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      Bystander Exposure to Ultra-Low-Volume Insecticide Applications Used for Adult Mosquito Management

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          Abstract

          A popular and effective management option for adult mosquitoes is the use of insecticides applied by ultra-low-volume (ULV) equipment. However, there is a paucity of data on human dermal exposure to insecticides applied by this method. The objective of the current study was to estimate dermal exposures to the insecticide active ingredient permethrin using water- (Aqua-Reslin ®) and oil-based (Permanone ® 30-30) formulations with passive dosimetry. No significant differences in deposition of permethrin were observed between years, distance from the spray source, front or back of the body, or the placement of the patches on the body. However, exposure to Aqua-Reslin was significantly greater than Permanone 30-30 and average concentrations deposited on the body were 4.2 and 2.1 ng/cm 2, respectively. The greater deposition of Aqua-Reslin is most likely due to the higher density of the water-based formulation which causes it to settle out faster than the lighter oil-based formulation of Permanone 30-30. The estimated average absorbed dermal exposure for permethrin from Aqua-Reslin and Permanone 30-30 was 0.00009 and 0.00005 mg/kg body weight, respectively. We also found that ground deposition of ULV insecticides can be used as a surrogate for estimating dermal exposure. The estimated exposures support the findings of previous risk assessments that exposure to ULV applications used for mosquito management are below regulatory levels of concern.

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          Epidemiologic Evaluation of Measurement Data in the Presence of Detection Limits

          Quantitative measurements of environmental factors greatly improve the quality of epidemiologic studies but can pose challenges because of the presence of upper or lower detection limits or interfering compounds, which do not allow for precise measured values. We consider the regression of an environmental measurement (dependent variable) on several covariates (independent variables). Various strategies are commonly employed to impute values for interval-measured data, including assignment of one-half the detection limit to nondetected values or of “fill-in” values randomly selected from an appropriate distribution. On the basis of a limited simulation study, we found that the former approach can be biased unless the percentage of measurements below detection limits is small (5–10%). The fill-in approach generally produces unbiased parameter estimates but may produce biased variance estimates and thereby distort inference when 30% or more of the data are below detection limits. Truncated data methods (e.g., Tobit regression) and multiple imputation offer two unbiased approaches for analyzing measurement data with detection limits. If interest resides solely on regression parameters, then Tobit regression can be used. If individualized values for measurements below detection limits are needed for additional analysis, such as relative risk regression or graphical display, then multiple imputation produces unbiased estimates and nominal confidence intervals unless the proportion of missing data is extreme. We illustrate various approaches using measurements of pesticide residues in carpet dust in control subjects from a case–control study of non-Hodgkin lymphoma.
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            Unidentified Inert Ingredients in Pesticides: Implications for Human and Environmental Health

            Background By statute or regulation in the United States and elsewhere, pesticide ingredients are divided into two categories: active and inert (sometimes referred to as other ingredients, adjuvants, or coformulants). Despite their name, inert ingredients may be biologically or chemically active and are labeled inert only because of their function in the formulated product. Most of the tests required to register a pesticide are performed with the active ingredient alone, not the full pesticide formulation. Inert ingredients are generally not identified on product labels and are often claimed to be confidential business information. Objectives In this commentary, we describe the shortcomings of the current procedures for assessing the hazards of pesticide formulations and demonstrate that inert ingredients can increase the toxicity of and potential exposure to pesticide formulations. Discussion Inert ingredients can increase the ability of pesticide formulations to affect significant toxicologic end points, including developmental neurotoxicity, genotoxicity, and disruption of hormone function. They can also increase exposure by increasing dermal absorption, decreasing the efficacy of protective clothing, and increasing environmental mobility and persistence. Inert ingredients can increase the phytotoxicity of pesticide formulations as well as the toxicity to fish, amphibians, and microorganisms. Conclusions Pesticide registration should require full assessment of formulations. Evaluations of pesticides under the National Environmental Policy Act, the Endangered Species Act, and similar statutes should include impact assessment of formulations. Environmental monitoring for pesticides should include inert ingredients. To enable independent research and risk assessment, inert ingredients should be identified on product labels.
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              Economic Cost Analysis of West Nile Virus Outbreak, Sacramento County, California, USA, 2005

              After its introduction into the eastern United States in 1999, West Nile virus (WNV) reached California in 2003 ( 1 ). In response, the state enhanced mosquito management programs to reduce vector populations and virus transmission ( 2 ). By late summer 2005, WNV disease was epidemic in Sacramento County, with more cases reported in Sacramento County than in any other county in the nation that year ( 3 ). The Sacramento-Yolo Mosquito and Vector Control District (SYMVCD) responded by conducting emergency aerial spraying over the city of Sacramento and surrounding areas to reduce mosquito populations. Effective management of infection rates, illness, and death from mosquito-borne pathogens such as WNV requires reduced contact between humans and infected mosquitoes ( 4 ). No effective treatment exists for WNV; prevention of disease relies on management of mosquitoes through various control tactics. Elnaiem et al. ( 5 ) and Carney et al. ( 6 ) examined the efficacy of the 2005 emergency aerial spray in Sacramento County, which used pyrethrins as the active ingredients to control adult mosquitoes. In both studies, an unsprayed area within the county was used as the control. Elnaiem et al. showed a total decrease in WNV-competent vector mosquitoes, Culex pipiens and Cx. tarsalis, of 57.5%, compared with the prespray population in the treated area ( 5 ). They also observed a decrease in WNV infection rates in mosquitoes to 3.9/1,000 for trapped females in the treated areas, compared with 6.7/1,000 in the untreated areas ( 5 ). Carney et al. used illness onset dates and residential locations for 152 of the 163 WNV disease cases reported in humans in 2005 to determine the efficacy of the spray event ( 6 ). Their results showed no incident human cases in the treated area after the spray event, compared with 18 cases in the untreated area. Consequently, the emergency aerial spray seemed to effectively reduce both mosquito populations ( 5 ) and human WNV cases ( 6 ). WNV infection can be asymptomatic or symptomatic in humans, with a 4:1 ratio ( 7 , 8 ). The disease can be mild, resulting in influenza-like symptoms (as in West Nile fever [WNF]), or severe, affecting the central nervous system symptom (as in West Nile neuroinvasive disease [WNND]) ( 7 ). Many WNF cases are not reported because they are not recognized as WNF; symptoms can resemble a cold or mild influenza-like illness, for which medical care is not sought, or is underdiagnosed because the additional cost of testing would not provide alternative direction to effective palliative medical care ( 7 , 9 ). Zohrabian et al. ( 10 ) estimated the economic impact of the WNV disease outbreak in 2002 in Louisiana, which resulted in 24 deaths. They included costs of inpatient and outpatient medical care, productivity loss, the state’s public health department, and vector control. Total epidemic costs were ≈$20.14 million for the 329 cases, including $9.2 million for mosquito control and public health agency costs. Zohrabian et al. ( 11 ) used the economic data from their 2004 study to determine the cost-effectiveness of the initiation of a potential WNV vaccination and found that the cost of vaccination would not offset the costs in medical care. Several studies have demonstrated the efficacy of mosquito management in response to WNV, but only the study by Carney et al. ( 6 ) suggested a reduction in human WNV cases associated with aerial adult-mosquito control. We estimated the economic cost of the 2005 WNV disease outbreak in Sacramento County, California, and evaluated the reduction in WNV disease necessary to offset the cost of emergency vector control. Economic costs for patients’ productivity loss and for treatment of disease symptoms, as well as for emergency vector control conducted in response to the outbreak were also investigated. Methods Medical Costs We estimated costs for the total number of Sacramento County WNV cases in 2005. Different costs were associated with WNF and the more severe WNND. The Centers for Disease Control and Prevention (CDC) summarizes the reported number of WNV cases for each state, including patient’s age, sex, date of onset, case reporting date, county of residence, diagnosis (WNF or WNND), and outcome (e.g., fatal). According to the CDC database for 2005, a total of 935 human WNV cases were reported in California, including 163 cases from Sacramento County ( 3 ). A total of 117 (71.8%) were diagnosed as WNF and 46 (28.2%) as WNND; 1 (0.6%) case was fatal. Forty-six (28.2%) patients were >60 years of age, and 2 (1.2%) were 60 years and 60 years of age who had WNND. We conservatively assumed an average of 50 work days missed ( 10 ) and 10 nonwork days missed (1 weekend day per week).Thus, total productivity loss was 60 days. For caretakers of WNND patients, productivity loss was assumed to be 25 days, and the associated cost was the value of a nonwork day missed ( 10 ). The cost attributed to productivity loss is an estimate; true monetary value for pain and distress and the productivity loss associated with chronic WNND are uncertain. WNF Assumed costs for treating WNF were those of a physician visit, a diagnostic test, and productivity loss during symptomatic WNF. We obtained the average costs for a physician visit for a diagnosis or treatment in the western United States from 2004 data ( 19 ) and updated to 2005, using the CPI ( 15 ) as discussed above. The CDC-approved diagnostic test for human WNV is an immunoglobulin (Ig)M and IgG ELISA for either serum or cerebrospinal fluid ( 7 ). According to CDC, an additional test is needed to indicate a false-positive result; however, our analysis assumed only costs for the initial diagnostic test. We obtained this value by contacting 4 laboratories suggested by the California Department of Public Health (C. Jean, pers. comm.) (ARUP Laboratories, Salt Lake City, UT, USA; Focus Diagnostics Inc., Cypress, CA, USA; Quest Diagnostics Inc., Madison, NJ, USA; and Specialty Laboratories, Valencia, CA, USA); the costs obtained were then averaged. Productivity loss for a missed day of work and a missed day of nonwork were calculated by using the methods detailed previously. We assumed 5 workdays missed because of WNF for persons 60 years of age. Cost of Mosquito Vector Control We obtained cost information for the 2005 emergency mosquito control aerial spray from SYMVCD. It included aerial ultra-low–volume adulticiding over 2 areas in Sacramento County comprising ≈477 km2 ( 6 ). Aerial spraying was conducted on 6 nights in early and mid-August ( 5 ). The event costs incorporated overtime hours for SYMVCD employees for August 2005. We calculated total overtime hours spent on the emergency spray using the difference between paid overtime hours for August 2005 and August 2004. Overtime hours for August 2005 were assumed to be additional hours to SYMVCD’s usual vector control program, including hours for additional prespray and postspray application mosquito trapping, plane preparation time, and preparation time for completing the spraying. These hours included time spent on other spray events and vector control procedures not directly involved in the emergency spray. However, our study incorporated total overtime hours for August to ensure conservatism. Total cost for the emergency spray also included outsource contracts (e.g., plane rental, pilot hours) and the insecticide used. Results Medical Costs for WNND A total of 46 WNND cases occurred in Sacramento County in 2005. Costs were ≈$33,143 per inpatient and ≈$6,317 per outpatient for all treatments (Table 2). Cost for each WNND patient estimated to have spent time in a nursing home was ≈$18,097. Productivity loss during symptomatic WNND cost $10,800 per patient 60 years of age (Table 3). Total medical costs accrued by all WNND patients was ≈$2,140,409; total costs for all cases (medical cost plus productivity loss) was ≈$2,844,338. Table 2 Estimated inpatient and outpatient economic costs of WNND cases, Sacramento County, California, 2005* Item Cost per case† No. cases to which cost applies‡ % Cases to which cost applies§ Total cost for all cases Total cost if treatment/service were used in all cases Inpatient treatment costs $33,143 46 100 $1,524,570 $1,524,570 Outpatient costs Cost per case¶ Outpatient hospital treatment $333 17 36 $5,668 $15,337 Physician visits $450 46 100 $20,708 $20,708 Outpatient physical therapy $909 46 100 $41,810 $41,810 Occupational therapy $4,037 3 7 $12,111 $185,699 Speech therapy $588 1 1 $588 $27,032 Total $80,885 $290,586 Nursing home costs Cost# Nursing home stay** $190 2 4 $36,195 $36,195 Transportation $65 46 100 $2,977 $2,977 Home health aides, babysitters, etc. $1,569 7 14 $10,983 $505,211 Total $50,154 $544,383 Total for WNND $2,140,409 $2,844,339 *WNND, West Nile neuroinvasive disease; BLS, Bureau of Labor Statistics of the US Department of Labor.
†Estimated by using 2005 data from California’s Office of Statewide Health Planning and Development (J. Teague and J. Morgan, pers. comm.).
‡WNND cases from the total number of cases reported by the Centers for Disease Control and Prevention ( 3 ).
§See ( 10 ).
¶Estimated by using data from Zohrabian et al. ( 10 ) and updated using data from the US Department of Labor’s Bureau of Labor Statistics (BLS) ( 13 – 15 ).
#Estimated by using data from MetLife Mature Market Institute ( 16 ), Zohrabian et al. ( 10 ), and BLS ( 13 – 15 ).
**Average length of nursing home stay was 96 days. Table 3 Estimated economic costs of WNND cases due to productivity loss, Sacramento County, California, 2005* Productivity loss Value of work day missed† Value of nonwork day missed‡ No. work days missed No. nonwork days missed No. patients % Cases Total costs for all cases 60 For patients 60 y $125 60 15 100 $112,500 For caretakers $125 25 8 4 26 $37,500 Total costs $484,800 *WNND, West Nile neuroinvasive disease.
†Estimated by using data from BLS ( 17 ).
‡Estimated by using data from Grosse ( 18 ) and BLS ( 17 ). We performed sensitivity analysis for medical treatment of WNND in which we had a range of values using 10,000 iterations. The hospitals’ CCRs contributed the largest amount of variance to the total cost (68.5%), followed by the average inpatient cost per WNND patient from the 2005 hospital patient discharge database from OSHPD (J. Teague and J. Morgan, pers. comm.) (31.4%), range $1,910,421–$7,770,354. Results were similar for the cost per WNND inpatient (range $13,201–$140,257) and the total medical cost for treating WNND. Medical Costs for WNF A total of 117 WNF cases were reported for Sacramento County in 2005. Treating each WNF patient cost ≈$167 for the diagnostic physician visit and ≈$135 for the diagnostic test. Productivity loss cost ≈$955 for each patient 60 years of age. The total cost for treating reported WNF cases was ≈$136,839 (Table 4). Table 4 Estimated economic impact for WNF cases (N = 117), Sacramento County, California, 2005* Item Cost No. patients by age, y Total cost 60 Physician visit for diagnosis or treatment in the western US, cost per case† $167 86 31 $19,539 Diagnostic tests, average cost per case‡ $135 Productivity loss Per work day missed§ Per nonwork day missed¶ Total individual cost# Value of a lost day $191 $125 $955 $625 $101,505 Total costs for WNF $136,839 *WNF, West Nile fever; BLS, Bureau of Labor Statistics, US Department of Labor.
†Estimated by using data from Brown and Beauregard ( 19 ) and BLS ( 15 ).
‡ELISA immunoglobulin (Ig) G and IgM serum and cerebrospinal fluid. Estimated by using laboratory list prices (ARUP Laboratories, Salt Lake City, UT, USA; Focus Diagnostics Inc., Cypress, CA, USA; Quest Diagnostics Inc., Madison, NJ, USA; Specialty Laboratories, Valencia, CA, USA).
§Estimated by using data from BLS ( 17 ).
¶Estimated by using data from Grosse ( 18 ) and BLS ( 17 ).
#Based on 5 workdays missed per person 60 y. Sensitivity analysis for the cost of treating WNF (range $132,008–$144,458) showed that the average cost for the diagnosis test contributed the largest amount of variance to the total cost (84.2%). The cost of a missed day of work for patients 18 cases ( 7 , 9 , 22 , 23 ). SYMVCD activities conducted before the emergency period most likely prevented some cases. Estimating the medical costs of WNV patients and the true number of cases prevented by the emergency spray are uncertain. The estimated dollar amount designated for productivity loss from WNV disease was based on the average annual salary of a Sacramento County citizen in 2005 and an estimated number of work days missed because of the disease. This study does not take into account extreme cases of WNND and total number of days a patient is affected by the disease. Therefore, the actual cost values associated with WNV may be higher. Our analysis may underestimate the actual cost of the WNV outbreak. Pain and distress are difficult to estimate monetarily but probably are important factors in the comprehensive costs of WNV disease. We also did not include medical costs associated with non-WNV issues, such as mosquito-bite allergenicity or sequelae, which are difficult to quantify but may be substantial ( 24 ). Additionally, we did not incorporate the benefits to the human population of reducing the nuisance of mosquito bites, irrespective of WNV transmission. In Jefferson County, Texas, the ratio of the cost of the total household benefit to the program cost for mosquito abatement was 1.8, according to a countywide study on the benefit of mosquito control in reducing the nuisance of mosquito bites ( 25 ). In addition, the actual number of persons affected with WNF remains unknown because the total number of WNF cases probably was underreported and underdiagnosed ( 7 , 9 ). Busch et al. ( 26 ) found 353 infections for each reported case of WNND in North Dakota from blood screening data in 2003 compared with CDC data indicating ≈256 WNV incident infections for each WNND case in the United States. We did not assess human and ecologic risks associated with the emergency spray. However, previous risk assessments that used exposure scenarios for pyrethroids and pyrethrins that would exceed those of the Sacramento County emergency aerial spray have shown risks substantially below Environmental Protection Agency levels of concern ( 27 – 34 ). The total economic impact of the 2005 WNV disease outbreak in Sacramento County was ≈$2.98 million. The total cost of medical treatment for the outbreak was $2.28 million. The actual number of WNV disease cases prevented by the emergency spray is uncertain. However, the offset in cost for the number of cases that may have been prevented can be compared with the costs of the vector control. If only 34 WNF and 14 WNND cases (by using the percentages of each from the diagnoses for Sacramento County in 2005) were prevented by the spray event, ≈$702,809 would have been averted in medical and productivity loss costs, thus offsetting the cost of the emergency spray. Also, the costs of the emergency spray would have been offset by preventing only 15 WNND cases at ≈$706,833.
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                Author and article information

                Journal
                Int J Environ Res Public Health
                101238455
                International Journal of Environmental Research and Public Health
                Molecular Diversity Preservation International (MDPI)
                1661-7827
                1660-4601
                June 2011
                14 June 2011
                : 8
                : 6
                : 2142-2152
                Affiliations
                Department of Land Resources and Environmental Sciences, Montana State University, 334 Leon Johnson Hall, Bozeman, Montana 59717, USA; E-Mails: cjpreftakes@ 123456gmail.com (C.J.P.); bpeterson@ 123456montana.edu (R.K.D.P.)
                Author notes
                [* ]Author to whom correspondence should be addressed; E-Mail: jerome.schleier@ 123456msu.montana.edu ; Tel.: +1-406-994-7927; Fax: +1-406-994-3933.
                Article
                ijerph-08-02142
                10.3390/ijerph8062142
                3138017
                21776222
                2cad92e6-75e5-4e24-8c7e-59a796d0b242
                © 2011 by the authors; licensee MDPI, Basel, Switzerland.

                This article is an open-access article distributed under the terms and conditions of the Creative Commons Attribution license ( http://creativecommons.org/licenses/by/3.0/).

                History
                : 26 April 2011
                : 4 June 2011
                : 9 June 2011
                Categories
                Article

                Public health
                dermal exposure,risk analysis,exposure assessment,pyrethroid,passive dosimetry
                Public health
                dermal exposure, risk analysis, exposure assessment, pyrethroid, passive dosimetry

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