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Monday, 18 April 2016

Persistent organic pollutants (POPs) and metals in primiparous women: a comparison from Canada and Mexico

Volumes 500–501, 1 December 2014, Pages 302–313
  Open Access

Highlights

Higher concentrations of p,p’-DDE, β-HCH, and lead among Mexican primiparous women.
PCB concentrations similar among Mexican and Canadian primiparous women.
Age, pre-pregnancy BMI, ethnicity group, and ever-smoked status were significant.

Abstract

Under the North American Commission for Environmental Cooperation (CEC) and its Sound Management of Chemicals (SMOC) program, a tri-national human contaminant monitoring initiative was completed to provide baseline exposure information for several environmental contaminants in Canada, Mexico and the United States (U.S). Blood samples were collected from primiparous women in Canada and Mexico, and were analysed for a suite of environmental contaminants including polychlorinated biphenyls (PCBs), dichlorodiphenyldichloroethylene(p,p′-DDE),beta-hexachlorocyclohexane (β-HCH), mercury and lead. A multiple stepwise linear regression analysis was conducted using data from Canadian and Mexican primiparous mothers, adjusting for ethnicity group, age, pre-pregnancy BMI, years at current city and ever-smoking status. Concentrations of p,p′-DDE, β-HCH, and lead were found to be higher among Mexican participants; however, concentrations of most PCBs among Mexican participants were similar to Canadian primiparous women after adjusting for covariates. Concentrations of total mercury were generally higher among Mexican primiparous women although this difference was smaller as age increased. This initial dataset can be used to determine priorities for future activities and to track progress in the management of the selected chemicals, both domestically and on a broader cooperative basis within North America.

Keywords

  • Primiparous women;
  • Persistent Organic Pollutants (POPs);
  • Metals;
  • Canada;
  • Mexico

1. Introduction

Prior to the initiation of the Trinational Biomonitoring study (CEC, 2011) there was relatively limited biomonitoring data available across parts of Canada and Mexico. In Canada, several targeted population and community-based based studies have been conducted among Aboriginal populations (Donaldson et al., 2010 and Wheatley and Paradis, 1995), and in specific regions including the Great Lakes (Cole et al., 2002) and the St. Lawrence region (St. Lawrence Vision, 2000), and in certain provinces (Alberta Health Wellness, 2008 and Institut national de santé publique du Québec, 2004). More recently however, a number of comprehensive surveys have been conducted such as the Canadian Health Measures Survey, and several others described by Haines et al., (2012), that provide a nation-wide level of information on contaminants present in the population. In Mexico, biomonitoring data was relatively scarce except for a few contaminants such as lead and DDT (López-Carrillo et al., 1996a and López-Carrillo et al., 1996b) although more recently, studies have been conducted that focus on environmental contaminants in suspected areas of higher levels (Domínguez-Cortinas et al., 2013, Meza-Montenegro et al., 2013, Trejo-Acevedo et al., 2012 and Trejo-Acevedo et al., 2009) at specific sites (Orta-Garcia et al., 2014) and at sites in proximity to point sources of contaminants (Soto-Jiménez and Fregal, 2011 and Soto-Ríos et al., 2010).
A tri-national human contaminant monitoring initiative was developed by the North American Commission for Environmental Cooperation (CEC) and its Sound Management of Chemicals (SMOC) program, which is tasked with implementing tri-national efforts to reduce the risks of exposure to toxic substances related to human health and the environment in the United States (U.S.), Canada and Mexico (CEC, 2011). The initiative was developed with two main objectives: 1) to obtain an initial profile of exposure to persistent organic pollutants (POPs) and selected metals in primiparous women for Canada and Mexico, and women of childbearing age in the U.S.; and 2) to enhance the capacity of Mexico to monitor Stockholm Convention POPs and selected metals, establishing the basis for the development of compatible and comparable databases of human biomonitoring results for the three countries. The data collected by this pilot biomonitoring study (Trinational Biomonitoring Study) provides a baseline profile of human exposure to environmental contaminants to help track progress in managing select chemicals in the three countries (CEC, 2011) and assist in the prioritization of future monitoring activities.

The POPs and metals contaminants measured in the Trinational Biomonitoring Study are some of the most well studied contaminants and human health effects associated with their exposure has been studied by numerous researchers. Studies have linked lead exposure to neurodevelopmental (Boucher et al., 2012a, Boucher et al., 2012b, Cho et al., 2010 and Wang et al., 2008a), cardiovascular (Glenn et al., 2006, Glenn et al., 2003 and Yazbeck et al., 2009), renal (Muntner et al., 2005 and Muntner et al., 2003) and reproductive effects (Cantonwine et al., 2010). Mercury exposure has been associated with neurotoxic effects in adults (Harada et al., 2005 and Harada, 1995) and children (Grandjean et al., 2003), cardiovascular effects (Choi et al., 2009), and developmental effects in children from prenatal exposure (Boucher et al., 2012a and Boucher et al., 2012b). In addition, several studies have identified a number of potential health effects associated with exposure to persistent organic pollutants (POPs), including exposure to dichlorodiphenyldichloroethylene (p,p′-DDE) and PCBs (Dallaire et al., 2006 and Dallaire et al., 2004), PCBs and dioxins (Weisglas-Kuperus et al., 2004) with immune system effects, and exposure to PCBs with cardiovascular effects (Huang et al., 2006 and Sergeev and Carpenter, 2005), and neurodevelopment effects (Boucher et al., 2009, Grandjean et al., 2001, Jacobson and Jacobson, 2003 and Muckle et al., 2004). An increasing number of studies are reporting increased risk of developing type II diabetes associated with exposure to POPs, such as PCBs and dioxins (Lee et al., 2006, Lee et al., 2010 and Wang et al., 2008b;) and p,p′-DDE (Rignell-Hydbom et al., 2009). Few studies have investigated health effects associated with exposure to polybrominated compounds (Kicinski et al., 2012), although several toxicology studies have documented developmental, neurotoxic, and endocrine disruption effects (Costa et al., 2008 and Darnerud, 2003).
Exposures for young children and the developing fetus carry the most cause for concern due to their rapid growth and physiological immaturity. Environmental chemicals can be passed on from the mother to the developing fetus through the placenta (Needham et al., 2011) and some contaminants such as mercury have been detected at higher concentrations in umbilical cord blood than in maternal blood (Ask et al., 2002, Sakamoto et al., 2004 and Soria et al., 1992). Even after birth, when the body is still developing and young children do not have a fully formed blood–brain barrier, further exposure to contaminants can occur through breastfeeding (Anderson and Wolff, 2000 and Lakind et al., 2001). For this reason, pregnant women were the target population for the CEC Trinational Biomonitoring Study. Primiparous women in particular, are an ideal population to study as they are not influenced by confounding variables such as parity and breast-feeding (James et al., 2002 and Sarcinelli et al., 2003). Several studies have investigated changes in maternal blood volume, body mass index and other factors during pregnancy, however recent studies indicate that the last weeks of the third trimester is the most suitable time period for the measuring of organochlorines in blood samples (Hansen et al., 2010).
Data on concentrations of chemicals in human populations are required by regulatory agencies to conduct risk assessments and for informing policy decisions. The monitoring of contaminant levels in human populations can provide information to track the effectiveness of regulations. In Canada, for example, a decline in blood lead concentrations has been observed over the last three decades, where 25% of Canadians aged 6 or older were found to have blood lead concentrations above 10 μg/dL as measured in the Canada Health Survey (1978–79), while less than 1% of Canadians were above 10 μg/dl as measured in the Cycle 1 of Canadian Health Measures Survey 30 years later (2007–2009; Wong and Lye, 2008). This may reflect the phase-out of leaded gasoline, lead-containing paints, and lead solder in food cans (Health Canada, 2004). The concentrations of a number of organochlorines, such as DDT and β-HCH, have also been measured to be declining in human breast milk in Ontario and Quebec over several decades (Craan and Haines, 1998), the use of which has been reduced or eliminated due to either restricted use or production, voluntary bans or regulated bans.
Comparison of biomonitoring datasets from different geographic areas and countries can provide valuable information to compare and contrast contaminants concentrations in human populations (a result of exposures from various sources including consumer products, food and environmental media), as well as to help evaluate the effectiveness of global regulations and other risk management efforts. Challenges exist, however, when comparing biomonitoring studies due to the potential for lack of consistency in study design, sample populations, time period, laboratory analytical methods, and interpretation of the data. To ensure comparisons for human biomonitoring data are scientifically meaningful, it is essential to evaluate the methodological components of the biomonitoring surveys and their impact on the comparability of the data (LaKind et al., 2012). The CEC biomonitoring data collected in this pilot study was conducted using similar methods and designs in Canada and Mexico, which provides a unique opportunity to make a meaningful statistical comparison between these two populations. Due to the different recruitment/sampling strategy used for the collection of US data, the analysis was restricted to Canadian and Mexican data. A descriptive comparison of all three countries is however presented in the original report (CEC, 2011). The objective of this paper is to use statistical methods to compare the concentrations of select POPs and metals in the blood of primiparous women from Canada and Mexico after adjusting for covariates.