Figure 2: Dust concentration (mg/m3 ), ventilation rate (m3/ pig h), temperature (°C), and relative humidity dust p ig 1) he n 2) origi n o tin g without bedding battery bedding from •/. % •/. feed 8 0 -9 080 -9 0n.r. bedding --5 5 -6 8an im a ls 5 -1 1 2 -1 2 m an u re n.r. OOiao1i

1991 ◽  
Vol 71 (2) ◽  
pp. 271-277 ◽  
Author(s):  
M. Butera ◽  
J. H. Smith ◽  
W. D. Morrison ◽  
R. R. Hacker ◽  
F. A. Kains ◽  
...  

In order to assess the effects of ventilation rate, temperature, relative humidity and source of air on bioaerosol levels and dust with particle size < 10 μm, a total of 120 pigs housed in 12 pens in two separate rooms were used. Pigs averaged 30 kg initially and the trials were discontinued when 20% of the pigs were marketed. A six-stage Andersen sampler and a light scattering particle counter were used to determine bioaerosols and respirable dust (0.1–10 μm), respectively. Total bioaerosols were assessed using Trypticase Soy Agar. Potato Dextrose Agar was used for fungal aeorsols and Baird-Parker Agar used for isolation of Staphylococcus aureus. Moulds amounted to less than 1% of total microorganisms. Gram positive bacteria made up 72% of the bacterial isolates. Respirable dust was not correlated with respirable bioaerosols. Ventilation rate (2, 5 or 8 changes h−1) did not affect bioaerosol level or respirable dust. Total bioaerosols were significantly reduced (P < 0.05) in higher temperatures only. Relative humidity did not influence total bioaerosols but in one series respirable bioaerosols were significantly (R = 0.53) (P < 0.05) correlated with RH. Total bioaerosols were not different in outside air or attic air. Key words: Dust, bioaerosols, pigs, ventilation


2020 ◽  
Author(s):  
Mytien Nguyen ◽  
Eric C. Holmes ◽  
Largus T. Angenent

AbstractWeatherization of residential homes is a popular retrofit procedure to improve the energy efficiency of older homes by reducing building leakage. It is a vital tool in the fight against climate change. Several studies have evaluated the effect of weatherization on indoor pollutants such as formaldehyde and radon, but few studies have evaluated the effect of weatherization on indoor particulates and microbial exposure. In this study, we compared the effect of change in building leakage on indoor pollutants and bacterial communities in weatherized compared to non-weatherized single-family residential homes in New York State. Nine weatherized and eleven non-weatherized single-family homes in Tompkins County, New York were sampled twice: before and after the weatherization procedures for case homes, and at least 3 months apart for control homes that were not weatherized. We found a significant increase in both indoor-outdoor temperature ratio and living-area- and basement-radon levels of weatherized homes compared to control homes. The indoor-outdoor relative humidity ratio significantly decreased in weatherized compared to control homes. The indoor microbiome also became less similar to the outdoor community after weatherization. Compared to the changes in ventilation rate, temperature, relative humidity, and occupancy, the change in season was a more predictive measure of indoor bacterial concentration. Ventilation rate reduction from weatherization procedures led to an increase in indoor radon levels, as well as a warmer and less humid indoor environment. However, it did not affect indoor particulate mass concentration or indoor airborne bacteria load, and did only marginally affect the microbiome composition of residential homes. Finally, we found that changes in airborne bacterial load are more sensitive to shifts in season, whereas radon levels are more sensitive to ventilation rate.


1961 ◽  
Vol 16 (3) ◽  
pp. 413-420 ◽  
Author(s):  
C. W. Suggs ◽  
W. E. Splinter

The heart rate, ventilation rate, oxygen consumption rate, and mechanical efficiency responses of a subject to a series of temperatures, relative humidities, and workloads were observed. A quadratic prediction equation of each of the responses as steady-state functions of the independent variables was derived. Each of the equations represents a four-dimensional hypersurface. For the heart rate, ventilation rate, and oxygen consumption rate the hypersurfaces are quite similar, the responses increasing rapidly with respect to workload and about one-third as rapidly with respect to temperature. The effect of relative humidity was present primarily as interactions. Mechanical efficiency was represented by a more complex hypersurface. In three dimensions, with relative humidity as a parameter, the response was a saddle-shaped surface with the highest efficiency at a condition of low temperature, high workload. At constant environment, the heart rate responses of 19 subjects to workloads was observed and found to be linear with a normal distribution of slopes. Submitted on May 2, 1960


2020 ◽  
Vol 172 ◽  
pp. 07008
Author(s):  
Martin Morelli ◽  
Eva Møller ◽  
Thor Hansen

A recently Danish study reported that no vapour barrier is needed in ceilings, if the attic is well ventilated and the ceiling towards the dwelling is airtight. Based on that study, new investigations were initiated with focus on the hygrothermal behaviour in ventilated attics with different air change rates. A test house with three sets of four different ceiling constructions – all airtight – was used in this study. The ventilation rate was reduced in two of the sets with approx. 35 % and 50 %, respectively. Air change rates were measured with tracer gas. Furthermore, temperature and relative humidity was measured every hour. Measurements in similar ceilings with mineral wool or cellulose-based insulation material show that hygroscopic properties of the insulation have very limited effect on relative humidity. Furthermore, only at low ventilation rate the effect of a vapour barrier could be measured with minor impact. Based on the short-measured period the calculations of the risk of mould growth showed no risk. The results indicate that even when the ventilation is reduced by 50 %, the ventilated attic still performs well if the ceiling is highly airtight. However, the importance of vapour barriers becomes more important at lower air change rates.


2021 ◽  
Author(s):  
Sarah Buet

<p><b>A common goal amongst building practitioners is to create warmer, healthier, and drier houses. A key barrier to this is the presence of excessive moisture, the leading cause of mould growth within buildings. New Zealand Building Code Clause E3 ‘Internal Moisture’ has been set out to control internal moisture within a house, however, there is currently no prescribed method which practitioners can use to demonstrate compliance. Tools such as ASHRAE Standard 160 ‘Criteria for Moisture Control Design Analysis in Buildings’ can be used to predict internal conditions; however, studies have shown that such tools rely upon a range of possibly inappropriate assumptions and may not give accurate results. When looking specifically at ASHRAE Standard 160, the Indoor Design Temperature and Indoor Design Humidity application requires assumptions such as the presence of heating systems, a minimum heating setpoint, ventilation rates, and moisture generation rates of occupants. This research aimed to understand whether, considering the assumptions it makes, can ASHRAE Standard 160 be used in New Zealand to predict mould growth? It went on further to understand how the results produced by ASHRAE Standard 160 aligned with measured data?</b></p> <p>Using the yearlong records of New Zealand houses' external conditions (temperature and relative humidity) collected from the 2015 Pilot Housing Survey, two ‘Design Parameters’, the Indoor Design Temperature and Indoor Design Humidity (Simplified and Intermediate Method), were applied from ASHRAE Standard 160. These two ‘Design Parameters’ were the only two parameters assessed due to the limitations of the data that was able to be used from the Pilot Housing Survey. Other ‘Design Parameters’ in ASHRAE Standard 160 include exposure conditions and material properties, as well as a Full Parameter Calculation of Indoor Design Humidity, however, there was insufficient information from the 2015 Pilot Housing Survey to compare these parameters to. Having applied the Indoor Design Temperature and Indoor Design Humidity formula, year-long records of the same houses' internal conditions (temperature and relative humidity) were then used to identify discrepancies between the measured data and the theoretical conditions developed by ASHRAE Standard 160.</p> <p>To understand how discrepancies may be occurring, it was important first to understand the assumptions that ASHRAE Standard 160 is making when applying the Indoor Design Temperature and Indoor Design Humidity formula. The five most critical assumptions that these two ‘Design Parameter’ were implementing were:• A minimum heating setpoint of 21.1°C would be applied whenever the running 24- hour average outdoor temperature dropped below 18.3°C.</p> <p>• Under the Simplified Indoor Design Humidity, the indoor relative humidity was closely dependent on the running 24-hour average outdoor temperature.</p> <p>• The number of occupants in a house was dependant on the number of bedrooms within the house.</p> <p>• Each occupant generates approximately 3L per day.</p> <p>• The buildings' infiltration is either 0.2 ACH for a standard construction or 0.1 ACH foran airtight construction.</p> <p>Having compared and analysed the measured indoor conditions and the conditions outlined by ASHRAE Standard 160, a number of discrepancies became evident. This in turn suggested that the above assumptions that ASHRAE Standard 160 made in order to apply Indoor Design Temperature and Indoor Design Humidity (Simplified and Intermediate Method) are not reflective of New Zealand. The key conclusions from this research were:• The minimum heating setpoint of 21.1°C is not applicable in New Zealand houses.</p> <p>Instead, the application of the To24h + 2.8°C formula across all outdoor temperatures was favourable. Alternatively, further research could suggest a more applicable minimum heating setpoint for New Zealand.</p> <p>• Overall the Simplified Indoor Design Humidity is a more suitable method of determining the Indoor Design Humidity than the Intermediate Indoor Design HumidityIt was found that overall, the Simplified Indoor Design Humidity matched the measured indoor relative humidity better than the Intermediate Indoor Design Humidity. This was concluded to be due to the fact that the assumptions in the Intermediate Indoor Design Humidity did not reflect the reality of New Zealand houses. However, there is the possibility for the Intermediate Indoor Design Humidity to be altered to reflect the reality of New Zealand houses better.</p> <p>• The Intermediate Indoor Design Humidity parameters are altered to reflect the reality of New Zealand houses better.</p> <p>This research identified that the two main parameters, Design Moisture Generation and Design Ventilation Rate, do not reflect how New Zealanders occupy their houses. By undertaking further research into refining these parameters, the application of the Intermediate Indoor Design Humidity may become more suitable for New Zealand.</p> <p>Having identified discrepancies and the reasons for these discrepancies, this research began to investigate areas in which further research could improve the suitability of ASHRAE Standard 160 in New Zealand. This included additional information such as occupant moisture generation rates and any significant renovations on the houses, being gathered in future Pilot Housing Surveys. Further analysis could be undertaken on inputs such as the Moisture generation Rate and the Design Ventilation Rate by gathering this additional information. This in turn would allow for the alternative inputs to be analysed to understand how these ‘Design Parameters’ could be altered to reflect the reality of New Zealand houses better.</p>


2021 ◽  
Vol 2069 (1) ◽  
pp. 012209
Author(s):  
C Legros ◽  
A Piot ◽  
M Woloszyn ◽  
M Pailha

Abstract The use of hygroscopic materials indoors has a significant impact on the hygrothermal balance of a room air. It affects both the temperature and the relative humidity. Numerical tools still lack of accuracy in predicting these parameters and some discrepancies are observed between their predictions and experimental measurements. It may be caused by the model itself or by incorrect inputs data (materials properties, occupancy schedule, ventilation rate, etc…) Therefore, an experimental study has been carried out at the room scale under real climate to obtain an experimental dataset as a basis for numerical comparisons. The hygrothermal parameters of the room air have been measured for different loads while all the inputs (heat and moisture generation, air exchange and materials properties) have been properly quantified. This article presents the experimental setup and some of the experimental data obtained.


emission of dust-borne odourants like volatile fatty acids (VFA) and simple phenols and indoles from piggeries, the impor­ tance of particle-borne odours, and the possibilities of con­ trolling dust-borne odours. 2. ORIGIN, NATURE AND RELEASE OF THE DUST It is estimated that the dust in animal houses originates mainly from the feed (15 ), (16 ), (17 ), the bedding material (18), (19), the manure (20) and the animals themselves (21),(22). Relevant values are rare. Table I shows that feed and bedding, when used, are the predominant sources of dust in pig and hen houses. Dust from animal houses consists mainly of organic matter (23). The preferred technique for investigating both the mate­ rial composition of the dust and feed stuff is the WEENDER An­ alysis Technique (24). Table II shows the composition of dust from pig and hen houses compared to the feed fed. The differ­ ences in the protein content between dust and feed support the opinion that an important part of the dust originates from feathers, hairs, and skin cells of the animals. The release of the dust is caused by the activity of ani­ mals or man or the function of technical equipments in the an­ imal house. Feeding, particularly dry feeding (25), as well as bedding and cleaning activities, the use of different systems of feed distribution, manure removal and ventilation (26) can increase the dust level in the air of animal houses consider­ ably (27). Figure 1 gives an example of the relation between the amount of dust in the air and different activities based on values as reported by CERMAK and ROSS (27) for poultry houses. In the course of a day the dust level in animal houses varies considerably. Mostly feeding increases the dust concen­ tration in the air as demonstrated in Figure 2 (22). However, within 30 to 120 min the "normal" background level is reached again (16),(22). The figure shows that even before the feed is distributed, the activity of the animals increases the dust concentration in the air considerably. Table III shows the influence of rel . humidity, pen vol­ ume, feeding system and air flow on the number of dust parti­ cles and weight of settled dust in an experimental piggery.The essential influence of animal activity on the formation of dust is shown by the fact that self-feeding results in significant­ ly greater atmospheric dust concentration (particles/volume of air) than does floor-feeding. However, a significantly greater amount of settled dust is associated with floor feeding. Prob­ ably, the self-fed pigs spend much more time eating than the floor-fed pigs. The intense activity of the pigs during floor feeding results in a great deal of visible dust for only a pe­ riod of time, while the self-fed pigs may play with the excess feed (28),(17). These studies indicate that the factors deter­ mining the amount of dust in confinements include animal ac­ tivity, temperature, relative humidity, ventilation rate,stock­ ing density and volumetric air-space per animal, feeding method, and nature of feed. This dust originating from various sources can carry gases, vapours and odours (7).


2014 ◽  
Vol 1000 ◽  
pp. 342-345 ◽  
Author(s):  
Jan Richter ◽  
Kamil Staněk ◽  
Filip Havlik ◽  
Jan Růžička

Clay and earthen materials are highly hygroscopic and thus able to effectively adsorb and release moisture from their surroundings. This paper analyses the ability of rammed earth to stabilize internal course of relative humidity. A numerical hygrothermal model is introduced and validated using a set of measured data according to IEA Annex 41. The model is then used to determine the stabilization effect of rammed earth in a residential room with defined moisture sources and ventilation rate. The simulation is performed for gypsum boards, concrete and red brick as well and a clear comparison is made. The results show that the rammed earth can most effectively moderate the indoor air humidity variations; followed by concrete, gypsum boards, and red brick.


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