Elsevier

Chemosphere

Volume 278, September 2021, 130438
Chemosphere

Pollution characteristics and health risk assessment of arsenic transformed from feed additive organoarsenicals around chicken farms on the North China Plain

https://doi.org/10.1016/j.chemosphere.2021.130438Get rights and content

Highlights

  • Arsenic is widely present in chicken feed, manure, and surface soil with different species.

  • Arsenic accumulated in chicken manure and surface soils.

  • A typical pollution pattern of arsenic was developed to clarify the pollution process from feed to soil.

Abstract

Arsenic is frequently found in poultry waste, most of which is transformed from feed additive organoarsenicals, resulting in arsenic pollution of soils and water around poultry farms. The North China Plain, an important area for livestock breeding of China, was chosen to investigate the pollution characteristics and assess the health risk of arsenic around chicken farms. Among the 138 chicken farms sampled, almost no roxarsone, a common organoarsenical, was detected in chicken feeds, manure, and surface soils, while the detectable rate of other arsenic species was high. Because of long-term enrichment, the concentrations of arsenic species in manure were generally higher than that in feed. As(III) was the main inorganic arsenic species in the manure, where is reducing environment. In surface soils beneath the accumulated manure, As(V) was the predominant arsenic species with 100% detectable rate. The detectable rate and average concentrations at 0 cm were generally higher than those at 25 cm depth, indicating that arsenic accumulated in the surface soils. In addition, a typical conceptual diagram of arsenic was developed to clarify the pollution process from feed to soil. Through health risk assessment of inorganic arsenic, the carcinogenic risk (CR) and non-carcinogenic risk (non-CR) were both negligible. The city of Jiaozuo had the highest CR and non-CR, which was 11 times higher than that of the city with the lowest risks. This study presents a clear picture and evaluation of arsenic pollution on chicken farms, inspiring future studies assessing arsenic pollution after the ban of organoarsenicals.

Introduction

Arsenic (As) is generally recognized as a toxicant and carcinogen that can cause serious disturbances of the cardiovascular and central nervous systems (Joseph et al., 2015). As is frequently found in poultry waste, which is often disposed of in open stockpiles or through farm land application, without appropriate leachate control or formal treatment. This can result in As contamination by poultry manure through precipitation and leaching into the surface soil, vadose zone, and groundwater. The poultry industry has been developing rapidly in China, accounting for an increasing proportion of the agricultural economy. The production of broiler chickens increased from 2 × 103 million in 1985 to 1 × 104 million in 2010 (Wei, 2014). The rapid development of poultry production has exacerbated As pollution from poultry manure.

As in poultry manure mainly comes from feed containing organoarsenicals. Organoarsenicals are low toxicity compounds that are used worldwide as feed additives to promote livestock growth, enhance meat pigmentation, and fight intestinal parasites (Kowalski and Reid, 1975; Lindsey and Konkel, 2016; Mangalgiri et al., 2015). There are many kinds of organoarsenicals, including roxarsone (ROX), p-arsanilic acid (ASA), carbarsone, and nitarsone, among which ROX is most common in chicken feed. Although most ROX is excreted unchanged to the environment through poultry urine and manure (Morrison and Louis, 1969), chickens fed with ROX had increased levels of inorganic arsenic (i-As) in livers and muscles when compared with blank controls (Lasky et al., 2004; Nachman et al., 2017). After ROX enters the environment, it is easily degraded into i-As, dimethylarsinate (DMA), monomethylarsonate (MMA), 3-amino-4-hydroxarsoneyphenylarsonic acid (HAPA), and other As species through biotic and abiotic action (Cortinas et al., 2006; Huang et al., 2019; Liu et al., 2017b, 2017c; Meng et al., 2019; Yang et al., 2016). Because of human and environmental health concerns, the European Union and the United States of America banned the use of ROX in 1999 (European Commission, 1999) and 2013 (U.S. Food and Drug Administration, 2013), respectively. In China, ROX and ASA were permitted to be used until May 1, 2019 (Ministry of Agriculture of the People’s Republic of China, 2018). However, ROX, which is stable and undergoes limited migration, has been used for decades, which has resulted in the accumulation of large amounts of As in the environment. Our previous study found that the As concentration in the compost site of a chicken farm in Liaocheng, China was significantly higher than that in the background soil (Liu et al., 2017a). The workers in chicken farms are likely exposed to As pollution through contact with ROX or i-As distributed in air, dusts, waste, and water. Because the toxicity of As is species dependent, describing the exact distribution of As species is important to evaluate their environmental impact.

The North China Plain is an important area for livestock breeding in China, and groundwater is an important water resource for daily life in this region. The As pollution from poultry farms could have great impact on residents in this region. The purpose of this study was to: (1) investigate the As pollution of chicken farm wastes in the North China Plain; (2) determine the different As species and concentrations in feed, manure, soils, and groundwater around the chicken farms; and (3) assess the health risk of i-As pollution in terms of heavy metal accumulation in soil. Because this study was carried out before organoarsenicals were banned, it provides a baseline that could be used as a comparison for future studies after the ban of organoarsenicals.

Section snippets

Sample collection and analysis

From July to August 2017, 138 chicken farms were surveyed and sampled in the North China Plain, including Hebei, and parts of Henan and Shandong provinces (Fig. 1). Most of the chicken farms concentrated in the central cities of Hebei Province, including Baoding, Hengshui and Cangzhou, while fewer chicken farms were located in the northern part of the North China Plain, including Beijing, Langfang and Tianjin. When compared with those in Hebei Province, the chicken farms were more scattered in

As speciation in chicken feeds

As speciation analysis for 138 feed samples showed that the detectable rates of As(III), DMA, MMA, HAPA, As(V), and ROX were 50.72%, 10.14%, 7.97%, 9.42%, 15.94%, and 0.72%, respectively (Table 2). The detectable rate of As(III) was the highest, followed by As(V). The main As species in the feed were i-As. Only one feed sample was found with ROX. The mean detectable concentrations of As(III), DMA, MMA, HAPA, As(V), and ROX were 37.5, 22, 16.5, 87, 152.6, and 17 μg kg−1, respectively. The mean

Conclusions

As pollution is often found in chicken farms of the North China Plain, with different As species detected in chicken feed, manure, and surface soil. Although ROX was previously reported to be common in chicken feed, it was not the main source of As in this study. As(III) was the main i-As species found in the manure, and As(V) was the predominant i-As species in surface soils beneath the accumulated manure. A typical pollution pattern of As was developed to clarify the pollution process from

Credit author statement

Yaci Liu: Writing – original draft, Methodology, Software. Xia Tian: Data curation, Validation. Shengwei Cao: Investigation. Yi Li: Supervision, Resources. Huijun Dong: Validation. Yasong Li: Writing – review & editing.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This research was funded by National Natural Science Foundation of China (No. 41907175), China Geological Survey Research Fund (No. JYYWF20182802), and China Geological Survey project (No.DD20190303). We thank Catherine Dandie, PhD, from Liwen Bianji, Edanz Editing China (www.liwenbianji.cn/ac), for editing the English text of a draft of this manuscript.

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