Heat Stress in Beef Cattle: Climate Change and the Global Scenario – A Review

✅ 全文

肉牛热应激:气候变化与全球情景——综述

作者 Alok Wankar; G. N. Bhangale; S. N. Rindhe; Babu Lal Kumawat; Tawheed Ahmad Shafi 期刊 Annals of Animal Science 发表日期 2024 ISSN 1642-3402 DOI 10.2478/aoas-2024-0026 类型 原创研究 (Original Research)

📄 英文摘要 English Abstract

EN

Abstract With the increasing human population and urbanization, the demand for animal origin products is going to grow, especially in the developing nations till the 2050s and the production needs to be escalated and optimized with the changing climate. Heat stress is known to reduce the animal performance, production, shelf life and meat quality in all animals. The beef cattle are globally reared, following different managemental practices, so the usage of natural resources like land and water, manpower, fodders, production systems and the environmental impact also varies profoundly. Recent changes in the climate, global warming and depletion of resources have severely affected the production and heat stress is now a common constraint all over the world. Due to evolutionary diversification the tropical and temperate breeds are comparatively more thermotolerant, but the beef cattle in the colder regions are vulnerable to high environmental temperatures. Also, the production of beef increases the carbon footprint and is much less eco-friendly than growing plant-based protein. So, we comprehended the environmental temperature variation over the continents and impact of heat stress on beef cattle. Also, other factors like cattle population, land and pasture usage, livestock units in trade, methane emissions and gross beef production value were examined to evaluate the collective impact of all these on the beef sector. Our findings and predictions reveal that, in the advent of climate change, depleting natural resources and rise in the greenhouse gases, beef production will be a constant challenge, which can be only achieved by maintaining a healthy cattle population and optimum usage of natural resources. Only then can the beef sector be efficient, sustainable, and a profitable enterprise in future.

📄 中文摘要 Chinese Abstract

中文
由于人口增长、城市化和经济扩张,全球对包括牛肉在内的动物源性食品的需求正在增加。预计到2025年,牛肉消费量将增长0.75%,到2050年将翻一番。牛肉生产消耗的能源和自然资源远高于农业生产——例如,来自牛肉的1卡路里蛋白质所需的能量是玉米的75倍,生产1公斤牛肉需要15,500升水,而谷物仅需1,600升。牛占农业温室气体排放量的77%。气候变化伴随着环境温度升高和极端事件,加剧了肉牛的热应激,导致生产性能下降和经济损失。热带和温带品种具有更强的耐热性,但寒冷地区的牛则较为脆弱。

📋 英文结构化总结 English Structured Summary

全文整理

EN

Header:

Background The demand for animal origin foods, including beef, is increasing globally due to population growth, urbanization, and economic expansion. Beef consumption is expected to rise by 0.75% by 2025 and double by 2050. Producing beef consumes significantly more energy and natural resources than agronomic operations—for example, 1 calorie of protein from beef requires 75 times more energy than from maize, and 15,500 litres of water are needed per kg of beef versus 1,600 litres for cereals. Cattle are responsible for 77% of agricultural greenhouse gas emissions. Climate change, with rising ambient temperatures and extreme events, exacerbates heat stress in beef cattle, leading to inferior performance and economic losses. Tropical and temperate breeds are more thermotolerant, but cattle in colder regions are vulnerable.

Header:

Methods This is a review article. We gathered data on “heat stress in beef cattle”, global temperature variation, and associated factors such as cattle population, land usage, livestock units in trade, methane emissions, and beef production value. Data mining was performed using search engines and online platforms including Google Scholar, Science Direct, Microsoft Scientific Research Engine, PLOS ONE, CORE, ResearchGate, Semantic Scholar, Education Research Information Centre, science.gov, and faostat.org. The information was collated to assess the influence of climate change and contributory factors on the global beef sector. Other meats (pork, chicken) were excluded.

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Results Our findings and predictions reveal that, in the advent of climate change, depleting natural resources, and rising greenhouse gases, beef production will be a constant challenge. Heat stress reduces animal performance, production, shelf life, and meat quality in all animals. The beef sector can only be efficient, sustainable, and profitable if a healthy cattle population is maintained and natural resources are used optimally. Cattle are responsible for 77% of emissions from the agricultural sector, while monogastrics account for just 10%.

Header:

Data Summary Between 1990 and 2018, per capita meat consumption increased by 88.1% for unprocessed meat and 152.8% for processed meat products. Producing 1 calorie of protein from beef requires 75 times more energy than from maize, and 54 calories of fossil fuel are needed instead of 2–3 calories. It takes 15,500 litres of water to make 1 kg of beef compared to 1,600 litres for 1 kg of cereals. Projected GHG emissions from livestock by the 2050s may reach 114 gigatons of CO₂-equivalents, with 73 GtCO₂-eq from cattle.

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Conclusions Beef production will remain a constant challenge under climate change, depleting natural resources, and rising greenhouse gases. The only way to achieve efficient, sustainable, and profitable beef production is by maintaining a healthy cattle population and using natural resources optimally.

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Practical Significance Real-world applications include optimizing natural resource usage and maintaining healthy cattle populations to sustain beef production in the face of climate change. This approach can help reduce the carbon footprint of beef, improve resource efficiency, and ensure the beef sector remains a profitable enterprise.

📋 中文结构化总结 Chinese Structured Summary

中文

背景:

由于人口增长、城市化和经济扩张,全球对包括牛肉在内的动物源性食品的需求正在增加。预计到2025年,牛肉消费量将增长0.75%,到2050年将翻一番。牛肉生产消耗的能源和自然资源远高于农业生产——例如,来自牛肉的1卡路里蛋白质所需的能量是玉米的75倍,生产1公斤牛肉需要15,500升水,而谷物仅需1,600升。牛占农业温室气体排放量的77%。气候变化伴随着环境温度升高和极端事件,加剧了肉牛的热应激,导致生产性能下降和经济损失。热带和温带品种具有更强的耐热性,但寒冷地区的牛则较为脆弱。

方法:

本文为综述文章。我们收集了关于"肉牛热应激"、全球温度变化以及相关因素的数据,包括牛群数量、土地使用、贸易中的牲畜单位、甲烷排放量和牛肉产值。数据挖掘通过搜索引擎和在线平台进行,包括Google Scholar、Science Direct、Microsoft Scientific Research Engine、PLOS ONE、CORE、ResearchGate、Semantic Scholar、Education Research Information Centre、science.gov和faostat.org。对信息进行了整理,以评估气候变化及相关因素对全球牛肉产业的影响。其他肉类(猪肉、鸡肉)被排除在外。

结果:

我们的研究结果表明,在气候变化、自然资源枯竭和温室气体排放增加的背景下,牛肉生产将面临持续的挑战。热应激会降低所有动物的生产性能、产量、保质期和肉类质量。只有维持健康的牛群并优化利用自然资源,牛肉产业才能实现高效、可持续和盈利。牛占农业部门排放量的77%,而单胃动物仅占10%。

数据摘要:

1990年至2018年间,人均未加工肉类消费量增长了88.1%,加工肉制品消费量增长了152.8%。生产来自牛肉的1卡路里蛋白质所需的能量是玉米的75倍,需要54卡路里的化石燃料而非2-3卡路里。生产1公斤牛肉需要15,500升水,而生产1公斤谷物仅需1,600升。预计到2050年代,畜牧业的温室气体排放量可能达到1,140亿吨二氧化碳当量,其中牛贡献730亿吨二氧化碳当量。

结论:

在气候变化、自然资源枯竭和温室气体排放增加的背景下,牛肉生产将面临持续的挑战。实现高效、可持续和盈利的牛肉生产的唯一途径是维持健康的牛群并优化利用自然资源。

实际意义:

实际应用包括优化自然资源利用和维持健康的牛群,以在气候变化面前维持牛肉生产。这种方法有助于减少牛肉的碳足迹,提高资源效率,并确保牛肉产业保持盈利能力。

📖 英文全文 English Full Text

EN

Ann. Anim. Sci., Vol. 24, No. 4 (2024) 1093–1105 DOI: 10.2478/aoas-2024-0026 Heat stress in beef cattle: climate change and the global scenario – a review

Alok Khemraj Wankar1♦, Gajendra Namdeo Bhangale2, Sandeep Narayanrao Rindhe3, Babu Lal Kumawat4, Tawheed Ahmad Shafi5 Department of Veterinary Physiology, Department of Veterinary Parasitology, 3 Livestock Products and Technology, 4 Department of Gynaecology, 5 Department of Veterinary Medicine, College of Veterinary and Animal Sciences, Parbhani-431402, Maharashtra, Maharashtra Animal and Fishery Sciences University, Nagpur, Maharashtra, India ♦ Corresponding author: wankaralok@gmail.com; alokwankar@mafsu.in 1

Abstract With the increasing human population and urbanization, the demand for animal origin products is going to grow, especially in the developing nations till the 2050s and the production needs to be escalated and optimized with the changing climate. Heat stress is known to reduce the animal performance, production, shelf life and meat quality in all animals. The beef cattle are globally reared, following different managemental practices, so the usage of natural resources like land and water, manpower, fodders, production systems and the environmental impact also varies profoundly. Recent changes in the climate, global warming and depletion of resources have severely affected the production and heat stress is now a common constraint all over the world. Due to evolutionary diversification the tropical and temperate breeds are comparatively more thermotolerant, but the beef cattle in the colder regions are vulnerable to high environmental temperatures. Also, the production of beef increases the carbon footprint and is much less eco-friendly than growing plant-based protein. So, we comprehended the environmental temperature variation over the continents and impact of heat stress on beef cattle. Also, other factors like cattle population, land and pasture usage, livestock units in trade, methane emissions and gross beef production value were examined to evaluate the collective impact of all these on the beef sector. Our findings and predictions reveal that, in the advent of climate change, depleting natural resources and rise in the greenhouse gases, beef production will be a constant challenge, which can be only achieved by maintaining a healthy cattle population and optimum usage of natural resources. Only then can the beef sector be efficient, sustainable, and a profitable enterprise in future. Key words: beef cattle, heat stress, climate change, sustainable production, carbon footprint

Livestock provide us 33% or more of our dietary protein (Rosegrant et al., 2009), support over 600 million farmers and employs 1.3 billion humans, globally (Thornton, 2010). Animal origin foods (AOF), such as red meat and other AOF, are in higher demand than ever in developing countries. The demand for animal products has increased by the growing world population, urbanisation, economic expansion, online marketing and delivery, favourable trade policies, and shifting consumer tastes (OECD, 2022). The consumption of beef worldwide is expected to increase by 0.75% by 2025 and double by 2050 from 460 to 570 million tonnes (OECD-FAO, 2021; OECD, 2022; World Consumption of Meat, 2023). Between 1990 and 2018, the per capita meat consumption increased tremendously, 88.1% for unprocessed meat and 152.8% for processed meat products (Miller et al., 2022). Studies have shown that the consumption of meat is directly proportional to its per capita disposable income, urbanization, and wealth of the nations, especially the developing nations (Ritchie et al., 2017; Miller et al., 2022).

This increase in AOF comes at a significant price, firstly majority of the agricultural and arable land is used for growing animal feeds, instead of using it for human food production. Currently, we grow cattle food on an area that is seven times larger than that of the European Union. Moreover, 90% of the soybeans farmed worldwide are used as animal feed. Secondly, producing meat consumes much more energy and natural resources than that required for agronomic operations. For example, producing 1 calorie of protein from beef requires 75 times more energy than producing the same amount of protein from maize, and 54 calories of fossil fuel are required instead of just 2–3 calories. And it takes 15500 litres of water to make 1 kg of beef as compared to 1600 litres to grow 1 kg of cereals (World Consumption of Meat, 2023). And lastly, it is the environmental impact and the greenhouse gases (GHG) emitted from the beef production systems. Presently, it is estimated that cattle are responsible for 77% of the emissions (direct emissions and from manure management) from agricultural sector, while monogastrics account just for 10% (Herreroa et al., 2013). The

projected GHG emission from the livestock by the 2050s might reach 114 gigatons of CO2-equivalents (GtCO2-eq) out of which 73 GtCO2-eq, will be from cattle (World Consumption of Meat, 2023). In the past two to three decades, the climate has undergone major changes and become more unpredictable, significantly affecting agri-animal husbandry. Extreme climatic events like sustained high environmental temperatures and humidity, heat waves, solar flares, scanty rainfall, droughts not only directly affect the livestock welfare and production systems, but also affect all food resources, food security, sustainability, and its supply in the same year and subsequent years (Lamy et al., 2012; Rojas-Downing et al., 2017). Several international agencies like Intergovernmental Panel on Climate Change (IPCC) and United States Environmental Protection Agency (USEPA) have predicted a steady increase in ambient temperatures (USEPA, 2016; IPCC, 2018). Numerous studies have confirmed that heat stress results in inferior performance, and production in cattle, culminating into billions of dollars of economic losses (St-Pierre et al., 2003; Nardone et al., 2010; Wankar et al., 2021; Mishra 2021). Producing meat in the context of climate change is therefore a challenging task; however, cultural preferences, consumer preferences, and health considerations also have a role in determining how much beef is consumed (De Boer et al., 2014; Graca et al., 2016; Leroy and Barnard, 2020; Malek and Umberger, 2021). Still, it is speculated that the meat industry will continue to grow till the year 2030 and further increase by up to 70% or more in coming times (FAO, 2003; Datar and Betti, 2010; Gaughan et al., 2010), primarily driven by the population growth, modernization, operational optimization, and cleaner value-added meat production (Kristensen et al., 2014; Gokirmakli and Bayram, 2017). Building on this background, we gathered data on “heat stress in beef cattle”, global temperature variation and other associated factors like cattle population, land usage, livestock units in trade, methane emissions and beef production value. Different search engines, online platforms, national and international websites like Google Scholar, Science Direct, Microsoft Scientific Research Engine, PLOS ONE, CORE, ResearchGate, Semantic Scholar, Education Research Information Centre, science.gov, faostat.org were used for data mining. Finally, we collated the information to assess the influence of climate change and contributory factors on the global beef sector. Other meats, pork and chicken meats were excluded from the study as it is not possible to comprehend everything at once, and the present work is restricted to beef sector only. Heat stress in animals and why high yielders are more affected due to heat stress? Climate has a substantial impact on livestock systems (both intensive and extensive), with extensive or pastoral systems being more severely affected, resulting in poor

animal growth, reproduction, performance and, in turn, productivity (Adams et al., 1998). Animals have evolved in a peculiar, eco-climatic zone with essential acclamatory adaptations, that allow them to be most comfortable and productive there. Extreme climatic events like high temperatures, humidity, or heat waves etc., compromise their thermoregulatory ability and they are unable to dissipate excess metabolic heat, making them vulnerable to deleterious effects of heat stress (Baumgard and Rhoads, 2012). In order to maintain homeothermy, various homeostatic responses are immediately activated to decrease excess metabolic heat generation, store it, and promote dissipation (Wankar et al., 2014; Herbut et al., 2021; Vasconcelos et al., 2020). Animals’ breed, stage of production and pregnancy, management, geographical location, physical attributes, and thermal plasticity, all collectively influence animals’ acclimation, acclimatization, and adaptation capacity to heat stress (Robertshaw, 1985; Hansen, 2004; Brown-Brandl and Jones, 2011; Saizi et al., 2019). High producing animals are already at the threshold of their maximum production and generate more heat energy which continues to accumulate, if the environmental conditions are adverse (Collier et al., 2019). Therefore, the more an animal produces, the more metabolic heat it generates and additional thermoregulatory pathways are triggered to maintain homeothermy, making the animal more vulnerable to heat stress (Ravagnolo and Misztal, 2000). Though, the selective breeding programs have multiplied production several fold over the past 3–4 decades, but it rendered livestock more vulnerable to changing climate, global warming, and heat stress (Renaudeau et al., 2012; Collier et al., 2019). Heat stress in beef cattle In contrast to the intensive dairy systems, beef cattle are primarily reared on pastoral (viz. feedlot, range) or semi-intensive facilities which provides them substantial access to shade, water, free movement, and behavioural expression. However, this also makes them easily susceptible to harsh environmental conditions (van den Polvan Dasselaar, 2015; Magrin et al., 2017; Rojas-Downing et al., 2017). Beef cattle respond differently to heat stress than dairy cows, owing to lower metabolic heat generation, breed variability, and their ability to withstand comparably higher temperature-humidity index (THI) (St-Pierre et al., 2003; Nardone et al., 2010). This does not imply that they are immune to heat stress and all the stress responses are activated once the THI exceeds the threshold (78–80, depending on the breed and geographical location). There is immediate reduction in feed intake which is more pronounced, especially if feed is of poor quality (Mitlöhner et al., 2002; Van Laer et al., 2014; Yadav et al., 2016; Wankar et al., 2017, 2019; Marchesini et al., 2018; Thornton et al., 2022). However, studies indicate that heat stress not only directly reduces feed

consumption, but it also has an indirect effect on energy metabolism, digestive processes, and nutrient assimilation. (Busby and Loy, 1997; Wheelock et al., 2010; Mahjoubi et al., 2014; Wankar et al., 2019). Soon after the decrease in feed intake, thermoregulatory processes like sweating, panting, increased water consumption, and behavioural changes are activated. The animals often prefer to move and feed during the cooler hours of the day (Magrin et al., 2017). All of these acclimatory responses divert the productive energy towards maintaining homeostasis resulting in poor growth rate, lower average daily weight gain, poor performance, and longer recovery periods in beef animals (Kadzere et al., 2002; Ravagnolo et al., 2002; Nardone et al., 2010; Marchesini et al., 2018). Heat stress is more difficult to quantify in beef cattle since there are several phases viz. the gestational phase, growing phase, adult phase, and the finishing phase. The impact of heat stress during postnatal life is well documented, but prenatal exposure and its effects are still not very clear. Thermal stress during the embryonic period has been shown to cause irreversible changes in animal physiology, behaviour, and metabolism, resulting in poor birth weight, growth, and meat composition (Foxcroft et al., 2006; Tao and Dahl, 2013; Zhang et al., 2020). While, in growing and finishing cattle heat stress reduces the weight gain, protein gain, fat gain and carcass yield (Geraert et al., 1996; Marchesini et al., 2018; Summer et al., 2019). Other meat attributes like meat quality, tenderness, colour, and pH also alter, lowering the meat price and its acceptability to consumers (Mitlöhner et al., 2001; Sofos, 2008; Johnson et al., 2015; Sant’Anna et al., 2019; Abhijith et al., 2021). A recent study (Bunning and Wall, 2022) reported poor growth rates, average daily carcass gain, carcass

weight and 200-day weight gain in heat stressed beef calves, while the age at slaughter and production costs increased significantly. Similarly, another study has identified metabolic and molecular biomarkers, their expression in heat stressed beef cattle and how they alter the stress response, modulate animal performance, growth, and meat yield (Kim et al., 2022). Other researchers have mainly attributed poor growth and compositional changes in heat stressed livestock to down regulation of DNA, RNA and protein synthesis, protein deposition and elevated fat accumulation (Jacob, 1995; Geraert et al., 1996; Ronchi et al., 1999; O’Brien et al., 2010). Higher protein turnover and proteolysis for energy production via gluconeogenesis, exacerbates the protein turnover and deposition in heat stressed cattle (Danfar, 1994; Temim et al., 2000; Kuo et al., 2013; Gao et al., 2017). Data analyses Data was sourced from FAOSTAT website for the period 1961 till 2020 and changes in average environmental temperature, number of cattle (cattle and buffalo), land usage, area under meadows and pastures, total livestock units (LSU) percent share in trade, methane emissions and gross production value of beef were analysed, and comparisons were made for the last two decades, i.e., 2000–2010 and 2010–2020, respectively. Predictions for all the above variants were made by using Microsoft Windows, IBM Excel Package forecast functions, for the years 2025 and 2030. The results of analysis are presented as Tables 1–5 and Supplementary Tables 1–6, in the text, respectively. Similarly, Microsoft Windows, IBM Excel Package were used to plot maps for the current buffalo, cattle populations, country wise meat and per capita beef consumption, which are depicted in Figures 1, 2, 3 and 4 respectively.

Table 1. Continent-wise ambient temperature (°C) Year Africa % Change America % Change 0.45 Asia % Change Europe 0.70 % Change 1.34 Oceania % Change 2000 0.78 2010 1.48 89.90 1.31 191.15 1.27 82.57 0.81

–39.22 0.16 0.69 308.88 2020 1.21 –18.11 1.33 1.52 1.53 20.11 3.35 311.78 1.38 99.86 2025 1.31 8.31 1.37 3.14 1.49 –2.61 2.13 –36.38 1.12 –18.39 2030 1.43 9.11 1.50 9.36 1.63 9.50 2.33 9.23 1.22 8.70 Europe

% Change Oceania % Change *Authors’ own calculations based on FAOSTAT data. Table 2. Global cattle population (millions) Year Africa % Change America % Change 460.69 Asia % Change 2000 232.23 2010 298.26

28.43 509.48 10.59 441.99 0.05 124.44 –15.86 37.34 –0.02 2020 376.31 26.17 531.12 4.25 465.67 5.36 116.12 –6.69 34.05 –8.82 2025 352.34 –6.37 568.15 6.97 488.34 4.87 107.11 –7.76 39.76 16.77 2030 372.20

5.64 587.54 3.41 501.70 2.74 95.38 –10.95 40.52 1.91 *Authors’ own calculations based on FAOSTAT data. 441.78 147.90 37.35 1096 A.K. Wankar et al. Table 3. Global buffalo population (millions) Year Africa

% Change America % Change Asia 1.11 % Change Europe 159.35 % Change Oceania 0.23 % Change 2000 3.53 2010 3.82 8.22 1.19 7.21 188.63 18.37 0.39 69.57 0.00015 0.00013 15.38 2020 1.35 –64.66 1.92 61.34 197.38

4.64 0.48 23.08 0.000174 16.00 2025 3.83 183.70 1.96 2.08 212.41 7.61 0.23 –52.08 0.000181 4.02 2030 4.00 4.44 2.12 8.16 222.43 4.72 0.19 –17.39 0.000191 5.52 % Change Europe % Change Oceania % Change

*Authors’ own calculations based on FAOSTAT data. Table 4. Land usage for cattle (LSU/ha) Year Africa % Change America % Change Asia 2000 0.11 2010 0.14 27.27 0.31 0.34 9.68 0.20 0.20 5.00 0.21 0.24 –12.50

0.09 0.07 28.57 2020 0.17 21.43 0.36 5.88 0.22 4.76 0.20 –4.76 0.08 –11.11 2025 0.15 –6.47 0.37 3.06 0.20 –5.45 0.22 14.50 0.09 13.75 2030 0.16 5.03 0.38 2.96 0.20 –0.48 0.23 0.44 0.09 4.40 % Change Oceania

% Change LSU = Total livestock units, ha = hectares. *Authors’ own calculations based on FAOSTAT data. Table 5. Area under meadows and pastures (1000 ha) Year Africa % Change America % Change Asia 44897.58

% Change Europe 2000 21375.48 2010 21668.26 1.37 29034.41 –35.33 45958.70 56479.38 –18.63 66303.17 66442.22 –0.21 114.90 171.64 2020 22091.69 1.95 22624.27 –22.08 41354.79 –10.02 63578.61 –4.11 124.23

8.12 2025 21949.02 –0.65 11317.52 –49.98 34226.57 –17.24 62964.11 –0.97 137.92 11.02 2030 21976.75 0.13 4558.15 –59.72 29752.83 –13.07 62228.36 –1.17 147.85 7.20 ha = hectares. *Authors’ own calculations based on FAOSTAT data.

Sourced from FAOSTAT, 2020. Figure 1. Global buffalo population 42.29 Heat stress in beef cattle, global scenario Sourced from FAOSTAT, 2020. Figure 2. Global cattle population

Sourced from worldpopulationreview.com: Meat Consumption by Country 2023. Figure 3. Global per capita meat consumption

Sourced from worldpopulationreview.com: Meat Consumption by Country 2023. Figure 4. Global per capita beef consumption 1097 1098 A.K. Wankar et al.

The global scenario and consumption of beef Global beef consumption significantly increased after World War II due to the start of industrialization, modernization, intensive cattle farming, food processing and urbanization. In addition, rising per capita income, consumer awareness, dietary preferences, and eating habits have accelerated the transformation of the food industry (OECD, 2022). Figures 3 and 4 show the current global status of beef consumption as well as the per capita consumption in different countries. The worldwide beef sector is driven by four key factors: 1. Increased consumption 2. Organized farming operations and distribution 3. Government policies, trade, and commerce 4. Climate change (Cerles et al., 2017; Hocquette et al., 2018). The per capita meat consumption (unprocessed or processed) increased tremendously in Southeast and East Asia, Latin America, Caribbean region, and sub-Saharan Africa during the period of 1990 to 2018. China, Japan, Brazil, South Africa, and Mexico topped the beef consumption. Contrarily, during the same period (1990–2018) beef consumption decreased in Central or Eastern Europe, Middle East, North Africa, other developed countries and central Asia, and the decline was between 14.0% and 47% for nations like Russia, Germany, Iran, and France (Miller et al., 2022). Despite this, both in developed and developing countries, beef consumption is rising, with a 15% increase predicted by 2031 (Pohjolainen et al., 2016). The consumption of beef will increase by 10% in Asia and the Pacific region during the next ten years, but it will decrease (by between 2 and 15%) in the United States, Argentina, Canada, Brazil, and Oceania (Whitnall and Pitts, 2019; OECD-FAO, 2022). Depleting cattle herds, low- or poor-quality feed, saturated markets, growing awareness of environmental impact and carbon footprint, health concerns, and animal welfare are the main causes of this drop in beef consumption (Graca et al., 2016). Brazil and the United States are the major exporters of beef to the world in the present and in future also. Other countries for example Argentina, Australia, India, Pakistan, the European Union, Thailand, Paraguay, and Turkey will also contribute significantly in the global exports. China, the Middle East, and Indonesia will be the major importing nations (OECD-FAO, 2022). Looking at the scenario, it appears that demand and production for beef will increase until 2031, but the increasing proportion from chicken and pork cannot be overlooked, which are the two most popular meats in the world. Our quest to find an alternative environmentally friendly source of protein appears faraway and we are mostly dependent on AOF. Climate change, the present status, and future implications on beef sector Americas The Americas can be sub-divided into the Northern and the Southern America, each of which have diversified beef producing systems. Feedlot system which primarily constitutes the cow-calf system, the stocker sys-

tem and feedlot-finisher system dominates the United States (US) and Canada. While beef cattle are mostly raised extensively in the southern areas (Brazil, Argentina, and Mexico) (Galyean et al., 2011). Climate and environmental conditions directly affect the monsoons and the summers, grazing season, ecosystems, crops, and fodders grown for the livestock, which in turn influence the marketability of the beef cattle (Polley et al., 2013; Drouillard, 2018; Havstad et al., 2018). The feedlot systems will be impacted by the climate’s rapid change, and vector-borne diseases will re-emerge as a result (Short et al., 2017). Also, the pastoral ecosystems, forage production, soil degradation, water scarcity and associated heat stress, animal death, decreased production and economic loss might be more pronounced (Havstad et al., 2018). The US uses roughly 41% of the total land area, whereas Mexico uses about 60% of it for livestock grazing on common or under-utilised pastoral land (Peel et al., 2010). In terms of the natural resources consumed, beef production by feedlot method seems most efficient (Capper, 2011). Transformation of the beef industry began during late 1950s and in the last 2–3 decades, we witnessed an astonishing degree of mechanization and specialization, with bigger well organized production units. Another prominent driver was involvement of the world’s largest corporations in the lucrative and ever-expanding food industry (MacDonald and McBride, 2009). However, the beef herds have seen decreasing patterns in the United States and Canada, and the size of the feedlot system has decreased from 34 million to 30.9 million heads (Galyean et al., 2011). In contrast, the cow herds in South America are stable and even growing slightly (Index Mundi, 2011). The US carbon footprint also substantially decreased as a result of the sector’s change, intensification, and development, increasing the value and environmentfriendliness of the industry (Capper, 2011). The demand for beef is expanding rapidly both worldwide and in the south Americas, while the domestic US consumption is fairly stable and can remain same by the 2030s (OECDFAO, 2017). New developing nations are now emerging as major exporters and competing with the giants like the United States, the European Union (EU) or Oceanic countries for the beef trade (OECD-FAO, 2017). The Americas witnessed an astonishing 191.15% temperature rise during 2000–2010. Following then, the environmental temperatures are expected to grow consistently till 2023 (Table 1). Cattle populations grew marginally over the last two decades and a small increase is anticipated in the next decade as well (Table 2). While, the buffalo population increased from 2010, reached maximum till 2020 and thereafter only a minimal growth is expected by 2023 (Table 3). The land usage increased from 2000 to 2020, and the predicted growth by the 2030s looks stagnant (Table 4). Meadows and pastures have declined here, since the beginning of the 20th century and same trend is predicted till the 2030s (Table 5).

From supplementary tables, we can see that the share of cattle in the total trade is declining in Americas, while the methane emissions have increased steadily (Supplementary Tables 1, 3, 4). The value of beef production grew substantially during 2000 to 2010 (from 41,416,764.00 to 89,398,768.00, 1000 US$), however for the period 2010–2020 a major decrease was recorded but expected returns appear promising by 2025 and 2030 (Supplementary Table 5). The production potential of cattle is fully exploited in the well-developed, organized American beef sector. The sector is equipped with well-established automation, processing, packaging, distribution, and supply chain. It is both a major beef importer and exporter nation. A major concern here are the already saturated domestic and international markets and the emergence of new players like Latin American nations, Australia, Africa, and India etc. The environmental temperatures ought to rise with time and maintaining a mature and maturing herd of thermotolerant beef cattle, is essential for sustained production. Shrinking usable lands, pastures and declining share in the trade are other issues to be critically addressed. For sustainable meat production immediate actions are required to reduce the GHG’s emissions and the carbon footprint. For the south American beef producing nations, changing climate demands the need for improved management, distribution systems, beef quality, trade policies and curbing environmental impact for sustainable beef production in the future. Africa The Africa region is still to be fully explored, with rich natural resources and animal population. Africa will be one of the continents with the fastest population growth when it reaches 2.5 billion people by 2050, up from the current 1.5 billion. The meat business has grown quickly over the past 10 to 15 years as a result of the expanding human population, rising per capita GDP, changing agricultural and animal husbandry practices, consumer preferences, and consumer demands (AfDB, 2017; FAO, 2017; World Bank, 2017). Today Africa produces more than 6% of the total beef and the production has doubled in the last two decades from 11.59 to 19.88 million metric tons. Beef consumption also increased and some of the leading producers, consumers and exporters of beef are South Africa, Botswana, Namibia, Sudan, Nigeria, Egypt, Ethiopia, Kenya, Chad and Tanzania (Benson, 2022; Jenane et al., 2022). The African beef industry is nascent and still developing in comparison to the Americas, Europe, Australia, or Asia, but with supportive government policies and foreign or domestic investment, the potential for expansion here is infinite, and soon Africa can become a global beef exporting global zone (African Business, 2019). A major constraint to the beef sector in Africa, is the hot climate and the effect of climate change is more pronounced in some of the vulnerable regions (Maplecroft, 2015). International climate agencies have already

warned about a drastic decrease in annual rainfall, particularly over the Southern African region, which is the top beef producer and exporter (Serdeczny et al., 2016). Also, by the end of the 21st century the mean temperature can rise by 2°C or more, affecting the agriculture, water ecosystems and predisposing livestock to heat stress (Pereira, 2017). The need to reduce the greenhouse gases (GHG) emissions for sustainable, cleaner production remains another major concern for the beef units (Bogale and Temesgen, 2021). Despite having vast herds of thermotolerant beef cattle, if the policies, management, and trade in this region are not improved and optimised, Africa will become the world’s largest importer rather than an exporter of beef (Christiaensen, 2020; Seleshi, 2021). The geographical location makes the African continent inadvertently warmer, and during last two decades, the environmental temperatures increased rapidly and same trend is expected through the 2030s (Table 1). The total cattle population in Africa increased during 2000–2020, and our results show a minor decline by the year 2025 followed by a slight increase by the 2030s (Table 2). Like cattle, the buffalo population in Africa also increased till 2010, then decreased drastically by a 64.66% in 2020 and thereafter, it is expected to rise again by the year 2030 (Table 3). The land usage by the cattle was maximum till the 2020s, then a drop is seen until 2025, followed by a slight increase till the 2030s (Table 4). In Africa, the acreage used for pastures and meadows remained constant from 2000 to 2020, and no significant changes are anticipated by the year 2030 (Table 5). From Supplementary Table 1 and 2, we can see that the livestock share in the trade has substantially decreased between 2010 and 2020 and continued to fall until 2025 for cattle, unlike the buffalo. Further decline in the share is expected for both cattle and buffalo by the 2030s. Methane emissions from cattle were highest for the last three decades, and thereafter a minor decrease is predicted in 2025, and then again, the emissions are to elevate by the 2030s (Supplementary Table 3). Comparatively, the GHG emissions from the buffalo were low during 2000–2010, decreased significantly by 2020 and are expected to steeply rise by the 2030s (Supplementary Table 4). The value of gross production of meat increased significantly between the years 2000 and 2010, declined insignificantly in the 2020s, and will continue to maximize in the 2030s (Supplementary Tables 5 and 6). The beef sector here is mainly extensive, pastoral, unorganized and so are the distribution systems. Still the growth of African beef industry is outstanding in the last decade. Selected African nations are major exporters of beef to the European Union. The cattle are average producers, but are fairly resistant to heat stress. Also, the increasing numbers of cattle and buffaloes is quite appreciable here. Here, the use of the land, meadows, and other natural resources can be greatly enhanced to increase productivity. The share of the beef in the trade and the revenue generated needs to be systematically boosted. Currently there is no recording of the GHG emissions

from the sector, but has to be critically monitored to reduce the environmental impact in future. Traditionally, as the summer heat intensifies, more and more farmers shift to rearing goats, sheep, and beef cattle, instead of dairy cattle. As Africa is naturally the warmest continent, this tradition needs to be combined with the modernization and production intensification in order to increase global distribution of high-quality meat and boost the continent’s economy. Asia The Asian beef industry is currently expanding rapidly to accommodate the growing human population, industrialization, urbanization, and cultural transformations. China, Japan, Taiwan, Singapore, and Korean Republic are the major importers of beef from the US, Brazil, Argentina, Australia, and Europe (OECD-FAO, 2017). The demand for beef and veal is growing rapidly in India in last two decades, and here mostly the water buffalo is used for beef production as cow slaughter is banned (Landes et al., 2016). In Asia, China consumes the most beef and imports the most beef (Zhang et al., 2015). However, traditionally China has always been a major beef producer, but recent rise in beef imports is essential to match the increased beef consumption, population explosion and largescale migration of people from rural to urbanized regions (National Bureau of Statistics of the People’s Republic of China, 2016; Wang et al., 2016). Other Asiatic nations like Thailand, Malaysia, Indonesia, Vietnam, Philippines, Myanmar, Brunei, Laos, Cambodia, and the Association of South East Asian Nations (ASEAN) where the labour is still cheap and economy is growing, will be major beef consumer and producer markets globally (Bunmee et al., 2018; MLA, 2020). The Asian meat industry is predicted to grow at a rate of 5.10% and beef markets alone are to generate more than $33,382.50 million with additional $57,360.50 million from the packaged meat industry, by the year 2026 (Research and Markets, 2023). After the COVID-19 pandemic and other quality control issues, the recovery of the beef industry is slow here, preventing the exports to developed nations. Although the beef consumption has increased significantly in nations like China, Pakistan, and Turkey the exports remain low and most of the Asiatic nations are major beef importers (Global Trade Magazine, 2020). In the advent of the changing climate, beef production is a challenge in itself and there has been an imbalance between the demand and supply equation for AOF in Asia. Asia’s animal husbandry industry is under threat from progressively rising environmental temperatures, frequent droughts, and erratic rainfall. During the summer, a rise in ambient temperatures is already perceptible throughout all of northern Asia. While at the same time the rainfall has precipitously decreased in China, India, Indonesia, Japan, Philippines, and Pakistan (Cruz et al., 2007). The harsh climatic conditions, poor nutrition, and

management, semi-intensive to extensive cattle rearing makes Asia one of the top GHG emitters on the global scale. In future, sustainable beef production under the climate change scenario, to supply the human population and to export the surplus meat will be a major challenge. Table 1 shows that the environmental temperature increased rapidly in Asia till 2010 and continued to grow by 2020. Thereafter, it is expected to decrease in 2025 and again increased by 2023, respectively (Table 1). Only a modest increase in the population of cattle and buffalo was observed until the year 2020, and the same slow growth trend is anticipated to continue into the 2030s (Table 2 and 3). Land usage by cattle was optimum till the 2020s, and it can be seen that thereafter it will decline steeply by the year 2025 and 2030, respectively (Table 4). Similarly, there is a significant reduction in the total meadows and pasture area in Asia, since the year 2010 and our predictions show a similar trend till the year 2030 (Table 5). Despite the largest cattle population (cattle and buffalo) in the world, Asia’s share in the trade is now small, has been dwindling in the previous 20 years, and is predicted to continue declining until the year 2030 (Supplementary Table 1–2). Since the beginning of the 20th century, a continuous increase in methane emissions is evident from the beef cattle and buffaloes, and they are expected to grow further by the end of the 2030s (Supplementary Table 3–4). The revenue generated by buffalo meat production continued to increase through the 2020s, but that of cattle meat production dropped by 2020 (Supplementary Table 5–6). Expected trends for cattle meat appear positive during 2025–2030, but buffalo meat will decrease slightly in 2025, and then increase again by the 2030s (Supplementary Table 5–6). Asia has the world’s largest populations of people, cattle, and buffalo. With the rapid growth in human population, urbanization, and economy in the entire region the demand for animal foods has also substantially increased. The animals in this area are average to elite yielders and evolved in hot temperate to tropical conditions, making them thermotolerant to heat stress. Here the major constraints are poor quality feed, management, pastoral or extensive rearing and prolonged harsh environmental conditions. The beef cattle often have infectious or zoonotic diseases which makes beef exports to developed nations impossible. Also, there is a direct conflict for natural resources like land and water resources for humans or livestock. Countries like China are the global importers of beef, although they also produce beef, but it is insufficient to fulfil the demands. The beef cattle and buffalo herd, seems to grow here, even with the climate change. However, the use of land and natural resources can be tightly optimized, for both humans and livestock. The prevalence of white meats has substantially reduced the cattle share in the trade, but the value of beef production and the potential for economic gains are rising, and still need to be fully explored. The steady increase in the GHG emissions from the beef systems will be a major constraint for future production in Asia. So, the beef

sector is currently blooming here and with optimization, futuristic planning, efficient use of resources and manpower, and supportive policy regulations, Asia will soon be a leading beef exporter and importer region. Europe In Europe, cattle rearing is mostly pastoral, semiintensive as well as intensive systems (cow-calf-finisher) and there is great variation like, totally extensive or intensive, on permanent or temporary grasslands, fully feeders or breeders or a mix of breeder, feeder or finishing beef cattle. Presently, the EU is the third largest producer of beef, with more than 50% share coming from France (21.20%), Germany (17.80%) and Italy (11.10%) alone (FAPRI, 2012; Vinci, 2022). Despite the potential, EU barely contributes to a meagre 2% in beef exports and 3% in imports, globally. Contrastingly, trade of beef and live animal within the EU countries is quite healthy (Chatellier, 2016). The European beef production is being significantly impacted by the cow herds’ ongoing decline (at a rate of 1.40% till 2021) (Buczinski, 2010; Clarke, 2021). In the future, production of dual-purpose cow breeds will be necessary to meet the rising demand for both milk and meat (Zehetmeier et al., 2012). Also, the local demand for beef will decrease slightly by the year 2025 as other meats coming from poultry, sheep and goat are preferred over beef (FAPRI, 2011). In addition, the growing competition from developing nations, increasing feed and labour costs and concerns over environmental pollution have been a constant threat to European beef industry (Hermansen and Kristensen, 2011; Vinci, 2022). To stabilize the prices, the EU regulates the beef price fluctuations in their domestic markets as and when necessary and trading here is mainly by quota system, either open to all non-EU nations or a small number of specifically selected ones (Agriculture and Rural Development, European Commission, 2023). European cattle are amongst some of the least thermotolerant breeds and primarily adapted to cold climates. But in recent years upsurge in the environmental temperatures and climatic fluctuations, led to a decline in animal performance. Here not only the livestock but even the grasslands are affected due to changing climate and soon might be converted into arable lands for sufficing the growing human demand (Havlík et al., 2012). People are becoming more aware of their health and the effects of livestock production systems on the environment, as well as their carbon footprint (Hocquette and Chatellier, 2011). Animal husbandry here is cleaner, emitting least amount of GHGs as compared to Asiatic or African regions. Data analysis reveals fascinating temperature fluctuations and a drop was observed during 2000–2010. Afterwards an astonishing rise in environmental temperatures (311.78%) was noted during the next decade (2020), to be decreasing by 2025 followed by an increment again in the next five years (Table 1). Over the years, the cattle population here is steadily depleting and a substan- 1101

tial decline was seen between 2000 and 2010 and same declining trend is expected till the 2030s (Table 2). The buffalo population was at its peak till 2020, but there is a projected decrease for the period 2025 to 2030 (Table 3). We witnessed a decrease in land usage by the cattle in last two decades but by 2025–2030s a small rise is anticipated (Table 4). From Table 5, it can be seen that the meadows and pastures in Europe are constantly shrinking and significant reduction was noted in the 2020s and the trend will continue till the 2030s. The share of cattle in Europe’s economy is continuously backsliding and it is expected to continue through the year 2030. Contrastingly, the buffaloes share was maximum till the late 2020s, and thereafter declined throughout the 2030s (Supplementary Table 1–2). The methane emissions from the cattle constantly decreased from 2000 to 2020 and are projected to fall further till the 2030s (Supplementary Table 3), but the GHG emissions from the buffalo were higher till 2020, which will drop by the 2030s (Supplementary Table 4). The production value and revenue generated for beef were maximum till 2010, then we noted a decrease in 2020 for cattle share, but the buffalo production grew significantly during the same period. Thereafter, for cattle a constant growth is expected till the 2030s, whereas for buffalo an initial decline of 16.35% (in 2025), followed by an increase is expected by the 2030s (Supplementary Table 5–6). The impact of climate change in Europe is noteworthy and severe. Here the pastoral and extensive systems are diminishing, affecting the beef sector adversely. In general, the summers are now longer, more intense, and more stressful due to the heat. The local cattle breeds are mainly adapted to cold environment for thousands of years and are now suddenly to acclimatize to the high ambient temperatures. This has resulted in compromised production and animal deaths. The need for introduction of thermotolerant and dual-purpose cattle breeds cannot be stalled any further in the EU. It is also absolutely essential to increase the beef cattle herds to continue and upscale the demands. The beef produced is of high quality and exported in the EU and other countries, generating substantial revenue from the animal husbandry. The environmental impact is very less and the European systems are the cleanest and have least carbon footprint. Increasing the animal numbers (especially those that are adapted to higher ambient temperatures), production intensification, conservation and proper utilization of natural resources is pertinent for future growth and sustainability of the EU beef sector. Oceania Australia and New Zealand are the two major economies of the Oceania region and both nations export more than 60–70% of their beef (MLA, 2022). Previously, there were only pasture-based cow-calf finishing system and rangeland-based cow-calf systems; but in recent years, intensive feedlot beef cattle finishing like the US has gained popularity here (AgriFutures Australia, 2017). Australia

housed more than 11.5 million beef cattle, producing slightly over 2.07 million tonnes of beef (for the years 2016–2017). The beef produced and exported is of high quality and is disease free, increasing its demand all over the world and in 2021 Australia and New Zealand collectively contributed 13 and 7%, respectively, to the global beef exports (MLA, 2017, 2022). Still, the Oceania faces a steep competition for the large Asian beef markets from the emerging south American nations, US, and India (Bell et al., 2011; Hyde et al., 2017). Japan was a major importer of beef from Australia and New Zealand, but in the year 2021, Australian exports decreased by 44% while exports from New Zealand increased by 35%. Although the beef sector is well established, the region’s extensive geographic climatic zones are a constant challenge to the pastoral and rangeland systems and unpredictable rainfall patterns, severe droughts and heat stress is common (Poppi and McLennan, 2010; AgriFutures Australia, 2017). The Oceanic region has all the potential to grow even more, increase productions and exports and become global leaders by 2024 as the demand for beef is ever increasing in the Asiatic continents and all over the world (MLA, 2022; Marel, 2023). During the first two decades of this century, the environmental temperatures drastically increased over the Oceanic region. The forecast for the year 2025 shows a decrease by 18.39% but the temperatures will once again rise by 2030 (Table 1). Both cattle and buffalo population declined here till the 2020s, thereafter the populations are expected to grow stably from 2025 to the 2030s (Table 2 and 3). As the Oceanic regions are sea-bound, expansion of land is difficult, still a 28.57% increase was seen in land use for livestock during 2000 to 2010, a reduction by the 2020s, and then a minimal increase by the 2030s (Table 4). Pasture utilization in the Oceanic nations increased significantly till 2010–2020, following then only small increments are expected in land utilization by the 2030s (Table 5). With the exception of 2020, the Oceanic regions have recorded a stable increase of share in the trade (Supplementary Table 1). From Supplementary Table 4, we can see that the methane emissions from the cattle were low till 2020 and then increased, while for the buffaloes’ emissions in the Oceanic regions gradually increased over time (Supplementary Table 3). Beef production value and the revenue generated soared till the 2010s, followed by slight decline in the late 2020s and are again anticipated to grow steadily till the 2030s (Supplementary Table 5). Although the beef breeds in this region are resistant to heat stress, the climate change not only predisposes them to heat stress but it also has a negative impact on the entire production system. Both Australia and New Zealand supply highest quality, disease free beef to the world. Here the beef cattle population and the amount of land, pasture and meadows utilization are all increasing gradually. Moreover, the well organised production, distribution systems and favourable trading policies give a genuine opportunity to improve the production, exports

and increase the profitability even under the climate change scenario. Although clean meat production is not a constraint presently, soon pressure for cleaner beef might be a challenge for the Oceanic nations. Conclusions and future outlook Consistent with the growth in the human population and urbanization, the demand for animal origin foods will also rise across the globe. We have two major categories of nations, the super developed ones and the developing ones and the gap is constantly shrinking in the two. Demand for meat is stable in the developed worlds, but it keeps soaring continuously in growing economies. The sector uses the land, water, grains, pastures, meadows, grasslands, rangelands, and the feedlot intensive systems for producing the beef, which increase the GHGs and the environmental carbon footprint. Besides, in the context of global warming and climate change, the targeted increase in beef production has to be accelerated and achieved, making it more challenging, stressful, and questionable for its sustainability over plant-based foods. Presently the demand for beef and all types of meats, is rapidly increasing and is expected to grow for the next 2–3 decades, at which point we may need to look for alternative plant-based or lab-grown protein sources. Future implications ● Do we really need to consume animal origin foods for nutrition, or can we search for better sustainable plantbased sources ● The beef sector has to be better organized; production should be intensified and global trade should be standardised and accessible to all nations ● Incorporation and conservation of native cattle, dual purpose, and crossbreeds suitable to local climatic conditions is essential to maintain a steady production and supply ● Cleaner beef production to reduce the methane, carbon dioxide, GHG footprint and overall ecological cost of the sector ● Regional amalgamation of traditional and modern scientific methods for rearing beef cattle ● Conservation of natural grasslands, pastures and rangelands while maintaining balance for the usable land ● Changing food preferences and consumption of white meats etc. Author contributions AKW and SNR conceived and conceptualized the study. AKW and GNB extracted the data and analysed it. TAS and BLK validated the data and prepared the tables. AKW prepared the figures and supplementary material. AKW and SNR drafted the manuscript, which was reviewed and edited by BLK, TAS and GNB. The manuscript was finalized by AKW and GNB, and AKW led the submission and all the correspondence. All the authors have agreed on the final version of the manuscript, and there is no conflict of interest.

📖 中文全文 Chinese Full Text

中文

# 肉牛热应激:气候变化与全球态势——综述

Alok Khemraj Wankar¹♦, Gajendra Namdeo Bhangale², Sandeep Narayanrao Rindhe³, Babu Lal Kumawat⁴, Tawheed Ahmad Shafi⁵

¹兽医学院兽医生理学系,²兽医学院兽医寄生虫学系,³畜产品与技术系,⁴兽医学院产科学系,⁵兽医学院兽医学系,印度马哈拉施特拉邦帕尔巴尼兽医学院,邮编431402;马哈拉施特拉邦动物与渔业科学大学,印度马哈拉施特拉邦那格浦尔

♦通讯作者:wankaralok@gmail.com; alokwankar@mafsu.in

## 摘要

随着人口增长和城市化进程的推进,对动物源性产品的需求将持续增长,尤其是在发展中国家,这一趋势将延续至2050年代。在气候不断变化的背景下,生产需要相应提升和优化。众所周知,热应激会降低所有动物的生产性能、产量、保质期和肉品质。全球范围内,肉牛的饲养管理方式各异,因此对土地和水资源、人力、饲料、生产系统以及环境的影响也存在显著差异。近年来,气候变化、全球变暖和资源枯竭已严重影响生产,热应激如今已成为全球性的制约因素。由于进化分化的原因,热带和温带品种相对更具耐热性,但寒冷地区的肉牛则易受高温环境影响。此外,牛肉生产增加了碳足迹,其生态友好性远低于植物蛋白的生产。因此,本文综合分析了各大洲环境温度的变化及热应激对肉牛的影响。同时,还考察了牛群数量、土地和牧场使用、贸易中的牲畜单位、甲烷排放和牛肉生产总值等因素,以评估上述因素对牛肉行业的综合影响。研究结果表明,在气候变化、自然资源枯竭和温室气体增加的背景下,牛肉生产将面临持续挑战,唯有维持健康的牛群数量和自然资源的最优利用,才能实现这一目标。只有这样,牛肉行业才能在未来的发展中保持高效、可持续和盈利。

**关键词:** 肉牛,热应激,气候变化,可持续生产,碳足迹

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畜牧业为我们提供了33%以上的膳食蛋白质(Rosegrant等,2009),支撑着全球6亿多农民的生计,并雇佣了13亿人(Thornton,2010)。在发展中国家,红肉及其他动物源性食品(AOF)的需求空前高涨。全球人口增长、城市化、经济发展、在线营销与配送、有利的贸易政策以及消费者偏好的转变,共同推动了动物产品需求的增长(OECD,2022)。预计到2025年,全球牛肉消费量将增长0.75%,到2050年将较4.6亿吨翻倍至5.7亿吨(OECD-FAO,2021;OECD,2022;World Consumption of Meat,2023)。1990年至2018年间,人均肉类消费大幅增长,未加工肉类增长88.1%,加工肉制品增长152.8%(Miller等,2022)。研究表明,肉类消费与人均可支配收入、城市化水平和国家财富直接相关,在发展中国家尤为明显(Ritchie等,2017;Miller等,2022)。

动物源性食品需求的增长付出了巨大代价。首先,大部分农业和可耕地被用于种植动物饲料,而非人类食品生产。目前,全球用于种植牛饲料的土地面积是欧盟的七倍。此外,全球90%的大豆被用作动物饲料。其次,肉类生产消耗的能源和自然资源远多于农作物种植。例如,生产1卡路里牛肉蛋白质所需的能量是生产等量玉米蛋白质的75倍,需要54卡路里的化石燃料而非仅2-3卡路里。生产1公斤牛肉需要15500升水,而生产1公斤谷物仅需1600升水(World Consumption of Meat,2023)。最后,牛肉生产系统排放的温室气体(GHG)对环境造成了严重影响。据估计,目前牛占农业部门排放量的77%(直接排放和粪便管理排放),而单胃动物仅占10%(Herreroa等,2013)。预计到2050年代,畜牧业的温室气体排放可能达到1140亿吨二氧化碳当量(GtCO₂-eq),其中73 GtCO₂-eq来自牛(World Consumption of Meat,2023)。

过去二三十年来,气候发生了重大变化且更加不可预测,严重影响了农牧业。持续高温高湿、热浪、太阳耀斑、降雨稀少、干旱等极端气候事件不仅直接影响牲畜福利和生产系统,还影响当年及后续年份的所有粮食资源、粮食安全、可持续性和供应(Lamy等,2012;Rojas-Downing等,2017)。政府间气候变化专门委员会(IPCC)和美国环境保护署(USEPA)等国际机构已预测环境温度将持续上升(USEPA,2016;IPCC,2018)。大量研究证实,热应激导致牛的生产性能和产量下降,造成数十亿美元的经济损失(St-Pierre等,2003;Nardone等,2010;Wankar等,2021;Mishra,2021)。

因此,在气候变化背景下生产肉类是一项具有挑战性的任务;然而,文化偏好、消费者偏好和健康考量也在决定牛肉消费量方面发挥着作用(De Boer等,2014;Graca等,2016;Leroy和Barnard,2020;Malek和Umberger,2021)。尽管如此,据推测肉类行业将持续增长至2030年,并在未来进一步增长70%或更多(FAO,2003;Datar和Betti,2010;Gaughan等,2010),主要受人口增长、现代化、运营优化和清洁增值肉类生产的驱动(Kristensen等,2014;Gokirmakli和Bayram,2017)。

基于上述背景,我们收集了"肉牛热应激"、全球温度变化及其他相关因素(如牛群数量、土地利用、贸易中的牲畜单位、甲烷排放和牛肉产值)的数据。利用Google Scholar、Science Direct、微软科研引擎、PLOS ONE、CORE、ResearchGate、Semantic Scholar、教育研究中心、science.gov、faostat.org等不同搜索引擎、在线平台、国家和国际网站进行数据挖掘。最后,我们整合信息以评估气候变化及相关因素对全球牛肉行业的影响。由于无法同时涵盖所有内容,本研究仅限于牛肉行业,排除了猪肉和鸡肉。

## 动物热应激及高产动物为何更易受热应激影响?

气候对畜牧系统(集约化和粗放化均有)有显著影响,其中粗放或牧养系统受影响更为严重,导致动物生长、繁殖、性能和生产性能下降(Adams等,1998)。动物在特定的生态气候区进化,具备必要的适应性特征,使其在该区域最为舒适和高效。高温、高湿或热浪等极端气候事件损害了它们的体温调节能力,使其无法散发多余的代谢热量,从而易受热应激的有害影响(Baumgard和Rhoads,2012)。

为维持恒温性,动物会立即激活各种稳态反应以减少多余代谢热的产生、储存并促进散热(Wankar等,2014;Herbut等,2021;Vasconcelos等,2020)。动物的品种、生产阶段和妊娠状态、管理方式、地理位置、体表特征以及热可塑性,共同影响动物对热应激的习服、气候适应和适应能力(Robertshaw,1985;Hansen,2004;Brown-Brandl和Jones,2011;Saizi等,2019)。

高产动物已处于最大生产能力的阈值,产生更多的热量,在不利环境条件下热量持续积累(Collier等,2019)。因此,动物产量越高,产生的代谢热越多,为维持恒温性而触发额外的体温调节途径,使动物更易受热应激影响(Ravagnolo和Misztal,2000)。尽管过去3-4十年间的选育计划使产量成倍增长,但也使牲畜更易受气候变化、全球变暖和热应激的影响(Renaudeau等,2012;Collier等,2019)。

## 肉牛的热应激

与集约化奶牛系统不同,肉牛主要在牧场(如饲养场、放牧场)或半集约化设施中饲养,这为它们提供了充足的遮荫、饮水、自由活动和行为表达的机会。然而,这也使它们更容易受到恶劣环境条件的影响(van den Pol-van Dasselaar,2015;Magrin等,2017;Rojas-Downing等,2017)。

肉牛对热应激的反应与奶牛不同,原因是代谢产热较低、品种差异以及它们能够承受相对较高的温湿指数(THI)(St-Pierre等,2003;Nardone等,2010)。这并不意味着它们对热应激免疫,一旦THI超过阈值(78-80,取决于品种和地理位置),所有应激反应都会被激活。采食量会立即下降,尤其在饲料质量较差时更为明显(Mitlöhner等,2002;Van Laer等,2014;Yadav等,2016;Wankar等,2017,2019;Marchesini等,2018;Thornton等,2022)。然而,研究表明,热应激不仅直接降低采食量,还对能量代谢、消化过程和营养吸收产生间接影响(Busby和Loy,1997;Wheelock等,2010;Mahjoubi等,2014;Wankar等,2019)。采食量下降后,出汗、喘息、饮水量增加和行为改变等体温调节过程随即被激活。动物往往偏好在一天中较凉爽的时段活动和采食(Magrin等,2017)。所有这些适应性反应将生产性能量转向维持内稳态,导致肉牛生长速度减慢、平均日增重降低、生产性能下降和恢复期延长(Kadzere等,2002;Ravagnolo等,2002;Nardone等,2010;Marchesini等,2018)。

肉牛的热应激较难量化,因为其涉及多个阶段,即妊娠期、生长期、成年期和育肥期。出生后热应激的影响已有充分记录,但产前暴露及其影响仍不十分明确。胚胎期的热应激已被证明会导致动物生理、行为和代谢发生不可逆的变化,导致出生体重低、生长不良和肉质变差(Foxcroft等,2006;Tao和Dahl,2013;Zhang等,2020)。而在生长期和育肥期,热应激会降低增重、蛋白质沉积、脂肪沉积和胴体产量(Geraert等,1996;Marchesini等,2018;Summer等,2019)。肉质、嫩度、色泽和pH值等其他肉质属性也会发生变化,降低肉价和消费者接受度(Mitlöhner等,2001;Sofos,2008;Johnson等,2015;Sant'Anna等,2019;Abhijith等,2021)。

最近一项研究(Bunning和Wall,2022)报告了热应激肉牛犊牛生长率、平均日胴体增重、胴体重和200日增重均下降,而屠宰年龄和生产成本显著增加。另一项研究则鉴定了热应激肉牛的代谢和分子生物标志物,以及它们的表达如何改变应激反应、调节动物生产性能、生长和产肉量(Kim等,2022)。其他研究人员主要将热应激牲畜生长不良和组成变化归因于DNA、RNA和蛋白质合成下调、蛋白质沉积减少和脂肪积累增加(Jacob,1995;Geraert等,1996;Ronchi等,1999;O'Brien等,2010)。较高的蛋白质周转和糖异生过程中的蛋白水解加剧了热应激牛的蛋白质周转和沉积(Danfar,1994;Temim等,2000;Kuo等,2013;Gao等,2017)。

## 数据分析

数据来源于FAOSTAT网站,时间跨度为1961年至2020年,分析了平均环境温度、牛群数量(牛和水牛)、土地利用、草地和牧场面积、贸易中总牲畜单位(LSU)的份额百分比、甲烷排放和牛肉生产总值的变化,并对最近两个十年(即2000-2010年和2010-2020年)进行了比较。使用微软Windows IBM Excel软件包的预测函数对上述各项指标进行了2025年和2030年的预测。分析结果分别以表1-5和补充表1-6呈现。同样,使用微软Windows IBM Excel软件包绘制了当前水牛和牛群数量、各国肉类和人均牛肉消费量的地图,分别如图1、2、3和4所示。

**表1. 各大洲环境温度(°C)**

| 年份 | 非洲 | 变化率% | 美洲 | 变化率% | 亚洲 | 变化率% | 欧洲 | 变化率% | 大洋洲 | 变化率% | |------|------|---------|------|---------|------|---------|------|---------|--------|---------| | 2000 | 0.78 | — | 1.48 | — | 1.31 | — | 1.27 | — | 0.81 | — | | 2010 | 1.48 | 89.90 | 1.31 | -39.22 | 1.27 | 0.45 | 0.70 | 0.16 | 0.69 | 308.88 | | 2020 | 1.21 | -18.11 | 1.33 | 1.52 | 1.53 | 20.11 | 3.35 | 311.78 | 1.38 | 99.86 | | 2025 | 1.31 | 8.31 | 1.37 | 3.14 | 1.49 | -2.61 | 2.13 | -36.38 | 1.12 | -18.39 | | 2030 | 1.43 | 9.11 | 1.50 | 9.36 | 1.63 | 9.50 | 2.33 | 9.23 | 1.22 | 8.70 |

*作者根据FAOSTAT数据自行计算。*

**表2. 全球牛群数量(百万头)**

| 年份 | 非洲 | 变化率% | 美洲 | 变化率% | 亚洲 | 变化率% | 欧洲 | 变化率% | 大洋洲 | 变化率% | |------|------|---------|------|---------|------|---------|------|---------|--------|---------| | 2000 | 232.23 | — | 460.69 | — | 441.99 | — | 124.44 | — | 37.34 | — | | 2010 | 298.26 | 28.43 | 509.48 | 10.59 | 441.78 | 0.05 | 147.90 | 15.86 | 37.35 | -0.02 | | 2020 | 376.31 | 26.17 | 531.12 | 4.25 | 465.67 | 5.36 | 116.12 | -6.69 | 34.05 | -8.82 | | 2025 | 352.34 | -6.37 | 568.15 | 6.97 | 488.34 | 4.87 | 107.11 | -7.76 | 39.76 | 16.77 | | 2030 | 372.20 | 5.64 | 587.54 | 3.41 | 501.70 | 2.74 | 95.38 | -10.95 | 40.52 | 1.91 |

*作者根据FAOSTAT数据自行计算。*

**表3. 全球水牛数量(百万头)**

| 年份 | 非洲 | 变化率% | 美洲 | 变化率% | 亚洲 | 变化率% | 欧洲 | 变化率% | 大洋洲 | 变化率% | |------|------|---------|------|---------|------|---------|------|---------|--------|---------| | 2000 | 3.53 | — | 1.11 | — | 159.35 | — | 0.23 | — | 0.00015 | — | | 2010 | 3.82 | 8.22 | 1.19 | 7.21 | 188.63 | 18.37 | 0.39 | 69.57 | 0.00013 | -15.38 | | 2020 | 1.35 | -64.66 | 1.92 | 61.34 | 197.38 | 4.64 | 0.48 | 23.08 | 0.000174 | 16.00 | | 2025 | 3.83 | 183.70 | 1.96 | 2.08 | 212.41 | 7.61 | 0.23 | -52.08 | 0.000181 | 4.02 | | 2030 | 4.00 | 4.44 | 2.12 | 8.16 | 222.43 | 4.72 | 0.19 | -17.39 | 0.000191 | 5.52 |

*作者根据FAOSTAT数据自行计算。*

**表4. 牛的牲畜单位土地利用(LSU/公顷)**

| 年份 | 非洲 | 变化率% | 美洲 | 变化率% | 亚洲 | 变化率% | 欧洲 | 变化率% | 大洋洲 | 变化率% | |------|------|---------|------|---------|------|---------|------|---------|--------|---------| | 2000 | 0.11 | — | 0.31 | — | 0.20 | — | 0.21 | — | 0.09 | — | | 2010 | 0.14 | 27.27 | 0.34 | 9.68 | 0.20 | 5.00 | 0.24 | -12.50 | 0.07 | 28.57 | | 2020 | 0.17 | 21.43 | 0.36 | 5.88 | 0.22 | 4.76 | 0.20 | -4.76 | 0.08 | -11.11 | | 2025 | 0.15 | -6.47 | 0.37 | 3.06 | 0.20 | -5.45 | 0.22 | 14.50 | 0.09 | 13.75 | | 2030 | 0.16 | 5.03 | 0.38 | 2.96 | 0.20 | -0.48 | 0.23 | 0.44 | 0.09 | 4.40 |

LSU = 总牲畜单位,ha = 公顷。*作者根据FAOSTAT数据自行计算。*

**表5. 草地和牧场面积(千公顷)**

| 年份 | 非洲 | 变化率% | 美洲 | 变化率% | 亚洲 | 变化率% | 欧洲 | 变化率% | 大洋洲 | 变化率% | |------|------|---------|------|---------|------|---------|------|---------|--------|---------| | 2000 | 21375.48 | — | 44897.58 | — | 56479.38 | — | 66303.17 | — | 114.90 | — | | 2010 | 21668.26 | 1.37 | 29034.41 | -35.33 | 45958.70 | -18.63 | 66442.22 | -0.21 | 171.64 | 15.38 | | 2020 | 22091.69 | 1.95 | 22624.27 | -22.08 | 41354.79 | -10.02 | 63578.61 | -4.11 | 124.23 | 8.12 | | 2025 | 21949.02 | -0.65 | 11317.52 | -49.98 | 34226.57 | -17.24 | 62964.11 | -0.97 | 137.92 | 11.02 | | 2030 | 21976.75 | 0.13 | 4558.15 | -59.72 | 29752.83 | -13.07 | 62228.36 | -1.17 | 147.85 | 7.20 |

ha = 公顷。*作者根据FAOSTAT数据自行计算。*

图1. 全球水牛种群分布(来源:FAOSTAT,2020) 图2. 全球牛群分布(来源:FAOSTAT,2020) 图3. 全球人均肉类消费量(来源:worldpopulationreview.com,2023) 图4. 全球人均牛肉消费量(来源:worldpopulationreview.com,2023)

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## 全球态势与牛肉消费

二战后,随着工业化、现代化、集约化养牛业、食品加工和城市化的推进,全球牛肉消费显著增长。此外,人均收入的提高、消费者意识的增强、饮食偏好和饮食习惯的变化加速了食品行业的转型(OECD,2022)。图3和4展示了当前全球牛肉消费状况及不同国家的人均消费量。全球牛肉行业由四个关键因素驱动:1. 消费增长;2. 有组织的养殖运营和分销;3. 政府政策、贸易和商业;4. 气候变化(Cerles等,2017;Hocquette等,2018)。1990年至2018年间,东南亚和东亚、拉丁美洲、加勒比地区和撒哈拉以南非洲的人均肉类消费(未加工或加工)大幅增长。中国、日本、巴西、南非和墨西哥位居牛肉消费前列。相反,同期(1990-2018年)中欧和东欧、中东、北非、其他发达国家和中亚的牛肉消费下降,俄罗斯、德国、伊朗和法国的降幅在14.0%至47%之间(Miller等,2022)。

尽管如此,发达国家和发展中国家的牛肉消费均在增长,预计到2031年将增长15%(Pohjolainen等,2016)。未来十年,亚太地区牛肉消费将增长10%,但在美国、阿根廷、加拿大、巴西和大洋洲将下降2%至15%(Whitnall和Pitts,2019;OECD-FAO,2022)。牛群减少、饲料质量低或劣质、市场饱和、对环境影响的认识增强、健康问题和动物福利是牛肉消费下降的主要原因(Graca等,2016)。巴西和美国是目前和未来世界主要的牛肉出口国。阿根廷、澳大利亚、印度、巴基斯坦、欧盟、泰国、巴拉圭和土耳其等其他国家也将在全球出口中做出重要贡献。中国、中东和印度尼西亚将是主要的进口国(OECD-FAO,2022)。从态势来看,牛肉需求和产量将持续增长至2031年,但鸡肉和猪肉的增长比例不容忽视,它们是全球最受欢迎的两种肉类。寻找替代性环保蛋白质来源的探索似乎仍很遥远,我们在很大程度上仍依赖动物源性食品。

## 气候变化、当前态势及对牛肉行业的影响

### 美洲

美洲可分为北美洲和南美洲,各自拥有多样化的牛肉生产系统。以犊牛-架子牛-育肥系统为主的饲养场系统在美国和加拿大占主导地位,而肉牛在南美洲(巴西、阿根廷和墨西哥)主要以粗放方式饲养(Galyean等,2011)。气候和环境条件直接影响季风和夏季、放牧季节、生态系统以及为牲畜种植的作物和饲料,进而影响肉牛的市场流通(Polley等,2013;Drouillard,2018;Havstad等,2018)。气候的快速变化将影响饲养场系统,媒介传播疾病将因此重新出现(Short等,2017)。此外,牧养生态系统、牧草生产、土壤退化、水资源短缺及相关的热应激、动物死亡、产量下降和经济损失可能更为明显(Havstad等,2018)。美国约41%的总土地面积用于畜牧业放牧,墨西哥约为60%,利用的是公共或未充分利用的牧场(Peel等,2010)。

从自然资源消耗来看,饲养场方式的牛肉生产似乎最为高效(Capper,2011)。牛肉行业的转型始于20世纪50年代末,过去二三十年来,我们见证了惊人的机械化和专业化程度,出现了更大、更有组织的生产单元。另一个重要驱动力是全球最大企业涉足利润丰厚且不断扩大的食品行业(MacDonald和McBride,2009)。然而,美国和加拿大的牛群数量呈下降趋势,饲养场规模从3400万头减少至3090万头(Galyean等,2011)。相比之下,南美洲的母牛群保持稳定甚至略有增长(Index Mundi,2011)。

由于行业的转型、集约化发展,美国的碳足迹大幅减少,提高了行业的价值和环境友好性(Capper,2011)。全球和南美洲南部对牛肉的需求正在快速增长,而美国国内消费相对稳定,到2030年代可能保持不变(OECD-FAO,2017)。新兴发展中国家正在成为主要出口国,与美国、欧盟或大洋洲国家等传统巨头在牛肉贸易中展开竞争(OECD-FAO,2017)。

2000-2010年间,美洲经历了惊人的191.15%的温升。此后,环境温度预计将持续上升至2023年(表1)。过去二十年间牛群数量略有增长,预计未来十年也将小幅增加(表2)。水牛数量从2010年开始增长,至2020年达到峰值,此后预计到2023年仅会有最小幅度的增长(表3)。土地利用从2000年至2020年有所增加,预计到2030年代的增长趋于停滞(表4)。自20世纪初以来,草地和牧场面积持续减少,预计到2030年代这一趋势将持续(表5)。

从补充表格中可以看出,美洲牛在贸易中的份额正在下降,而甲烷排放则稳步增加(补充表1、3、4)。2000年至2010年间牛肉产值大幅增长(从41,416,764.00增至89,398,768.00千美元),但2010-2020年间出现大幅下降,预计到2025年和2030年回报前景良好(补充表5)。

在发达、有组织的美国牛肉行业中,牛的生产潜力已得到充分发挥。该行业拥有完善的自动化、加工、包装、分销和供应链体系。它既是主要的牛肉进口国也是出口国。主要关注点在于国内外市场已经饱和,以及拉丁美洲国家、澳大利亚、非洲和印度等新参与者的出现。环境温度将随时间推移而上升,维持成熟和正在成熟的耐热肉牛群对于持续生产至关重要。可用土地和牧场萎缩以及贸易份额下降是其他需要认真解决的问题。为实现可持续肉类生产,需要立即采取行动减少温室气体排放和碳足迹。对于南美洲牛肉生产国而言,气候变化要求改善管理、分销系统、牛肉质量、贸易政策,并遏制环境影响,以实现未来的可持续牛肉生产。

### 非洲

非洲地区仍有待充分开发,拥有丰富的自然资源和动物种群。到2050年,非洲人口将从目前的15亿增至2.5亿,成为人口增长最快的大陆之一。过去10至15年来,随着人口增长、人均GDP提高、农牧业实践变化、消费者偏好和需求转变,肉类行业快速增长(AfDB,2017;FAO,2017;World Bank,2017)。如今,非洲牛肉产量占全球总量的6%以上,过去二十年间产量从1159万吨翻倍至1988万吨。牛肉消费也有所增加,南非、博茨瓦纳、纳米比亚、苏丹、尼日利亚、埃及、埃塞俄比亚、肯尼亚、乍得和坦桑尼亚是主要的牛肉生产国、消费国和出口国(Benson,2022;Jenane等,2022)。与美洲、欧洲、澳大利亚或亚洲相比,非洲牛肉行业仍处于起步和发展阶段,但在支持性政府政策和国内外投资的推动下,这里的扩张潜力无限,非洲很快可能成为全球牛肉出口区(African Business,2019)。

非洲牛肉行业的一个主要制约因素是炎热的气候,气候变化的影响在一些脆弱地区更为明显(Maplecroft,2015)。国际气候机构已警告年降雨量将急剧减少,特别是在作为顶级牛肉生产国和出口国的南部非洲地区(Serdeczny等,2016)。此外,到21世纪末,平均气温可能上升2°C或更多,影响农业、水生态系统并使牲畜易受热应激影响(Pereira,2017)。减少温室气体排放以实现可持续、清洁生产仍是牛肉生产单位的另一重大关切(Bogale和Temesgen,2021)。尽管拥有大量耐热肉牛,但如果该地区的政策、管理和贸易得不到改善和优化,非洲将成为全球最大的牛肉进口国而非出口国(Christiaensen,2020;Seleshi,2021)。

地理位置使非洲大陆不可避免地较为温暖,过去二十年间环境温度迅速上升,预计到2030年代这一趋势将持续(表1)。2000-2020年间非洲牛群总数增加,研究结果显示到2025年将出现小幅下降,随后到2030年代略有增加(表2)。与牛类似,非洲水牛数量在2010年前持续增长,到2020年大幅下降64.66%,此后预计到2030年将再次上升(表3)。牛的土地利用在2020年代达到峰值,随后到2025年出现下降,到2030年代略有增加(表4)。2000年至2020年间,非洲用于牧场和草地的面积保持不变,预计到2030年不会有显著变化(表5)。从补充表1和2可以看出,2010年至2020年间牲畜在贸易中的份额大幅下降,牛的份额持续下降至2025年,水牛则不同。预计到2030年代牛和水牛的贸易份额都将进一步下降。过去三十年牛的甲烷排放最高,预计到2025年将略有下降,随后到2030年代再次上升(补充表3)。相比之下,2000-2010年间水牛的温室气体排放较低,到2020年大幅下降,预计到2030年代将急剧上升(补充表4)。2000年至2010年间肉类生产总值显著增加,2020年代略有下降,到2030年代将继续增长(补充表5和6)。

该地区的牛肉行业主要是粗放式、牧养式、无组织的,分销系统也是如此。尽管如此,过去十年非洲牛肉行业的增长令人瞩目。部分非洲国家是欧盟的主要牛肉出口国。牛的平均产量较低,但对热应激有相当强的抵抗力。此外,牛和水牛数量的增长值得肯定。在这里,土地、草地和其他自然资源的利用可以大幅提高以增加生产力。牛肉在贸易中的份额和产生的收入需要系统性地提升。目前该行业没有温室气体排放记录,但必须进行严格监测以减少未来的环境影响。传统上,随着夏季气温升高,越来越多的农民转向饲养山羊、绵羊和肉牛,而非奶牛。由于非洲自然是最温暖的大陆,这一传统需要与现代化和生产集约化相结合,以增加优质肉类的全球分销并促进大陆经济发展。

### 亚洲

随着人口增长、工业化、城市化和文化转型,亚洲牛肉行业目前正在快速扩张。中国、日本、台湾、新加坡和韩国是美国、巴西、阿根廷、澳大利亚和欧洲牛肉的主要进口国(OECD-FAO,2017)。过去二十年间,印度对牛肉和小牛肉的需求快速增长,由于禁止屠宰奶牛,这里主要使用水牛生产牛肉(Landes等,2016)。在亚洲,中国消费和进口牛肉最多(Zhang等,2015)。然而,中国历来是主要的牛肉生产国,但近期牛肉进口的增加对于满足不断增长的牛肉消费、人口爆炸以及大规模农村向城市地区迁移至关重要(中国国家统计局,2016;Wang等,2016)。

泰国、马来西亚、印度尼西亚、越南、菲律宾、缅甸、文莱、老挝、柬埔寨和东南亚国家联盟(东盟)等其他亚洲国家,由于劳动力仍然廉价且经济正在增长,将成为全球主要的牛肉消费和生产市场(Bunmee等,2018;MLA,2020)。预计亚洲肉类行业将以5.10%的速度增长,仅牛肉市场到2026年将产生超过333.825亿美元的收入,包装肉类行业还将额外产生573.605亿美元(Research and Markets,2023)。新冠疫情和其他质量控制问题之后,该地区牛肉行业的复苏缓慢,阻碍了向发达国家的出口。尽管中国、巴基斯坦和土耳其等国家的牛肉消费显著增加,但出口仍然很低,大多数亚洲国家是主要的牛肉进口国(Global Trade Magazine,2020)。

在气候变化背景下,牛肉生产本身就是一项挑战,亚洲动物源性食品的供需之间出现了失衡。亚洲畜牧业面临环境温度持续上升、频繁干旱和降雨不稳定的威胁。夏季期间,整个北部亚洲的环境温度上升已经显而易见。与此同时,中国、印度、印度尼西亚、日本、菲律宾和巴基斯坦的降雨量急剧减少(Cruz等,2007)。恶劣的气候条件、营养不良……

粗放至半集约化的畜牧业管理使亚洲成为全球温室气体排放的主要来源之一。未来,在气候变化情景下实现可持续的牛肉生产,以满足人口需求并出口剩余肉类,将是一项重大挑战。表1显示,亚洲的环境温度在2010年前迅速上升,并持续增长至2020年。此后,预计2025年将有所下降,随后在2023年再次上升(表1)。牛和水牛的数量增长较为缓慢,直至2020年,预计这一缓慢增长趋势将持续至2030年代(表2和表3)。牛的用地量在2020年代前保持最优水平,此后预计将在2025年和2030年急剧下降(表4)。同样,自2010年以来,亚洲的草地和牧场总面积显著减少,我们的预测显示这一趋势将持续至2030年(表5)。尽管亚洲拥有全球最大的牛和水牛种群,但其贸易份额目前较小,过去20年间持续萎缩,并预计将持续下降至2030年(补充表1-2)。自20世纪初以来,肉牛和水牛的甲烷排放量持续增加,预计到2030年代末将进一步增长(补充表3-4)。水牛肉生产带来的收入在2020年代持续增长,但牛肉生产收入在2020年有所下降(补充表5-6)。牛肉生产在2025-2030年间预计呈积极趋势,但水牛肉产量将在2025年略有下降,随后在2030年代再次增长(补充表5-6)。

亚洲拥有全球最多的人口、牛和水牛。随着整个地区人口、城市化和经济的快速增长,对动物性食品的需求也大幅增加。该地区的牲畜产量从平均水平到优良水平不等,且适应于炎热温带至热带环境,使其对热应激具有耐受性。这里的主要限制因素包括饲料质量差、管理粗放、放牧或粗放饲养方式以及长期严酷的环境条件。肉牛常患有传染病或人畜共患病,这使得向发达国家出口牛肉变得不可能。此外,人类与牲畜在土地和水资源等自然资源方面存在直接冲突。中国等国家是全球牛肉进口国,尽管它们也生产牛肉,但产量不足以满足需求。尽管面临气候变化,亚洲的肉牛和水牛种群似乎仍在增长。然而,土地和自然资源的使用可以得到严格优化,以兼顾人类和牲畜的需求。白肉的普及已大幅减少了牛在贸易中的份额,但牛肉生产的价值和经济收益潜力正在上升,仍需进一步探索。牛肉生产系统中温室气体排放的稳步增长将是亚洲未来生产的主要制约因素。因此,亚洲的牛肉产业目前正在蓬勃发展,通过优化、前瞻性规划、高效利用资源和人力以及支持性政策法规,亚洲将很快成为领先的牛肉出口和进口地区。

欧洲

在欧洲,牛的饲养方式主要为放牧、半集约化以及集约化体系(母牛-犊牛-育肥牛),且存在较大差异,包括完全粗放或集约化饲养、在永久或临时草地上饲养、完全饲养者或繁育者,或繁育者、饲养者与育肥肉牛的混合模式。目前,欧盟是全球第三大牛肉生产国,其中超过50%的份额来自法国(21.20%)、德国(17.80%)和意大利(11.10%)(FAPRI,2012;Vinci,2022)。尽管具备潜力,欧盟在全球牛肉出口和进口中的贡献分别仅为微不足道的2%和3%。相反,欧盟国家之间的牛肉和活畜贸易相当活跃(Chatellier,2016)。欧洲牛肉生产正受到牛群持续减少的显著影响(截至2021年,减少率为1.40%)(Buczinski,2010;Clarke,2021)。未来,为同时满足日益增长的牛奶和肉类需求,生产兼用型牛品种将是必要的(Zehetmeier等,2012)。

此外,到2025年,由于禽肉、羊肉和山羊肉等其他肉类更受青睐,当地对牛肉的需求将略有下降(FAPRI,2011)。同时,来自发展中国家的竞争加剧、饲料和劳动力成本上升以及对环境污染的担忧,一直是欧洲牛肉产业的持续威胁(Hermansen和Kristensen,2011;Vinci,2022)。为稳定价格,欧盟在必要时调控其国内市场的牛肉价格波动,贸易主要通过配额制度进行,该制度对所有非欧盟国家开放,或仅针对少数特定国家(欧盟委员会农业与农村发展总司,2023)。

欧洲牛种属于耐热性最差的品种之一,主要适应寒冷气候。但近年来,环境温度的上升和气候波动导致动物生产性能下降。在这里,不仅牲畜受到气候变化的影响,草地也受到影响,并可能很快被转化为耕地,以满足人类日益增长的需求(Havlík等,2012)。人们越来越关注自身健康以及牲畜生产系统对环境的影响,包括其碳足迹(Hocquette和Chatellier,2011)。这里的畜牧业更为清洁,与亚洲或非洲地区相比,温室气体排放量最低。

数据分析揭示了有趣的温度波动,2000-2010年间温度有所下降。随后,在下一个十年(2020年)环境温度出现了惊人的上升(311.78%),预计到2025年将下降,随后五年再次上升(表1)。多年来,这里的牛群数量持续减少,2000年至2010年间出现了大幅下降,预计这一下降趋势将持续至2030年代(表2)。水牛数量在2020年前达到峰值,但预计2025年至2030年间将有所减少(表3)。过去二十年间,牛的用地量有所减少,但预计到2025-2030年代将略有增加(表4)。从表5可以看出,欧洲的草地和牧场正在持续萎缩,2020年代出现了显著减少,这一趋势将持续至2030年代。牛在欧洲经济中的份额持续下滑,预计将持续至2030年。相反,水牛的份额在2020年代末达到最高,此后在整个2030年代持续下降(补充表1-2)。牛的甲烷排放量从2000年到2020年持续下降,预计到2030年代将进一步减少(补充表3),但水牛的温室气体排放量在2020年前较高,到2030年代将有所下降(补充表4)。牛肉的生产价值和收入在2010年前达到最高,随后我们注意到2020年牛的份额有所下降,但同期水牛的生产显著增长。此后,预计牛的生产将持续增长至2030年代,而水牛的生产预计在2025年最初下降16.35%,随后在2030年代有所增长(补充表5-6)。

欧洲受到气候变化的影响显著且严重。这里的放牧和粗放体系正在萎缩,对牛肉产业产生了不利影响。总体而言,夏季现在更长、更炎热,热应激更为严重。当地牛种数千年来主要适应寒冷环境,现在突然需要适应较高的环境温度。这导致了生产性能下降和动物死亡。在欧盟引入耐热和兼用型牛品种的需求已刻不容缓。同时,增加肉牛群数量以维持和扩大需求也绝对必要。所生产的牛肉质量高,出口到欧盟及其他国家,从畜牧业中获得了可观收入。环境影响很小,欧洲体系最为清洁,碳足迹最低。增加动物数量(特别是那些适应较高环境温度的动物)、生产集约化、保护和合理利用自然资源,对于欧盟牛肉产业未来的增长和可持续性至关重要。

大洋洲

澳大利亚和新西兰是大洋洲地区的两大经济体,两国均出口其60-70%以上的牛肉(MLA,2022)。此前,这里仅有基于牧场的母牛-犊牛育肥体系和基于牧场的母牛-犊牛体系;但近年来,类似美国的集约化饲养场肉牛育肥方式在此流行起来(AgriFutures Australia,2017)。澳大利亚饲养了超过1150万头肉牛,生产略高于207万吨牛肉(2016-2017年)。所生产和出口的牛肉质量高且无疾病,增加了全球需求,2021年澳大利亚和新西兰分别贡献了全球牛肉出口的13%和7%(MLA,2017,2022)。尽管如此,大洋洲在亚洲大型牛肉市场上面临来自新兴南美国家、美国和印度的激烈竞争(Bell等,2011;Hyde等,2017)。日本曾是澳大利亚和新西兰牛肉的主要进口国,但2021年,澳大利亚出口下降了44%,而新西兰出口增长了35%。

尽管牛肉产业已十分成熟,但该地区广阔的地理气候区对放牧和牧场体系构成了持续挑战,降雨模式不可预测、严重干旱和热应激十分常见(Poppi和McLennan,2010;AgriFutures Australia,2017)。大洋洲地区具备进一步增长的潜力,能够增加生产和出口,并在2024年成为全球领导者,因为亚洲大陆及全球对牛肉的需求持续增长(MLA,2022;Marel,2030)。

在本世纪的前二十年间,大洋洲地区的环境温度急剧上升。2025年的预测显示温度将下降18.39%,但到2030年将再次上升(表1)。牛和水牛的数量在此前持续下降至2020年代,此后预计种群数量将从2025年至2030年代稳定增长(表2和表3)。由于大洋洲地区四面环海,土地扩张困难,但在2000年至2010年间,牲畜用地仍增加了28.57%,到2020年代有所减少,随后到2030年代略有增加(表4)。大洋洲国家的牧场利用率在2010-2020年间显著增加,此后预计到2030年代土地利用率仅有小幅增长(表5)。除2020年外,大洋洲地区的贸易份额一直保持稳定增长(补充表1)。从补充表4可以看出,牛的甲烷排放量在2020年前较低,随后有所增加,而大洋洲地区水牛的排放量则随时间逐渐增加(补充表3)。牛肉生产价值和收入在2010年代前飙升,随后在2020年代末略有下降,预计到2030年代将再次稳步增长(补充表5)。

尽管该地区的肉牛品种具有抗热应激能力,但气候变化不仅使它们易受热应激影响,还对整个生产系统产生负面影响。澳大利亚和新西兰向全球供应最高质量、无疾病的牛肉。这里的肉牛数量以及土地、草地和牧场的利用率均在逐步增加。此外,良好的生产、分销体系和有利的贸易政策为在气候变化情景下提高生产、出口和盈利能力提供了真正的机会。尽管清洁肉类生产目前尚不构成制约,但很快对更清洁牛肉的需求可能成为大洋洲国家面临的挑战。

结论与未来展望

随着人口增长和城市化进程,全球对动物源性食品的需求也将上升。我们主要有两类国家:超级发达国家和发展中国家,两者之间的差距正在不断缩小。发达国家的肉类需求稳定,而发展中经济体的需求则持续飙升。该产业利用土地、水、谷物、草地、牧场、草原、牧场和集约化饲养系统生产牛肉,这增加了温室气体排放和环境的碳足迹。此外,在全球变暖和气候变化的背景下,必须加速实现牛肉生产的目标增长,这使其比植物性食品更具挑战性、压力更大,且可持续性受到质疑。

目前,对所有类型肉类的需求正在快速增长,预计在未来2-3个十年内将持续增长,届时我们可能需要寻找替代性的植物性或实验室培育蛋白质来源。

未来启示

● 我们是否真的需要消费动物源性食品来获取营养,还是可以找到更好的可持续植物性来源? ● 牛肉产业必须更好地组织;生产应实现集约化,全球贸易应标准化并向所有国家开放。 ● 引入和保护适应当地气候条件的本地牛种、兼用型牛和杂交牛,对于维持稳定的生产和供应至关重要。 ● 更清洁的牛肉生产,以减少甲烷、二氧化碳、温室气体足迹以及该产业的整体生态成本。 ● 区域性地融合传统和现代科学方法饲养肉牛。 ● 保护天然草地、牧场和草场,同时保持可用土地的平衡。 ● 食物偏好的变化以及白肉等的消费。

作者贡献

AKW和SNR构思并概念化了本研究。AKW和GNB提取并分析了数据。TAS和BLK验证了数据并制作了表格。AKW制作了图表和补充材料。AKW和SNR起草了手稿,由BLK、TAS和GNB审阅和编辑。手稿由AKW和GNB定稿,AKW负责投稿和所有通信。所有作者均同意手稿的最终版本,且无利益冲突。