Ortega-García Juan A, López-Hernández Fernando A, Cárceles-Álvarez Alberto, Fuster-Soler José L, Sotomayor Diana I, Ramis Rebeca
Pediatric Environmental Health Speciality Unit, Department of Paediatrics, Laboratory of Environmental and Human Health (A5), Institute of Biomedical Research, IMIB-Arrixaca, Clinical University Hospital Virgen de la Arrixaca, University of Murcia, Murcia, Spain.
Departamento de Métodos Cuantitativos e Informáticos, Universidad Politécnica de Cartagena, Spain.
Environ Res. 2017 Jul;156:63-73. doi: 10.1016/j.envres.2017.03.009. Epub 2017 Mar 19.
Pediatric cancer has been associated with exposure to certain environmental carcinogens. The purpose of this work is to analyse the relationship between environmental pollution and pediatric cancer risk.
We analysed all incidences of pediatric cancer (<15) diagnosed in a Spanish region during the period 1998-2015. The place of residence of each patient and the exact geographical coordinates of main industrial facilities was codified in order to analyse the spatial distribution of cases of cancer in relation to industrial areas. Focal tests and focused Scan methodology were used for the identification of high-incidence-rate spatial clusters around the main industrial pollution foci.
The crude rate for the period was 148.0 cases per 1,000,0000 children. The incidence of pediatric cancer increased significantly along the period of study. With respect to spatial distribution, results showed significant high incidence around some industrial pollution foci group and the Scan methodology identify spatial clustering. We observe a global major incidence of non Hodgkin lymphomas (NHL) considering all foci, and high incidence of Sympathetic Nervous System Tumour (SNST) around Energy and Electric and organic and inorganic chemical industries foci group. In the analysis foci to foci, the focused Scan test identifies several significant spatial clusters. Particularly, three significant clusters were identified: the first of SNST was around energy-generating chemical industries (2 cases versus the expected 0.26), another of NHL was around residue-valorisation plants (5 cases versus the expected 0.91) and finally one cluster of Hodgkin lymphoma around building materials (3 cases versus the expected 2.2) CONCLUSION: Results suggest a possible association between proximity to certain industries and pediatric cancer risk. More evidences are necessary before establishing the relationship between industrial pollution and pediatric cancer incidence.
儿童癌症与接触某些环境致癌物有关。本研究的目的是分析环境污染与儿童癌症风险之间的关系。
我们分析了1998年至2015年期间在西班牙某地区诊断出的所有儿童癌症(<15岁)病例。对每位患者的居住地和主要工业设施的确切地理坐标进行编码,以便分析癌症病例相对于工业区的空间分布。使用焦点检验和聚焦扫描方法来识别主要工业污染源周围的高发病率空间集群。
该时期的粗发病率为每100万儿童中有148.0例。在研究期间,儿童癌症的发病率显著上升。关于空间分布,结果显示在一些工业污染源组周围存在显著的高发病率,并且扫描方法识别出了空间聚类。考虑所有污染源,我们观察到非霍奇金淋巴瘤(NHL)的总体发病率较高,在能源与电力以及有机和无机化学工业污染源组周围,交感神经系统肿瘤(SNST)的发病率较高。在逐个污染源分析中,聚焦扫描检验识别出了几个显著的空间集群。特别是,识别出了三个显著集群:第一个是SNST集群,位于能源生产化学工业周围(2例,预期为0.26例),另一个是NHL集群,位于残渣回收工厂周围(5例,预期为0.91例),最后一个是霍奇金淋巴瘤集群,位于建筑材料周围(3例,预期为2.2例)。结论:结果表明靠近某些行业与儿童癌症风险之间可能存在关联。在确定工业污染与儿童癌症发病率之间的关系之前,还需要更多证据。