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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2023, Vol. 17 Issue (5) : 56    https://doi.org/10.1007/s11783-023-1656-6
RESEARCH ARTICLE
Relationship between groundwater cadmium and vicinity resident urine cadmium levels in the non-ferrous metal smelting area, China
Yujie Pan1, Yalan Li2, Hongxia Peng3, Yiping Yang2, Min Zeng4, Yang Xie5,6, Yao Lu2,7(), Hong Yuan2,8()
1. College of Environmental Sciences and Engineering, Peking University, Beijing 100091, China
2. Clinical Research Center, The Third Xiangya Hospital, Central South University, Changsha 410013, China
3. Department of Geography, School of Geography and Information Engineering, China University of Geosciences, Wuhan 430079, China
4. Wuhan Geological Survey Center of China Geological Survey, Wuhan 430205, China
5. School of Economics and Management, Beihang University, Beijing 100191, China
6. Laboratory for Low-carbon Intelligent Governance, Beihang University, Beijing 100191, China
7. School of Life Course Sciences, King’s College London, London, WC2R 2LS, UK
8. Department of Cardiology, The Third Xiangya Hospital, Central South University, Changsha 410013, China
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Abstract

● This study systematically examined the relationship between groundwater Cd and UCL.

● The study covered 211 UCL and sociological characteristic from nine groundwater samples.

● We found a significant positive correlation between groundwater Cd and UCL.

● Smoking status and education level also significantly affected UCL.

Cadmium (Cd) has received widespread attention owing to its persistent toxicity and non-degradability. Cd in the human body is mainly absorbed from the external environment and is usually assessed using urinary Cd. Hunan Province is the heartland of the Chinese non-ferrous mining area, where several serious Cd pollution events have occurred, including high levels of Cd in the urine of residents. However, the environmental factors influencing high urinary Cd levels (UCLs) in nearby residents remain unclear. Therefore, 211 nearby residents’ UCLs and the corresponding sociological characteristics from nine groundwater samples in this area were analyzed using statistical analysis models. Groundwater Cd concentration ranged from 0.02 to 1.15 μg/L, aligning with class III of the national standard; the range of UCL of nearby residents was 0.37–36.60 μg/L, exceeding the national guideline of 0–2.5 μg/L. Groundwater Cd levels were positively correlated with the UCL (P < 0.001, correlation coefficient 95 % CI = 9.68, R2 = 0.06). In addition, sociological characteristics, such as smoking status and education level, also affect UCL. All results indicate that local governments should strengthen the prevention and abatement of groundwater Cd pollution. This study is the first to systematically evaluate the relationship between groundwater Cd and UCL using internal and external environmental exposure data. These findings provide essential bases for relevant departments to reduce Cd exposure in regions where the heavy metal industry is globally prevalent.

Keywords Groundwater Cd      Urinary Cd level      Relationship      Non-ferrous metal smelting area      China     
Corresponding Author(s): Yang Xie,Yao Lu,Hong Yuan   
Issue Date: 30 November 2022
 Cite this article:   
Yujie Pan,Yalan Li,Hongxia Peng, et al. Relationship between groundwater cadmium and vicinity resident urine cadmium levels in the non-ferrous metal smelting area, China[J]. Front. Environ. Sci. Eng., 2023, 17(5): 56.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-023-1656-6
https://academic.hep.com.cn/fese/EN/Y2023/V17/I5/56
Sampling point Longitude Latitude Groundwater Cd concentration (ug/L) Average urinary Cd concentration (ug/L)
S1 113°04′32″ 27°53′02″ 1.159 18.169
S2 113°32′27″ 26°49′17″ 0.103 14.087
S3 113°10′23″ 27°47′01″ 0.094 7.692
S4 113°05′21″ 27°17′18″ 0.067 13.454
S5 113°12′10″ 27°05′30″ 0.063 11.520
S6 113°12′28″ 27°52′56″ 0.056 4.912
S7 112°37′39″ 28°02′34″ 0.186 9.044
S8 112°58′31″ 28°10′59″ 0.027 2.189
S9 113°07′40″ 28°10′16″ 0.026 4.108
Tab.1  Sampling point and Cd concentration of groundwater and urine
Fig.1  Carcinogenic and non-carcinogenic health risks of heavy metals in groundwater.
N (%) Obs Variable Total
Groundwater (ug/L) Median (P25, P75) 9 Groundwater Cd 0.094 (0.094,0.094)
Urine (ug/L) Median (P25, P75) 211 UCL 6.30 (3.97,10.76) ; 48.06 (42.27,51.61)
Sociological characteristics Gender, N (%) 211 Male 190 (90.05)
Female 21 (9.95)
Education, N (%) 211 Primary or below 6 (2.84)
Junior school 25 (11.85)
High school 119 (56.40)
College school 60 (28.44)
Postgraduate 1 (0.47)
Smoking, N (%) 207 No Smoking 61 (29.47)
Now 132 (63.77)
Before 14 (6.76)
Drinking, N (%) 207 No 137 (66.18)
Now 64 (30.92)
Before 6 (2.90)
Exercise, N (%) 209 No 78 (37.32)
Yes 131 (62.68)
Sleep quality, N (%) 210 Good 2 (0.95)
General 108 (51.43)
Poor 66 (31.43)
Need sleeping pills 34 (16.19)
Income (yuan), N (%) 211 < 10,000 6 (2.84)
10,000–30,000 59 (27.96)
30,000–50,000 77 (36.49)
50,000–100,000 56 (26.54)
100,000–200,000 12 (5.69)
> 200,000 1 (0.47)
Tab.2  Descriptive statistical analysis table (statistics of groundwater concentration, urine concentration, and sociological characteristics of 211 participants)
Fig.2  Relationship between total Cd of groundwater samples and UCL of urine samples of residents.
Fig.3  The comprehensive effects of groundwater Cd and sociodemographic factors on UCL.
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