{"title":"大温哥华地区和弗雷泽河守护者在福尔溪收集的大肠杆菌数据的比较","authors":"Anastasia Wilcott","doi":"10.47339/ephj.2019.39","DOIUrl":null,"url":null,"abstract":"Background: False Creek is a small inlet centered within Vancouver, British Columbia. Its long and narrow shape facilitates the build-up of contaminants and limits dilution of fresh water. The lack of flushing coupled with sources of fecal contamination results in high levels of Escherichia coli particularly in the summer months. High levels of E. coli in recreational water pose a health hazard to the public. Two organizations Metro Vancouver and Fraser Riverkeeper monitored E. coli levels in False Creek over the 2018 summer season. Methods: Data collected by Metro Vancouver and Fraser Riverkeeper over the 2018 summer season was collected and compared. The secondary data was analyzed from July 8, 2018 to September 29, 2018 from thirty-day geometric means. Each organization sampled on a weekly basis in False Creek, Metro Vancouver sampled from twelve locations and Fraser Riverkeeper sampled from seven locations. Both organizations used similar methodologies in the collection of data with both analyzing for microbiological enumerations of most probable number [MPN] of E. coli per 100/mL samples. All sample sites were divided into three locations representative of False Creek: West, Central and East. The data was then analyzed in terms of overall weekly samples by organization, locational weekly samples by organization and locational weekly samples overall. Results: The data was analyzed using an Aspin Welch Unequal Variance T-test to compare the overall weekly E. coli counts between the organization. Where p = 0.000 and power = 1.00. An Equal Variance T-test was used to compare the locational weekly E. coli counts from the West, Central and East regions of each organization. This yielded a p = 0.000 where power = 1.00. A Kruskal Wallis One-Way ANOVA was used to compare the locational weekly E. coli counts from the West, Central and East regions. This found p = 0.000 and power = 1.00. A MANOVA was used as a reiteration to compare the weekly E. coli counts at each location (West, Central and East) when collected by each organization. This confirmed the same p-value and power results from the three previous tests. Conclusions: There is a statistically significant difference between the two organizations. Not only in overall samples but there is a statistically significant difference between the two organizations when E. coli is amalgamated by location. When accounting for location only, the East region obtained statistically higher E. coli counts as the mean E. coli count for West was 90.8, Central was 248 and East was 1040. \n ","PeriodicalId":433101,"journal":{"name":"BCIT Environmental Public Health Journal","volume":"3 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"1900-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"1","resultStr":"{\"title\":\"A comparison of Escherichia coli data collected in False Creek by Metro Vancouver and Fraser Riverkeeper\",\"authors\":\"Anastasia Wilcott\",\"doi\":\"10.47339/ephj.2019.39\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"Background: False Creek is a small inlet centered within Vancouver, British Columbia. Its long and narrow shape facilitates the build-up of contaminants and limits dilution of fresh water. The lack of flushing coupled with sources of fecal contamination results in high levels of Escherichia coli particularly in the summer months. High levels of E. coli in recreational water pose a health hazard to the public. Two organizations Metro Vancouver and Fraser Riverkeeper monitored E. coli levels in False Creek over the 2018 summer season. Methods: Data collected by Metro Vancouver and Fraser Riverkeeper over the 2018 summer season was collected and compared. The secondary data was analyzed from July 8, 2018 to September 29, 2018 from thirty-day geometric means. Each organization sampled on a weekly basis in False Creek, Metro Vancouver sampled from twelve locations and Fraser Riverkeeper sampled from seven locations. Both organizations used similar methodologies in the collection of data with both analyzing for microbiological enumerations of most probable number [MPN] of E. coli per 100/mL samples. All sample sites were divided into three locations representative of False Creek: West, Central and East. The data was then analyzed in terms of overall weekly samples by organization, locational weekly samples by organization and locational weekly samples overall. Results: The data was analyzed using an Aspin Welch Unequal Variance T-test to compare the overall weekly E. coli counts between the organization. Where p = 0.000 and power = 1.00. An Equal Variance T-test was used to compare the locational weekly E. coli counts from the West, Central and East regions of each organization. This yielded a p = 0.000 where power = 1.00. A Kruskal Wallis One-Way ANOVA was used to compare the locational weekly E. coli counts from the West, Central and East regions. This found p = 0.000 and power = 1.00. A MANOVA was used as a reiteration to compare the weekly E. coli counts at each location (West, Central and East) when collected by each organization. This confirmed the same p-value and power results from the three previous tests. Conclusions: There is a statistically significant difference between the two organizations. Not only in overall samples but there is a statistically significant difference between the two organizations when E. coli is amalgamated by location. When accounting for location only, the East region obtained statistically higher E. coli counts as the mean E. coli count for West was 90.8, Central was 248 and East was 1040. \\n \",\"PeriodicalId\":433101,\"journal\":{\"name\":\"BCIT Environmental Public Health Journal\",\"volume\":\"3 1\",\"pages\":\"0\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"1900-01-01\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"1\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"BCIT Environmental Public Health Journal\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.47339/ephj.2019.39\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"BCIT Environmental Public Health Journal","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.47339/ephj.2019.39","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 1
摘要
背景:假溪是一个小入口中心在温哥华,不列颠哥伦比亚省。它的长而窄的形状有利于污染物的积聚,限制了淡水的稀释。由于缺乏冲洗,再加上粪便污染源,导致大肠杆菌水平很高,特别是在夏季。游憩用水中大肠杆菌含量高,对公众健康构成危害。大温哥华地区和弗雷泽河守护者两个组织在2018年夏季监测了福斯克里克的大肠杆菌水平。方法:收集大温哥华地区和弗雷泽河管理员在2018年夏季收集的数据并进行比较。二级数据分析时间为2018年7月8日至2018年9月29日,时间为30天几何均值。每个组织每周在福尔斯克里克采样,大温哥华从12个地点采样,弗雷泽河守护者从7个地点采样。这两个组织在收集数据时使用了类似的方法,分析了每100/mL样品中大肠杆菌的最可能数量[MPN]的微生物计数。所有样本地点被分为三个代表福溪的地点:西部、中部和东部。然后,根据组织的总体每周样本、组织的地点每周样本和总体的地点每周样本,对数据进行分析。结果:使用Aspin Welch不等方差t检验对数据进行分析,以比较组织之间的总每周大肠杆菌计数。其中p = 0.000, power = 1.00。使用等方差t检验比较每个组织的西部、中部和东部地区的每周位置大肠杆菌计数。这产生了p = 0.000,其中功率= 1.00。采用Kruskal - Wallis单因素方差分析比较西部、中部和东部地区的每周地点大肠杆菌计数。结果发现p = 0.000, power = 1.00。使用方差分析作为重申,比较每个组织收集的每个地点(西部,中部和东部)的每周大肠杆菌计数。这证实了与前三个测试相同的p值和功率结果。结论:两组织间存在统计学差异。不仅在总体样本中,而且当大肠杆菌按位置合并时,两个组织之间存在统计学上的显着差异。如果只考虑地理位置,东部地区的大肠杆菌数量在统计学上较高,西部的平均大肠杆菌数量为90.8,中部为248,东部为1040。
A comparison of Escherichia coli data collected in False Creek by Metro Vancouver and Fraser Riverkeeper
Background: False Creek is a small inlet centered within Vancouver, British Columbia. Its long and narrow shape facilitates the build-up of contaminants and limits dilution of fresh water. The lack of flushing coupled with sources of fecal contamination results in high levels of Escherichia coli particularly in the summer months. High levels of E. coli in recreational water pose a health hazard to the public. Two organizations Metro Vancouver and Fraser Riverkeeper monitored E. coli levels in False Creek over the 2018 summer season. Methods: Data collected by Metro Vancouver and Fraser Riverkeeper over the 2018 summer season was collected and compared. The secondary data was analyzed from July 8, 2018 to September 29, 2018 from thirty-day geometric means. Each organization sampled on a weekly basis in False Creek, Metro Vancouver sampled from twelve locations and Fraser Riverkeeper sampled from seven locations. Both organizations used similar methodologies in the collection of data with both analyzing for microbiological enumerations of most probable number [MPN] of E. coli per 100/mL samples. All sample sites were divided into three locations representative of False Creek: West, Central and East. The data was then analyzed in terms of overall weekly samples by organization, locational weekly samples by organization and locational weekly samples overall. Results: The data was analyzed using an Aspin Welch Unequal Variance T-test to compare the overall weekly E. coli counts between the organization. Where p = 0.000 and power = 1.00. An Equal Variance T-test was used to compare the locational weekly E. coli counts from the West, Central and East regions of each organization. This yielded a p = 0.000 where power = 1.00. A Kruskal Wallis One-Way ANOVA was used to compare the locational weekly E. coli counts from the West, Central and East regions. This found p = 0.000 and power = 1.00. A MANOVA was used as a reiteration to compare the weekly E. coli counts at each location (West, Central and East) when collected by each organization. This confirmed the same p-value and power results from the three previous tests. Conclusions: There is a statistically significant difference between the two organizations. Not only in overall samples but there is a statistically significant difference between the two organizations when E. coli is amalgamated by location. When accounting for location only, the East region obtained statistically higher E. coli counts as the mean E. coli count for West was 90.8, Central was 248 and East was 1040.