Indoor exposure control

The specimen has no specified size. Specimens for this test may consist of any standard fabricated test specimen or cut/punch pieces of sheet or machined sample. Specimens are mounted outdoors on racks slanted at 45° and facing south. It is recommended that concurrent exposure be carried out in many varied climates to obtain the broadest, most representative total body of data. Sample specimens are kept indoors as controls and for comparison. Reports of weathering describe all changes noted, areas of exposure, and period of time. 

In 1985, Berteau and Mengle (1985) of the California Department of Health Services and Maddy of the Department of Food and Agriculture conducted a preliminary review of pesticides used indoors. They noted several cases (six) from the Pesticide Illness Surveillance system in which illness was reported after structural pest control. Hypothetical exposure estimates for infants, children, and adults following label use for propoxur, DDVP, and chlorpyrifos were sometimes greater than toxic levels. In 1987, Berteau et al. (1989) reiterated the concern about the potential magnitude of indoor exposures, particularly for children. 

This study was conducted to evaluate and compare ADD determined using whole-body dosimetry with results of two situational exposure studies conducted following use of a flea fogger under natural conditions. Chlorpy-rifos was selected due to its general availability as a fogger for indoor flea control. Chlorpyrifos is poorly absorbed by the dermal route and readily cleared from the body in urine (Nolan et al., 1984). Trichloropyridinol was measured in 24-hr urine specimens of the volunteers and was converted to chlorpyrifos equivalents as a measure of absorbed dose. The study provided an opportunity to determine the relationship between intensive, high-contact dosimetry studies and the amounts of chlorpyrifos absorbed by two sets of adults who re-entered fogger-treated homes. 

Bioavailability from Environmental Media. Diazinon can be absorbed following inhalation, dermal, or oral exposures. Absorption through the skin is of major concern for exposures of farmers, farm workers, commercial applicators, or homeowners related to the use of diazinon as an insecticide or nematocide (Davis et al. 1983). Absorption via inhalation is a major concern particularly with respect to indoor exposures to diazinon within 2 days postapplication of the compound as a pest control agent in commercial buildings and homes (Currie et al. 1990 Jackson and Lewis 1981 Lenhart and Kawamoto 1994 Williams et al. 1987). Additional information on the concentrations of diazinon in indoor air and in groundwater from domestic wells, particularly from environments near hazardous waste sites, is needed to determine the bioavailability of diazinon in these media. 

Ventilation is often adopted as a control measure to keep VOCs and C02 below specified threshold levels. The effect of operation of the ventilation system on spatial and temporal profiles is illustrated from two separate buildings. With adequate ventilation, the C02 levels are easily controlled within threshold levels. However, VOCs present a problem due to their build-up overnight between the time of ventilation shutdown after office hours and its reactivation in the morning just before occupancy. Purging the building as an effective means to reduce the exposure risks is discussed and illustrated. Some concluding remarks on other changes to indoor exposures are made at the end of the chapter. 

Indoors— Most indoor insect control is aimed at prevention or eradication of the pest problem while minimizing the exposure of humans and animals to chemicals. The most common application techniques are crack and crevice treatments, spot treatments, and fumigation of entire structures, commodities, or individual pieces of equipment. 

Present studies describe the findings in many 100s of control Hungarians who were healthy and were selected from environmental viewpoints, depending on outdoor and indoor exposures. 

The interest in understanding the mechanisms that control indoor air pollution is related to the effects of indoor exposure on human health. People in developed countries spend up to 90% of their time indoors. In addition, modem electrical appliances such as TVs, personal computers, electronic gaming units, or Internet suggest that people, especially children, spend more time in their homes today than... 

Over the past decades, positive associations between development of asthma and asthma attacks have been reported in children that have existing disease and exposure to ETS in the indoor environment. In contrast, data on the effects of ETS exposure on adults with asthma are limited. Hersoug et al. (2010) found that indoor exposure to ETS is associated with respiratory symptoms and diminished lung function in adults (Hersoug et al. 2010). Furthermore, in one recent 10-year cohort smdy, Polosa et al. (2011) revealed that cigarette smoking is an important predictor of asthma severity and poor asthma control (Polosa et al. 2011). 

ConsExpo 4.1. Based on exposure-relevant information for main categories of consumer products (children s toys, cleaning products, cosmetics, disinfectant products, do-it-yourself products, paint products, pest control products), estimates indoor exposure by adults and children. 

Hawthorne, A., et al. (1987) Models for estimating organic emissions from building materials formaldehyde example. Atmos. Environ. 21, No. 2. Lewis, R. G., et al. (1986) Monitoring for non-occupational exposure to pesticides in indoor and personal respiratory air. Presented at the 79th Annual Meeting of the Air Pollution Control Association, Minneapolis, MN. 

Deals with issues that affect the quality of our air and protection from exposure to harmful radiation. OAR de >el-ops national programs, technical policies, and regulations for controlling air pollution and radiation exposure. Areas of concern to OAR include indoor and outdoor air quality, stationaiy and mobile sources of air pollution, radon, acid rain, stratospheric ozone depletion, radiation protection, and pollution prevention. 

The different toxicity and bioavailability of Cr(III) and Cr(VI) are a public health concern and therefore require strict control. Cr(VI) is considered to be toxic and carcinogenic, especially for the respiratory tract. In occupational health, the OEL (Occupational Exposure Limits) for water soluble and certain water insoluble compounds in indoor air is set at 0.5 mg/m for Cr, 0.5 mg/m for Cr(III), and 0.05 mg/m for Cr(VI), reflecting the different toxicities of both species. 

Since ETS contains phenol, reducing the amount of smoking indoors will reduce phenol exposures. Household products and over-the-counter medications containing phenol should be stored out of reach of young children to prevent accidental poisonings and skin bums. Always store household chemicals in their original labeled containers. Never store household chemicals in containers that children would find attractive to eat or drink from, such as old soda bottles. Keep your Poison Control Center s number next to the phone. 

Sampling rates for the case of total boundary layer-control can be expected to be nearly independent of temperature, since both the diffusion coefficients in air, and the kinematic viscosity of air are only weak functions of temperature (Shoeib and Harner, 2002). This leaves the air-flow velocity as the major factor that can be responsible for the seasonal differences among sampling rates observed by Ockenden et al. (1998). The absence of large R differences between indoor and outdoor exposures may be indicative of membrane-control, but it may also reflect the efficient damping of high flow velocities by the deployment devices used for SPMD air exposures (Ockenden et al., 2001). 

Production, Import/Export, Use, and Release and Disposal. Currently, heptachlor use in the United States is limited to fire ant control in power transformers (EPA 1990b). However, because of former widespread use of heptachlor and the persistence of heptachlor epoxide, these compounds and their degradation products can still be found at low levels in indoor air, water, soil, and food. Disposal methods are well documented in the literature however, more current information would be useful. Information on historical disposal practices would be helpful in evaluating the potential for environmental contamination. More information on the volume of heptachlor used in fire ant control would be useful in estimating potential occupational exposure. 

Some carbonation tests have been reported on plain and air-entrained concretes using two aggregate types, where the depth of carbonation on indoor and atmospheric exposure for 5 years have been measured [40]. The results are given in Table 3.24. In all cases, the air-entrained mixes have shown less carbonation than similar controls, suggesting that air-entrained concrete should provide a better reinforcement protection in the long term. 

At the beginning of this book, we presented some discussion of health-based air quality standards. In the final chapter, which follows this one, the scientific bases of control measures for various pollutants are discussed. In between, the complex chemistry that occurs in both polluted and remote atmospheres, and that converts the primary pollutants into a host of secondary species, has been detailed. To provide further perspective on airborne gases and particles and human exposure levels, we briefly treat indoor air pollution in this chapter. As we shall see, for many species it is simply a question of emissions leading to elevated levels indoors. However, there is some chemistry that occurs in indoor atmospheres as well, and it is of interest to compare this to that occurring outdoors. 

SC 80-1 Hot Particles on the Skin Assessment of Exposures from Therapy Control of Indoor Radon... 

---