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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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Front. Environ. Sci. Eng.    2024, Vol. 18 Issue (4) : 43    https://doi.org/10.1007/s11783-024-1803-8
RESEARCH ARTICLE
Endosulfan residues and farmers’ replacement behaviors of endosulfan in the north-west inland cotton region
Shuyan Zhou1, Yang Zhang2(), Jingjing Wang3, Shikun Cheng1, Fuyan Zhuo4, Yun Hong3()
1. School of Energy and Environmental Engineering, University of Science and Technology Beijing 100083, China
2. Foreign Environmental Cooperation Center, Ministry of Ecology and Environment of the People’s Republic of China, Beijing 100035, China
3. United Nations Development Programme in China, Beijing 100600, China
4. National Agro-Tech Extension and Service Center, Beijing 100125, China
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Abstract

● The situation of endosulfan residues in cotton fields were assessed.

● A KAP survey was carried out for cotton farmers.

● Endosulfan sulfate was the main endosulfan residue in the soil.

● Cotton farmers scored low on knowledge about the phase-out of endosulfan.

We assessed the situation of endosulfan residues in cotton fields after the endosulfan ban came into effect and the current knowledge, attitude, and practice (KAP) of cotton farmers on the phase-out of endosulfan and the application of alternative technologies. Topsoil samples (n = 91) of cotton fields were collected from the major cotton-producing areas in China, namely the north-west inland cotton region, and the endosulfan residues were analyzed. A KAP survey was carried out for cotton farmers, and 291 questionnaires were distributed. The influences of gender, age, education background, cotton planting years, publicity and training, income sources, and other factors on cotton farmers’ KAP were analyzed. The results showed that endosulfan sulfate was the main endosulfan residue in the soil, followed by β-endosulfan and α-endosulfan, the average residual contents were 0.569, 0.139, and 0.060 µg/kg, respectively. The results of the KAP study showed that cotton farmers scored low on knowledge about the phase-out of endosulfan and the application of alternative technologies but high on attitude and practice. The number of family members, years of cotton planting, age, and the cotton-planting area had different degrees of influence on KAP scores. The training could significantly improve the KAP scores of cotton farmers; training should be more targeted and designed reasonably for key groups, such as men and the population under 30, followed by training them to use pesticides safely. For large-scale cotton growers, training should focus on green prevention and control technologies.

Keywords Cotton fields      Endosulfan residues      Farmers      KAP survey      Replacement behaviours     
Corresponding Author(s): Yang Zhang,Yun Hong   
Issue Date: 15 December 2023
 Cite this article:   
Shuyan Zhou,Yang Zhang,Jingjing Wang, et al. Endosulfan residues and farmers’ replacement behaviors of endosulfan in the north-west inland cotton region[J]. Front. Environ. Sci. Eng., 2024, 18(4): 43.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-024-1803-8
https://academic.hep.com.cn/fese/EN/Y2024/V18/I4/43
Compound Mean SD GM Min Max Percentiles DF(%)
P25 P50 P75 P90
α-ES 0.060 0.103 0.021 N.D. 0.655 N.D. N.D. 0.074 0.164 49.5
β-ES 0.139 0.216 0.050 N.D. 1.197 N.D. 0.061 0.179 0.237 60.4
ES-sulfate 0.569 0.991 0.151 N.D. 6.170 N.D. 0.189 0.707 0.698 71.4
∑ESs 0.769 1.294 0.260 N.D. 8.022 0.072 0.274 0.914 1.864 83.5
Tab.1  Basic statistical parameters of endosulfan residues in cotton field soil (n = 91, µg/kg)
Survey region Year α-ES β-ES ES-sulfate ∑ESs References
North-west inland cotton region, China 2020 0.142 ± 0.123 0.281 ± 0.257 0.828 ± 1.155 0.946 ± 1.518 This research
Daiyunshan region of Fujian, China 2009 0.81 ± 1.78 2.50 ± 9.05 6.93 ± 27.33 Qu et al. (2013)
Pearl River Delta, China 2009 0.19 ± 1.74 1.11 ± 5.45 3.81 ± 22.58 Dou & Yang (2015)
Wuhan, China 2009 0.34 ± 1.25 0.94 ± 3.89 1.28 ± 4.25 Zhou et al. (2013)
Huizhou City 0.56 ± 1.30 0.94 ± 1.08 10.11 ± 59.61 Ma Jin et al. (2010)
Shanghai, China 2007 0.13 ± 0.3 0.19 ± 0.54 BDL Jiang et al. (2009)
Campania, Italy 2011 0.41 ± 0.96 0.50 ± 1.32 1.06 ± 2.60 1.96 ± 3.75 Qu et al. (2017)
Himalayan region of India 0.22 ± 0.16 0.20 ± 0.29 0.19 ± 0.28 0.62 ± 0.73 Devi et al. (2015)
Punjab, Pakistan 2011 0.33 ± 0.41 3.0 ± 1.3 Syed et al. (2013)
Kathmandu, Nepal 2015 4.21 Pokhrel et al. (2018)
Republic of Korea 2015 0.06 0.09 0.63 0.77 Kim et al. (2020)
Tab.2  Comparison of endosulfan residues in soil from different region and countries (µg/kg)
Fig.1  The value of α/β-endosulfan.
Fig.2  The socio-demographic characteristic of participants.
Fig.3  The lowest, highest, and average scores for each KAP section.
Category Variable Classification Mean Standard deviation P value
Knowledge Gender Male 4.03 1.794 0.262
Female 4.28 1.816
The main labor force of cotton planting in the family Yes 4.06 1.767 0.249
No 4.38 1.958
Join a cooperative Yes 3.93 1.691 0.111
No 4.28 1.888
Cotton planting is the main income source of the family Yes 4.13 1.851 0.705
No 4.03 1.618
Attitude Gender Male 4.27 1.908 0.002
Female 4.91 1.487
The main labor force of cotton planting in the family Yes 4.43 1.807 0.275
No 4.74 1.759
Join a cooperative Yes 4.45 1.771 0.724
No 4.52 1.829
Cotton planting is the main income source of the family Yes 4.47 1.812 0.731
No 4.56 1.764
Practice Gender Male 6.13 2.111 0.003
Female 6.84 1.797
The main labor force of cotton planting in the family Yes 6.32 2.005 0.382
No 6.60 2.176
Join a cooperative Yes 6.34 2.063 0.783
No 6.40 2.017
Cotton planting is the main income source of the family Yes 6.25 2.049 0.054
No 6.81 1.934
Tab.3  T-test results of participants’ basic information, knowledge, attitude and practice
Category Variable Classification Average value Standard deviation P value
Knowledge Education level Below primary school 4.00 1.732 0.745
Primary school 3.46 2.145
Junior middle school 4.10 1.704
Senior middle school 4.20 1.772
Junior college or above 4.15 1.892
Age 20–30 3.44 1.826 0.074
31–40 4.02 1.893
41–50 4.19 1.794
51–60 4.37 1.659
More than 60 1.00 0.000
Cotton planting area 50 mu and below 4.17 1.977 0.179
51–100 mu 4.23 1.654
100–499 mu 4.13 1.684
500 mu and above 3.29 1.648
Permanent resident population of the family 1–2 4.68 1.911 0.002
3–4 4.14 1.728
5 and above 3.40 1.777
Cotton planting years 0–9 3.82 1.983 0.039
10–19 3.91 1.802
20–29 4.44 1.599
30-39 4.76 1.480
40 and above 3.86 1.864
Attitude Education level Below primary school 3.67 3.215 0.510
Primary school 4.85 1.519
Junior middle school 4.20 1.933
Senior middle school 4.53 1.768
Junior college or above 4.69 1.670
Age 20–30 3.59 1.760 0.042
31–40 4.33 1.768
41–50 4.68 1.680
51-60 4.66 1.974
60 and above 3.00 0.00
Cotton planting area 50 mu and below 4.65 1.641 0.025
51–100 mu 4.75 1.679
100–499 mu 4.02 2.068
500 mu and above 3.90 1.972
Permanent resident population of the family 1–2 5.02 1.545 0.006
3–4 4.50 1.768
5 and above 3.85 2.000
Cotton planting years 0–9 3.92 1.979 0.003
10–19 4.56 1.638
20–29 4.90 1.464
30–39 4.97 1.880
40 and above 4.57 2.507
Practice Education level Below primary school 5.00 2.646 0.245
Primary school 7.23 1.423
Junior middle school 6.10 2.223
Senior middle school 6.47 1.871
Junior college or above 6.43 2.066
Age 20–30 5.78 2.063 0.347
31–40 6.20 2.174
41–50 6.44 1.983
51–60 6.61 1.984
60 and above 8.00 0.00
Cotton planting area 50 mu and below 6.79 1.790 0.012
51–100 mu 6.30 1.989
100–499 mu 6.02 2.214
500 mu and above 5.48 2.502
Permanent resident population of the family 1–2 6.92 1.441 0.107
3–4 6.27 2.129
5 and above 6.19 2.133
Cotton planting years 0–9 5.47 2.282 0.000
10–19 6.69 2.013
20–29 6.84 1.613
30–39 6.90 1.520
40 and above 7.43 0.976
Tab.4  ANOVA results of participants’ basic information, knowledge, attitude and practice
Category Variable Classification Average value Standard deviation P value
Knowledge Relevant government departments have organized trainings on green prevention and control technologies Yes 4.31 1.761 0.000
No 3.30 1.757
Relevant government departments have publicized green prevention and control technologies Yes 4.20 1.801 0.025
No 3.45 1.697
Attitude Relevant government departments have organized trainings on green prevention and control technologies Yes 4.93 1.445 0.000
No 2.68 1.964
Relevant government departments have publicized green prevention and control technologies Yes 4.77 1.556 0.000
No 2.36 2.104
Practice Relevant government departments have organized trainings on green prevention and control technologies Yes 6.81 1.682 0.000
No 4.61 2.379
Relevant government departments have publicized green prevention and control technologies Yes 6.64 1.818 0.001
No 4.27 2.375
Tab.5  T-test results of government departments’ trainings and publicity on KAP
Category Knowledge Attitude Practice
Knowledge 1
Attitude r = 0.368 1
p = 0.000
Practice r = 0.212 r = 0.619 1
p = 0.000 p = 0.000
Tab.6  Pearson correlation coefficient between knowledge, attitude and practice
1 A Ahmad, M Shahid, S Khalid, H Zaffar, T Naqvi, A Pervez, M Bilal, M A Ali, G Abbas, W Nasim. (2019). Residues of endosulfan in cotton growing area of Vehari, Pakistan: an assessment of knowledge and awareness of pesticide use and health risks. Environmental Science and Pollution Research International, 26(20): 20079–20091
https://doi.org/10.1007/s11356-018-3169-6
2 P Chen, Q Xiao, J Zhang, C Xie, B Wang. (2020). Occurrence prediction of cotton pests and diseases by bidirectional long short-term memory networks with climate and atmosphere circulation. Computers and Electronics in Agriculture, 176: 105612
https://doi.org/10.1016/j.compag.2020.105612
3 N L Devi, I C Yadav, P Raha, Q Shihua, Y Dan. (2015). Spatial distribution, source apportionment and ecological risk assessment of residual organochlorine pesticides (OCPs) in the Himalayas. Environmental Science and Pollution Research International, 22(24): 20154–20166
https://doi.org/10.1007/s11356-015-5237-5
4 L Dou, G Y Yang (2015). Distribution characteristics and risk assessment of organochlorine residues in surface soil of Pearl River delta economic zone. Environmental Science, 36(8): 2954–2963 (in Chinese)
5 D Fang, L Ma, S Wei, Y Wang (2015). Investigation and risk analysis of agrochemical in major cotton producing. China Cotton, 42: 1–5 (in Chinese)
6 L L Guo, H J Li, A D Cao, X T Gong. (2022). The effect of rising wages of agricultural labor on pesticide application in China. Environmental Impact Assessment Review, 95: 106809
https://doi.org/10.1016/j.eiar.2022.106809
7 M A Hassaan, A El Nemr. (2020). Pesticides pollution: classifications, human health impact, extraction and treatment techniques. Egyptian Journal of Aquatic Research, 46(3): 207–220
https://doi.org/10.1016/j.ejar.2020.08.007
8 Y Huang, X Luo, L Tang, W Yu (2020). The power of habit: Does production experience lead to pesticide overuse? Environmental Science and Pollution Research International, 27(20): 25287–25296
https://doi.org/10.1007/s11356-020-08961-4 pmid: 32347493
9 A M HulsekempH AshrafiX Zheng F WangK A HoegenauerA B MaedaS YangK Stoffel M MatvienkoK Clemons, et al.. (2014). Development and bin mapping of gene-associated interspecific SNPs for cotton (Gossypium hirsutum L.) introgression breeding efforts. BMC Genomics 15: 945
10 H Jia, Y F Li, D Wang, D Cai, M Yang, J Ma, J Hu. (2009). Endosulfan in China 1-gridded usage inventories. Environmental Science and Pollution Research International, 16(3): 295–301
https://doi.org/10.1007/s11356-008-0042-z
11 Y F Jiang, X T Wang, Y Jia, F Wang, M H Wu, G Y Sheng, J M Fu. (2009). Occurrence, distribution and possible sources of organochlorine pesticides in agricultural soil of Shanghai, China. Journal of Hazardous Materials, 170(2–3): 989–997
https://doi.org/10.1016/j.jhazmat.2009.05.082
12 L Kim, J W Jeon, J Y Son, C S Kim, J Ye, H J Kim, C H Lee, S M Hwang, S D Choi (2020). Nationwide levels and distribution of endosulfan in air, soil, water, and sediment in South Korea. Environmental Pollution, 265(Pt B): 115035
https://doi.org/10.1016/j.envpol.2020.115035 pmid: 32806455
13 H Li, C Wang, W Y Chang, H N Liu. (2023a). Factors affecting Chinese farmers’ environment-friendly pesticide application behavior: a meta-analysis. Journal of Cleaner Production, 409: 137277
https://doi.org/10.1016/j.jclepro.2023.137277
14 X Lv (2012). Study on the influence factors of vegetable production safety and the farmers’ behaviors and attitude. Journal of Anhui Agricultural Sciences, 40: 12636–12639 (in Chinese)
15 Q X Ma Jin, Y Zhou. (2010). Multivariate -Geo statistics and GIS-base approach to studying residues and spatial distribution of OCPs in soil of Huizhou city, China. Acta Pedologica Subuca, 47(3): 439–450
16 T Mayire, T Asiye, Y Puchinay (2016). Study on the influencing factors of cotton farmer’s cognition on the risk of excessive application of chemical fertilizer. China Agricultural GreenDvelopent Research Society, 37(04): 38–42 (in Chinese)
17 Y Mou (2016). Knowledge, attitude and practice of using agricultural chemicals by rural residents of Jilin Province Chinese Rural Health Service Administration, 36(36): 222–225 (in Chinese)
18 National Bureau of Statistics, National Statistical Yearbook. 2020 (in Chinese)
19 B Pokhrel, P Gong, X Wang, M Chen, C Wang, S Gao. (2018). Distribution, sources, and air-soil exchange of OCPs, PCBs and PAHs in urban soils of Nepal. Chemosphere, 200: 532–541
https://doi.org/10.1016/j.chemosphere.2018.01.119
20 C Qu, S Albanese, A Lima, J Li, A L Doherty, S Qi, B De Vivo (2017). Residues of hexachlorobenzene and chlorinated cyclodiene pesticides in the soils of the Campanian Plain, southern Italy. Environmental Pollution, 231(Pt 2): 1497–1506
https://doi.org/10.1016/j.envpol.2017.08.100 pmid: 28964601
21 C K Qu, S H Qi, L Zhang, H F Huang, J Q Zhang, Y Zhang, D Yang, H X Liu, W Chen (2013). Distribution characteristics of organochlorine pesticides in soil from Daiyun mountain range in Fujian, China. Environmental Science, 34(11): 4427–4433
pmid: (in Chinese) 24455955
22 M Shahid, M S Khan. (2022). Ecotoxicological implications of residual pesticides to beneficial soil bacteria: a review. Pesticide Biochemistry and Physiology, 188: 105272
https://doi.org/10.1016/j.pestbp.2022.105272
23 K Sharafi, M Pirsaheb, S Maleki, H Arfaeinia, K Karimyan, M Moradi, Y Safari. (2018). Knowledge, attitude and practices of farmers about pesticide use, risks, and wastes: a cross-sectional study (Kermanshah, Iran). Science of The Total Environment, 645: 509–517
https://doi.org/10.1016/j.scitotenv.2018.07.132
24 A Sharma, V Kumar, B Shahzad, M Tanveer, G P S Sidhu, N Handa, S K Kohli, P Yadav, A S Bai, R D Parihar. et al.. (2019). Worldwide pesticide usage and its impacts on ecosystem. SN Applied Sciences, 1: 1446
https://doi.org/10.1007/s42452-019-1485-1
25 S Shekoohiyan, F Parsaee, S Ghayour. (2022). Assessment of knowledge, attitude and practice about biomedical waste management among healthcare staff of Fasa educational hospitals in COVID-19 pandemic. Case Studies in Chemical and Environmental Engineering, 6: 100207
https://doi.org/10.1016/j.cscee.2022.100207
26 J H Syed, R N Malik, D Liu, Y Xu, Y Wang, J Li, G Zhang, K C Jones. (2013). Organochlorine pesticides in air and soil and estimated air-soil exchange in Punjab, Pakistan. Science of Total Environment, 444: 491–497
https://doi.org/10.1016/j.scitotenv.2012.12.018
27 R Tang, L Yu, Y Gao, H Wang, Z Zheng, H Kahaerman, H Yang (2020). Assessment and screen of alternative pest control approaches for endosulfan in Xinjiang cotton production area. Xinjiang Agricultural Sciences, 57: 1071–1080 (in Chinese)
28 M Thiombane, A Petrik, M Di Bonito, S Albanese, D Zuzolo, D Cicchella, A Lima, C Qu, S Qi, B De Vivo. (2018). Status, sources and contamination levels of organochlorine pesticide residues in urban and agricultural areas: a preliminary review in central-southern Italian soils. Environmental Science and Pollution Research International, 25(26): 26361–26382
https://doi.org/10.1007/s11356-018-2688-5
29 UNEP (2011). Listing of Technical Endosulfan and Its Related Isomers. Nairobi: United Nations Environment Programme
30 J Weber, C J Halsall, D Muir, C Teixeira, J Small, K Solomon, M Hermanson, H Hung, T Bidleman. (2010). Endosulfan, a global pesticide: a review of its fate in the environment and occurrence in the Arctic. Science of Total Environment, 408(15): 2966–2984
https://doi.org/10.1016/j.scitotenv.2009.10.077
31 I C Yadav, N L Devi, J Li, G Zhang, P R Shakya. (2016). Occurrence, profile and spatial distribution of organochlorines pesticides in soil of Nepal: implication for source apportionment and health risk assessment. Science of Total Environment, 573: 1598–1606
https://doi.org/10.1016/j.scitotenv.2016.09.133
32 Y Yang, L Zhu, W Sun (2019). Farmers’ participation in agro-ecological transformation: expected benefits or policy incentives? China Population, Resources and Environment, 29(8): 140–147 (in Chinese)
33 Y Zhang, R Guo, Y Li, M Qin, J Zhu, Z Ma, Y Ren. (2022). Concentrations, distribution, and risk assessment of endosulfan residues in the cotton fields of northern Xinjiang, China. Environmental Geochemistry and Health, 44(11): 4063–4075
https://doi.org/10.1007/s10653-021-01111-w
34 Q Zhou, J Wang, B Meng, J Cheng, G Lin, J Chen, D Zheng, Y Yu. (2013). Distribution and sources of organochlorine pesticides in agricultural soils from central China. Ecotoxicology and Environmental Safety, 93: 163–170
https://doi.org/10.1016/j.ecoenv.2013.03.029
35 Z Zhou, Q Ma, Y Hou, D Yue, X Yao (2021). Study on factors influencing environmental protection willingness and behavior of cotton farmers in Xinjiang under the restriction of environmental regulation. Journal of Arid Land Resources and Environment, 35: 8–13 (in Chinese)
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