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Using bivariate linear mixed models to monitor the change in spatial distribution of heavy metals at the site of a historic landfill

机译:使用二元线性混合模型来监测历史性垃圾填埋场中重金属的空间分布变化

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To improve accuracy and efficiency of monitoring remediated sites, the current study proposed the use of bivariate linear mixed modelling and subsequent hypothesis testing to determine significant change in contaminant concentrations over time. The modelling method integrated soil heavy metal (arsenic-As, lead-Pb and zinc-Zn) concentrations obtained from Bicentennial Park, Sydney, Australia, in the years 1990 (n = 144) and 2015 (n = 60), alongside potential influencing factors as predictor variables. Following variable selection, significant predictors included As (1990)plan curvature, land cover change; As (2015)-multi-resolution ridge top flatness (MRRTF); Pb (1990)-elevation, MRRTF, type of nearest road; Pb (2015)-land cover change; Zn (1990)-distance to the nearest road and road type; and for Zn (2015)-aspect and land cover change. Model quality statistics (standardised squared prediction error; SSPE) indicated relatively good estimates of the prediction variance (mean similar to 1.0 for all metals, median = 0.512 for As (1990), 0.420 for As (2015), 0.417 for Pb (1990), 0.388 for Pb (2015), 0.342 for Zn (1990) and 0.263 for Zn (2015)), however Lin's concordance correlation coefficient indicated poor prediction of point estimates (LCCC = 0.263 for As (1990), 0.414 for As (2015), 0.250 for Pb (1990), 0.166 for Pb (2015), 0.233 for Zn (1990) and 0.408 for Zn (2015)). Pb in 1990 exceeded the Australian guide value of 600 mgkg(-1) in small, isolated areas of the park, and by 2015, these 'hotspots' had significantly diminished (P < 0.05). Concentrations of As were low in both 1990 and 2015, not exceeding the 300 mg kg(-1) guide; yet, in 2015, As had significantly increased in the south of the study area (P < 0.2). Zn concentrations in 1990 were elevated but did not exceed the guide value of 30,000 mg kg(-1). Overall, the models exhibited good estimation of prediction variance and therefore are suitable for hypothesis testing; however, they exhibited poor prediction quality at times. Despite this, bivariate linear mixed modelling is worth exploring as it provides an advantage over modelling single time points and can assist with tracking potential contaminant sources before they cause harm.
机译:为了提高监测修复部位的准确性和效率,当前的研究提出了使用二元线性混合建模和随后的假设检验来确定污染物浓度随时间的显着变化。该模型方法将1990年(n = 144)和2015年(n = 60)从澳大利亚悉尼的百年纪念公园获得的土壤重金属(砷,铅,铅和锌-锌)浓度进行了综合,并进行了潜在影响因素作为预测变量。在选择变量之后,重要的预测因子包括As(1990)平面曲率,土地覆盖变化;作为(2015)-多分辨率脊顶平坦度(MRRTF);铅(1990)-高程,MRRTF,最近道路的类型; PB(2015)-土地覆被变化; Zn(1990)-最接近的道路和道路类型的距离;而对于Zn(2015)-纵横比和土地覆被变化。模型质量统计数据(标准平方的预测误差; SSPE)显示出相对较好的预测方差估计值(对于所有金属,均值类似于1.0,As(1990)的中位数= 0.512,As(2015)的中位数= 0.420,Pb(1990)的中位数= 0.417 ,铅的含量为0.388(2015年),锌的含量为0.342(1990年),锌的含量为0.263(2015年)),但是Lin的一致性相关系数表明对点估算值的预测较差(砷的LCCC = 0.263(1990年),砷的0.414%(2015年) ,铅(1990年)0.250,铅(2015年)0.166,锌(1990)0.233和锌(2015)0.408)。 1990年,Pb在公园的偏远小区域超过了澳大利亚指导值600 mgkg(-1),到2015年,这些“热点”已大大减少(P <0.05)。 1990年和2015年的As含量都很低,不超过300 mg kg(-1)指导值;然而,在2015年,研究区南部的砷含量显着增加(P <0.2)。 1990年的锌浓度有所升高,但未超过指导值30,000 mg kg(-1)。总体而言,这些模型显示出对预测方差的良好估计,因此适用于假设检验;但是,它们有时显示出较差的预测质量。尽管如此,双变量线性混合建模还是值得探索的,因为它在建模单个时间点方面具有优势,并且可以帮助在潜在的污染源造成危害之前对其进行跟踪。

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