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1.
对家庭室内空气的细菌浓度,在不同时间段的分布进行了研究分析。采用平皿沉降法,测得结果:清晨7:00为强污染时,晚19:00为弱污染时。并对居室清扫方式提出建议,以促进生存空间的环境质量的改善。  相似文献   

2.
针对室内空气挥发性有机物测定方法的不足,本文采用预冷浓缩系统和气相色谱,质谱联用。建立了测定室内空气中39种挥发性有机物的分析方法,该方法采用苏码罐采样,经液氮预冷冻浓缩后,用心城由检测。该方法灵敏度高,操作简便、重现性好、准确度高,适用于室内空气中挥发性有机物的测定。  相似文献   

3.
分光光度法测定室内空气中甲醛的方法研究   总被引:12,自引:0,他引:12  
针对室内空气中甲醛的特点,在环境空气甲醛的测定方法—乙酰丙酮分光光度法(GB/T15516-95)的基础上,进一步优化了该方法的采样时间、采样流量、样品收集器等,使优化后的测定方法更加适应室内空气监测需要的准确性、简便性、快速性的特点。  相似文献   

4.
建立了扩散吸附管采样,热脱附仪和气相色谱联用测定室内空气中BTEX的监测分析方法,方法的最低检出限为0.0002mg/m3。该方法使用方便、便于携带、无需电源,且与传统的泵采样方法具有较好的可比性,适合于室内空气中BTEX的监测。  相似文献   

5.
阐述了对室内空气品质进行远程监测与评价的必要性,介绍了基于三层C/S模式的室内空气品质监测与评价系统的结构与工作流程,以及网络环境下三层C/S模式的实时监测系统的结构与功能,指出该系统为准确监测和科学评价室内空气质量提供了有力的工具和保障。  相似文献   

6.
关于我国氨室内空气质量评价标准的建议   总被引:7,自引:1,他引:7  
当前,室内空气污染已成为社会关注的热点问题,氨(NH3)含量高低是室内空气质量(IAQ)好坏的重要指示指标。文章通过分析氨(NH3)的理化特性、来源、毒理学研究和流行病学研究结果,在参考国外相关标准的基础上,结合我国的实际情况和目前污染水平,提出我国氨(NH3)室内空气质量三级标准建议值。  相似文献   

7.
活性炭法测量室内空气中氡浓度的影响因素研究   总被引:1,自引:0,他引:1  
探讨了各种因素对活性炭法测量室内空气中氡浓度的影响,并提出既能保证检测质量,又能符合工程检测需要、提高检测效率的检测条件范围。  相似文献   

8.
室内空气污染物中氨的测定分析方法探讨   总被引:2,自引:0,他引:2  
研究了(纳氏试剂比色法和次氯酸钠—水杨酸分光光度法)在室内空气监测中存在的问题,得出次氯酸钠—水杨酸分光光度法不适合于装修后有机物含量较高的室内空气监测的结论。同时,针对纳氏试剂比色法分别进行了不同采样时间、不同采样流量以及不同吸收瓶等条件下室内空气中氨的监测技术的研究,确定了室内空气中氨的最佳监测条件。  相似文献   

9.
空气中挥发性有机物(VOCs) 的监测方法研究   总被引:11,自引:4,他引:11  
建立了热脱附仪和气相色谱-质谱联用测定室内空气和环境空气中35种挥发性有机污染物的分析方法,方法的最低检出限为0.1~0.9μg/m3, 20μg/m3挥发性有机物标准经6次的重复测定,其相对标准偏差小于8.4%.该方法已用于室内空气和环境空气的测定,取得令人满意的结果.  相似文献   

10.
随着社会经济的高速发展,人们的生活水平不断提高,在追求居住环境、办公环境的美观舒适的同时,各种各样的装修带来的一系列的室内空气污染问题.光触媒作为一种新兴的治理室内空气污染的催化剂逐渐被人们认可和接受.  相似文献   

11.
Direct-reading aerosol measurement usually uses the optical properties of airborne particles to detect and measure particle concentration. In the case of occupational hygiene, mass concentration measurement is often required. Two aerosol monitoring methods are based on the principle of light scattering: optical particle counting (OPC) and photometry. The former analyses the light scattered by a single particle, the latter by a cloud of particles. Both methods need calibration to transform the quantity of scattered light detected into particle concentration. Photometers are simpler to use and can be directly calibrated to measure mass concentration. However, their response varies not only with aerosol concentration but also with particle size distribution, which frequently contributes to biased measurement. Optical particle counters directly measure the particle number concentration and particle size that allows assessment of the particle mass provided the particles are spherical and of known density. An integrating algorithm is used to calculate the mass concentration of any conventional health-related aerosol fraction. The concentrations calculated thus have been compared with simultaneous measurements by conventional gravimetric sampling to check the possibility of field OPC calibration with real workplace aerosols with a view to further monitoring particle mass concentration. Aerosol concentrations were measured in the food industry using the OPC GRIMM? 1.108 and the CIP 10-Inhalable and CIP 10-Respirable (ARELCO?) aerosol samplers while meat sausages were being brushed and coated with calcium carbonate. Previously, the original OPC inlet had been adapted to sample inhalable aerosol. A mixed aerosol of calcium carbonate and fungi spores was present in the workplace. The OPC particle-size distribution and an estimated average particle density of both aerosol components were used to calculate the mass concentration. The inhalable and respirable aerosol fractions calculated from the OPC data are closely correlated with the results of the particle size-selective sampling using the CIP 10. Furthermore, the OPC data allow calculation of the thoracic fraction of workplace aerosol (not measured by sampling), which is interesting in the presence of allergenic particles like fungi spores. The results also show that the modified COP inlet adequately samples inhalable aerosol in the range of workplace particle-size distribution.  相似文献   

12.
In the metropolitan area of S?o Paulo, Brazil, ozone and particulate matter (PM) are the air pollutants that pose the greatest threat to air quality, since the PM and the ozone precursors (nitrogen oxides and volatile organic compounds) are the main source of air pollution from vehicular emissions. Vehicular emissions can be measured inside road tunnels, and those measurements can provide information about emission factors of in-use vehicles. Emission factors are used to estimate vehicular emissions and are described as the amount of species emitted per vehicle distance driven or per volume of fuel consumed. This study presents emission factor data for fine particles, coarse particles, inhalable particulate matter and black carbon, as well as size distribution data for inhalable particulate matter, as measured in March and May of 2004, respectively, in the Janio Quadros and Maria Maluf road tunnels, both located in S?o Paulo. The Janio Quadros tunnel carries mainly light-duty vehicles, whereas the Maria Maluf tunnel carries light-duty and heavy-duty vehicles. In the Janio Quadros tunnel, the estimated light-duty vehicle emission factors for the trace elements copper and bromine were 261 and 220 microg km(-1), respectively, and 16, 197, 127 and 92 mg km(-1), respectively, for black carbon, inhalable particulate matter, coarse particles and fine particles. The mean contribution of heavy-duty vehicles to the emissions of black carbon, inhalable particulate matter, coarse particles and fine particles was, respectively 29, 4, 6 and 6 times higher than that of light-duty vehicles. The inhalable particulate matter emission factor for heavy-duty vehicles was 1.2 times higher than that found during dynamometer testing. In general, the particle emissions in S?o Paulo tunnels are higher than those found in other cities of the world.  相似文献   

13.
Sediments are disturbed by wind frequently, especially in the shallow lakes. The characteristics of resuspended sediment particles in Taihu Lake were studied under different wind velocities. It showed that sediment particles suspended obviously and particle number in overlying water increased directly under high wind-induced disturbance. Suspended solid (SS) concentration was less than 50 mg/l when the wind velocity was below 3.0 m/s, however, it increased to more than 300 mg/l when the wind velocity was 10.0 m/s. Two methods were used to measure the fractal characteristics of particles. One was light scattering and the other was image analysis. The three-dimensional fractal dimensions of suspended particles, measured by light scattering, were between 2.26 and 2.44; correspondingly, the two-dimensional fractal dimensions, calculated by image analysis, were between 1.44 and 1.77. Moreover, the three-dimensional fractal dimensions were directly proportional to two-dimensional fractal dimensions. The characteristic length of particles was calculated by image analysis. The minimum characteristic length was close to 8.5 μm when the wind velocity was 1.5 m/s at 50 cm beneath lake surface, while, the maximum characteristic length was approximate to 24 μm when the wind velocity was 10 m/s at the depth of 150 cm.  相似文献   

14.
空气净化器可有效改善雾霾天气下室内空气质量,颗粒物去除效果与洁净空气量(CADR)是衡量其性能的主要参数。在典型室内环境下,以香烟源颗粒物为目标,开展空气扰动对净化器去除颗粒物效果和CADR的影响实验与评价分析。结果显示,在室内空气扰动下,净化器对粒径≥5μm的颗粒物去除率为75.6%,在无空气扰动情况下的去除率为46.6%。空气净化器对粒径0.3μm^5μm的颗粒物有较好的去除效果,而对于粒径10μm的较大颗粒物,空气扰动造成CADR增加。空气扰动在一定程度上提升了空气净化器的净化能力,同时在性能方面也存在影响。  相似文献   

15.
The use of hydrated magnesium carbonate hydroxide (magnesia alba) for drying the hands is a strong source for particulate matter in indoor climbing halls. Particle mass concentrations (PM10, PM2.5 and PM1) were measured with an optical particle counter in 9 indoor climbing halls and in 5 sports halls. Mean values for PM10 in indoor climbing halls are generally on the order of 200-500 microg m(-3). For periods of high activity, which last for several hours, PM10 values between 1000 and 4000 microg m(-3) were observed. PM(2.5) is on the order of 30-100 microg m(-3) and reaches values up to 500 microg m(-3), if many users are present. In sports halls, the mass concentrations are usually much lower (PM10 < 100 microg m(-3), PM2.5 < or = 20 microg m(-3)). However, for apparatus gymnastics (a sport in which magnesia alba is also used) similar dust concentrations as for indoor climbing were observed. The size distribution and the total particle number concentration (3.7 nm-10 microm electrical mobility diameter) were determined in one climbing hall by an electrical aerosol spectrometer. The highest number concentrations were between 8000 and 12 000 cm(-3), indicating that the use of magnesia alba is no strong source for ultrafine particles. Scanning electron microscopy and energy-dispersive X-ray microanalysis revealed that virtually all particles are hydrated magnesium carbonate hydroxide. In-situ experiments in an environmental scanning electron microscope showed that the particles do not dissolve at relative humidities up to 100%. Thus, it is concluded that solid particles of magnesia alba are airborne and have the potential to deposit in the human respiratory tract. The particle mass concentrations in indoor climbing halls are much higher than those reported for schools and reach, in many cases, levels which are observed for industrial occupations. The observed dust concentrations are below the current occupational exposure limits in Germany of 3 and 10 mg m(-3) for respirable and inhalable dust. However, the dust concentrations exceed the German guide lines for work places without use of hazardous substances. In addition, minimizing dust concentrations to technologically feasible values is required by the current German legislation. Therefore, substantial reduction of the dust concentration is required.  相似文献   

16.
Until 2009, the limit values for airborne sulfuric acid in Europe were based on the inhalable particle fraction (e.g. MAK (Maximum allowed concentration at workplace) value 0.1 mg m(-3) as the inhalable fraction). With the publication of the Commission Directive 2009/161/EU, an Indicative Occupational Exposure Limit Value (IOELV) of 0.05 mg m(-3) for sulfuric acid aerosols was based for the first time on the thoracic particle fraction. To permit a comparison of the measured values for the inhalable fraction with those of the thoracic fraction and to quantify the thoracic fraction, a cyclone was fabricated out of sulfuric-acid-resistant stainless steel that achieves suitable collection characteristics (PM(10)) at a flow rate of 5.34 L min(-1). 49 measurements were carried out in parallel in 21 companies. At concentrations well below the IOELV, there is little difference between the thoracic and inhalable particle concentrations. At higher concentrations (>0.1 mg m(-3) inhalable aerosol), larger droplets have a marked effect on the measured values and the thoracic fraction accounts for only 32.1 ± 12.5% of the inhalable fraction. The EU's IOELV and the proposal of the MAK Commission therefore provide a comparable level of protection. In the transposition of the IOELV into national law, an air limit of 0.1 mg m(-3) could therefore be implemented for the inhalable fraction.  相似文献   

17.
Inhalable sampler efficiency depends on the aerodynamic size of the airborne particles to be sampled and the wind speed. The aim of this study was to compare the behaviour of three personal inhalable samplers for welding fumes generated by Manual Metal Arc (MMA) and Metal Active Gas (MAG) processes. The selected samplers were the ones available in Spain when the study began: IOM, PGP-GSP 3.5 (GSP) and Button. Sampling was carried out in a welding training center that provided a homogeneous workplace environment. The static sampling assembly used allowed the placement of 12 samplers and 2 cascade impactors simultaneously. 183 samples were collected throughout 2009 and 2010. The range of welding fumes' mass concentrations was from 2 mg m(-3) to 5 mg m(-3). The pooled variation coefficients for the three inhalable samplers were less than or equal to 3.0%. Welding particle size distribution was characterized by a bimodal log-normal distribution, with MMADs of 0.7 μm and 8.2 μm. For these welding aerosols, the Button and the GSP samplers showed a similar performance (P = 0.598). The mean mass concentration ratio was 1.00 ± 0.01. The IOM sampler showed a different performance (P < 0.001). The mean mass concentration ratios were 0.90 ± 0.01 for Button/IOM and 0.92 ± 0.02 for GSP/IOM. This information is useful to consider the measurements accomplished by the IOM, GSP or Button samplers together, in order to assess the exposure at workplaces over time or to study exposure levels in a specific industrial activity, as welding operations.  相似文献   

18.
沈阳市室内空气细菌与真菌粒子的关系   总被引:3,自引:0,他引:3  
用ANDERSEN生物粒子采样器和平皿沉降法观测了室内空气细菌和真菌粒子浓度、浓度分布、粒度分布、粒数中值直径和沉降量.结果表明,室内空气细菌粒子浓度为真菌粒子浓度的2.5倍,细菌粒数中值直径为真菌粒数中值直径的1.4倍,细菌粒子沉降量为真菌粒子沉降量的5,3倍。<8.2μm的空气细菌和真菌粒子浓度差别不大,而>8.2μm的空气细苗比真苗粒子浓度高4.1倍.<8.2μm的可吸入真菌粒数百分比大于<8.2μm的细菌粒数百分比.在一天的7:00时~22:00时,室内空气细菌和真菌粒子的浓度、沉降量均呈双峰变化;细苗和真菌粒子浓度的相关系数为0.822,细菌和真菌粒子沉降量的相关系数为0.896,均呈明显的正相关关系;细菌和真菌粒数中值直径的相关系数为-0.096,相关关系不大。  相似文献   

19.
The purpose of this study was to evaluate the level and composition of bacteria and fungi in the indoor air of an Italian office building equipped with a heating, ventilation and air conditioning (HVAC) system. Airborne bacteria and fungi were collected in three open-space offices during different seasons. The microbial levels in the outdoor air, supply air diffusers, fan coil air flow and air treatment unit humidification water tank were used to evaluate the influence of the HVAC system on indoor air quality (IAQ). A medium–low level of bacterial contamination (50–500 CFU/m3) was found in indoor air. Staphylococcus and Micrococcus were the most commonly found genera, probably due to human presence. A high fungal concentration was measured due to a flood that occurred during the winter. The indoor seasonal distribution of fungal genera was related to the fungal outdoor distribution. Significant seasonal and daily variation in airborne microorganisms was found, underlining a relationship with the frequency of HVAC system switching on/off. The results of this monitoring highlight the role of the HVAC system on IAQ and could be useful to better characterise bacterial and fungal population in the indoor air of office buildings.  相似文献   

20.
An investigation of the relationship between observed nickel aerosol exposures and urinary nickel excretion was undertaken at a Scandinavian nickel refinery. The goal of the study was to assess the impact of nickel aerosol speciation, the use of particle size-selective sampling instrumentation and adjustment of urinary levels for creatinine excretion on the usefulness of urinary nickel excretion as a marker for exposure. Urinary nickel measurements and paired 'total' and inhalable aerosol exposure measurements were collected each day for one week from refinery workers in four process areas. The mean observed urinary nickel concentration was 12 micrograms L-1 (11 micrograms of Ni per g of creatinine). The strongest relationships between urinary excretion and aerosol exposure were found when urinary nickel levels were adjusted for creatinine excretion and when exposure to only soluble forms of nickel aerosol was considered. No significant difference was observed between measures of 'total' and inhalable aerosol in the ability to predict urinary excretion patterns. In the light of these results, it is recommended that consideration be given to the chemical species distribution of nickel aerosol in the use of urinary nickel measurements as a screening tool for cancer risk in occupationally-exposed populations.  相似文献   

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