首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到18条相似文献,搜索用时 93 毫秒
1.
测点高度对道路交通噪声监测数据的影响   总被引:1,自引:0,他引:1       下载免费PDF全文
通过在4城市对132条道路进行了道路交通噪声测点高度试验,系统分析了测点高度从手工监测的1.2 m向自动监测的4.5 m转化后,在不同道路情况对道路交通噪声监测数据的影响。结果表明,测点高度提高后监测结果变化在±3 dB(A)以内。待测道路的车道数和测点与机动车道的距离是其主要影响因素。对两测点高度进行对比,4.5 m高度噪声值随水平距离增加衰减较小,测量结果更稳定。  相似文献   

2.
公交车已成为当前北京市道路交通噪声的主要束源之一,针对公交车声源模型缺乏而沿用大型车声源模型所致的噪声预测误差问题,在北京市选取了两类常见公交车进行了537辆车的单车通过噪声测试,在无效数据剔除和背景噪声修正后,利用回归分析法获得了北京市公交车声源模型,通过与现有《公路建设项目环境影响评价规范》中大型车声源模型的比较,显示出建立北京市公交车噪声声源模型的必要性。基于《公路建设项目环境影响评价规范》中的道路交通噪声预测方法,提出了符合北京市实际情况的道路交通噪声预测模型。  相似文献   

3.
以深圳市前海湾车辆段和横岗车辆段试车线为例,对其试车过程中的噪声影响源强及传播情况进行实测分析。结果表明,试车线车辆行驶速度约为36 km/h,噪声源强LeqA约为73 d B左右,试车中噪声最大值约为83 d B;试车线内噪声源的传播并不完全遵循一般的线性递减规律,在距声源30 m范围内,距声源越近,衰减量越小,反之,主要是由于距离声源越远,受到墙体或立柱等阻挡引起的附加衰减就越大。  相似文献   

4.
1 实验 淮安市环境监测站开展了固定和流动噪声源在不同距离,对不同高度建筑物影响的噪声监测,监测点设在该市淮海国际大酒店各楼层临近阳台的窗口,共设置7个监测点,监测点距离地面高度(垂直高度)分别为1.5 m、12 m、17 m、23 m、30 m、35 m、42 m.监测方法按照GB/T 14623-1993<城市区域环境噪声测量方法>和<环境监测技术规范>(噪声部分),监测仪器为噪声积分统计分析仪.固定声源监测频次:监测4次,每次测10 min,以等效声级(Leq)值参加统计;复合声源按功能区测量方法监测,监测4次,每次为24 h连续监测,测量每小时的Leq值,实测20 min,Leq值参加统计,同时记录车流量.噪声监测点见图1.  相似文献   

5.
在工业企业厂界噪声测量中经常遇到的问题主要有监测点位布设和背景噪声扣除两类,并对敏感点距声源距离与布点监测、背景噪声的测量和受外来声源严重影响时如何测量厂界噪声等问题提出了解决办法.  相似文献   

6.
通过布设不同类型的多个点位,对山东省某城市多条道路两侧建筑物的室内外交通噪声进行了测量,并对实测数据进行了分析。结果表明,为降低道路两侧建筑物的环境噪声,通过在道路与两侧建筑物之间的区域采取降噪措施,降噪幅度是有限的;为降低建筑物内的房间噪声,通过对建筑物本身采取噪声防护措施,降噪效果明显。  相似文献   

7.
待兴建的厂房在投入生产运行时,厂房内设备、机器将产生噪声影响周围环境,其噪声影响值为Lp.正确预测Lp值是环境影响评价工作中的主要内容.本文阐述了Lp值的预测方法;通过测算待建厂房内的各种机器,设备声源的声功率级,掌握待建厂房的建筑构造和构件材料组成以及机器、设备在该厂房内的空间布局,然后,就可以运用声扩散、传播的数学处理方法,预测出厂房内声源机器、设备对环境的噪声影响声级值Lp.单个或多个机器、设备被设置在厂房内确定的空间位置上,当机器、设备运行时,厂房  相似文献   

8.
青岛市主干道沿线高层建筑的交通噪声研究   总被引:2,自引:1,他引:1       下载免费PDF全文
采用A计权网络对青岛市东西快速路沿线高层建筑进行监测。利用Grapher软件,以Leq为监测值的基准值绘制连续线状图,分析城市主干道周边高层建筑上交通噪声的峰值点。根据道路中心线到高层建筑的距离信息,得出高层建筑交通噪声峰值点与道路中心线的连线与水平地面间的角度约为30°。  相似文献   

9.
为科学全面地开展城市道路交通噪声影响评估,更精确地服务道路交通噪声污染治理工作,选取南京市具有代表性的道路交通干线,采用手工监测和自动连续监测的方法,进行不同路段噪声污染程度及其随时间、空间变化规律的研究。结果表明,地面快速路段、高架路段以及衔接路段两侧噪声敏感建筑物受道路交通噪声影响较大,夜间均超标;相邻区域要达到2类声环境功能区昼间标准限值要求,需距离地面快速路慢车道约45 m,距离高架路段慢车道约92 m;要达到2类声环境功能区夜间标准限值要求,需距离地面快速路慢车道约175 m,距离高架路段慢车道约172 m;敏感建筑物所受噪声影响随楼层高度升高而增大,同时噪声影响情况与道路两侧建筑物密度、道路车辆行驶速度有关。建议严格道路及噪声敏感建筑物规划控制,采取阻断传声路径、受声建筑物强化保护等措施控制噪声影响。  相似文献   

10.
通过对高速公路交通噪声现场测定与研究分析,结果表明,由于高速公路上行驶的车辆速度很快,致使在高速公路两侧近距离接收点上,当车辆迎面驶来到背离驶去时,交通噪声出现明显的频率漂移和A声级的显著差异,即出现高速公路交通噪声的多普勒效应。  相似文献   

11.
It is highly important to analyze the acoustic properties of workrooms in order to identify best noise control measures from the standpoint of noise exposure limits. Due to the fact that sound pressure is dependent upon environments, it cannot be a suitable parameter for determining the share of workroom acoustic characteristics in producing noise pollution. This paper aims to empirically analyze noise source characteristics and acoustic properties of noisy embroidery workrooms based on special parameters. In this regard, reverberation time as the special room acoustic parameter in 30 workrooms was measured based on ISO 3382-2. Sound power quantity of embroidery machines was also determined based on ISO 9614-3. Multiple linear regression was employed for predicting reverberation time based on acoustic features of the workrooms using MATLAB software. The results showed that the measured reverberation times in most of the workrooms were approximately within the ranges recommended by ISO 11690-1. Similarity between reverberation time values calculated by the Sabine formula and measured values was relatively poor (R 2?=?0.39). This can be due to the inaccurate estimation of the acoustic influence of furniture and formula preconditions. Therefore, this value cannot be considered representative of an actual acoustic room. However, the prediction performance of the regression method with root mean square error (RMSE)?=?0.23 s and R 2?=?0.69 is relatively acceptable. Because the sound power of the embroidery machines was relatively high, these sources get the highest priority when it comes to applying noise controls. Finally, an objective approach for the determination of the share of workroom acoustic characteristics in producing noise could facilitate the identification of cost-effective noise controls.  相似文献   

12.
天津市春季典型道路积尘负荷分布特征   总被引:1,自引:0,他引:1  
道路积尘负荷表征路面清洁程度,是道路扬尘排放清单中一个十分重要的参数,也是各地环境管理的一个重要方面。根据AP-42道路扬尘排放因子模型,2015年春季用真空吸尘法采集了天津市11条道路的扬尘样品,得到了不同道路类型以及不同车道的积尘负荷,并分析了积尘负荷的变化规律。结果表明:天津市春季非机动车道和机动车道慢车道的积尘负荷分别为0.282 0~1.064 5 g/m~2和0.050 4~0.173 9 g/m~2;5种道路类型的非机动车道的积尘负荷中位值均大于机动车慢车道积尘负荷的中位值;对于不同道路类型积尘负荷而言,非机动车道从大到小顺序依次为次干道主干道环线支路快速路,机动车道慢车道从大到小顺序依次为次干道环线主干道支路快速路;东西走向和南北走向道路两侧积尘负荷差异均无统计学意义。  相似文献   

13.
换流变压器是高压直流换流站中主要的噪声源,对换流变压器噪声的预测精度直接影响到后期整个换流站噪声预测模型的准确性,因此,准确获得换流变压器的声功率至关重要。根据《声学 户外声传播衰减 第2部分:一般计算方法》(ISO 9613-2:1996)中的户外声传播声功率计算方法,构建了声源声功率反推数学模型。利用某变压器周围大量测点现场实测数据,结合可靠度理论,识别并剔除了实测点中受相干声场影响较大的点,实现了换流变压器声功率反演计算,并对测点个数的选取进行了初步研究及优化。与其他声功率测量方法相比,该方法操作简单,对仪器设备要求较低,适用于复杂的声学环境,具有一定的应用前景。  相似文献   

14.
Wastewater treatment works effluent is often considered to be one of the most important point sources of a wide range of anthropogenic contaminants to aquatic systems, however, this paper discusses other potential sources. With the aim of establishing the important sources of UV filters, insect repellent and biocides to the aquatic environment, samples were collected from sites with direct (bathing areas and marinas) and indirect (sites receiving wastewater effluent) human influences. Sunscreens containing UV filters are used in large volumes during the summer months and often applied shortly before a person enters the water for swimming activities. The results presented here demonstrate that washing directly from the skin is an important point source of 4 UV filters to the Oslofjord. The insect repellent, diethyl toluamide, was also measured and it was concluded that washing from the skin was not such an important point source into the fjord. Concentrations of the biocide Irgarol 1051 were also measured and were elevated in the small boat marina and surrounding enclosed area. This work demonstrates that man recreational water-based activities are a diffuse source of some contaminants into coastal and fjord environments and this study provides an initial assessment of the levels being released.  相似文献   

15.
A Simple Model for Urban Background Pollution   总被引:1,自引:0,他引:1  
A simple urban background pollution model is presented. Contributions from the individual area sources, subdivided into a grid net of a resolution of 2km × 2km, are integrated along the wind direction path assuming linear dispersion with the distance to the receptor point. Horizontal dispersion is accounted for by averaging the calculated concentrations over a certain, wind speed dependent wind direction sector, centred on the average wind direction. Formation of the nitrogen dioxide due to oxidation of nitrogen monoxide by ozone is calculated using a simple chemical model based on assumption of a photochemical equilibrium on the time scale of the pollution transport across the city area. The rate of entrainment of fresh rural ozone is governed by this time scale. The model is suitable for calculations of urban background when the dominating source is the road traffic. For this source the emissions take place at ground level, and a good approximation is to treat the emissions as area sources, but with an initial vertical dispersion determined by the height of the buildings.  相似文献   

16.
This work develops a source-oriented approach to locate the influential pollution sources and estimate their contributions to pollutant concentrations observed at a receptor site. The domain containing possible influential pollution sources is divided into systematic grid cells, and the influential grid sources are determined based on the locations of the segment endpoints of air trajectories arriving at the receptors. The contribution of each grid source is initially calculated using a formula derived from a Lagrangian box model and including the effects of source emissions, atmospheric dilution, and chemical transformation and deposition. The formula is described in detail in this study. Finally, the average contribution of each grid source is determined based on numerous analyzed events. The proposed approach was used to locate influential pollution sources and determine their contributions to a rural monitoring station during periods of high SO2 pollution in southern Taiwan. The contributions of sources in various 2 km by 2 km grid cells, five districts, three source categories, 8 industrial areas, and a power plant were evaluated. The results show that the major influential sources were in the northwestern region of south Taiwan, and belonged to three district and point sources. Furthermore, two industrial areas close to the evaluated stations were also very significant, and contributed about 30% of the total pollution.  相似文献   

17.
A practical optimization approach developed in this paper derives effective monitoring configurations for detecting contaminants in ground water. The approach integrates numerical simulation of contaminant transport and mathematical programming. Well sites identified by the methodology can be monitored to establish the occurrence of a contaminant release before a plume migrates to a regulatory compliance boundary. Monitoring sites are established along several horizons located between the downgradient margin of a contaminant source and a compliance boundary. A horizon can form an effective line of defense against contaminant migration to the compliance boundary if it is spanned (covered) by a sufficient number of sites to yield a well spacing that is equal to or less than a maximum value established by numerical modeling. The objective function of the integer programming model formulation expresses the goals of: (1) covering a maximum number of siting horizons, and (2) allocating wells to the single most effective horizon. The latter is determined from well spacing requirements and the width of the zone of potential contaminant migration traversed by the horizon. The methodology employs a highly tractable linear programming model formulation, and the user is not required to predefine a set of potential well sites. These attributes can facilitate its implementation in practice.  相似文献   

18.
An accurate prediction of the transport-reaction behaviour of atmospheric chemical species is required to fully understand the impact on the environment of pollution emissions. Elevated levels of secondary pollutants such as ozone in the lower atmosphere can be harmful to the health of both plants and animals, and can cause damage to property present in the urban environment. Detailed models of pollution mechanisms must therefore be developed through comparisons with field measurements to aid the selection of effective abatement policies. Such models must satisfy accuracy requirements both in terms of the number of species represented, and the spatial resolution of species profiles. Computational expense often compels current models to sacrifice detail in one of these areas. This paper attempts to address the latter point by presenting an atmospheric transport-reaction modelling strategy based upon a finite volume discretisation of the atmospheric dispersion equation. The source terms within this equation are provided by an appropriate reduced chemical scheme modelling the major species in the boundary layer. Reaction and transport discretisations are solved efficiently via a splitting technique applied at the level of the non-linear equations. The solution grid is generated using time dependant adaptive techniques, which provide a finer grid around regions of high spatial error in order to adequately resolve species concentration profiles. The techniques discussed are applied in two dimensions employing emissions from both point and area sources. Preliminary results show that the application of adaptive gridding techniques to atmospheric dynamics modelling can provide more accurately resolved species concentration profiles, accompanied by a reduced CPU time invested in solution. Such a model will provide the basis for high resolution studies of the multiple scale interactions between spatially inhomogeneous source patterns in urban and regional environments.  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号