增压站低频噪声识别与控制

目的解决天然气增压站低频噪声严重的问题,识别低频噪声源,并对低频噪声加以控制。方法结合压缩机组的实际工作情况及结构,首先利用频谱及1/3倍频程分析增压站机组的振动和噪声特性,初步确定压缩站机组低频噪声与机组振动的关系,进一步利用相干函数分析法分析振动与低频噪声的相干关系,判定低频噪声并不是由振动主要引起的。结果机组的主要噪声源为冷却器和压缩缸的进排气管,低频噪声污染主要是由于机组周期性吸排气时,管道和机组壁投射出的空气动力性噪声所造成的,而机组振源的剧烈振动不是产生低频噪声污染的主要原因。进排气管可产生高达80 d B(A)的全频带噪声,其中包含声压级可高达100 dB的次声,尤其以频率11 Hz和17 Hz为主,并且传播距离远,通透力强,对人员和环境危害大。结论首先依据进排气管为主要噪声源,其次结合压缩站实际情况,从压缩器机组整体的降噪设计及厂房治理的降噪设计两部分考虑提出相应的改进措施,从而为机组的降噪提供有效的方法。     

含弹内埋弹舱缩尺模型气动噪声特性研究

目的对含弹的内埋弹舱模型进行噪声仿真和试验研究。方法计算采用"CFD+CAA"的混合方法,采用DDES计算流场,基于M?hring声学类比方法得到测量点的噪声信息。采用该方法与空腔M219标准试验结果进行对比。内埋弹舱吹风试验在全消声室中进行,并采用传声器阵列识别主要噪声源。结果计算与试验得到的不同来流条件下,不同测量点的噪声频谱曲线基本一致。弹舱内最大声压级出现在中间弹翼附近的侧壁上,与声源识别的主要噪声源的位置一致。结论该研究可为内埋弹舱的设计提供参考和技术支持。     

Health impact and noise exposure assessment in the cricket bat industry of Kashmir,India

Aim. The aim of the present study was to identify and evaluate predominant noise sources in the cricket bat industry of Kashmir, India. Methods. Sound levels were measured at operator’s ear level in the working zone of the workers of seven cricket bat factories. The impact assessment was made through personal interviews with each worker separately during their period of rest. Results. On average, 62.5% of the workers reported difficulty in hearing and 24.1% of the workers have become patients for hypertension. Only 58.1% of the workers complained of headache due to high noise level. Conclusions. The workers engaged in the cricket bat industry of Kashmir are exposed to high noise levels. It is suggested that personal protective equipment like ear plugs and ear muffs be used by these workers as a protection against this hazard.     

Evaluation of noise environments during daily activities of university students

Noise conditions specifically in areas inside university facilities and its impact on the quality of life of university students are topics that have received little attention. This paper presents a study of the noise conditions in which university students of various institutions in Madrid, Spain, carry out their daily studies. A representative number of measurements was carried out using noise dosemeters and dataloggers in order to evaluate the levels of noise, noise dose and exposure to noise during school periods and extracurricular activities. The results were compared with the recommendations given by current environmental noise regulations. This paper was complemented with a survey to get to know how students perceive the exposure to noise in university environments.     

隔声屏障对街道峡谷污染物扩散的影响

对带有隔声屏障的街道峡谷内流场和污染物浓度场进行了数值模拟,探讨了风速、隔声屏障高度及与建筑物间的距离对流场及污染物扩散的影响。模拟结果显示:街谷内由1个稳定的主涡及街角两侧隔声屏障所在区域的3个附属涡组成。隔声屏障改变了街谷底部的流型,提高了街谷内的x、y方向速度峰值,但在隔声屏障附近区域x方向速度场明显减弱,这也是污染物聚集原因之一。与无隔声屏障相比,隔声屏障的存在物理性阻隔了污染物扩散路径,提高了街道峡谷内污染物浓度峰值,其中行人高度处背风面污染物浓度升高27.51%~28.72%,迎风面污染物浓度升高11.64%~19.99%。街谷内污染物浓度的分布和峰值由风场、隔声屏障高度及与建筑物之间的距离共同决定。     

温岭市东环高架交通对声环境的影响评价与预测

相较于一般的城市道路,城市高架具有通行能力大、行车速度高、车辆行驶状态复杂的特点,噪声污染极为突出.温岭市东环高架穿越温岭市区,是进出市区唯一的快速通道.以温岭市东环高架道路为例,对其进行实地监测从而了解其声环境,同时运用BREEZE NOISE软件模拟其噪声污染状况.根据监测模拟结果,从合理进行道路规划、装设声屏障和铺设低噪声路到提出高架复合道路噪声污染控制的对策建议.     

环境规划中声环境管控分级研究——以长春市龙嘉机场为例

文章以长春市龙嘉机场为研究对象,结合机场参数指标,绘制机场噪声等值线图,并与城市规划相结合,评价机场周边噪声影响程度以及机场噪声对城市发展的限制作用.文章首先对机场周边56个噪声监测点位进行机场噪声数据采集,通过专业软件进行飞行事件分析,在飞行程序及飞行数据分析基础上,利用INM模拟软件进行机场模型构建,绘制机场噪声等值线图.结果表明,龙嘉机场Lwecpn 70以上区域总面积11.28平方公里,机场周边各类建设用地布局符合声环境标准当中土地用地的布局要求.     

Resistance of Villages to Elevated-Road Traffic Noise

The purpose of this study is to evaluate the methods of reducing elevated-road traffic-noise levels in rural residential areas by controlling the relative locations and morphological parameters and to investigate the effect of noise barriers on noise attenuation along elevated roads and building facades in villages. This study selected six morphological parameters and used noise-mapping techniques to estimate the noise attenuation in 60 village sites. The results indicate that ‘quiet areas’ increase by approximately 10% for each additional 100 m increase in the distance between the elevated road and the village. The best strategy for noise reduction is keeping the elevated road 1,000 m away from the village and raising the road height to 20 m. The building façade conditions only affect the traffic noise level attenuation when the buildings are within 100 m of the elevated road. It was found that the cost-effective length of the road noise barrier is 600 m on both sides of the village parallel to the road. The results highlight the importance of using morphology to improve the traffic noise resistance of villages. The landscape shape indices of buildings and roads are the most important parameters that affect the traffic noise attenuation of elevated roads.     

卧具烘干房蒸汽噪声的治理

针对卧具烘干房蒸汽噪声严重的情况，利用小孔喷射消声原理，采用喷射小孔扩散式蒸汽消声器，并结合工程实际对消声器作了适当改进，治理效果均达到《城市区域环境噪声标准》ＧＢ９０９６—８２二类混合区标准。     

Environmental Equity and the Role of Public Policy: Experiences in the Rijnmond Region

This Φ Ψ study of environmental equity uses secondary quantitative data to analyze socioeconomic disparities in environmental conditions in the Rijnmond region of the Netherlands. The disparities of selected environmental indicators—exposure to traffic noise (road, rail, and air), NO₂, external safety risks, and the availability of public green space—are analyzed both separately and in combination. Not only exposures to environmental burdens (“bads”) were investigated, but also access to environmental benefits (“goods”). Additionally, we held interviews and reviewed documents to grasp the mechanisms underlying the environmental equity situation, with an emphasis on the role of public policy. Environmental equity is not a priority in public policy for the greater Rotterdam region known as the Rijnmond region, yet environmental standards have been established to provide a minimum environmental quality to all local residents. In general, environmental quality has improved in this region, and the accumulation of negative environmental outcomes (“bads”) has been limited. However, environmental standards for road traffic noise and NO₂ are being exceeded, probably because of the pressure on space and the traffic intensity. We found an association of environmental “bads” with income for rail traffic noise and availability of public green space. In the absence of regulation, positive environmental outcomes (“goods”) are mainly left up to market forces. Consequently, higher-income groups generally have more access to environmental “goods” than lower-income groups.