs 19%). Asthma severity and recent acute health care visits for asthma were not associated with ECP use. Most ECPs were not linked to allergen sensitization (eg, mite and mouse), although cockroach-sensitized children were more likely to have cockroach control than nonsensitized individuals (65% vs 45%). Caregivers of asthmatic children with rhinitis were more likely than those without rhinitis to report ECPs, including pet avoidance (44% vs 15%), smoking avoidance (78% vs 53%), cockroach control (65% vs 42%), mouse control (78% vs 42%), air-conditioning (45% vs 24%), and allergyproof covers (7% vs 0%).
The presence of asthma, asthma severity, and allergen sensitization seem to have little relationship to ECP use in the homes of inner-city children. Rhinitis was consistently linked to ECPs, which suggests that caregivers may make changes in the home environment for upper airway but not lower airway symptoms.
Annals of allergy, asthma & immunology: official publication of the American College of Allergy, Asthma, & Immunology 10/2006; 97(3):409-17. · 2.83 Impact Factor
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ABSTRACT: Inner-city children experience disproportionate asthma morbidity, and suspected reasons include indoor environmental exposures.
To determine if mouse allergen exposure is a risk factor for asthma morbidity.
Preschool children with asthma were recruited from inner-city Baltimore, MD. Skin testing was performed and blood was collected at the baseline visit for quantification of mouse allergen specific IgE. A questionnaire evaluated symptoms, medication, and health care use at baseline, 3 months, and 6 months. A trained technician collected dust samples from the child's home for analysis of Mus m 1 at baseline, 3 months, and 6 months. Outcomes were compared between mouse-sensitized, highly exposed children and all other children.
A total of 127 children had complete data for mouse sensitization status and bedroom settled dust mouse allergen levels at baseline. The mean age of the children was 4.4 years, 92% were African American, and 26% were sensitized to mouse. Mouse-sensitized children exposed to higher levels of Mus m 1 (>0.5 microg/g) had 50% more days of symptoms (incidence rate ratio [IRR], 1.5; 95% confidence interval [CI], 1.1-2.1) and 80% more days of beta-agonist use than other children (IRR, 1.8; 95% CI, 1.3-2.5). Children in the sensitized and highly exposed group were also more likely to have an unscheduled physician visit (odds ratio [OR], 3.1; 95% CI, 1.6-6.3), emergency department visit (OR, 2.1; 95% CI, 1.1-4.1), and hospitalization (OR, 36.6; 95% CI, 4.1-327.3) than other children. These associations between mouse allergen exposure and asthma symptoms and morbidity remained statistically significant after adjusting for potential confounders, including atopy and cockroach sensitization and exposure.
In mouse-sensitized inner-city children, exposure to mouse allergen may be an important cause of asthma morbidity.
Annals of allergy, asthma & immunology: official publication of the American College of Allergy, Asthma, & Immunology 10/2006; 97(4):514-20. · 2.83 Impact Factor
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ABSTRACT: Limited data exist regarding extended, long-term immunologic effects of immunotherapy in polysensitized individuals. To study possible long-term effects, skin tests and specific IgE levels were obtained from subjects who had previously received broad-spectrum aeroallergen immunotherapy years before.
Eighty-two subjects (78% male, mean age 23 years) previously enrolled in a randomized, placebo-controlled trial of immunotherapy for treatment of childhood allergic asthma were reevaluated in adulthood (mean follow-up interval, 10.8 years) by puncture skin tests and CAP-RAST levels for major aeroallergens. All completed at least 18 months (median 27 months) of maintenance active treatment or placebo injections without subsequent immunotherapy.
At adult follow-up, 36% of all skin tests to treatment allergens among subjects who received immunotherapy (n = 41) had significantly reduced intensity versus 26% of skin tests among placebo recipients (n = 41; p = 0.03). No significant differences were noted for individual treatment allergens. No significant differences were observed in the long-term changes of serum-specific IgE antibody levels for all treatment allergens between immunotherapy treatment and placebo groups (p = 0.43). The treatment and placebo groups had a similar acquisition of new skin test sensitivities from time of randomization in the original childhood trial to debriefing (15 vs. 20%; p = 0.28) and to adult follow-up (30 vs. 31%; p = 0.75).
Immunotherapy suppresses skin test sensitivity 8-16 years after discontinuation of treatment, but long-term effects on specific IgE levels in serum are not observed. Broad-spectrum immunotherapy does not appear to affect the acquisition of new inhalant sensitivities.
International Archives of Allergy and Immunology 02/2006; 140(3):245-51. · 2.40 Impact Factor
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ABSTRACT: Asthma, traditionally characterized as reversible airway obstruction, might lead to structural changes and permanent impairment.
We sought to study the frequency, severity, and reversibility of pulmonary deficits in adults with a history of moderate-to-severe childhood allergic asthma.
Subjects (n = 121) previously enrolled in a randomized trial of immunotherapy for childhood asthma were recalled. Eighty-four young adults (age, 17-30 years; 78% male) were reevaluated by means of spirometry. Subjects with a postbronchodilator FEV1, forced vital capacity, or FEV1/forced vital capacity ratio less than or equal to the 5th percentile or 2 or more indices less than or equal to the 10th percentile (National Health and Nutrition Examination Survey III normative data) were invited to undergo complete pulmonary function testing, physical examination, and chest radiography after 1 week of 1 mg/kg daily prednisone.
Of 84 subjects reevaluated, 40 (48%) had one or more spirometric indices less than or equal to the 5th and 10th percentiles (P < .0001). Twenty-eight of the 40 subjects were reassessed after prednisone treatment, of whom 21 (75%) did not improve. Adult and childhood (age 5-12 years) spirometric results were positively correlated (r = 0.49-0.72, P < .001). Abnormal adult spirometric results were associated with a longer duration of asthma at enrollment in the original trial (4.6 vs 6 years, P=.02), increased childhood methacholine sensitivity (PC20, 0.11 vs 0.18 mg/mL; P = .01), and birth prematurity (adjusted odds ratio, 10.7; 95% CI, 1.4-84.5). Immunotherapy status was unrelated to adult lung function.
Many adults with a history of moderate-to-severe allergic asthma in childhood have irreversible lung function deficits. Childhood spirometry, duration of asthma, methacholine sensitivity, and birth prematurity might identify such individuals at a young age.
Journal of Allergy and Clinical Immunology 01/2006; 116(6):1213-9. · 11.00 Impact Factor
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Peyton A Eggleston,
Arlene Butz,
Cynthia Rand,
Jean Curtin-Brosnan,
Sukon Kanchanaraksa,
Lee Swartz,
Patrick Breysse,
Timothy Buckley,
Gregory Diette,
Barry Merriman,
Jerry A Krishnan
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ABSTRACT: Airborne pollutants and indoor allergens increase asthma morbidity in inner-city children; therefore, reducing exposure, if feasible, should improve asthma morbidity.
To conduct a randomized controlled trial of methods to reduce environmental pollutant and allergen exposure in the homes of asthmatic children living in the inner city.
After the completion of questionnaires, spirometry and allergen skin tests, home inspection, and measurement of home air pollutant and allergen levels, 100 asthmatic children aged 6 to 12 years were randomized to the treatment group (home-based education, cockroach and rodent extermination, mattress and pillow encasings, and high-efficiency particulate air cleaner) or to the control group (treated at the end of the 1-year trial). Outcomes were evaluated by home evaluations at 6 and 12 months, clinic evaluation at 12 months, and multiple telephone interviews.
In the treatment group, 84% received cockroach extermination and 75% used the air cleaner. Levels of particulate matter 10 microm or smaller declined by up to 39% in the treatment group but increased in the control group (P < .001). Cockroach allergen levels decreased by 51% in the treatment group. Daytime symptoms increased in the control group and decreased in the treatment group (P = .04). Other measures of morbidity, such as spirometry findings, nighttime symptoms, and emergency department use, were not significantly changed.
A tailored, multifaceted environmental treatment reduced airborne particulate matter and indoor allergen levels in inner-city homes, which, in turn, had a modest effect on morbidity.
Annals of allergy, asthma & immunology: official publication of the American College of Allergy, Asthma, & Immunology 12/2005; 95(6):518-24. · 2.83 Impact Factor
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ABSTRACT: The National Children's Study will address, among other illnesses, the environmental causes of both incident asthma and exacerbations of asthma in children. Seven of the Centers for Children's Environmental Health and Disease Prevention Research (Children's Centers), funded by the National Institute of Environmental Health Sciences and the U.S. Environmental Protection Agency, conducted studies relating to asthma. The design of these studies was diverse and included cohorts, longitudinal studies of older children, and intervention trials involving asthmatic children. In addition to the general lessons provided regarding the conduct of clinical studies in both urban and rural populations, these studies provide important lessons regarding the successful conduct of community research addressing asthma. They demonstrate that it is necessary and feasible to conduct repeated evaluation of environmental exposures in the home to address environmental exposures relevant to asthma. The time and staff required were usually underestimated by the investigators, but through resourceful efforts, the studies were completed with a remarkably high completion rate. The definition of asthma and assessment of disease severity proved to be complex and required a combination of questionnaires, pulmonary function tests, and biologic samples for markers of immune response and disease activity. The definition of asthma was particularly problematic in younger children, who may exhibit typical asthma symptoms sporadically with respiratory infections without developing chronic asthma. Medications confounded the definition of asthma disease activity, and must be repeatedly and systematically estimated. Despite these many challenges, the Children's Centers successfully conducted long-term studies of asthma.
Environmental Health Perspectives 11/2005; 113(10):1430-6. · 7.04 Impact Factor
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Peyton A Eggleston
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ABSTRACT: Homes cannot be made allergen free, but exposure to the major indoor allergens can be reduced. All reduction recommendations are based on the principle of reducing or isolating the source, and certain recommendations can be made on the basis of published evidence. House dust mite avoidance measures include fitting allergen-proof mattress and pillow encasings, washing bedding regularly, and reducing humidity. Furred pet avoidance requires removal of the pet form the home, followed by thorough and repeated cleaning; room air cleaners, washing the pet, and isolating the pet from a bedroom are ineffective alternatives. Cockroach allergen avoidance begins with effective pest control, followed by thorough and repeated cleaning; 1 to 2 months are required to eliminate roaches, and an additional 4 to 6 months are required to remove residual allergen. Once allergen levels have been reduced, continued efforts are necessary to maintain the home free of allergen sources.
Journal of Allergy and Clinical Immunology 08/2005; 116(1):122-6. · 11.00 Impact Factor
