Elsevier

Agricultural Systems

Volume 186, January 2021, 102959
Agricultural Systems

Carbon footprint and water footprint of rice and wheat production in Punjab, India

https://doi.org/10.1016/j.agsy.2020.102959Get rights and content

Highlights

  • Nitrogen fertilizer use is the greatest hotspot for mitigation.

  • Geoclimatic factors do not majorly affect CF variation, management practices do.

  • Disparity between CROPWAT estimates and actual irrigation water use is established.

  • Solely using theoretical WF values can lead to wrong conclusions and inappropriate policies.

  • Government role is crucial in mitigating CF and WF by revamping policies.

Abstract

Carbon footprint and water footprint assessments can be powerful tools to guide sustainable food production systems. The present study simultaneously quantified the carbon footprint (CF) and water footprint (WF) of rice and wheat production in the five agro-climatic zones of Punjab, India using farm survey data. Further, the variability in CF among the five agro-climatic zones and farm sizes was analysed. The carbon footprint per unit area of rice and wheat was found to be 8.80 ± 5.71 and 4.18 ± 1.13 t CO2eq/ha respectively. The CF per tonne of rice and wheat was 1.20 ± 0.70 and 0.83 ± 0.23 t CO2eq/t respectively. Large farms had 39% lower CF per tonne of rice compared to small farms. Residue burning, direct methane emissions and fertilizer use were the most important factors that contributed to the CF of rice and wheat production in Punjab. Nitrogen fertilizer use was identified as the major hotspot for mitigation. The average WF of rice and wheat was found to be 1097 and 871 m3/t respectively. A disparity between CROPWAT estimates of blue WF and actual blue water use was established indicating the need for actual blue WF accounting, particularly for flood irrigated crop production. Additionally, policy measures based on ground situation are discussed and the major role of local government policies in mitigating carbon and water footprint is highlighted.

Introduction

Food production has large impacts on both global warming and freshwater consumption. The agriculture, forest and other land use (AFOLU) sector, which accounted for 24% of the global greenhouse gas (GHG) emissions in 2010, is the second largest sectoral GHG emitter (Smith et al., 2014). Agriculture is also the largest freshwater user accounting for 70% of global freshwater withdrawals, and 95% of water withdrawals in some developing countries (FAO, 2017). India, a leading food producer and predominantly agrarian nation, is the third largest GHG emitter (WRI, 2014), and a severely water-stressed country. It is among the 17 highly water-stressed countries in the world, with three times higher population than the combined population of all the other 16 countries (WRI, 2019). With its growing population, India is facing the twin challenge of increasing food production, given its limited water resources, while mitigating the associated GHG emissions.

Carbon footprint (CF) and water footprint (WF) are two widely used ‘pressure indicators’ that measure the human use of natural resources and the anthropogenic emissions; and can be used to direct mitigation policy (Ercin and Ertug Hoekstra, 2012). Few studies have utilised farm survey data for CF assessments (Yan et al., 2015; Arunrat et al., 2016; Zhang et al., 2017; Tahmasebi et al., 2018); and studies reporting WF of crops using farm level data are negligible (Cao et al., 2018; Ghosh and Chakma, 2019). Previous estimates of GHG emissions from crop production using life cycle assessment (LCA) approach in India were also based on secondary data sources (Pathak et al., 2010; Vetter et al., 2017; Benbi, 2018). Moreover, CF accounting at a high resolution, including crop management practices, like residue burning, has not been reported earlier in any of the LCA based study from India. Variability in CF among agro-climatic regions or farm sizes has not been studied previously in India. It is important to study regional variations to identify the hotspots across regions so that mitigation efforts can be specifically and effectively targeted. In this regard, primary data can capture the variability that is lost when statistical data is used (Schafer and Blanke, 2012). Based on first-hand information, survey-based studies reflect the existing regional diversity in farming practices that can be critical in environmental assessments (Zhang et al., 2017; Tahmasebi et al., 2018). This becomes significant in case of production of staple crops like rice and wheat that are produced in large quantities.

The study region, Punjab, also known as ‘the granary of India’ is the highest contributor to the central pool of grains in India (Government of India, 2018). It contributed 25.5% and 35.5% respectively in the central pool of rice and wheat during 2018–19 (ENVIS, 2020). The high productivity of the region was made possible due to introduction of irrigation, high yield variety (HYV) seeds, and consequent higher inputs of fertilizers and chemicals (Sarkar and Das, 2014). However, post green revolution, this has caused the over-exploitation of natural resources to the extent that sustainability of the present farming system of Punjab is uncertain unless major steps are taken towards improvement (Hira, 2009; Benbi, 2018).

Rice and wheat have the largest blue water footprints among crops (Mekonnen and Hoekstra, 2011). Water consumption is directly linked with the GHG emissions of groundwater irrigation, and therefore, there is an opportunity for concurrent mitigation of both. In Punjab, 99.3% of the gross cropped area is irrigated; of this, groundwater irrigation accounts for 71% (Statistical Abstracts of Punjab, 2019). Rice cultivation has expanded into non-suitable porous and coarse soils solely due to irrigation (Chauhan et al., 2012). Therefore, simultaneous assessment of CF and WF, based on farmer inputs, has the potential to reveal key insights such as the disparity between theoretical and actual water consumption. This disparity can be critical in policy framing. This study simultaneously estimated the CF and WF of crop production using farm survey data. CF and WF was previously estimated for tomato (Page et al., 2012) and pumpkin (Schafer and Blanke, 2012) using primary data of crop production. To the best of our knowledge, no such studies on grain production have been attempted globally. Therefore, the present study was planned to address this gap by quantifying both CF and WF of rice and wheat using farm survey data. It also aimed to analyse the variability in CF of different agroclimatic zones and farm sizes; assess the contribution of different inputs and suggest policy measures for mitigation of GHG emissions and water consumption from agriculture in a local as well as global context.

Section snippets

Study area

The study was conducted in the state of Punjab (extending from 29° 32′ to 32° 32′ N latitude and 73° 55′ to 76° 50′ E longitude) located in the north-western part of India. A part of trans Indo-Gangetic plains, Punjab is divided into five agro-climatic zones (ACZ) i.e. sub-mountain undulating zone (Zone I), undulating plain zone (Zone II), central plain zone (Zone III), western plain zone (IV) and western zone (V). Zone I & II are humid to sub-humid with an average rainfall of 900 mm; Zone III

Carbon footprint of rice and wheat

The mean carbon footprint per unit area of rice production in Punjab was found to be 8.80 ± 5.71 t CO2eq/ha and the CF per unit weight was 1.20 ± 0.70 t CO2eq/t. The CF of wheat was 4.18 ± 1.13 t CO2eq/ha and 0.83 ± 0.23 t CO2eq/t. Thus, the CF of the rice-wheat system in Punjab was 12.98 ± 5.82 t CO2eq/ha and 2.02 ± 0.78 t CO2eq/t. The CF of rice and wheat are presented in Table 2. The CF distribution for rice and wheat was positively or right-skewed (mean > median) with a Pearson coefficient

Carbon footprint of rice and wheat

Previous studies reporting CF of rice and wheat in India (Pathak et al., 2010; Vetter et al., 2017, 2019) have reported lower values as compared to this study. This could be because the afore-mentioned studies used national average inputs. Resource consumption in the study area (Punjab) is much higher as compared to India (average). The average fertilizer (N, P, K) consumption and agricultural energy consumption in Punjab was respectively 82% and 28% higher as compared to the national average

Conclusion

Carbon footprint and water footprint of rice and wheat production was quantified for five agroclimatic zones of Punjab using questionnaire-based survey data. The CF was found to be significantly different among the five zones. Crop residue burning was found to be the principal determinant of variation among zones. Rice production had a higher CF and a wider CF variability across regions as compared to wheat. The semi-arid zones (Zone IV and V) had higher CF for rice and wheat as compared to

Funding

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

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.

Acknowledgement

We thank Punjab Agricultural University, Ludhiana, Punjab and Krishi Vigyan Kendras (extension centers) of Ludhiana, Ballowal, Bhatinda, Fazilka, Ropar for their support in data collection. One of the authors acknowledges the fellowship received from the host institute (NIFTEM). We acknowledge the anonymous reviewers for their valuable inputs.

References (51)

  • K. Thanawong et al.

    Eco-efficiency of paddy rice production in Northeastern Thailand: a comparison of rainfed and irrigated cropping systems

    J. Clean. Prod.

    (2014)
  • S.H. Vetter et al.

    Greenhouse gas emissions from agricultural food production to supply Indian diets: Implications for climate change mitigation

    Agric. Ecosyst. Environ.

    (2017)
  • S.H. Vetter et al.

    Corrigendum to Greenhouse gas emissions from agricultural food production to supply Indian diets: Implications for climate change

    Agric. Ecosyst. Environ.

    (2019)
  • M. Yan et al.

    Carbon footprint of grain crop production in China - based on farm survey data

    J. Clean. Prod.

    (2015)
  • R. Aggarwal et al.

    Water resource management for sustainable agriculture in Punjab, India

    Water Sci. Technol.

    (2009)
  • S.A. Ali et al.

    Effect of different crop management systems on rainfed durum wheat greenhouse gas emissions and carbon footprint under Mediterranean conditions

    J. Clean. Prod.

    (2017)
  • N. Arunrat et al.

    Alternative cropping systems for greenhouse gases mitigation in rice field: a case study in Phichit province of Thailand

    J. Clean. Prod.

    (2016)
  • BSI and Carbon Trust

    Specification for the Assessment of the Life Cycle Greenhouse Gas Emissions of Goods and Services

    (2011)
  • X. Cao et al.

    Water footprint assessment for crop production based on field measurements: a case study of irrigated paddy rice in East China

    Sci. Total Environ.

    (2018)
  • CGWB (Central Ground Water Board). 2013. Ground water information booklet Hoshiarpur district, Punjab. Ministry of...
  • CGWB (Central Ground Water Board). 2011. Ropar District Punjab. Ground water information booklet Ropar district,...
  • ENVIS

    Envis Centre: Punjab

  • ENVIS

    Agriculture. Ministry of Environment, Forests & Climate Change, Govt of India

  • EPA

    List of Drinking Water Contaminants: Ground Water and Drinking Water, US Environmental Protection Agency

  • A. Ercin et al.

    Carbon and water footprints concepts, methodologies and policy responses

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